Arisaema maxwellii
Hett. & Gusman
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
VU · Vulnérablecritères B1ab(iii)↘Décroissante- Évaluation
- 2013 · v3.1
- Altitude
- 100 – 1000 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
There are no population data available for this species.
Menaces identifiées(10 menaces classées CMP-IUCN)
5_2_1Intentional use (species is the target)UnknownUnknownOngoing1_1Housing & urban areasOngoing1_3Tourism & recreation areasOngoing2_1_1Shifting agricultureOngoing2_1_2Small-holder farmingOngoing2_1_3Agro-industry farmingOngoing5_3_5Motivation Unknown/UnrecordedOngoing6_1Recreational activitiesOngoing7_1_3Trend Unknown/UnrecordedOngoing8_1_1Unspecified speciesOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Conversion of forest for agriculture and settlement, as well as frequent fires, are prevalent threats to the Central Indochina dry forests and Kayah-Karen montane rain forests ecoregions, where this species is found. In areas such as northern Thailand, where previously nomadic tribal peoples have been settled, pressure exists to convert forest into more intensive agricultural land devoted to cash crops such as cabbage, coffee, and lychee. Opium replacement efforts have compelled local people to grow alternative crops that need more cultivated land area and higher pesticide inputs. The land needs of an increasing population have forced itinerant farmers to reduce the cycle of cultivation-fallow periods and have pushed them deeper into the forest and into more marginal areas.
About a third of the Kayah-Karen mountain rain forests ecoregion has been cleared or degraded, however 28 protected areas cover almost 20% of its area (23,500 km2). However, many of these protected areas are threatened. Several settlements have been built within the boundaries of the Doi Suthep-Pui National Park (where it has been collected) since it was designated a national park. Agricultural intensification, introduction of exotic plant species, urban development, recreation and tourism, and selective logging are threats facing this national park, many of which are compounded by the site's proximity to Chiang Mai city. The vegetation has been greatly modified at mid-elevations, where large areas of hill evergreen forest have been cleared for shifting cultivation; consequently this altitudinal band now supports a mosaic of grassland, scrub and secondary growth (BirdLife 2008). Pha Ngam Cave in Chae Son National Park, where the type collection of this species was collected, is regularly visited by tourists and trampling and plant collecting may be problems there.
There has been a recent increase in interest for cultivating Arisaema species (D. Roberts pers. comm. 2008) and harvesting from the wild may be a threat for this species.
About a third of the Kayah-Karen mountain rain forests ecoregion has been cleared or degraded, however 28 protected areas cover almost 20% of its area (23,500 km2). However, many of these protected areas are threatened. Several settlements have been built within the boundaries of the Doi Suthep-Pui National Park (where it has been collected) since it was designated a national park. Agricultural intensification, introduction of exotic plant species, urban development, recreation and tourism, and selective logging are threats facing this national park, many of which are compounded by the site's proximity to Chiang Mai city. The vegetation has been greatly modified at mid-elevations, where large areas of hill evergreen forest have been cleared for shifting cultivation; consequently this altitudinal band now supports a mosaic of grassland, scrub and secondary growth (BirdLife 2008). Pha Ngam Cave in Chae Son National Park, where the type collection of this species was collected, is regularly visited by tourists and trampling and plant collecting may be problems there.
There has been a recent increase in interest for cultivating Arisaema species (D. Roberts pers. comm. 2008) and harvesting from the wild may be a threat for this species.
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland6Rocky areas (eg. inland cliffs, mountain peaks)
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Subpopulations of this species are known from two national parks in Thailand, namely Doi Suthep-Pui and Chae Son (Jae Sawn), which cover 280 and 780 km2 respectively. The type collection was made from Chae Son in 1996. Although threats within the protected areas are known to exist, at least 1,000 km2 of its habitat is under some form of protection. The species is cultivated in the Leiden Botanical Garden. No seed is currently stored in the Millennium Seed Bank, UK.
Actions de conservation (1)Conservation Actions Classification Scheme — IUCNExpert
3_4_2Genome resource bank
Stress écologiques (16)Stresses Classification — IUCNExpert
1_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_2Species disturbance2_2Species disturbance
Priorités de recherche (2)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Indomalayan
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or HerbGeophyte
Références bibliographiques (8)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 12 June 2013).
- WCSP. 2008. World Checklist of Selected Plant Families. Facilitated by the Royal Botanic Gardens, Kew. Available at: <a href="http://www.kew.org/wcsp/monocots/">http://www.kew.org/wcsp/monocots/</a>. (Accessed: 2008).
- Thailand Travel Tours. 2008. Chae Son National Park. Available at: <a href="http://www.thailandtraveltours.com/chae-son-national-park.htm">http://www.thailandtraveltours.com/chae-son-national-park.htm</a>. (Accessed: 23/09/2008).
- BirdLife International. 2008. Doi Suthep-Pui National Park. Available at: <a href="http://www.birdlife.org/datazone/sites/index.html?action=SitHTMDetails.asp&sid=15081&m=0">http://www.birdlife.org/datazone/sites/index.html?action=SitHTMDetails.asp&sid=15081&m=0</a>. (Accessed: 22/09/2008).
- Gusman, G. and Gusman, L. 2006. <i>The Genus </i>Arisaema<i>. A Monograph for Botanists and Nature Lovers</i>. A.R.G. Gantner Verlag K.G., Brussels.
- Wikramanayake, E. and Carpenter, C. 2001. Kayah-Karen montane rain forests (IM0119). Available at: <a href="http://worldwildlife.org/ecoregions/im0119">http://worldwildlife.org/ecoregions/im0119</a>.
- Wikramanayake, E., Boonratana, R., Rundel, P. and Aggimarangsee, N. 2001. Central Indochina dry forests (IM0202). Available at: <a href="worldwildlife.org/ecoregions/im0202">worldwildlife.org/ecoregions/im0202</a>. (Accessed: 20/09/2008).
- Hetterscheid, W.L.A. 1994. Notes on the genus <i>Amorphophallus</i> (Araceae) - 2 new species from Tropical Asia. <i>Blumea</i> 39: 237-281.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Crook, V.
evaluator
Scott, J.A.
Crook, V. 2013. Arisaema maxwellii. The IUCN Red List of Threatened Species 2013: e.T44393096A44480077. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.