Factors Affecting Lion (Panthera Leo) Home Range, Movement and Diet in Waza National Park, Cameroon

Total Page:16

File Type:pdf, Size:1020Kb

Factors Affecting Lion (Panthera Leo) Home Range, Movement and Diet in Waza National Park, Cameroon J. Zool., Lond. (2009) 300, 131-142 © 2009 The Zoological Society of London Printed in the United Kingdom DOI:10.1018/S0952201 Factors affecting lion (Panthera leo) home range, movement and diet in Waza National Park, Cameroon. H.D. Visser1*, L. Müller1, P.N. Tumenta1,2, R. Buij1,2, H.H. de Iongh1 1Institute of Environmental Sciences, Leiden University, P.O.Box 9518, 2300 RA Leiden, The Netherlands 2 Centre for Environment and Development studies in Cameroon, Maroua/Department of Forestry, University of Dschang, PO Box 479, Dschang, Cameroon Abstract Key words: lions, habitats, home range, diet, movement INTRODUCTION pressure on the environment, lion habitat and prey de- creased and lions became less abundant and locally All over the world large carnivore populations are threatened (Bauer & Van de Merwe 2004). Bauer and under pressure from the increasing human popula- Van der Merwe (2004) estimated 16,500 – 30,000 free tion (Fuller, 1995; Nowell & Jackson, 1996). Threats ranging lions in all of Africa. to large carnivores include habitat loss, declining Although lions are threatened all over Africa, the In- natural prey populations and commercial exploita- ternational Union for Conservation of Nature (IUCN) tion, but most large carnivores are killed by people has listed the lion as Vulnerable on the global Red that defend their livestock (Woodroffe, 2001; Bauer, List (Bauer et al., 2008), populations in Southern Nowell & Packer, 2008). This conflict with livestock and East Africa seem to be quite viable and lions ex- owners is caused by the fact that carnivores have to ist in high densities locally (Bauer & ven der Mer- kill other animals to feed. In areas where wild prey we, 2004; Nowell & Jackson, 1996). Eastern Africa species are being replaced by livestock the conflict is counts 11,000 lions and Southern Africa 10,000. In intense (Ramakrishnan, Coss & Pelkey, 1999, Saber- Central and West Africa only 1800 lions are left and wal et al., 1994; Seidensticker, Christie & Jackson., populations are fragmented and declining (Bauer & 1999). When carnivores attack livestock, measures Van der Merwe, 2004). The population of lions over from livestock owners to protect their property are the past two decades has reduced by approximately inevitable. Often these measures include retaliatory 30% (Bauer et al., 2008). Only a few lion populations killing of the carnivores (Seidensticker et al., 1999; remain in protected areas with the largest in Central Woodroffe, 2000). African Republic (300) and second largest in Cam- A carnivore species that has suffered from conflict eroon (260). with humans in particular is the lion (Panthera leo) In Cameroon lions exist in two areas in the north: The (Patterson et al., 2004). In history lions were abundant Bénoué Ecosystem and Waza National Park (Bauer from Eurasia to Africa (Turner & Antón, 1997). When & De Iongh, 2005). In Waza National Park (WNP), human population expanded and pressure on the en- the research area of this study, lion population has de- vironment increased, lions disappeared from all of creased to the brink of extinction (Tumenta et al., in Europe and remained only in sub-Saharan Africa and press; De Iongh et al., 2009). In 1962, the lion popu- a small part of Asia (Nowell & Jackson, 1996). Due lation was estimated a 100 (Flizot, 1962), in 2001 at to human population growth and resulting increasing 50 (Bauer et al., 2003) and in 2008 only 14-22 lions were left (Kok, et al., 2008). The decreasing numbers of lions in WNP are mainly attributed to the increas- *All correspondence to: H.D. Visser, Institute of Environmental Sciences, Leiden University, P.O.Box 9518, 2300 RA Leiden, ing human activity in and outside the park that results The Netherlands. in prey base depletion and lion-livestock conflict (De E-mail: [email protected] Iongh & Bauer, 2008). The lion-livestock conflict is 2 H.D. VISSER ET AL. Table 1 Number of prey species at Waza National Park from 1962 – 2007. Table is modified from De Iongh et al. (2004) with ad- dition of data from Omondi et al. (2007) Only the main prey species of lions are includedd in the table. O = numbers based on regular observations in the park; T = transect; W = waterhole count; A = aereal survey; - = number unknown; * = number heavily underestimated. Jan- Dec- 1962 1977 1977 1988 1994 1995 1996 1997 1998 2000 2001 2002 2007 Species O T T O W W W W/T T W A Kobus kob 25000 21993 13238 1700 2062 2573 4559 4517* 7665 1246* 9548 14489 1562 Damaliscus kor- 20000 749 605 - 1682 842 2395 720* 2198 236* 4284 7068 848 rigum Hippotragus 4000 349 223 - 1166 126 498 295* 1331 572 3868 5055 604 equinus Gazelle - 147 10 >300 621 455 440 204* 525 56* 593 228 28 rufifrons Phacochoerus 600- 675 200 - 38 3 61* 16* 298* 44* 575 47* 21 aethiopicus 700 Redunca arun- 2000 25 39 - 66 50 301 54* 70 9* - - dicum Kobus 200 - - - 0 0 0 0 0 0 - 0 defassa a well known problem all over Africa (Bauer et al., and activities also had an impact on the prey species 2008). Often lion habitats are surrounded by human of lions in WNP. All herbivore species have decreased settlements. Livestock forms a competition for wild drastically since 1965. In the 1960s WNP counted herbivores with reduction of the prey population as a 25,000 kobs, about 5000 in the 1990s and in 2007 result. Livestock is a relatively easy prey to catch and only 1500 in 2007. The same holds for topi, with with the intrusion of livestock into the living area of 20,000 in the 1960s, 2000 in the 1990s and less than lions, easy prey is presented. Lions kill livestock and 1000 in 2007. Less drastically is the decrease of the to protect their property, lions get killed by herdsmen. roan antelope population with 4000 in the 1960s, less Although livestock is relatively easy to catch and than 1500 in the 1990s and less than 1000 in 2007 present in high numbers in WNP, it is not preferred as (Table 1). The southern reedbuck and defassa water- food source (Van Rijssel et al., 2008). buck have become locally extinct since the 1960s (De The negative effects of increased human population Iongh, Bauer & Hamling, 2004). In the late 1970s a 30,000 Roan 25,000 Western kob Topi 20,000 r e b m 15,000 u N 10,000 5,000 0 1960 1970 1980 1990 2000 2010 Figure 1 Counts of three common, resident antelope species in WazaY eNationalar Park, western kob (Kobus kob kob), topi (Damalis- cus korrigum), and roan (Hippotragus equinus) since 1962 to present. Data from Scholte et al. (2007), Bobo Kadiri et al. (1998) and Omondi et al. (2007). 30,000 Roan 25,000 Western kob Topi 20,000 r e b m 15,000 u N 10,000 5,000 0 1960 1970 1980 1990 2000 2010 Year Factors affecting Home range, Movement and Diet in lions 3 drastic decrease in herbivore numbers was caused by a body weight of about 181 kg to 227 kg for males the construction of the Maga dam in 1979 (Scholte, and 113 kg to 136 kg for females, this means that lions Saleh & Serge, 2007). This dam prevented inunda- feed normally on large prey (Schaller, 1972). The size tion from the Logone river east of the park with a of prey lions are capable of killing is dependent on the dramatic impact on perennial vegetation, livestock, group size of the lion. When hunting alone, lions kill fisheries and birdlife in the downstream area of this smaller prey and when hunting in a group they kill river (Bauer, 2003; Scholte et al., 2007; Loth, 2007). larger prey (Schaller, 1972). Reversibly group size is Other factors inducing the rapid reduction of the an- smaller in areas with lower prey densities (Bauer, De telope species were rinderpest transmitted from live- Iongh & Di Silvestre, 2003). Small prey is killed in- stock because of an increase in livestock-antelope cidentally or out of necessity and animals weighing contact. Poaching was not seen as factor contributing more than 1000 kg are said to be relatively safe from to the decrease (Scholte et al., 2007). In the 1990s lion predation (Schaller, 1972). In an analysis of 32 and the beginning of 2000s populations of kob and different studies about lion diet Hayward & Kerley topi recovered little possibly by the (re)flooding of (2005) showed that lions prefer prey species within the floodplain (Scholte, 2007). In the 2000s this re- a weight range of 190-550 kg. The most preferred covery came drastically to an end and populations of weight was 350 kg, with gemsbok, buffalo, wilde- kob, roan and topi decreased again, with historic low beest, giraffe and zebra as favorite prey species. numbers of kob (Figure 1). Reason for this decrease Lions prefer prey species in a certain weight is an explosive increase in illegal activities inside the class, but what they actually eat is another thing. Be- park due to a breakdown of management (Tumenta et side prey preference many factors influence what a al., in press). lion eats. Most important are the characteristics of To get an idea of the lion-livestock conflict in WNP, the prey population: prey size, availability and den- it is important to gather ecological data of the lions. sity and scavenging (Schaller, 1972). Despite prefer- In this study we focus on two important factors that ences species that are not available can’t simply be might influence the lion-livestock conflict: sex and hunted. Ratios of prey occurrence in the environment habitat type.
Recommended publications
  • Aerial Surveys of Wildlife and Human Activity Across the Bouba N'djida
    Aerial Surveys of Wildlife and Human Activity Across the Bouba N’djida - Sena Oura - Benoue - Faro Landscape Northern Cameroon and Southwestern Chad April - May 2015 Paul Elkan, Roger Fotso, Chris Hamley, Soqui Mendiguetti, Paul Bour, Vailia Nguertou Alexandre, Iyah Ndjidda Emmanuel, Mbamba Jean Paul, Emmanuel Vounserbo, Etienne Bemadjim, Hensel Fopa Kueteyem and Kenmoe Georges Aime Wildlife Conservation Society Ministry of Forests and Wildlife (MINFOF) L'Ecole de Faune de Garoua Funded by the Great Elephant Census Paul G. Allen Foundation and WCS SUMMARY The Bouba N’djida - Sena Oura - Benoue - Faro Landscape is located in north Cameroon and extends into southwest Chad. It consists of Bouba N’djida, Sena Oura, Benoue and Faro National Parks, in addition to 25 safari hunting zones. Along with Zakouma NP in Chad and Waza NP in the Far North of Cameroon, the landscape represents one of the most important areas for savanna elephant conservation remaining in Central Africa. Aerial wildlife surveys in the landscape were first undertaken in 1977 by Van Lavieren and Esser (1979) focusing only on Bouba N’djida NP. They documented a population of 232 elephants in the park. After a long period with no systematic aerial surveys across the area, Omondi et al (2008) produced a minimum count of 525 elephants for the entire landscape. This included 450 that were counted in Bouba N’djida NP and its adjacent safari hunting zones. The survey also documented a high richness and abundance of other large mammals in the Bouba N’djida NP area, and to the southeast of Faro NP. In the period since 2010, a number of large-scale elephant poaching incidents have taken place in Bouba N’djida NP.
    [Show full text]
  • Panthera Pardus) Range Countries
    Profiles for Leopard (Panthera pardus) Range Countries Supplemental Document 1 to Jacobson et al. 2016 Profiles for Leopard Range Countries TABLE OF CONTENTS African Leopard (Panthera pardus pardus)...................................................... 4 North Africa .................................................................................................. 5 West Africa ................................................................................................... 6 Central Africa ............................................................................................. 15 East Africa .................................................................................................. 20 Southern Africa ........................................................................................... 26 Arabian Leopard (P. p. nimr) ......................................................................... 36 Persian Leopard (P. p. saxicolor) ................................................................... 42 Indian Leopard (P. p. fusca) ........................................................................... 53 Sri Lankan Leopard (P. p. kotiya) ................................................................... 58 Indochinese Leopard (P. p. delacouri) .......................................................... 60 North Chinese Leopard (P. p. japonensis) ..................................................... 65 Amur Leopard (P. p. orientalis) ..................................................................... 67 Javan Leopard
    [Show full text]
  • Other Large Mammals and Human Activities in Waza National Park, Cameroon
    African Journal of Environmental Science and Technology Vol. 4(6), pp. 401-411, June, 2010 Available online at http://www.academicjournals.org/AJEST DOI: 10.5897/AJEST09.158 ISSN 1991-637X ©2010 Academic Journals Full Length Research Paper Aerial survey of Elephants (Loxodonta africana africana), other large mammals and human activities in Waza National Park, Cameroon Désiré Foguekem¹ ²*, Martin Ngankam Tchamba¹, Patrick Omondi³ 1WWF Cameroon Program Office, P.O. Box 6776, Yaoundé, Cameroon. 2Department of Animal Biology Faculty of science, University of Yaounde 1, P.O. Box 812 Yaoundé, Cameroon. 3Kenya wildlife Service, P.O. Box 40241, Nairobi, Kenya. Accepted 18 March, 2010 Total aerial count of elephants, other large mammals and human activities in Waza National Park was conducted between 21st and 23rd February 2007. Total counts of elephants and other wildlife species were done and livestock numbers were estimated. A Cessna 206 Stationair six-seater aircraft fitted with GPS was used in navigation, recording survey paths and waypoints. A total of three different herds of 180 and 66 in the park along with a further 250 migrating elephant population towards Kalamaloue National Park were counted. The herds in the park were aggregated around central part of the park along watering point. The consideration of the number of the migrating herd then put the total Waza ecosystem elephant population at 496 individuals. The total number of carcasses recorded was 7 giving a carcass ratio of 2.85%. About 21,002 heads of livestock and over 50 farmlands and human settlement were estimated in the zone abutting the park. This signifies a high level of human pressures at the periphery and thus a high potential for loss of range for the elephants and illegal killing.
    [Show full text]
  • Threat of Rapid Extermination of the Lion (Panthera Leo Leo) in Waza National Park, Northern Cameroon
    Threat of rapid extermination of the lion (Panthera leo leo) in Waza National Park, Northern Cameroon P. N. Tumenta1,2*, J. S. Kok1, J. C. van Rijssel1, R. Buij1,2, B. M. Croes1,2, P. J. Funston3, H. H. de Iongh1 and H. A. Udo de Haes1 1Institute of Environmental Sciences, Leiden University, PO Box 9518, 2300RA Leiden, The Netherlands, 2Centre for Environment and Development studies in Cameroon, Maroua ⁄ Department of Forestry, University of Dschang, PO Box 479, Dschang, Cameroon and 3Department of Nature Conservation, Tshwane University of Technology Pretoria, Private Bag X680 Pretoria, 0001, South Africa en identifiant individuellement ses membres. On a estime´ Abstract que cette population comptait de 14 a` 21 adultes. La Lion populations in West and Central Africa are small and structure d’aˆge e´tait biaise´e en faveur des adultes; les fragmented. In areas where park management is weak, lionceaux repre´sentaient 22% de tous les lions identifie´set threats will likely facilitate the extinction of the lion. le sex-ratio e´tait de 1 ⁄ 3. Deux des quatre lions e´quipe´s d’un Wildlife management requires knowledge of the popula- collier e´metteur furent tue´s ille´galement en un an, en guise tion estimate. The population of lions in Waza National de repre´sailles; deux autres maˆles et une autre femelle Park (Waza NP) was assessed by individual identification furent aussi tue´s pendant cette pe´riode. La population de of members in the population. The population was assessed lions semble avoir de´cline´ au cours des cinq dernie`res to comprise of 14–21 adult individual lions.
    [Show full text]
  • Overview of Human Wildlife Conflict in Cameroon
    Overview of Human Wildlife Conflict in Cameroon Poto: Etoga Gilles WWF Campo, 2011 By Antoine Justin Eyebe Guy Patrice Dkamela Dominique Endamana POVERTY AND CONSERVATION LEARNING GROUP DISCUSSION PAPER NO 05 February 2012 Contents EXECUTIVE SUMMARY ................................................................................................................ 3 1. Introduction ......................................................................................................................... 4 2. Evidence of HWC in Cameroon............................................................................................ 4 3. Typology of HWC ................................................................................................................. 7 3.1 Crop destruction ........................................................................................................... 7 3.2 Attacks on domestic animals ..................................................................................... 10 3.3 Human death, injuries and damage to property ....................................................... 11 4. The Policy and Institutional Framework for Human-Wildlife Conflict Management at the State level in Cameroon ............................................................................................................ 11 4.1. Statutory instruments and institutions for HWC management ................................. 12 4.1.1 Protection of persons and property against animals ......................................... 12 4.1.2 Compensation
    [Show full text]
  • The Status of Cheetah and Af- Rican Wild Dog in the Bénoué Ecosystem, North Cameroon
    original contribution HANS H. DE IONGH1*, BARBARA CROES1, GREG RASMUSSEN2, RALPH BUIJ3 AND Study area PAUL FUNSTON4 The North Province of Cameroon (Fig. 1) is covered (44%) by natural woodland and con- The status of cheetah and Af- tains three national parks and 28 hunting zones. Poaching is a threat to wildlife and is rican wild dog in the Bénoué mainly related to rapid human encroachment in this area. Human population growth is re- Ecosystem, North Cameroon latively high in the area at around 2.6 % p.a. and mostly results from immigration from Here we present the results of a research programme on large carnivores imple- other provinces or neighbouring countries mented in the Bénoué Ecosystem of North Cameroon. The area comprises three na- with a diverse ethnic background (De Iongh tional parks (Bénoué, Bouba-Ndjidda and Faro, with a total surface of 7,300 km2) and et al. 2010) a large area comprising 28 hunting zones (with a total surface of 15,700 km2) that is The Bénoué Ecosystem (BE) is part of an ex- contiguous and surrounds all three parks. Three years of surveys (2007-2010) covered tensive protected area complex, the Bénoué- 4,200 km of spoor transects, 1,200 camera-trap days, 109 interviews with local villag- Gashaka Gumti area, of about 30,000 km2 in ers, and direct observations. From these data we conclude that cheetahs Acinonyx North Cameroon and Nigeria. The Bénoué- jubatus and African wild dogs Lycaon pictus are functionally extinct in the Bénoué Gashaka Gumti area consists of these Natio- Ecosystem and probably also in other areas of the country.
    [Show full text]
  • Cameroon Country Profile Update 2019
    Country Profile Republic of Cameroon Giraffe Conservation Status Report August 2019 General statistics Size of country: 475,400 km² Size of protected areas / percentage protected area coverage: 15.2 % Species and subspecies In 2016 the International Union for the Conservation of Nature (IUCN) completed the first detailed assessment of the conservation status of giraffe, revealing that their numbers are in peril. This was further emphasised when the majority of the IUCN recognised subspecies where assessed in 2018 – some as Critically Endangered. While this update further confirms the real threat to one of Africa’s most charismatic megafauna, it also highlights a rather confusing aspect of giraffe conservation: how many species/subspecies of giraffe are there? The IUCN currently recognises one species (Giraffa camelopardalis) and nine subspecies of giraffe (Muller et al. 2016) historically based on outdated assessments of their morphological features and geographic ranges. The subspecies are thus divided: Angolan giraffe (G. c. angolensis), Kordofan giraffe (G. c. antiquorum), Masai giraffe (G. c. tippleskirchi), Nubian giraffe (G. c. camelopardalis), reticulated giraffe (G. c. reticulata), Rothschild’s giraffe (G. c. rothschildi), South African giraffe (G. c. giraffa), Thornicroft’s giraffe (G. c. thornicrofti) and West African giraffe (G. c. peralta). However, over the past decade GCF together with their partner Senckenberg Biodiversity and Climate Research Centre (BiK-F) have performed the first-ever comprehensive DNA sampling and analysis (genomic, nuclear and mitochondrial) from all major natural populations of giraffe throughout their range in Africa. As a result, an update to the traditional taxonomy now exists. This study revealed that there are four distinct species of giraffe and likely five subspecies (Fennessy et al.
    [Show full text]
  • Wildlife Crime and Monitoring: Applications for Ranger-Collected
    Wildlife Crime and Monitoring: Applications for Ranger-Collected Data Duncan Graeme Lister Master of Science (by Research) University of York Biology November 2018 Abstract Anthropogenic factors such as habitat loss, over-harvesting and the introduction of non-native species are causing declines in global biodiversity. In sub-Saharan Africa, illegal hunting for bushmeat or high-value products such as rhino horn and ivory is threatening many mammal populations. Monitoring these populations is vital to ensuring their survival, yet professional scientific monitoring programs are costly and logistically difficult. Ranger-based monitoring, where rangers record evidence of illegal activities or wildlife sightings when on patrol is becoming increasingly popular. Here, we use maps of occurrence probability of bushmeat poaching derived from ranger-collected data in Queen Elizabeth National Park (QENP), Uganda, to determine the direct impacts of illegal hunting on herbivore populations. We found that the main target species for bushmeat poaching, Uganda kob, showed declines in areas predicted to have high poaching risk, reporting population level impacts of illegal hunting in a savannah for the first time. We go on to document how ranger-collected elephant sightings data can be used to predict their spatial distribution within QENP, using Bayesian hierarchical occupancy modelling to address the non-systematic method of data collection. We also attempt to create a time series model of elephant abundance in order to predict rapid declines that can occur in elephant populations. We conclude by highlighting the potential for ranger-based monitoring and ranger- collected data, suggesting ways it might be incorporated to continually monitor vulnerable populations in light of a rapidly expanding human population.
    [Show full text]
  • The International Tropical Timber Organization
    INTERNATIONAL TROPICAL TIMBER ORGANIZATION ITTO PRE-PROECT PROPOSAL INTITULÉ: SUPPORT TO THE CREATION OF GREEN BELTS AROUND THE WAZA, BENOUÉ, FARO AND BOUBA NDJIDDA NATIONAL PARKS SERIAL NUMBER PPD 178/14 Rev.2 (F) COMMITTEE REFORESTATION AND FOREST MANAGEMENT SUBMITTED BY THE GOVERNMENT OF CAMEROON ORIGINAL LANGUAGE FRENCH SUMMARY The plant formations of the Waza, Faro, Benue and Bouba Ndjidda National Parks are subject to multiple threats that jeopardize their existence. These threats stem from the way subsistence needs of local communities are addressed including their needs for fuel wood and wood material for rural infrastructure and fences, and this situation is maintained through a lack of local initiatives to rehabilitate the degrading plant cover. National Parks are the least degraded areas in the different regions. To reduce the rate of degradation of the plant cover and improve the supply of fuel wood and construction wood in the areas surrounding these parks, it is appropriate to launch a project to establish green belts around these national parks. However, the lack of information required for setting up such project calls for the prior formulation of a pre- project whose implementation will consist in the conduct of baseline studies and the formulation of a full project proposal. EXECUTING AGENCY DIRECTORATE OF WILDLIFE AND CONSERVATION AREAS (DFAP) /MINFOF COLLABORATING AGENCY --- DURATION 6 MONTHS APPROXIMATE STARTING DATE TO BE DECIDED BUDGET AND FUNDING Source Contribution Local currency SOURCES : in US$ equivalent ITTO $ 86,240 Govn’t of Cameroon $ 13,650 TOTAL $ 99,890 Table of Contents LIST OF ACRONYMS .................................................................................................................................................. 1 PART 1. PRE-PROJECT CONTEXT ......................................................................................................................
    [Show full text]
  • 2011 Impact of Trophy Hunting
    Biological Conservation 144 (2011) 3064–3072 Contents lists available at SciVerse ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/biocon The impact of trophy hunting on lions (Panthera leo) and other large carnivores in the Bénoué Complex, northern Cameroon ⇑ B.M. Croes a, P.J. Funston b, G. Rasmussen c,d, R. Buij a, A. Saleh e, P.N. Tumenta a,f, H.H. de Iongh a, a Institute of Environmental Sciences (CML), Leiden University, PO Box 9518, 2300 RA Leiden, The Netherlands b Department of Nature Conservation, Tshwane University of Technology, Private Bag X680, Pretoria 0002, South Africa c Painted Dog Conservation (PDC), Hwange National Park, Box 72, Dete, Zimbabwe d Wildlife Conservation Research Unit, Department of Zoology, University of Oxford, South Parks Road, Oxford OX1 3PS, UK e Ministry of Fauna and Forests (MINFOF), BP 126 Garoua, Cameroon f Department of Forestry, University of Dschang, Cameroon article info abstract Article history: In West and Central Africa large carnivores have become increasingly rare as a consequence of rapid hab- Received 30 June 2011 itat destruction and lack of resources for protected area management. The Bénoué Complex (23,394 km2) Received in revised form 23 September in northern Cameroon is a regionally critical area for large mammal conservation. In the complex lions 2011 (Panthera leo), leopards (Panthera pardus) and spotted hyenas (Crocuta crocuta) are formally protected Accepted 25 September 2011 in three national parks and 28 hunting zones. Over-hunting may be having a strong additive effect Available online 3 November 2011 precipitating declines in large carnivore numbers across the complex.
    [Show full text]
  • NAPA News from African Protected Areas
    NAPA News from African Protected Areas Nouvelles des Aires Protégées N°66 en Afrique July 2013 What future for lions (Panthera leo) in Waza the tourism industry, lions are fast disappearing from National Park, Cameroon? much of their historical range and are threatened in (directions 4 and 5 of the road map for African PAs) part of their present range. By Dr Pricelia Tumenta Fobuzie, University of Dschang, Cameroon. Protected areas play a key role in the conservation of biodiversity. Cameroon currently has an important network of protected areas, covering 19.2% of the national territory. This is credited to government’s efforts to put in place strategies to conserve the different ecosystems in the country together with the flora and fauna they contain. Waza National Park is one of the best examples of protected areas in Cameroon, situated in the Sudano-sahelian savanna ecosystem in the extreme north region of the country. About one third of Waza National Park falls within the Waza-Logone wetlands making this park a haven for water birds. The mammalian diversity of the park is quite rich including elephant, giraffe, roan antelope, topi, hyena, jackal and the lion. The park is a popular destination for tourists because of its openness and richness in wildlife species. The lion (Panthera leo) is a species of international importance due to its keystone, flagship, cultural and charismatic attributes. Widely distributed in the past, more than 95% of lions have disappeared from the surface of the earth the past c.10, 000 years. The steady and rapid increase in human population with the commensurate increase in demand for living space and resources seems to be the main overriding factor working against many conservation There are presently about 32, 000 lions left in Africa efforts.
    [Show full text]
  • LDPI Working Paper
    Property and Negotiation in Waza National Park Alice Kelly LDPI Working Paper Property and Negotiation in Waza National Park By Alice Kelly Published by: The Land Deal Politics Initiative www.iss.nl/ldpi [email protected] in collaboration with: Institute for Development Studies (IDS) University of Sussex Library Road Brighton, BN1 9RE United Kingdom Tel: +44 1273 606261 Fax: +44 1273 621202 E-mail: [email protected] Website: www.ids.ac.uk Initiatives in Critical Agrarian Studies (ICAS) International Institute of Social Studies (ISS) P.O. Box 29776 2502 LT The Hague The Netherlands Tel: +31 70 426 0664 Fax: +31 70 426 0799 E-mail: [email protected] Website: www.iss.nl/icas The Institute for Poverty, Land and Agrarian Studies (PLAAS) School of Government, Faculty of Economic and Management Sciences University of the Western Cape, Private Bag X17 Bellville 7535, Cape Town South Africa Tel: +27 21 959 3733 Fax: +27 21 959 3732 E-mail: [email protected] Website: www.plaas.org.za The Polson Institute for Global Development Department of Development Sociology Cornell University 133 Warren Hall Ithaca NY 14853 United States of America Tel: +1 607 255-3163 Fax: +1 607 254-2896 E-mail: [email protected] Website: polson.cals.cornell.edu © February 2013 All rights reserved. No part of this publication may be reproduced or transmitted in any form or by any means without prior permission from the publisher and the author. Published with support from the UK Department for International Development (DfID), Atlantic Philanthropies, Inter‐Church Organization for Development Cooperation (ICCO), Ford Foundation and Miserior.
    [Show full text]