Ontologia

Dioscorea brownii

Schinz

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

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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 complète
Évaluation
2017 · v3.1
Altitude
6501450 m
Profondeur
m
État de la populationExpert
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.

Menaces identifiées(6 menaces classées CMP-IUCN)

  • 1_2
    Commercial & industrial areas
    Rapid DeclinesMinority (<50%)Past, Unlikely to Return
  • 2_2_3
    Scale Unknown/Unrecorded
    Rapid DeclinesMajority (50-90%)Ongoing
  • 8_1_1
    Unspecified species
    Negligible declinesMajority (50-90%)Ongoing
  • 5_2_1
    Intentional use (species is the target)
    UnknownUnknownUnknown
  • 1_1
    Housing & urban areas
    Slow, Significant DeclinesMinority (<50%)Ongoing
  • 2_3_4
    Scale Unknown/Unrecorded
    Slow, Significant DeclinesMajority (50-90%)Ongoing
Description complète des menacesExpert
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).

Habitats préférentiels (classification IUCN)

  • 4_6Grassland - Subtropical/Tropical Seasonally Wet/Flooded
Mesures de conservation recommandéesExpert
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)Expert
  • 1_1Site/area protection
  • 3_1_1Harvest management
Stress écologiques (11)Expert
  • 1_1Ecosystem conversion
  • 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_3_2Competition
Usage & commerce (1)Expert
  • 3Medicine - human & veterinary
    subsistance
Priorités de recherche (1)Expert
  • 1_2Population size, distribution & trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Afrotropical

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Forb or HerbGeophyte
Références bibliographiques (8)Expert
  1. 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).
  2. 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.
  3. 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.
  4. 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.
  5. Scott-Shaw, C.R. 1999. <i>Rare and Threatened Plants of KwaZulu-Natal and Neighbouring Regions</i>. KwaZulu-Natal Nature Conservation Services, Pietermaritzburg.
  6. Abbott, T. 1998. The rediscovery of <i>Dioscorea brownii</i>. <i>PlantLife</i> 18: 29.
  7. Hilton-Taylor, C. (ed.). 1996. <i>Red Data List of Southern African Plants</i>. Strelitzia 4. National Botanical Institute, Pretoria.
  8. 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)Expert
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.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
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