Crinum thaianum
J.Schulze
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
EN · En dangercritères B1ab(ii,iii,iv,v)+2ab(ii,iii,iv,v)↘Décroissante- Évaluation
- 2011 · v3.1
- Altitude
- 50 – 150 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Menaces identifiées(9 menaces classées CMP-IUCN)
11_4Storms & floodingOngoing2_1_3Agro-industry farmingOngoing2_2_1Small-holder plantationsOngoing2_2_2Agro-industry plantationsOngoing3_2Mining & quarryingOngoing5_2_1Intentional use (species is the target)Ongoing7_2_3Abstraction of surface water (agricultural use)Ongoing7_2_9Small damsOngoing9_3_2Soil erosion, sedimentationOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
A major threat to the habitat of this species is the dredging of rivers and streams for removal of sediment and rock for construction and land reclamation purposes (this has also increased the speed of water flow in habitats of the Water Onion, where entire subpopulations have been dislodged). Also threatened by diversion of the rivers and streams for agricultural purposes. There is also extensive changes in the ecology of the streams and rivers due to land use changes in the adjoining areas (e.g., clearing of forest for agriculture) and resultant land-based erosion and river bank erosion (the substrate of the Nakha and Kuraburi rivers has changed drastically over the past 10 years, due to erosion. The muddy substrate that facilitates the growth of Water Onion has been replaced by pebbles, rock and gravel, in large areas of these rivers. Collection of bulbs from the wild for sale to the international trade for home fish ponds and aquaria is also a threat which needs closer monitoring.
Habitats préférentiels (classification IUCN)
5_1Wetlands (inland) - Permanent Rivers/Streams/Creeks (includes waterfalls)★5_2Wetlands (inland) - Seasonal/Intermittent/Irregular Rivers/Streams/Creeks
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Actions de conservation (8)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management2_3Habitat & natural process restoration3_1_1Harvest management3_1_2Trade management3_3_1Reintroduction3_4_1Captive breeding/artificial propagation4_2Training4_3Awareness & communications
Stress écologiques (18)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 degradation2_1Species mortality2_1Species mortality2_2Species disturbance
Usage & commerce (3)Use & Trade — IUCNExpert
13Pets/display animals, horticultureinternational16Establishing ex-situ production *3Medicine - human & veterinarynationalsubsistance
Priorités de recherche (7)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_4Harvest, use & livelihoods1_5Threats3_1Population trends3_2Harvest level trends3_3Trade trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (2)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2011. IUCN Red List of Threatened Species (ver. 2011.2). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 10 November 2011).
- Leeratiwong, C. and Jornead, S. 2005. Species diversity of vascular plants in Si Phang-nga National Park, Phangnga Province. <i>J.Songklanakarin Journal of Science and Technology</i> 27(4): 769-787.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
Soonthornnawaphat, S., Bambaradeniya, C. & Sukpong, P. 2011. Crinum thaianum. The IUCN Red List of Threatened Species 2011: e.T201627A9154955. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.