Musa cheesmanii
N.W.Simmonds
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Musa cheesmanii.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
LC · Préoccupation mineure?Inconnue- Évaluation
- 2022 · v3.1
- Altitude
- 93 – 1500 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Simmonds (1956) describes Musa cheesmanii as very abundant on the lower stretches of Manipur road, while recent observations indicate that the species grows abundantly throughout the states of Arunachal Pradesh, Nagaland and Manipur (Joe et al. 2014) and in the areas of Likabali and Jonai in Assam (Gogoi et al. 2017). Gogoi et al. (2014) observe that it is among the most dominant species in the genus in Arunachal Pradesh, growing in almost all districts between 200–1,500 m asl in large colonies on hilly slopes, and also report it as common in Nagaland and Manipur. Given its relatively large range and reported frequency, it is suspected that the population is large. However, no numerical population information is available, and the current population trend is unknown. Research into population status and trends is therefore recommended.
Menaces identifiées(5 menaces classées CMP-IUCN)
2_1_1Shifting agricultureOngoing2_1_2Small-holder farmingOngoing2_1_3Agro-industry farmingOngoing2_3_1Nomadic grazingOngoing5_3_5Motivation Unknown/UnrecordedOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Within the native range of the species, forestry is the dominant driver of tree cover loss (GFW 2019) and the region has witnessed excessive logging historically (Chatterjee 2008). Other drivers of this land use change are shifting cultivation (jhum), encroachment for grazing, and an increase in commercial agricultural plantations (Chatterjee 2008). However, the specific impact of deforestation on members of the Musa genus is somewhat difficult to quantify: while clear-felling or land conversion is likely to be detrimental to the species, wild bananas spring up in transient, often man-made, habitats and thus may benefit from human disturbance to some extent (Simmonds 1962). Little has been documented about the habitat and ecological preferences of M. cheesmanii so it is difficult to infer whether the species is tolerant of disturbed habitat. As such, research into the threats affecting the species, as well as its ecological requirements, is recommended.
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
The genus Musa is listed in Annex I of the International Treaty on Plant Genetic Resources for Food and Agriculture (ITPGRFA) which aims to guarantee sustainable agriculture and food security through the conservation and sustainable use of plant genetic resources for food and agriculture, as well as ensuring the fair and equitable sharing of the benefits arising out of their use (FAO 2009). A single M. cheesmanii germplasm accession of wild origin is held by the Bioversity International Musa Germplasm Transit Centre (ITC) in Belgium and one botanical garden is listed as a site of ex situ conservation for this species (Ruas et al. 2017, BGCI 2019, Genesys Global Portal on Plant Genetic Resources 2019). It is in ex situ conservation at the Botanical Survey of India, Arunachal Pradesh Regional Center in Itanagar (S. Borah pers. comm. 2021). The species has been collected from the Sessa Orchid Sanctuary in Arunachal Pradesh, so passive conservation is presumed here (UNEP-WCMC and IUCN 2019); it is unclear whether active management is apparent. Joe et al. (2014) recommend that the species be categorised as Least Concern using IUCN Red List Criteria, based on several years of field experience.
Stress écologiques (18)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance
Usage & commerce (3)Use & Trade — IUCNExpert
1Food - humansubsistance13Pets/display animals, horticultureinternationalnational17Other (free text)internationalnational
Priorités de recherche (4)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Indomalayan
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or Herb
Références bibliographiques (18)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2022. The IUCN Red List of Threatened Species. Version 2022-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 08 December 2022).
- WCSP. 2019. World Checklist of Selected Plant Families. Available at: <a href=" http://apps.kew.org/wcsp/"> http://apps.kew.org/wcsp/</a>.
- GFW. 2019. Global Forest Watch. Available at: <a href="http://www.globalforestwatch.org/">http://www.globalforestwatch.org/</a>.
- Genesys Global Portal on Plant Genetic Resources. 2019. Genesys. Available at: <a href="https://www.genesys-pgr.org/welcome">https://www.genesys-pgr.org/welcome</a>. (Accessed: 4 February 2019).
- IUCN and UNEP-WCMC. 2019. The World Database on Protected Areas (WDPA). Cambridge, UK Available at: <a href="https://www.protectedplanet.net/">https://www.protectedplanet.net/</a>. (Accessed: 4 January 2019).
- BGCI (Botanic Gardens Conservation International). 2018. PlantSearch online database. Richmond, UK Available at: <a href="www.bgci.org/plant_search.php">www.bgci.org/plant_search.php</a>. (Accessed: 2018).
- Gogoi, R., Borah, S. and Häkkinen, M. 2017. Diversity of wild Bananas (<i>Musa</i> L.-Musaceae) in the state of Assam, India. In: P. Medhi and H. Roy (eds), <i>Compendium on Botanical Research in Eastern India</i>, pp. 81-98. Eastern Publisher.
- Ruas, M., Guignon, V., Sempere, G., Sardos, J., Hueber, Y., Duvergey, H., Andrieu, A., Chase, R., Jenny, C., Hazekamp, T., Irish, B., Jelali, K., Adeka, T., Ayala-Silva, T., Chao, C.P., Daniells, J., Dowiya, B., Effa effa, B., Gueco, L., Herradura, L., Ibobondji, L., Kempenaers, E., Kilangi, J., Muhangi, S., Xuan, P.N., Paofa, J., Pavis, C., Thiemele, D., Tossou, C., Sandoval, J., Sutanto, A., Vangu Paka, G., Yi, G., Van den houwe, I., Roux, N. and Rouard, M. 2017. MGIS: managing banana (<i>Musa</i> spp.) genetic resources information and high-throughput genotyping data. <i>Database</i> 2017(2017): bax046.
- Joe, A., Sreejith, P.E. and Sabu, M. 2014. On the rediscovery and extended distribution of <i>Musa cheesmanii Musaceae</i> from north-east India. <i>International Journal of Plant, Animal and Environmental Sciences</i> 4(2): 1-4.
- Gogoi, R., Häkkinen, M., Borah, S. and Satyanarayana, P. 2014. Taxonomic identity of <i>Musa cheesmanii</i> (Musaceae) in northeast India. <i>Nordic Journal of Botany</i> 32(4): 474-478. DOI: 10.1111/j.1756-1051.2013.00429.x.
- Häkkinen, M. 2013. Reappraisal of sectional taxonomy in Musa (<i>Musaceae</i>). <i>Taxon</i> 62(4): 809-813.
- 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.
- FAO. 2009. International Treaty on Plant Genetic Resources for Food and Agriculture (ITPGRFA) [Online]. Rome: Food and Agriculture Organisation. Available at: <a href="ftp://ftp.fao.org/docrep/fao/011/i0510e/i0510e.pdf">ftp://ftp.fao.org/docrep/fao/011/i0510e/i0510e.pdf</a>. (Accessed: 18/12/2012).
- Chatterjee, S. 2008. Biodiversity conservation issues of Northeast India. <i>International Forestry Review </i> 10(2): 315-324.
- Maxted, N., Ford-Lloyd, B.V., Jury, S., Kell, S. and Scholten, M. 2006. Towards a definition of a crop wild relative. <i>Biodiversity and Conservation</i> 15: 2673-2685.
- Olson, D.M., Dinerstein, E., Wikramanayake, E.D., Burgess, N.D., Powell, G.V.N., Underwood, E.C., D'Amico, J.A., Itoua, I., Strand, H.E., Morrison, J.C., Loucks, C.J., Allnutt, T.F., Ricketts, T.H., Kura, Y., Lamoreux, J.F., Wettengel, W.W., Hedao, P. and Kassem, K.R. 2001. Terrestrial ecoregions of the world: a new map of life on earth. <i>Bioscience</i> 51: 933-938.
- Simmonds, N.W. 1962. <i>The evolution of the Bananas</i>. Longmans, London.
- Simmonds, N.W. 1956. Botanical results of the banana collecting expedition, 1954-5. <i>Kew Bulletin</i> 11(3): 463-489.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Plummer, J. & Kallow, S.
contributor
Mertens, A.
evaluator
Borah, S.
facilitators
Hargreaves, S.
Plummer, J. & Kallow, S. 2022. Musa cheesmanii. The IUCN Red List of Threatened Species 2022: e.T158541133A158544268. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s