Culcasia bosii
Ntépé-Nyamè
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
EN · En dangercritères B1ab(ii,iii)+2ab(ii,iii)?Inconnue- Évaluation
- 2020 · v3.1
- Altitude
- 0 – 100 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Menaces identifiées(9 menaces classées CMP-IUCN)
1_2Commercial & industrial areasRapid DeclinesMinority (<50%)Ongoing2_1_1Shifting agricultureRapid DeclinesMajority (50-90%)Ongoing2_1_2Small-holder farmingRapid DeclinesMajority (50-90%)Ongoing3_2Mining & quarryingRapid DeclinesMajority (50-90%)Ongoing1_1Housing & urban areasUnknownMinority (<50%)Ongoing4_1Roads & railroadsUnknownMinority (<50%)Ongoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]UnknownUnknownOngoing2_1_3Agro-industry farmingVery Rapid DeclinesMinority (<50%)Ongoing5_3_4Unintentional effects: (large scale) [harvest]Very Rapid DeclinesMajority (50-90%)Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
This species has been collected at four sites in the South Region of Cameroon: Dipikar, south east Massif des Mamelles, Elom, and north of Bipindi. All of this species’ collection localities are within or very near to mining concessions (Global Forest Watch 2020). A particular threat is from a mining concession at Massif des Mamelles (Onana and Cheek 2011, Global Forest Watch 2020). The area has substantial iron ore deposits which have been explored and are set to be exploited (Onana and Cheek 2011). Therefore, the development of an open cast iron-ore mine at this site poses a future threat to this species and is likely to cause the loss and degradation of relatively intact forest (Tchouto et al. 2006, Onana and Cheek 2011, Global Forest Watch 2020). Additionally, the collection at Massif de Mamelles lies within a logging concession (Global Forest Watch 2020). The species has also been collected in the Bipindi area. The main economic activity of Bipindi is agriculture, with a slash and burn approach used in the area to grow crops including plantain, cassava, macabo, and cocoa (Communes et Villes Unies du Cameroun 2020). Although crops are mainly grown for grown for local consumption, food grown in Bipindi is increasingly being sold to Kribi (Communes et Villes Unies du Cameroun 2020). Additionally, in 2018, an oil palm concession was signed for over 18,000 ha of land near to Bipindi town (Ngeunga 2019). Logging concessions have also previously operated across the Bipindi area (Communes et Villes Unies du Cameroun 2020, Prabhu et al. 1998), and this species was collected near to a current concession (Global Forest Watch 2020).
The collection at Elom was collected near a large rubber plantation (WWF 2018, Global Forest Watch 2020). This collection is also near to Kribi and in this area, large amounts of forest have been lost, mainly due to urban expansion (WWF 2018, Google Earth 2020). A particular threat in this area is from the development of the Kribi Port and Industrial Complex, and the associated urbanisation and extractive industry infrastructure (Onana and Cheek 2011, WWF 2018, Foonde 2018). The port complex, which includes an industrial zone and a residential area, is being developed on a 26,000 ha site around Kribi, where it is reported to be responsible for forest loss and degradation (Romain et al. 2017, Tichafogwe and Nji 2018). Additionally, the port has led to many roads and paths opening up within Campo Ma'an National Park, where this species has also been collected, and this is making protecting the park increasingly challenging (WWF 2018). Additionally, logging also poses a threat here, with areas of the Campo Ma'an National Park having previously been selectively logged (Tchouto 2004). The area immediately surrounding the park is also currently being, or has previously been, subject to logging (Fotso et al. 2001, Global Forest Watch 2020), with the collection of this species near to a logging concession (Global Forest Watch 2020). Subsistence agriculture is also a considerable threat, with slash and burn agriculture widely practiced across Cameroon, including in the Campo Ma'an area (Tchouto 2004, Onana and Cheek 2011).
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
There are no targeted conservation actions for this species and there are currently no known ex-situ conservation sites (BGCI 2020). However, the species does occur within the Campo Ma'an National Park (Protected Planet 2020). This locality, at Dipikar, is probably the most secure site for this species (Onana and Cheek 2011). Further research is needed into the species' current distribution. In particular, surveys should focus on the Kribi-Campo area where records are concentrated as this is probably the best prospect for rediscovery and long term preservation of this species (Onana and Cheek 2011). Surveys should also be focused in the Mount Cameroon area and in the Ngounié Province of Gabon where uncertain records of this species exist. Additionally, basic population information for this species should be collected as a baseline for future monitoring, and further research is needed into this species' life history and ecology.
Actions de conservation (3)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management3_4_1Captive breeding/artificial propagation
Stress écologiques (24)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_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_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality
Priorités de recherche (3)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (21)Sources scientifiques de l'évaluation IUCNExpert
- Communes et Villes Unies du Cameroun. 2020. Carte Communale. Available at: <a href="http://cvuc.cm/national/index.php/fr/">http://cvuc.cm/national/index.php/fr/</a>.
- BGCI. 2020. Botanic Gardens Conservation International (BGCI) - Plant Search. Available at: <a href="https://tools.bgci.org/plant_search.php">https://tools.bgci.org/plant_search.php</a>.
- CJB (Conservatoire et Jardin botaniques de la Ville de Genève and South African National Biodiversity Institute, Pretoria (CJB-SANBI). 2020. African Plant Database (version 3.4.0). Available at: <a href="http://www.ville-ge.ch/musinfo/bd/cjb/africa/">http://www.ville-ge.ch/musinfo/bd/cjb/africa/</a>.
- Google Earth. 2020. Satellite Imagery. Available at: <a href="https://earth.google.com/web/">https://earth.google.com/web/</a>.
- Protected Planet. 2020. Protected Planet: The World Database on Protected Areas (WDPA). Cambridge, UK Available at: <a href="www.protectedplanet.net">www.protectedplanet.net</a>. (Accessed: 2020).
- Global Forest Watch. 2020. Interactive Forest Change Mapping Tool. Available at: <a href="http://www.globalforestwatch.org/">http://www.globalforestwatch.org/</a>.
- IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 December 2020).
- Ngeunga, M. 2019. Cameroon: The Bagyeli women strongly opposing Biopalm. Available at: <a href="https://www.forestpeoples.org/en/node/50402">https://www.forestpeoples.org/en/node/50402</a>.
- Foonde, J.M. 2018. Change Detection: Estimating the Footprint of the Kribi Agro-Industrial and Urban Port Complex (Cameroon) from Landsat Imagery. <i>Open Access Library Journal</i> 5(e4550).
- WWF. 2018. The saving of Campo Ma’an National Park. Available at: <a href="https://wwf.panda.org/?325912/The-saving-of-Campo-Maan-National-Park">https://wwf.panda.org/?325912/The-saving-of-Campo-Maan-National-Park</a>.
- Tichafogwe, T.R. and Nji, F.Z. 2018. The Kribi deep sea port creation as acatalyst to population mobility and development. <i>International Journal of Development and Sustainability</i> 7(4): 1273-1285.
- Romain, N.J., Lagarde, B.J., Emmanuel, D.K., Caroline, M.S.M. and Félicité, T.L. 2017. Deforestation, biodiversity and biomass losses in Kribi deep sea port area (Cameroon): Some mitigating measures. <i>Journal of Ecology and The Natural Environment</i> 9(6): 87-98.
- Onana, J.-M. 2013. <i>Synopsis des espèces végétales vasculaires endémiques et rares du Cameroun. Check-liste pour la conservation de la biodiversité</i>. Ministère de la Recherche Scientifique et de l'Innovation (MINRESI), Yaoundé, Cameroon.
- Haigh, A., Clark, B., Reynolds, L., Mayo, S.J., Croat, T.B., Lay, L., Boyce, P.C., Mora, M., Bogner, J., Sellaro, M., Wong, S.Y., Kostelac, C., Grayum, M.H., Keating, R.C., Ruckert, G., Naylor, M.F. and Hay, A.. 2011. CATE Araceae. Available at: <a href="http://www.cate-araceae.org/">http://www.cate-araceae.org/</a>.
- Onana, J.M. and Cheek, M. 2011. <i>Red Data Book of the Flowering Plants of Cameroon: IUCN Global Assessments</i>. Kew Publishing, Kew, Richmond, Surrey, UK.
- Bachman, S., Moat, J., Hill, A. W., de Torre, J. & Scott, B. 2011. Supporting Red List threat assessments with GeoCAT: Geospatial conservation assessment tool. . <i>ZooKeys</i> 150: 117-126.
- Tchouto, M.G.P., Yemefack, M., de Boer, W.F., de Wilde, J.J.F.E., van der Maesen, L.J.G. and Cleef, A.M. 2006. Biodiversity hotspots and conservation priorities in the Campo-Ma‘an rain forests, Cameroon. <i>Biodiversity and Conservation</i> 15(4): 1219-1252.
- Tchouto, M.G.P. 2004. Plant diversity in a central African rain forest: implications for biodiversity conservation in Cameroon. PhD Thesis. Department of Plant Sciences, Biosystematics Group, Wageningen University.
- Fotso, R.; Dowsett-Lemaire, F.; Dowsett, R. J.; Cameroon Ornithological Club; Scholte, P.; Languy, M.; Bowden, C. 2001. Cameroon. In: Fishpool, L.D.C.; Evans, M.I. (ed.), <i>Important Bird Areas in Africa and associated islands: Priority sites for conservation</i>, pp. 133-159. Pisces Pubications and BirdLife International (BirdLife Conservation Series No.11), Newbury and Cambridge, UK.
- 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.
- Prabhu, R., Maynard, W., Atyi, R.E., Colfer, C.J.P., Shepherd, G., Venkateswarlu, P. and Tiayon, F. 1998. Testing and Developing Criteria and Indicators for Sustainable Forest Management in Cameroon: The Kribi Test - Fina Report. Center for International Forestry Research (CIFOR), Jakarta, Indonesia.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
Lovell, R. & Cheek, M. 2020. Culcasia bosii. The IUCN Red List of Threatened Species 2020: e.T110097146A110097148. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.