Roystonea princeps
(Becc.) Burret
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
EN · En dangercritères A2c↘Décroissante- Évaluation
- 2025 · v3.1
- Altitude
- 0 – 150 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Most of the individuals of this species occur within the Negril or Black River Morass regions of western Jamaica; other localities where this species have been recorded typically only contain a few isolated individuals and are therefore assumed to comprise a negligible proportion of the total global population. The Black River Morass covers an area of approximately 57 km2 while the smaller Negril Morass covers an area of approximately 20 km2. Within these areas, Roystonea princeps is restricted to the highly threatened swamp forest habitat, within which it is locally abundant and a dominant canopy-forming pioneer species. This habitat formerly covered large areas of the morass regions, but is now restricted to small, isolated, and severely threatened fragments. Swamp forest has experienced serious declines; 80% of this habitat has been estimated to have been lost in the larger Black River Morass over the past 80 years (Ramsar 2021). Loss of swamp forest has not been quantified in the smaller Negril morass but given the similarity in land-use history, the rate of decline is suspected to be similar. As R. princeps is restricted to swamp forests, yet is generally uniformly abundant within them, the rate of population reduction is inferred to be the same as the rate of habitat reduction. Given that the generation length of R. princeps is estimated at 19–40 years (see Habitat and Ecology section for details), this corresponds to a 57–80% decline in the past 3 generations (57–120 years), if it is assumed that the population was stable between 1824–1944. Thus, across the entire range a population reduction of 42–80% is suspected over the past 3 generations, where the lower estimate assumes that no decline has occurred outside of the Black River region, where data on habitat trends is lacking, while the upper estimate assumes that the rate of habitat reduction in the Negril Morass has been the same as has been calculated for the Black River Morass. We consider the best estimate for the rate of population reduction to be 57–80%, given the likelihood that habitat reduction rates in the Negril Morass have been as high or higher than in the larger Black River Morass.
Menaces identifiées(11 menaces classées CMP-IUCN)
2_1_1Shifting agricultureUnknownUnknownOngoing2_1_2Small-holder farmingUnknownUnknownOngoing2_3_2Small-holder grazing, ranching or farmingUnknownMinority (<50%)Ongoing5_2_2Unintentional effects (species is not the target)UnknownUnknownOngoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]UnknownWhole (>90%)Ongoing5_4_3Unintentional effects: (subsistence/small scale) [harvest]UnknownUnknownOngoing7_1_1Increase in fire frequency/intensityUnknownUnknownOngoing7_2_8Abstraction of ground water (unknown use)UnknownUnknownOngoing8_1_1Unspecified speciesUnknownUnknownOngoing8_1_2Named speciesUnknownUnknownOngoing
+ 1 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
This species is a characteristic and dominant species of the swamp forests of the Great Morass in western Jamaica. This highly threatened habitat once covered large areas of the Morass but is now restricted to a few small, isolated fragments. These remaining fragments are severely threatened by encroachment for agriculture and settlements, wildfires set to clear land, woodcutting, harvesting of timber and other forest and wetland products (e.g. palm leaves and shrimp), livestock grazing at the margins, and the effects of invasive species (Prospere et al. 2016, Birdlife International 2024a). It is likely that these threats are acting in nearly all remaining patches of swamp forest, and that most are already degraded to some extent; one study found signs of anthropogenic disturbance in all of ten forest fragments surveyed, with woodcutting being the most prevalent type of disturbance (Prospere et al. 2016). Alpinia nigra is a particularly problematic invasive species in the Great Morass; it is now a dominant species in the upper Black River morass (Prospere et al. 2016, Ramsar 2021). This species can completely overrun patches of swamp forest, displacing and preventing the regeneration of native flora (Prospere et al. 2016, Ramsar 2021). Prospere et al. (2016) noted that controlling the spread of A. nigra and restricting anthropogenic disturbance will be critical for ensuring that remaining patches of swamp forest are conserved. The Negril Morass is adjacent to major tourist destinations and is threatened by associated residential and commercial development (Birdlife International 2024b). Changes to the hydrological regime of the Negril Morass as a result of the construction of canals has caused wetlands to dry out, increased the risk of wildfires set to clear land, and encouraged further encroachment, particularly of tourism infrastructure on the western margin (Birdlife International 2024b).
Habitats préférentiels (classification IUCN)
1_8Forest - Subtropical/Tropical Swamp★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species occurs within the Black River Lower Morass Ramsar Site and the Royal Palm Reserve near Negril. It is held in at least five ex situ conservation collections (BGCI 2024).
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management2_2Invasive/problematic species control
Stress écologiques (18)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_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_1Species mortality2_1Species mortality2_1Species mortality
Priorités de recherche (3)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Neotropical
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Tree - largeTree - small
Références bibliographiques (9)Sources scientifiques de l'évaluation IUCNExpert
- 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).
- BirdLife International. 2024. Important Bird Area factsheet: Black River Great Morass. Available at: <a href="https://datazone.birdlife.org/site/factsheet/black-river-great-morass-iba-jamaica">https://datazone.birdlife.org/site/factsheet/black-river-great-morass-iba-jamaica</a>.
- 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).
- Birdlife International. 2024. Important Bird Area factsheet: Negril. Available at: <a href="https://datazone.birdlife.org/site/factsheet/negril-iba-jamaica/text">https://datazone.birdlife.org/site/factsheet/negril-iba-jamaica/text</a>.
- Ramsar. 2021. Black River Lower Morass, Jamaica. Available at: <a href="https://rsis.ramsar.org/RISapp/files/RISrep/JM919RIS_2111_en.pdf">https://rsis.ramsar.org/RISapp/files/RISrep/JM919RIS_2111_en.pdf</a>.
- Fung, H.C. and Waples, R.S. 2017. Performance of IUCN proxies for generation length. <i>Conservation Biology</i> 31(4): 883-893.
- Prospere, K., McLaren, K.P. and Wilson, B. 2016. Characterizing the Status (Disturbed, Hybrid or Novel) of Swamp Forest Fragments in a Caribbean Ramsar Wetland: The Impact of Anthropogenic Degradation and Invasive Plant Species. <i>Environment Management</i> 58: 655-681.
- Connor, K.F. 2002. <i>Roystonea borinquena</i> O.F. Cook. In: Vozzo, J.A. (ed.), <i>Tropical Tree Seed Manual. Agric. Handbook 721</i>, pp. 695-697. Department of Agriculture, Forest Service, Washington, DC: US.
- Zona, S. 1996. Roystonea (Arecaceae: Arecoideae). <i>Flora Neotropica</i> 71: 1-35.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Svahnström, V.
contributor
Bevan, H. & Zona, S.
evaluator
Balick, M., Mosquera Medrano, M.A.M. & Campbell, K.C.St.E.
facilitators
Barker, A.
institutions
Royal Botanic Gardens, Kew
Svahnström, V. 2025. Roystonea princeps. The IUCN Red List of Threatened Species 2025: e.T38689A256809783. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.
Consulter sur les bases externes
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (1)— redirigent vers cette page
- Oreodoxa princepsBecc.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).