An Overview of the Conservation Status of and Threats to Rhinoceros Species in the Wild

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An Overview of the Conservation Status of and Threats to Rhinoceros Species in the Wild 96 ELEPHANTS AND RHINOCEROS Int. Zoo Yb. (2006) 40: 96–117 © The Zoological Society of London An overview of the conservation status of and threats to rhinoceros species in the wild R. AMIN1, K. THOMAS1, R. H. EMSLIE2, T. J. FOOSE3, 5 & N. VAN STRIEN4 1Zoological Society of London, Regent’s Park, London NW1 4RY, United Kingdom, 2IUCN/SSC African Rhino Specialist Group, Box 1212, Hilton 3245, KwaZulu-Natal, South Africa, 3International Rhino Foundation, 20 Pen Mar Street, Waynesboro, Pennsylvania 17268, USA, and 4IUCN/SSC Asian Rhino Specialist Group, Kondominium Taman Anggrek 3-23B, Jalan Parman. Slipi, Jakarta 11470, Indonesia E-mail: [email protected] This paper summarizes the recent status of rhino- species (Foose et al., 1995) for the ecosys- ceros species, as provided by IUCN Species Survival tems they inhabit because their conserva- Commission’s Rhinoceros Specialist Groups, and describes some of the current conservation measures. tion requirements, by default, encompass At the time of writing there are c. 14 950 rhinoceros those of other smaller species. If rhino- remaining in Africa and c. 2850 in Asia. During the ceros can be successfully conserved and last decade conservation initiatives have achieved protected within an area, then the other notable successes; however, numbers of some species and subspecies have declined over this period and species in the area will also benefit. Before three subspecies are close to extinction. The illegal considering the status of each rhinoceros demand for rhinoceros horn and the subsequent species in turn, it is worth first examining poaching this generates continue to pose a serious the main threats to rhinoceros species threat to rhinoceros populations worldwide. How- worldwide. ever, experience indicates that where anti-poaching efforts are concentrated above minimum threshold levels population losses as a result of poaching can be reduced to a low and sustainable level. However, THREATS TO RHINOCEROS POPULATIONS not all populations receive sufficient protection and Rhinoceros have been hunted for centu- declining budgets of range-state governments for ries as agricultural pests, for trophies and field conservation are a major cause for concern. The role of donor support is, therefore, becoming meat, their skin has been used for shields increasingly important. For some subspecies lack of and good luck charms, and their horn has adequate habitat protection rather than lack of suit- been used in traditional medicines and as able habitat is a major constraint for population handles for ceremonial daggers (Emslie & expansion and growth. Many rhinoceros popu- lations in Africa are managed as part of bigger meta- Brooks, 1999). Over the last century a populations. However, sub-optimal biological significant area of rhinoceros habitat has management is also reducing population growth been degraded or lost as result of land- rates in a number of populations. management practices and human settlement. Key-words: conservation status, endangered species, habitat, illegal trade, protected areas, rhinoceros, Increasing poverty in many African threats countries has often been associated with war and civil unrest, and the associated free flow of weapons has also had a neg- Rhinoceros, like other charismatic megah- ative impact on conservation efforts for erbivores, require large areas to support rhinoceros. For example, insurgencies and viable populations. They act as umbrella civil wars in Nepal, parts of Assam and 5 Dr Tom Foose, International Rhino Foundation Program Director, died on 18 May 2006. One of the foun- ders of the IRF and with a passion for rhinoceros conservation, Tom will be remembered for the enormous contribution he made to the shaping of rhinoceros conservation programmes. REVIEW: RHINOCEROS CONSERVATION STATUS AND IN SITU THREATS 97 the Democratic Republic of the Congo parks in Africa and Asia have increased have led to considerable reductions in over the last 10 years. Evidence suggests numbers in specific parks in recent years that in order to be effective, anti-poaching (Hillman-Smith & Ndey, 2005). efforts need to be concentrated above The use of large tracts of land for wild- minimum threshold levels. Where this can life conservation is under continued threat be achieved, poaching invariably has been in Asia and Africa, as demand for land reduced to low and sustainable levels. For for subsistence farming, cattle grazing and this reason many rhinoceros are main- commercial use, such as plantations and tained in fenced sanctuaries or in intensive logging, increases. Human population protection zones within larger national growth and rising unemployment add to parks where manpower and resources can the pressure for land. In particular, hab- be concentrated at effective levels (Leader- itat loss has had a significant impact on Williams, 1988; Emslie & Brooks, 1999). the Sumatran rhinoceros Dicerorhinus In contrast, attempting to reintroduce sumatrensis. However, many range states rhinoceros into vast tracts of land without still have sufficient land to maintain the necessary budgets and manpower to rhinoceros populations. protect them successfully is not Protection and conservation-manage- recommended. ment programmes for rhinoceros can be Rhinoceros poached in Africa and Asia extremely expensive and beyond the reach are targeted primarily for their horn but of some range states. In both Africa and in some cases the entire carcass is used. Asia effective anti-poaching efforts and However, the preparation and transpor- management of rhinoceros can cost up to tation of other body parts is difficult and US$1000 annually for every square kilo- in practice only the horn is taken from metre of habitat (N. Leader-Williams, most poached animals (E. B. Martin, pers. comm.; T. Conway, pers. comm.). pers. comm.). Well-armed poaching gangs Declining government budgets in real that cross international boundaries in terms and, in some cases, declining search of rhinoceros have also impacted capacity, pose a threat to the continued populations. While most of the profit successes in a number of range states from poaching goes to a few traders and where population numbers have been middlemen, even the small amounts increasing under effective protection and earned by poachers are enough incentive management strategies. Therefore, the to risk fines, imprisonment or death. One assistance of donor agencies is becoming problem is a tendency of the press to pub- increasingly important, as are attempts by licize the high value of rhinoceros horn. a number of range states to increase rev- These are usually quotes of the final resale enue for conservation through eco- prices for rhinoceros horn, which does not tourism. In some southern African bear any relation to the much lower countries rhinoceros contribute towards amount poachers may get for whole horns the cost of conservation through sustain- (especially in Africa). This can send the able-use ventures, such as ecotourism, live misleading message to potential criminals sales and limited sport hunting of old and that there is a lot of money to be made surplus 77. from poaching, when the reality is that in The major threat to rhinoceros is the Africa the rhinoceros are worth far more illegal demand for horn and the poaching alive than the horns are worth to pressure that this trade stimulates. Over poachers. There have been a number of the last few decades poaching has been the cases in Africa in recent years where local main cause of decline in some areas. How- dealers have not been able to sell horn and ever such declines have not been universal have in the end been caught in undercover as populations in many well-protected sting operations, where it became clear 98 ELEPHANTS AND RHINOCEROS that the price poachers thought they could 2005 came from the Northern white command was much higher than the rhinoceros Ceratotherium simum cottoni actual black-market price. (Vigne & Martin, 2006). Jambiya with new rhinoceros-horn handles have been TRADE found on sale openly suggesting that There are two main uses for Rhinoceros craftsmen have little reason to hide them horn. It is carved to make ornate handles because government inspectors are not for jambiyas (ceremonial daggers worn in doing enough to curb the trade (Vigne & Yemen). Rhinoceros horn is also used in Martin, 2006). traditional Chinese medicine (TCM) Even though the use of rhinoceros horn (Martin & Martin, 1982; Emslie & in TCM is now banned in most countries, Brooks, 1999). Although the media rhinoceros horn is still being traded routinely claim that a major use of rhino- throughout Asia. It has been suggested ceros horn is as an aphrodisiac, this has that in the late 1980s and early 1990s been found to be largely a myth (Martin rhinoceros horn may have been stockpiled & Martin, 1982). Historically, the Guja- as a speculative investment (Emslie & rati in India did use rhinoceros horn as an Brooks, 1999). With the increased imple- aphrodisiac but following the increase in mentation of domestic trade bans the the price of horn this practice effectively trade has gone underground and it is now ceased (E. B. Martin, pers. comm.). more difficult to monitor and assess levels Since the early 1970s Yemen has of illegal trading. imported the largest quantity of African While some TCM practitioners have rhinoceros horn, which is preferred to identified a number of acceptable substi- Asian rhinoceros horn owing to its larger tutes, others believe that rhinoceros horn size, thus allowing more jambiya dagger is irreplaceable for the treatment of cer- handles to be made per horn. Most illegal tain, sometimes life-threatening, condi- horn from eastern Africa has been smug- tions. In TCM rhinoceros horn is used gled by traders into Yemen. Africa’s primarily for the treatment of ailments, Black rhinoceros Diceros bicornis popu- such as epilepsy, fevers and strokes. Many lation fell from c. 65 000 in 1970 to 2450 pharmacists consider Asian rhinoceros by the early 1990s. It is only in recent horn to be more effective than African years that Yemen became a party to rhinoceros horn.
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