Chlorophytum mamillatum
Elden & Nordal
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Calcul du tissu écologique de Chlorophytum mamillatum.
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Liste rouge IUCN
EN · En dangercritères B2ab(iii)?Inconnue- Évaluation
- 2025 · v3.1
- Altitude
- 1220 – 1900 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Menaces identifiées(7 menaces classées CMP-IUCN)
11_2DroughtsUnknownMajority (50-90%)Ongoing1_1Housing & urban areasUnknownUnknownOngoing2_1_2Small-holder farmingUnknownUnknownOngoing2_1_3Agro-industry farmingUnknownUnknownFuture2_3_2Small-holder grazing, ranching or farmingUnknownUnknownOngoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]UnknownUnknownOngoing7_1_1Increase in fire frequency/intensityVery Rapid DeclinesUnknownOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
The species is known from nine collecting localities which are considered to correspond to five to six locations. The five collecting localities at the southern edge of the Harenna Forest, on the periphery of the Bale Mountains National Park (BMNP), are considered to correspond to two locations, both in Delo Menna woreda of Bale Zone: a cluster of four collecting sites on the lower slopes of the Harenna Forest are considered to correspond to one location, while a single collecting site on the fringe of the forest and close to the Welmel River and the settlement of Shawe is considered to be a separate location. At its southern edge, the Harenna Forest blends into a mosaic of open woodland and rapidly expanding agricultural land; the woodland areas are used for dry season grazing, with nearly 60% of native resident households living in Delo Mena along the forest edge involved in transhumant pastoralism. The woodland is also used for forest beekeeping, subsistence wood extraction and forest coffee production (Wakjira et al. 2013, 2015). The main threats to the natural habitat at the altitude where the species has been recorded are therefore overgrazing by unsupervised livestock and wood harvesting. Satellite imagery reveals the proximity of extensive small-scale agriculture to the location closer to Shawe. A further threat here is also that of expanding settlements, and this also poses a threat to the four collecting localities in the forest area itself as these are situated along a road through the forest and therefore accessible to human encroachment. In addition to these threats, the Bale Mountains National Park Management Plan also identifies fire as a high-level threat in the Harenna Forest (Ethiopian Wildlife Conservation Authority 2023); with climate change, and the projected increase in periods of drought, this threat can be expected to increase.
The four collecting localities to the south of Harar are considered to correspond to three to four locations. Two collecting localities to the southeast of Harar, which can be considered as one or two locations, are within the Babile Elephant Sanctuary. A major threat affecting the habitat of the Sanctuary is 'habitat contraction’ due to settlement, agricultural expansion and overgrazing, and other unsustainable practices such as charcoal production, with the increasing demand for charcoal destroying the woodland habitats in all the valleys (EWCA and WSD 2010, Mengistu Wale et al. 2017). All these threats can be assumed to be impacting the habitat of the species at the location to the southwest of Harar. Satellite imagery reveals that the location less than 10 km from the city of Harar is also threatened by significant habitat conversion to small-scale agriculture.
Habitats préférentiels (classification IUCN)
2_1Savanna - Dry3_5Shrubland - Subtropical/Tropical Dry
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Wakjira et al. (2015) note that ‘the provision of sustainable, viable livelihoods to forest-adjacent communities is of prime concern, both with regards to community well-being and to the well-being of the forest’, while Gulte et al. (2023) identify the need for the BMNP authorities to provide environmental education as well as tangible economic benefits for local communities in order to elicit support for conservation objectives. The Management Effectiveness Evaluation of the Babile Elephant Sanctuary was reported on in 2005 and 2014 (UNEP-WCMC and IUCN 2022). In 2023 concern was expressed that Babile’s ecosystem is ‘under grave threat from the expansion of agricultural investment, encroachment, and the pressure caused by illegal land occupations and vulnerable people’, and regional and national authorities were urged to ‘heed the concerns of EWCA, the EPIF and protect this reserve before it suffers irreparable damage’ (Elephant Protection Initiative Foundation 2023). There are no specific conservation measures or management plan in place for this species, and the species is also not known to occur in any ex situ plant collections (BGCI 2022).
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management3_4_2Genome resource bank
Stress écologiques (9)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_3Indirect ecosystem effects2_1Species mortality
Priorités de recherche (1)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (13)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2025. The IUCN Red List of Threatened Species. Version 2025-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 October 2025).
- Elephant Protection Initiative Foundation. 2023. EPI Foundation's Statement on the Situation in Babile Elephant Sanctuary. Elephant Protection Initiative Foundation. Available at: <a href="https://www.elephantprotectioninitiative.org/post/epi-foundation-s-statement-on-the-situation-in-babile-elephant-sanctuary">https://www.elephantprotectioninitiative.org/post/epi-foundation-s-statement-on-the-situation-in-babile-elephant-sanctuary</a>.
- Ethiopian Wildlife Conservation Authority. 2023. Bale Mountains National Park General Management Plan 2017-2027. Ethiopian Wildlife Conservation Authority, Addis Ababa.
- Gulte, E., Tadele, H., Haileslassie, A. and Mekuria, W. 2023. Perception of local communities on protected areas: lessons drawn from the Bale Mountains National Park, Ethiopia. <i>Ecosystems and People</i> 19(1): Article: 2227282.
- BGCI. 2022. Botanic Gardens Conservation International (BGCI) - PlantSearch. Available at: <a href="https://tools.bgci.org/plant_search.php">https://tools.bgci.org/plant_search.php</a>. (Accessed: 2022).
- UNEP-WCMC and IUCN. 2022. Protected Planet: The World Database on Protected Areas (WDPA) and World Database on Other Effective Area-based Conservation Measures (WD-OECM) [Online]. Cambridge, UK. UNEP-WCMC and IUCN. Available at: <a href="https://www.protectedplanet.net">https://www.protectedplanet.net</a>. (Accessed: 1 January 2022, 2021).
- Bjorå, C.S., Elden, M., Nordal, I., Brysting, A.K., Awas, T., Sebsebe, D. and Bendiksby, M. 2017. Speciation in the genera <i>Anthericum</i> and <i>Chlorophytum</i> (Asparagaceae) in Ethiopia—a molecular phylogenetic approach. <i>Phytotaxa</i> 297(2): 139-156.
- Mengistu Wale, Abeje Kassie, Getachew Mulualem, Weldemariam Tesfahunegny, Abraham Assefa. 2017. Wildlife Threats and Their Relative Severity of Eastern Ethiopia Protected Areas. <i>Ecology and Evolutionary Biology</i> 2(4): 59-67.
- Wakjira, D.T., D’Udine, F. and Crawford, A. 2015. Migration and Conservation in the Bale Mountains Ecosystem. International Institute for Sustainable Development . Available at: <a href="https://www.iisd.org/system/files/publications/migration-conservation-bale-mountains-ecosystem-policy-brief.pdf">https://www.iisd.org/system/files/publications/migration-conservation-bale-mountains-ecosystem-policy-brief.pdf</a>.
- Wakjira, D.T., Fischer, A. and Pinard, M. 2013. Governance change and institutional adaptation: A case study from Harenna Forest, Ethiopia. <i>Environmental Management </i> 51: 912-925.
- Bachman, S., Moat, J., Hill, A., de la Torre J. and Scot, B. 2011. Supporting Red List threat assessments with GeoCAT: Geospatial Conservation Assessment Tool. <i>ZooKeys</i> 150: 117-126.
- EWCA and WSD. 2010. Management Plan of Babile Elephant Sanctuary. Addis Ababa.
- Friis, I., Demissew, S. and Breugel, P. V. 2010. Atlas of the potential vegetation of Ethiopia. <i>Det Kongelige Danske Videnskabernes Selskab</i> 58: 1-307.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
Roberts, A., Sebsebe Demissew & Tesfanesh Feseha 2025. Chlorophytum mamillatum. The IUCN Red List of Threatened Species 2025: e.T220978844A221000401. Accessed on 05 May 2026.