Black Rhinoceros - Diceros bicornis
( Linnaeus, 1758 )

 

 

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Subspecies: Unknown
Est. World Population: 3142

CITES Status: NOT LISTED
IUCN Status: Critically Endangered
U.S. ESA Status: NOT LISTED

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Top Speed:
Jumping Ability: (Horizontal)

Life Span: in the Wild
Life Span: in Captivity

Sexual Maturity: (Females)
Sexual Maturity: (Males)
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Habitat:
Black Rhino occur in a wide variety of habitats from desert areas in Namibia to wetter wooded areas. The highest densities of rhinos are found in savannas on nutrient-rich soils and in succulent Valley Bushveld areas. Black Rhino are browsers and favour small acacia's and other palatable woody species (Grewia's, Euphorbiaceae species, etc.) as well as palatable herbs and succulents. However, because of high levels of secondary plant chemicals, much woody plant browse (especially many evergreen species) in some areas is unpalatable. Failure to appreciate this, has in the past led to carrying capacities being over-estimated in some areas. Apart from plant species composition and size structure, Black Rhino carrying capacity is related to rainfall, soil nutrient status, fire histories, levels of grass interference, extent of frost and densities of other large browsers. To maintain rapid population growth rates and prevent potential habitat damage if the population overshoots carrying capacity, populations of Black Rhinos should be managed at densities below long term ecological carrying capacity (i.e., below zero growth densities). Surplus rhino that are removed from such established populations are routinely being profitably invested in new areas with suitable habitat and protection where populations can grow rapidly.

Range:

There are now three remaining recognised subspecies/genetic management clusters of Black Rhino occupying different areas of Africa. Strong support for this classification has been provided by independent analyses of different genetic data sets by different researchers using different analytical methods. See Taxonomic Notes for more details. A fourth recognised subspecies Diceros bicornis longipes once ranged through the savanna zones of central-west Africa but it is now considered to have gone Extinct in its last known habitats in northern Cameroon.

The other three more numerous subspecies are found in the eastern and southern African countries. Today putative D. b. bicornis range includes Namibia, southern Angola, western Botswana, and southwestern and southeastern South Africa (up to the Kei River), although today they occur only in Namibia (the stronghold) and South Africa with a sighting of one animal in Angola and unconfirmed reports of possibly another three animals.

Diceros b. michaeli was distributed from South Sudan, Ethiopia, and Somalia, through Kenya into northern-central Tanzania and Rwanda. Its current stronghold is Kenya. Smaller but growing numbers occur in northern Tanzania. The single animal that survived in Rwanda has died. One important free-ranging subpopulation occurs outside its range in a private game reserve in South Africa. Contractually, these D. b. michaeli animals may only be translocated back to historical range and not elsewhere in South Africa. The repatriation of some of these animals back to four areas of former subspecies range in Tanzania commenced in 1997, with animals also subsequently going to found a subpopulation in Rwanda.

Diceros b. minor is believed to have occurred from southern Tanzania through Zambia, Zimbabwe, and Mozambique to the northern, northwestern and northeastern parts of South Africa (north of the Mtamvuna River). It also probably occurred in southern Democratic Republic of the Congo, northern Angola, eastern Botswana, Malawi, and Eswatini. Today, its stronghold is South Africa and to a lesser extent Zimbabwe, with smaller numbers remaining in southern Tanzania. The South-central Black Rhino is now thought to be extinct in Angola and only one individual has been sighted in Mozambique since the 2008 IUCN African Rhino Specialist Group (AfRSG) meeting. The subspecies has also been reintroduced to Botswana, Malawi, Eswatini and Zambia. Based on very small sample sizes, Moodley et al.'s (2017) results suggested that perhaps the original historical Black Rhino that used to occur in Zambia but which had been wiped out by poaching by 1995 might be better classified as D. b. michaeli rather than D.b.minor. However, on account of the small sample sizes, and given that the species was reintroduced with D. b. minor founders, and that historically Zambia had been considered D. b. minor range, and climate and habitats are more similar to some D. b. minor range; reviewers recommended that historical pre-1995 Zambian animals should continue to be allocated to D. b. minor for this Red List revision (as has historically been the case). With further data this may change in future. As there were still significant numbers of Black Rhinos in Zambia in the early 1970s, how these animals are allocated influences the D. b. minor subspecies Red List assessment which would change to Endangered under criteria A2 and A4. The D. b. michaeli assessment remains the same whether or not the historical animals are classified as D. b. minor or D. b. michaeli

Note: At the request of certain members and countries, the IUCN SSC African Rhino Specialist Group (AfRSG) has a policy of not releasing detailed information (including maps) showing the whereabouts and names of all rhino subpopulations for security reasons. For this reason, only whole countries of occurrence are indicated on the range maps produced by the AfRSG.


Conservation:
Black Rhino have been listed on CITES Appendix I since 1977. All international commercial trade in Black Rhinos and their products have been prohibited. To help reduce illegal trade, and complement CITES international trade bans, domestic anti-trade measures and legislation were implemented in the 1990s by a number of consumer states. Effective field protection of rhino subpopulations has been critical. Many remaining rhino are now concentrated in fenced sanctuaries, conservancies, rhino conservation areas and intensive protection zones where law enforcement effort can be concentrated at effective levels. Monitoring has also provided information to guide biological management decision-making aimed at managing rhino subpopulations for rapid population growth. This has resulted in surplus animals being translocated to set up new populations both within and outside the species' former range. Following a decline in breeding performance in some areas, increased effort has recently been given to improving biological management with a view to increasing metapopulation growth rates. Increasing efforts are also being made to integrate local communities into conservation efforts (most notably in the Kunene region of Namibia). Strategically, Black Rhinos are now managed by a range of different stakeholders (private sector and state) in a number of countries increasing their long term security. In contrast to Southern White Rhino, most Black Rhino on privately owned land are managed on a custodianship basis for the state. Since CITES CoP13 limited sport hunting quotas have been approved for the two Range States with biggest populations (South Africa and Namibia). Removal of specific individuals can enhance demographic and/or genetic conservation. In addition to local and, national initiatives, there are a number of regional African rhino conservation initiatives: the SADC Rhino Management Group, the Southern African Rhino and Elephant Security Group and the East African Community Rhino Management Group. In addition to National Rhino Plans there is a Continental African Rhino Range States Conservation Plan. IUCN SSC African Rhino Specialist Group is the continental coordinating body for rhino conservation in Africa.

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