Ontologia

Musa cheesmanii

N.W.Simmonds

LCLR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

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Calcul du tissu écologique de Musa cheesmanii.

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Liste rouge IUCN

LC · Préoccupation mineure?Inconnue
Évaluation complète
Évaluation
2022 · v3.1
Altitude
931500 m
Profondeur
m
État de la populationExpert
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_1
    Shifting agriculture
    Ongoing
  • 2_1_2
    Small-holder farming
    Ongoing
  • 2_1_3
    Agro-industry farming
    Ongoing
  • 2_3_1
    Nomadic grazing
    Ongoing
  • 5_3_5
    Motivation Unknown/Unrecorded
    Ongoing
Description complète des menacesExpert
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 Lowland
  • 1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesExpert
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)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
Usage & commerce (3)Expert
  • 1Food - human
    subsistance
  • 13Pets/display animals, horticulture
    internationalnational
  • 17Other (free text)
    internationalnational
Priorités de recherche (4)Expert
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Forb or Herb
Références bibliographiques (18)Expert
  1. 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).
  2. WCSP. 2019. World Checklist of Selected Plant Families. Available at: <a href=" http://apps.kew.org/wcsp/"> http://apps.kew.org/wcsp/</a>.
  3. GFW. 2019. Global Forest Watch. Available at: <a href="http://www.globalforestwatch.org/">http://www.globalforestwatch.org/</a>.
  4. 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).
  5. 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).
  6. 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).
  7. 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.
  8. 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.
  9. 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.
  10. 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.
  11. Häkkinen, M. 2013. Reappraisal of sectional taxonomy in Musa (<i>Musaceae</i>). <i>Taxon</i> 62(4): 809-813.
  12. 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.
  13. 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).
  14. Chatterjee, S. 2008. Biodiversity conservation issues of Northeast India. <i>International Forestry Review </i> 10(2): 315-324.
  15. 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.
  16. 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.
  17. Simmonds, N.W. 1962. <i>The evolution of the Bananas</i>. Longmans, London.
  18. Simmonds, N.W. 1956. Botanical results of the banana collecting expedition, 1954-5. <i>Kew Bulletin</i> 11(3): 463-489.
Évaluateurs & contributeurs (4)Expert
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.

Répartition mondiale (heatmap GBIF)Construction en cours

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Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

Distribution mondiale

Calcul de la distribution GBIF· ~10–60 s

Phénologie

Calcul du calendrier d'apparition· ~5–30 s

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Observations & statuts

Bibliographie