|Scientific Name:||Raphicerus melanotis (Thunberg, 1811)|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Palmer, G., Birss, C., Kerley, G., Feely, J., Peinke, D. & Castley, G.|
|Reviewer(s):||Child, M.F. & Mallon, D.|
The species is listed as Least Concern. Despite its restricted range, the Cape Grysbok is common, relatively adaptable, and there are no major threats that could cause range-wide declines. This species is well represented in protected areas and occurs on private farms where it can typically adapt to the predominant forms of land use provided that there is sufficient suitable structured habitat remaining. However estimates of population sizes are scarce and it is therefore difficult to extrapolate data from individual studies or locations to discern the status of the population nationally. Some studies are also relatively dated thus highlighting the need for more robust estimates of Cape Grysbok populations from sites throughout their distribution. The population trend is assumed to be generally stable in protected areas and on private land, but decreasing in some other areas where human population densities are high. The effects of private conservation and wildlife ranching on this species should further be monitored and managed. There is also little information on the possible impacts of climate change, alien invasive vegetation and the expansion of certain agricultural industries in some areas (e.g., rooibos tea plantations and vineyards). However, climate change may make marginal habitats more suitable for agricultural expansion, putting pressure on remaining habitat patches where this species occurs, and thus represents an emerging threat. This should be monitored for its impacts on Cape Grysbok.
|Range Description:||The Cape Grysbok is endemic to South Africa, and is largely confined to the Cape Floristic Region. It remains widespread and locally common within its historical range in the Western Cape and Eastern Cape provinces. It also marginally occurs in the Northern Cape. The most northern confirmed record and locality is van Rhynsdorp, Western Cape Province (Skead 2011). In the Eastern Cape, little is known about its historical distribution (Skead 2007). Boshoff and Kerley (2013) provide two records for the Drakensberg/Lesotho but caution that they may be of material transported there through trade. The range has not expanded either naturally or through the private sector. If anything it has contracted through the loss of scattered habitat fragments that have been structurally altered (become less dense), or have been totally transformed through the introduction and expansion of alien invasive vegetation (Kerley et al. 2010), increased densities of megaherbivores (Tambling et al. 2013) and the expansion of certain agricultural industries in some areas (for example, rooibos tea plantations and vineyards). This trend is likely to continue with the effects of climate change making such fragments amenable to alternative land uses. In the Western Cape, the area of occupancy (AOO) calculated for properties for which Cape Grysbok presence is confirmed is 9,104 km², of which 5,451 km² is in provincial nature reserves, 1.8 km² in local authority nature reserves, 2,319 km² in national parks and 1,331 km² on private land (C. Birss unpubl. data). For more detailed discussion of the distribution range see East (1999) and Castley and Lloyd (2013).|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Cape Grysbok are normally solitary and cryptic in their behaviour and therefore seldom seen. They are particularly difficult to see in dense vegetation, which is exacerbated in fire-prone areas such as the fynbos of the Western Cape (Castley and Lloyd 2013). Estimates of population sizes are scarce and it is therefore difficult to extrapolate data from individual studies or locations to discern the status of the population nationally. Some studies are also relatively dated and more recent data are needed. For example, Scott (1991) studied the distribution of small antelopes in De Hoop Nature Reserve between 1985 and 1987 and recorded densities of 0.21 animals / 100 km travelled for Cape Grysbok compared with 2.64 for Steenbok (Raphicerus campestris). Castley and Lloyd (2013) suggest that comparisons such as this may not be accurately accurate estimates of Cape Grysbok populations given their relative lack visibility and dense habitat preferences. Once again this highlights the need for more robust estimates of Cape Grysbok subpopulations from sites throughout their distribution. All indications are however that Cape Grysbok occur “freely” in the landscape—on and off protected areas, on agricultural land, on game farms, and in vineyards.|
Based on available habitat, and a requirement of between 6 and 456 ha per animal depending on the vegetation type, Cape Grysbok numbers could be up to 231,448 in the Cape Floristic Region, down from an estimated population of 322,977 in the pre-habitat transformation model (Kerley et al. 2003). This modelled estimate is almost an order of magnitude higher than earlier estimates (East 1999). Current data from CapeNature indicate that Cape Grysbok occur on 58 provincial protected areas, with a total estimated abundance of 1,196 individuals. Using the number of land parcels (2,438) on which Cape Grysbok are either present (720 land parcels) or persist (indicating that the subpopulation is persistent and breeding; 1,718 land parcels) in the Western Cape Province, at the calculated densities of 6 to 456 hectares per animal it is estimated that the 77,269 ha of protected area could sustain between 1,704 to 129,544 animals. In the City of Cape Town area, Cape Grysbok occur in high densities on some relatively small (less than 100 ha) isolated properties, such as False Bay Nature Reserve, Zandvlei, University of the Western Cape and Millerton Race Course. The reduced predation from dogs and natural predators and the lack of competition from Common Duiker (Sylvicapra grimmia) are possible reasons for these elevated densities (C. Dorse pers. comm. 2015). Cape Grysbok are present in Table Mountain National Park (D. Winterton pers. comm. 2015), West Coast National Park (Avery 1990), Bontebok National Park (Novellie et al. 1994), Agulhas National Park (M. Raselabe pers. comm. 2016), Garden Route National Park (L. Moolman-van der Vyver pers. comm. 2016), Baviaanskloof and Groendal Nature Reserve (D. Peinke unpubl. data), and Addo Elephant National Park (AENP) but are absent from Namaqua and Tankwa Karoo National Parks. This is according to the Mammals Tool that the Cape Research Centre produced in 2011, based on putative distribution maps (Skinner and Chimimba 2005), as well as the references mentioned above.
No comprehensive subpopulation trend data are available but the population is suspected to be stable (for example, aerial counts suggest a stable subpopulation on Baviaanskloof Nature Reserve between 2008 and 2014; D. Peinke unpubl. data), although there are indications of localised declines. Anecdotal evidence suggest that numbers of Cape Grysbok and Bushpig (Potamochoerus larvatus) both declined in the Main Camp section of AENP as mega-herbivore numbers increased (Tambling et al. 2013, G. Castley unpubl. data) and no evidence could be found of their presence there in 2014/2015 (G. Kerley unpubl. data).
|Current Population Trend:||Stable|
|Habitat and Ecology:||The natural (historical) distribution of Cape Grysbok is primarily associated with the Fynbos Biome and extends into the Forest, Succulent Thicket and Succulent Karoo Biomes and marginally into the Nama-Karoo and Grassland Biomes. They are absent from the Desert and Savanna Biomes. They are locally common in thickets, shrublands and the fynbos habitats. Dense cover is an important habitat requirement. Their presence in the high-altitude grasslands of the north-eastern Cape is conditional on the proximity of forest fragments and bush clumps, although they may also use long grass for cover (Castley and Lloyd 2013). They also enter developed areas such as vineyards and agricultural areas (East 1999), and have been blamed, along with the Common Duiker, for extensive damage to young shoots in tea plantations in the Cedarberg (C.T. Stuart and T. Stuart pers. comm. in Castley and Lloyd 2013). This only happens where there is suitable habitat in close proximity. Cape Grysbok are generally regarded as browsers (Stynder 2009). The inclusion of grass in the diet has also been reported (Manson 1974) but has been regarded as unimportant (Skinner and Chimimba 2005), but its importance may fluctuate with environmental changes (Faith 2011). More recently, however, some studies have shown that the Cape Grysbok is a highly selective browser (Kigozi et al. 2008, Kerley et al. 2010). Furthermore, Kerley et al. (2010) reported significant selection for grasses in their study. This is an adaptable species and can survive in human-modified landscapes provided that vegetation with the required understorey cover remains.|
|Use and Trade:||This species is poached as bushmeat, as they are vulnerable to being caught in snares, but this is not expected to cause widespread population decline. There is also limited international trophy hunting from hunters targeting the “tiny 10”. Cape Grysbok parts have also been recorded from traditional herbalist shops but at relatively low frequencies (number of items for sale) and rates of occurrence (number of outlets where items are for sale) (Simelane and Kerley 1998). CapeNature aims to manage off-takes through permits and requests that land owners provide evidence of the persistence of their subpopulations and registers of hunting history. Captive breeding is discouraged by CapeNature and the Eastern Cape Parks and Tourism Agency, and local translocations from within the ecotypic range are preferred. Landowners are required to supply evidence of the status of their population before permits to capture and translocate are supplied. The receiving property is also evaluated for suitability of habitat.|
There are no major threats to the species, although the increase in agriculture and human settlements have reduced available habitat. Localised declines occur due to habitat transformation and loss of dense vegetation in some areas. For example, Cape Grysbok ranges have seen local declines in numbers from areas such as the AENP where escalating numbers of elephants have opened up or destroyed thicket habitats (Castley and Lloyd 2013, Tambling et al. 2013). Additionally, some game farms are over stocked and under managed resulting in the opening up of areas of dense vegetation, thus reducing habitat for Cape Grysbok. Even where numbers are not excessive, extra-limital browsers can compete for forage and space (Spear and Chown 2009, Spear et al. 2011).
Cape Grysbok are illegally hunted with dogs, which may lead to local subpopulation declines. They are also both accidentally and deliberately caught with snares for bush meat. Localised unsustainable offtakes of trophy males for hunting may lead to population structure disruptions and localised declines.
Additionally, the habitat available to this species is declining in area and quality. Agriculture and urbanisation has reduced habitat, but there has not been a severe decrease in habitat quality. For example, Pence (2014) calculated that between 2006 and 2011, 536 km² of land was converted to agriculture in the Western Cape Province (107 km² per year, which equates to 0.08% of the surface area of the province per year). Urban human settlements have expanded by 8.6% and 6.3% between 2000 and 2013 in the Western and Eastern Cape provinces, respectively (GeoTerraImage 2015), which we infer to mean increasing mortality from poaching, snaring and dog hunting. Even though there may not be any empirical evidence for specific impacts of extra-limital species on Cape Grysbok, several publications have highlighted the detrimental impacts of introducing extra-limital and/or exotic species that compete for resources with an endemic species (Castley et al. 2001, Spear and Chown 2009, Spear et al. 2011). Observational data from AENP further indicate that the increase in numbers of larger herbivores is associated with declines in the more cryptic species (for example, Grysbok and Bushpig). Finally, we suspect that habitat loss from agricultural expansion may become likely as climate change makes marginal habitats more suitable for cultivation. For example, climate change is projected to increase the suitability of upslope habitats for viticulture, increasing the footprint of winelands by 14% by 2050 (Hannah et al. 2013).
Cape Grysbok are conserved in protected areas throughout their natural distribution range in the Western and Eastern Cape Provinces. In the Western Cape, the protected areas in which Cape Grysbok occurs, comprise ca 9,104 km², of which 5,451 km² is provincial nature reserves, 1.8 km² is local authority nature reserves, and 2,319 km² is national parks (C. Birss unpubl. data). Regulated harvesting through conservation legislation aims to ensure that off-takes are sustainable. In addition, it occurs widely in local authority and forestry reserves and on private land (East 1999). Research is being initiated by CapeNature and the Cape Leopard Trust to investigate the impacts of bush meat poaching in natural areas where Cape Grysbok occurs in close proximity to highly populated urban areas.While no direct conservation interventions are necessary at present, several interventions will benefit this and other species in the region:
|Citation:||Palmer, G., Birss, C., Kerley, G., Feely, J., Peinke, D. & Castley, G. 2017. Raphicerus melanotis. The IUCN Red List of Threatened Species 2017: e.T19306A50193334.Downloaded on 21 November 2017.|
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