Dioscorea brownii
Schinz
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Dioscorea brownii.
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Liste rouge IUCN
EN · En dangercritères B2ab(i,ii,iii,iv,v); C2a(i)↘Décroissante- Évaluation
- 2017 · v3.1
- Altitude
- 650 – 1450 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Dioscorea brownii was first discovered in 1883, and since then it has been rarely collected. Historical records are from a wide area stretching from the Richmond district in southern KwaZulu-Natal to Umtata in the Eastern Cape. These records, however, have very imprecise locality descriptions, and many have never been relocated. Since the 1970s, the species was known only from a small area on state land around Weza, southern KwaZulu-Natal. Here the species remains on small remnants of mistbelt grassland. Three small, isolated subpopulations are currently known, the largest one consisting of around 200 mature individuals, and the other two with between 10 and 50 plants. A fourth subpopulation, recorded by the local conservation authority in the same area, is likely to still exist, but survey data lacks an estimate of the subpopulation size. Recently, another small subpopulation was discovered about 80 km north of Ngele, in the Richmond district, where it was last recorded in 1946. About 100 plants occur in scattered, small clumps in mistbelt grassland fragmented by timber plantations.
This species is easily overlooked within its grassland habitat, and may be under-sampled. However, with less than 30% of its habitat remaining intact, it is unlikely that many more subpopulations exist, and all are likely to be small and confined to isolated grassland fragments. Remaining known subpopulations require ongoing monitoring. Estimating the global population size is difficult, but it is likely to be small. All known subpopulations consist of fewer than 200 mature individuals, and therefore it is unlikely that the population size exceeds 2,500 mature individuals. A present the known population numbers around 400 mature individuals.
This species' extent of occurrence (EOO) is very uncertain: historical records are from an area of over 10 000 km². Current known occurrences of this species are, however, confined to an area of 500-6,941 km².
This species is easily overlooked within its grassland habitat, and may be under-sampled. However, with less than 30% of its habitat remaining intact, it is unlikely that many more subpopulations exist, and all are likely to be small and confined to isolated grassland fragments. Remaining known subpopulations require ongoing monitoring. Estimating the global population size is difficult, but it is likely to be small. All known subpopulations consist of fewer than 200 mature individuals, and therefore it is unlikely that the population size exceeds 2,500 mature individuals. A present the known population numbers around 400 mature individuals.
This species' extent of occurrence (EOO) is very uncertain: historical records are from an area of over 10 000 km². Current known occurrences of this species are, however, confined to an area of 500-6,941 km².
Menaces identifiées(6 menaces classées CMP-IUCN)
1_2Commercial & industrial areasRapid DeclinesMinority (<50%)Past, Unlikely to Return2_2_3Scale Unknown/UnrecordedRapid DeclinesMajority (50-90%)Ongoing8_1_1Unspecified speciesNegligible declinesMajority (50-90%)Ongoing5_2_1Intentional use (species is the target)UnknownUnknownUnknown1_1Housing & urban areasSlow, Significant DeclinesMinority (<50%)Ongoing2_3_4Scale Unknown/UnrecordedSlow, Significant DeclinesMajority (50-90%)Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Midlands Mistbelt Grassland between Weza and Richmond is already at least 70% irreversibly modified, predominantly for timber plantations. Remaining grasslands are fragmented, and continue to be degraded due to inappropriate fire management, overgrazing by livestock, and alien invasive plants. Of the four known existing locations, one is in a patch of grassland between a recently established timber plantation and an expanding rural village. The area is heavily grazed (I.M. Johnson pers. obs. 2009), and the subpopulation is likely to be severely impacted, should either the village or plantation expand any further. The second location is in a very small grassland fragment among timber plantations, and requires management and clearing of alien invasive plants. This site is also being degraded due to heavy overgrazing (I.M. Johnson pers. obs. 2009). A third subpopulation was recently recorded in a grassland fragment next to a sawmill. Although this grassland is burnt annually, it is still in good condition, and has a high species diversity (G. Grieve pers. obs. 2011). A fourth location is also in a grassland fragment adjoining expanding timber plantations. The subpopulation near Richmond occurs in a site contracted for conservation through the Biodiversity Stewardship Programme. The site is grazed by livestock, but in relatively good condition. Ongoing clearing of alien invasive plants is needed, which currently occur in low densities.
Some Dioscorea species are used medicinally, but the use of D. brownii has not specifically been reported (Arnold et al. 2002).
Some Dioscorea species are used medicinally, but the use of D. brownii has not specifically been reported (Arnold et al. 2002).
Habitats préférentiels (classification IUCN)
4_6Grassland - Subtropical/Tropical Seasonally Wet/Flooded★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species occurs on state-owned land often referred to as 'Ngele Nature Reserve', however, this area is not recognized as a formal protected area in terms of South Africa's National Protected Areas Act (National Biodiversity Assessment 2011 protected areas dataset). Seeds have been banked for ex situ conservation, but more effort is required to preserve this species in situ. A subpopulation recently discovered near Richmond occurs on a communally owned site that has been contracted for conservation through South Africa's Biodiversity Stewardship Programme.
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection3_1_1Harvest management
Stress écologiques (11)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_3_2Competition
Usage & commerce (1)Use & Trade — IUCNExpert
3Medicine - human & veterinarysubsistance
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
Afrotropical
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or HerbGeophyte
Références bibliographiques (8)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 5 December 2017).
- 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.
- Raimondo, D., von Staden, L., Foden, W., Victor, J.E., Helme, N.A., Turner, R.C., Kamundi, D.A. and Manyama, P.A. (eds). 2009. <i>Red List of South African Plants</i>. Strelitzia 25. South African National Biodiversity Institute, Pretoria.
- Arnold, T.H., Prentice, C.A., Hawker, L.C., Snyman, E.E., Tomalin, M., Crouch, N.R. and Pottas-Bircher, C. 2002. <i>Medicinal and magical plants of southern Africa: an annotated checklist. </i>Strelitzia<i> 13</i>. National Botanical Institute, Pretoria.
- Scott-Shaw, C.R. 1999. <i>Rare and Threatened Plants of KwaZulu-Natal and Neighbouring Regions</i>. KwaZulu-Natal Nature Conservation Services, Pietermaritzburg.
- Abbott, T. 1998. The rediscovery of <i>Dioscorea brownii</i>. <i>PlantLife</i> 18: 29.
- Hilton-Taylor, C. (ed.). 1996. <i>Red Data List of Southern African Plants</i>. Strelitzia 4. National Botanical Institute, Pretoria.
- Hilliard, O.M. and Burtt, B.L. 1976. Notes on some plants of Southern Africa chiefly from Natal: V. <i>Notes from the Royal Botanic Garden Edinburgh</i> 34(3): 253-286.
Évaluateurs & contributeurs (4)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
von Staden, L.
contributor
Abbott, A.T.D., Grieve, G. & Johnson, I.M.
evaluator
Raimondo, D.
institutions
Royal Botanic Gardens, Kew
von Staden, L. 2017. Dioscorea brownii. The IUCN Red List of Threatened Species 2017: e.T63729383A63729402. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s