Aloe peglerae Schönland
|Bergaalwyn (a), Grootaalwyn (a), Magaliesberg Aloe (e), Red-hot Poker (e)|
Status and Criteria
Critically Endangered A4abd
|M.F. Pfab, L. von Staden & N. Hahn|
|Aloe peglerae is a localized, range restricted species (EOO 3415 km²). It is known from two extensive subpopulations and two smaller ones. Field monitoring of selected sites indicated a 43% population reduction over 10 years. Should this trend continue, which is likely as the illegal removal of plants from the wild is very difficult to control, it is estimated that the overall population reduction will exceed 80% within three generations, which includes the past 10 years as well as the next 60 years, representing two generations into the future.|
|South African endemic|
|Gauteng, North West|
|Magaliesberg and Witwatersberg.|
Habitat and Ecology
|Gold Reef Mountain Bushveld, Waterberg-Magaliesberg Summit Sourveld, Rand Highveld Grassland|
|Grassland, in shallow, gravely quartzitic soils on rocky, north-facing slopes or summits of ridges.|
|The most severe threat to Aloe peglerae is illegal collection of mature individuals from the wild. As a long-lived, slow growing species, even very low levels of harvesting is unsustainable. Most illegal collection is thought to be incidental and opportunistic, making it very hard to control (Pfab and Scholes 2004). Monitoring indicates that this threat is ongoing across the population, and is not just confined to areas with public access (Phama et al. 2014). High levels of seed harvesting for the horticultural trade is also likely to have a long term impact on the viability of this species (Pfab and Scholes 2004), particularly in that it limits the population's ability to recover from ongoing, rapid decline.
Habitat loss to urban expansion and other land development is a threat around Pretoria, Krugersdorp and Hartbeespoort. Most of this species' habitat is however protected in formally protected areas as well as many private nature reserves, and development is therefore a minor threat, affecting only a small proportion of the population.|
Aloe peglerae has a limited distribution range, and is localized to quartzitic ridges in northern Gauteng and adjacent areas in North West Province. Within this area, the species is still relatively abundant, but local declines due to illegal removal of plants from the wild is concerning. There are four known subpopulations, one recently discovered during a survey of suitable habitat in North West (Hahn 2013). The two largest subpopulations occur along the summit ridges of the Magaliesberg and Witwatersberg between Rustenburg and Pretoria, each consisting of more than 10 000 mature individuals. Two smaller subpopulations of around 1000-2000 mature individuals occur near Krugersdorp and in the Koster district.
Field observations indicate that the species has become scarce or extirpated in places accessible to the public (Pfab and Scholes 2004). At least 200 plants were recorded in the Kgaswane Nature Reserve near Rustenburg in the 1980s (Hahn 2013), but fewer than 10 plants could be found in a 1999 survey (M.F. Pfab pers. comm. 2005), and no plants could be found during the most recent field surveys (2008-2013, Hahn 2013).
Demographic monitoring over a period of 19 years indicate that Aloe peglerae is slow growing, long-lived and recruitment is very low (Scholes 1998). Based on this data, the generation length for the species is estimated to be 30-40 years. Due to these demographics, Aloe peglerae is extremely sensitive to illegal wild collecting of plants. A population viability model indicate that the removal of only one plant per year in subpopulations consisting of 1000 mature individuals or less causes a high probability of local extinction within three generations (Pfab and Scholes 2004). For larger subpopulations, wild harvesting is sustainable only at extremely low harvesting levels of 0.12% or less per annum, which in a subpopulation of 10 000 mature individuals equates to 12 plants per annum. With the wild population of Aloe peglerae estimated to be around 70 000 mature individuals in 2004 (Pfab and Scholes 2004), wild harvesting of more than 70-80 mature individuals per annum is estimated to lead to ongoing population decline.
Repeat sampling of nine selected sites across the Magaliesberg in 1999 and 2009-2010 indicates ongoing population decline at seven of the nine sites, with an overall population reduction of 43% over this 10 year period (Phama et al. 2014). Significant declines were not just limited to publicly accessible land, but also occurred on privately owned sites. Should this trend continue, population reduction would exceed 80% within three generations.
Status and Criteria
Citation/Red List version
|Aloe peglerae Schönland||EN A2d; B1ab(ii,v)+2ab(ii,v)||Raimondo et al. (2009)|
|Aloe peglerae Schönland||EN A2d+3d+4d; B1ab(ii,v)+2ab(ii,v)||Pfab and Victor (2002)|
|Aloe peglerae Schönland||EN A1acdeB1B2bce||Victor (2002)|
|Aloe peglerae Schönland||Rare ||Hilton-Taylor (1996)|
|Aloe peglerae Schönland||Rare ||Hall et al. (1980)|
Germishuizen, G. and Fabian, A. 1997. Wild flowers of northern South Africa. Fernwood Press, Vlaeberg.
Hahn, N. 2013. Rare, endangered and endemic flora of the North West Province. Unpublished Report to the Department of Economic Development, Conservation and Tourism, North West Provincial Government.
Hall, A.V., De Winter, M., De Winter, B. and Van Oosterhout, S.A.M. 1980. Threatened plants of southern Africa. South African National Scienctific Programmes Report 45. CSIR, Pretoria.
Hankey, A. and Turner, S. Field observations and surveys: Results from Red Data plant project. (Surveys of Krugersdorp populations were completed by staff of Witwatersrand Botanical Gardens). Gauteng Nature Conservation.
Hilton-Taylor, C. 1996. Red data list of southern African plants. Strelitzia 4. South African National Botanical Institute, Pretoria.
Pfab, M.F. and Patterson, C. 1998. Aloe peglerae. TRAFFIC East/Southern Africa Species Update: No 2.
Pfab, M.F. and Scholes, M.A. 2004. Is the collection of Aloe peglerae from the wild sustainable? An evaluation using stochastic population modelling. Biological Conservation 118:695-701.
Pfab, M.F. and Victor, J.E. 2002. Threatened plants of Gauteng, South Africa. South African Journal of Botany 68:370-375.
Phama, J., Panagos, M., Myburgh, W. and Pfab, M. 2014. The population status of the Endangered endemic plant Aloe peglerae: Area of occupancy, population structure, and past population trends. South African Journal of Botany 93:247-251.
Raimondo, D., von Staden, L., Foden, W., Victor, J.E., Helme, N.A., Turner, R.C., Kamundi, D.A. and Manyama, P.A. 2009. Red List of South African Plants. Strelitzia 25. South African National Biodiversity Institute, Pretoria.
Scholes, M.A. 1988. A population study of Aloe peglerae in habitat. South African Journal of Botany 54(2):137-139.
Van Wyk, B.-E. and Smith, G. 2003. Guide to aloes of South Africa. (2nd ed.). Briza Publications, Pretoria.
Victor, J.E. 2002. South Africa. In: J.S. Golding (ed), Southern African plant Red Data Lists. Southern African Botanical Diversity Network Report 14 (pp. 93-120), SABONET, Pretoria.
|Pfab, M.F., von Staden, L. & Hahn, N. 2016. Aloe peglerae Schönland. National Assessment: Red List of South African Plants version 2017.1. Accessed on 2017/04/30|
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© C. Paterson-Jones
© C. Paterson-Jones
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