Kerriodoxa elegans
J.Dransf.
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
EN · En dangercritères B1ab(iii)+2ab(iii)?Inconnue- Évaluation
- 2025 · v3.1
- Altitude
- 100 – 300 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The overall population size and current population trend are not known, though there are only two known subpopulations. It is described as being gregarious, extremely common and reproducing at Khao Phra Thaeo Non-Hunting Area on Phuket (Middleton and Henderson pers. comm.), where it is the most dominant element in the forest undergrowth (Barfod and Dransfield 2013). It is particularly abundant in a valley on the western side of the park (Elixhauser et al. 2003). Its relative abundance in Khao Sok National Park is unknown.
Menaces identifiées(8 menaces classées CMP-IUCN)
1_1Housing & urban areasOngoing1_3Tourism & recreation areasOngoing2_1_2Small-holder farmingOngoing2_2_1Small-holder plantationsOngoing3_2Mining & quarryingOngoing5_3_5Motivation Unknown/UnrecordedOngoing6_1Recreational activitiesOngoing9_3_2Soil erosion, sedimentationOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Both of the known subpopulations occur within protected areas. The Khao Phra Thaew Non-Hunting Area (KPT) on Phuket, where this species is abundant, comprises the only remaining rainforest on the island and covers an area of approximately 2,230 hectares. According to the definitions by the Thai Ministry of Natural Resources and Environment, Non-hunting areas are usually of limited extent and protection is targeting specific species, thus collection of plants and herbs is usually permitted. The remaining natural forests on the island have been lost due to large-scale mining, rubber plantations and the rapid expansion of tourism on the island (Elixhauser et al. 2013). KPT is surrounded by villages and plantations and has been heavily encroached upon, with almost 25% of the parks total area thought to be taken up by orchards (Elixhauser et al. 2013). Heavy levels of tourism within the park may also threaten this species and its habitat (Tovaranonte et al. 2015).
Khao Sok National Park is a much larger protected area of over 74,500 hectares and is under less pressure from human activities. However, threats from logging, plantations, soil erosion and unregulated tourism have still been identified (Khao Sok National Park 2023). Given this species occurs at lower elevations, it is likely to have increased vulnerability as generally lowland areas are the first to be affected by human activities. Tree cover loss around the edges of Khao Phra Thaeo Non-Hunting Area has been recorded on Global Forest Watch (2023) and also within Khao Sok National Park. This tree cover loss is assumed to largely be a consequence of the human activities noted here.
Khao Sok National Park is a much larger protected area of over 74,500 hectares and is under less pressure from human activities. However, threats from logging, plantations, soil erosion and unregulated tourism have still been identified (Khao Sok National Park 2023). Given this species occurs at lower elevations, it is likely to have increased vulnerability as generally lowland areas are the first to be affected by human activities. Tree cover loss around the edges of Khao Phra Thaeo Non-Hunting Area has been recorded on Global Forest Watch (2023) and also within Khao Sok National Park. This tree cover loss is assumed to largely be a consequence of the human activities noted here.
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species is only known from protected areas: Khao Sok National Park and Khao Phra Thaew Non-Hunting Area (UNEP-WCMC and IUCN 2023). There are 36 ex situ collections held by botanic gardens worldwide (BGCI 2023), meaning this species is well represented in ex situ conservation.
Actions de conservation (1)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management
Stress écologiques (24)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_3Indirect ecosystem effects2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance
Usage & commerce (1)Use & Trade — IUCNExpert
13Pets/display animals, horticultureinternational
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Indomalayan
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Tree - small
Références bibliographiques (16)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).
- POWO. 2023. Plants of the World Online. Facilitated by the Royal Botanic Gardens, Kew. Available at: <a href="http://powo.science.kew.org/">http://powo.science.kew.org/</a>. (Accessed: 2023).
- GBIF. 2023. Global Biodiversity Information Facility. Available at: <a href="https://www.gbif.org/">https://www.gbif.org/</a>.
- Khao Sok National Park. 2023. Facts: Threats and Conservation in Khao Sok National Park. Available at: <a href="https://www.khaosok.com/facts/">https://www.khaosok.com/facts/</a>.
- BGCI. 2023. 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: 2023).
- UNEP-WCMC and IUCN. 2023. 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: 2023).
- Global Forest Watch. 2023. Interactive Forest Change Mapping Tool. Available at: <a href="http://www.globalforestwatch.org/">http://www.globalforestwatch.org/</a>.
- Tovaranonte, J., Blach-Overgaard, A., Pongsattayapipat, R., Svenning, J-C. and Barfod, A.S. 2015. Distribution and diversity of palms in a tropical biodiversity hotspot (Thailand) assessed by species distribution modeling. <i>Nordic Journal of Botany</i> 33: 214–224.
- Barfod, A.S. and Dransfield, J. 2013. Arecaceae. In: T. Santisuk and K. Larsen (eds), <i>Flora of Thailand Volume 11 Part 3</i>, pp. 323–498. The Forest Herbarium, Bangkok.
- Smith, G. and Price, J. 2013. <i>Kerriodoxa elegans</i>. Available at: <a href="http://www.pacsoa.org.au/wiki/Kerriodoxa_elegans">http://www.pacsoa.org.au/wiki/Kerriodoxa_elegans</a>.
- 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: V. Smith and L. Penev (eds) e-Infrastructures for data publishing in biodiversity science. <i>Zookeys</i> 150: 117–126.
- Henderson, A. 2009. <i>Field Guide to the Palms of Southern Asia</i>. Princeton University Press, Princeton, New Jersey.
- LLIFLE. 2005. <i>Kerriodoxa elegans</i> J.Dransf. Available at: <a href="http://www.llifle.net/Encyclopedia/PALMS_AND_CYCADS/Family/Arecaceae/28505/Kerriodoxa_elegans">http://www.llifle.net/Encyclopedia/PALMS_AND_CYCADS/Family/Arecaceae/28505/Kerriodoxa_elegans</a>.
- Elixhauser, S., Snelder, D., Minter, T. and Persoon, G. 2003. The Sierra Madre Mountain Range: Global relevance, local realities. Chapter 25: Ecotourism in the Northern Sierra Madre Natural Park: Potentials and Realities. In: J. van der Ploeg, E.C. Bernardo and A.B. Masipiquena (eds), 4th Regional Conference on Environment and Development. Isabela State University, Cabagan.
- Hodel, D. 1998. <i>The palms and cycads of Thailand</i>. Allen Press, Lawrence, Kansas.
- Dransfield, J. 1983. <i>Kerriodoxa</i>, a new coryphoid palm genus from Thailand. <i>Principes</i> 21(1): 3-11.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Barker, A.
evaluator
Barfod, A.
institutions
Royal Botanic Gardens, Kew
Barker, A. 2025. Kerriodoxa elegans. The IUCN Red List of Threatened Species 2025: e.T191348A1976694. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.