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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. -
Western Zambian Sable: Are They a Geographic Extension of the Giant Sable Antelope?
View metadata, citation and similarWestern papers at core.ac.uk Zambian sable: Are they a brought to you by CORE geographic extension of theprovided by Stellenbosch University SUNScholar Repository giant sable antelope? Bettine Jansen van Vuuren1,2*, Terence J. Robinson1, Pedro VazPinto3, Richard Estes4 & Conrad A. Matthee1 1Evolutionary Genomics Group, Department Botany and Zoology, Stellenbosch University, Private Bag X1, Matieland, 7602 South Africa 2Centre for Invasion Biology, Department Botany and Zoology, Stellenbosch University, Private Bag X1, Matieland, 7602 South Africa 3Universidade Catolica de Angola, Rua Nossa Senhora da Muxima, 29 Luanda, Angola 45 Granite Street, Peterborough, NH 03458, U.S.A. Received 5 September 2008. Accepted 21 January 2010 The giant sable (Hippotragus niger variani ) is one of Africa’s most spectacular large antelope. Years of civil unrest in Angola, a highly localized distribution and interbreeding with its congener the roan antelope (H. equinus) has led to this subspecies being considered as critically endangered. Sable antelope occurring ~600 km to the east in western Zambia superficially resemble giant sable in phenotype, prompting speculation in the popular media that the distribution of giant sable may be larger than currently documented. Our aim here was to investigate the evolutionary placement of western Zambian sable using mitochon- drial DNA control region data. Phylogenetic analyses (maximum likelihood and Bayesian analyses) supported the monophyly of H. n. variani (Bayesian posterior probability of >0.95, bootstrap support >80%) and nested the western Zambian sable within H. n. niger. This find- ing was supported by an analysis of molecular variance that discretely grouped western F Zambian sable from giant sable ( ST = 0.645, P = 0.001). -
Central African Republic Giraffe Conservation Status Report February 2020
Country Profile Central African Republic Giraffe Conservation Status Report February 2020 General statistics Size of country: 622,984 km² Size of protected areas / percentage protected area coverage: 13% 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. -
Hippotragus Equinus – Roan Antelope
Hippotragus equinus – Roan Antelope authorities as there may be no significant genetic differences between the two. Many of the Roan Antelope in South Africa are H. e. cottoni or equinus x cottoni (especially on private properties). Assessment Rationale This charismatic antelope exists at low density within the assessment region, occurring in savannah woodlands and grasslands. Currently (2013–2014), there are an observed 333 individuals (210–233 mature) existing on nine formally protected areas within the natural distribution range. Adding privately protected subpopulations and an Cliff & Suretha Dorse estimated 0.8–5% of individuals on wildlife ranches that may be considered wild and free-roaming, yields a total mature population of 218–294 individuals. Most private Regional Red List status (2016) Endangered subpopulations are intensively bred and/or kept in camps C2a(i)+D*†‡ to exclude predators and to facilitate healthcare. Field National Red List status (2004) Vulnerable D1 surveys are required to identify potentially eligible subpopulations that can be included in this assessment. Reasons for change Non-genuine: While there was an historical crash in Kruger National Park New information (KNP) of 90% between 1986 and 1993, the subpopulation Global Red List status (2008) Least Concern has since stabilised at c. 50 individuals. Overall, over the past three generations (1990–2015), based on available TOPS listing (NEMBA) Vulnerable data for nine formally protected areas, there has been a CITES listing None net population reduction of c. 23%, which indicates an ongoing decline but not as severe as the historical Endemic Edge of Range reduction. Further long-term data are needed to more *Watch-list Data †Watch-list Threat ‡Conservation Dependent accurately estimate the national population trend. -
EAZA Antelope & Giraffe
EAZA Antelope & Giraffe TAG Introduction & report on some activities Joint TAG chairs meeting 2016, Omaha Dr. Jens-Ove Heckel Zoo Landau in der Pfalz, Germany EAZA Antelope & Giraffe TAG chair [email protected] EAZA Antelope & Giraffe TAG • Antelope & Giraffe TAG continues as one of the largest and most complex TAGs representing 50 species (and approximately 90 taxa) in EAZA zoos • our remit: try to retain as many species as possible in healthy populations in EAZA collections • currently the TAG holds 11 EEPs and 11 ESBs; 4 species are part of ISBs; the remaining species are monitored (Mon-P, Mon-TAG). Chair Jens-Ove Heckel Landau Vice chair Sander Hofman Antwerp Vice chair (till 11.2015) Tania Gilbert Marwell Vice chair (since 12.2015) Kim Skalborg Simonsen Givskud Sub-group Okapi & Giraffe SG Sander Hofman Antwerp Sub-group Woodland antelope SG Kim Skalborg Simonsen Givskud Sub-group Savannah antelope SG Catrin Hammer Goerlitz Sub-group Aridlands antelope SG Ian Goodwin Marwell (Sub-group) (Mini antelope SG) (Klaus Müller-Schilling) (Hanover) Studbook keepers/Program managers EAZA Antelope & Giraffe TAG meeting 2015, Wroclaw Coordinator Conservation Tania Gilbert Marwell Coordinator Research Eulalia Moreno Almeria Advisor Veterinary Sven Hammer Goerlitz Advisor Genetics Rob Ogden Edinburgh Advisor Population management Laurie Bingaman Lackey USA Advisor Nutrition Marcus Clauss Zuerich Advisor Husbandry n.n. Advisor Education n.n. Regular support and advice also provided by: Exec. Coordinator - Collect. Coordin. & Conserv. Merel Zimmermann EPMAG / Population Management Kristin Leus Population Biologist - Collect. Coordin. & Conserv. Kristine Schad Good links to: IUCN SSC Antelope SG, IUCN Giraffe & Okapi SG/Giraffe Conservation Fdn., other EAZA Ungulate TAGs, BIAZA Hoof stock focus group, AZA Antelope & Giraffe TAG, Sahara Conservation Fund/SSIG etc. -
Kordofan GIRAFFE Giraffe Population in the WBE Western Bénoué Ecosystem, Northern Cameroon
CONSERVATION INITIATIVES KORDOFAN Long-term population monitoring Systematic surveys of the Kordofan GIRAFFE giraffe population in the WBE Western Bénoué Ecosystem, Northern Cameroon At the species level, giraffes are considered Vulnerable on the IUCN Red List; however, the population as a whole has dropped Human-wildlife coexistence substantially in recent decades with less than 80,000 individuals Understand the impact of cattle grazing, mining and poaching within the remaining across Africa. protected areas The subspecies of Kordofan giraffe (Giraffa camelopardalis antiquorum) numbers less than 2000 individuals across West Central Africa and have recently been assessed as Critically Endangered on the IUCN Red List. In addition to their diminishing population size, the Kordofan giraffe inhabits some of the most unstable regions in the world: southern Chad, the Central African Republic, northern Cameroon and northern Democratic Republic of Congo. Conservation of threatened species is difficult under the best of circumstances, but protecting species in areas with significant political and/or socio-economic challenges, or regions that lack enforced laws, is even more difficult. Building capacity The North Region of Cameroon is one of the last strongholds for the charismatic Train eco-guards in wildlife survey species of the Sudanian savanna woodland, including the Kordofan giraffe. In the techniques and use of new technologies heart of this area, the Western Bénoué Ecosystem (WBE) is composed of a UNESCO Biosphere Reserve (Bénoué National Park) and four neighbouring hunting zones. Despite its rich biodiversity, the WBE is faced with several threats, the most critical of which is uncontrolled pastoralism by non-local herders. Overgrazing by cattle can negatively impact large herbivore populations by reducing food abundance. -
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 -
Kordofan Giraffe (Giraffa Camelopardalis Antiquorum), Garamba National Park, Democratic Republic of Congo
Quarterly conservation update – Kordofan giraffe (Giraffa camelopardalis antiquorum), Garamba National Park, Democratic Republic of Congo October-December 2016 Mathias D’haen Czech University of Life Sciences (CULS), Kamýcká 961/129, 165 21 Prague 6-Suchdol, Czech Republic Introduction Garamba National Park (GNP) in the Democratic Republic of Congo (DRC) was first established in 1938 by virtue of its uniqueness, one of the first Parks in Africa. Throughout its long history the Park was initially made famous with the world’s only elephant domestication program, coupled with its high numbers of elephant and buffalo, and home to the world’s last northern white rhino (Ceratotherium simum cottoni) population. The Park was designated a UNESCO World Heritage site in 1980 and on the List of World Heritage in Danger in 1996. Sadly, the Park’s infamy has increased through losing the last northern white rhino, and being plagued by numerous groups of rebels, in particular the Lord’s Resistance Army. In fact, the Park, being nestled in the far north-eastern corner of the country, is writing history every day again, not because of the countries’ own destabilised politics (the 2000km between the Park and the countries’ capital creates an efficient buffer), but because of its war against armed militia coming from within and neighbouring countries. GNP, and its adjacent Hunting Reserves, are also home to DRC’s only population of giraffe, historically named ‘Congo giraffe’ (Amube et al. 2009; De Merode et al. 2000; East 1999) but reclassified as they are genetically identical to other Kordofan giraffe (Giraffa camelopardalis antiquorum) across Central Africa (Fennessy et al. -
Common Eland
Tragelaphus oryx – Common Eland recognised, though their validity has been in dispute (Thouless 2013): Tragelaphus o. livingstonii (Sclater 1864; Livingstone's Eland): also called kaufmanni, niediecki, selousi and triangularis. It is found in the Central Zambezian Miombo woodlands i.e. south- central Africa (Angola, Zambia, Democratic Republic of the Congo, Zimbabwe, Mozambique and Malawi). Livingstone's Eland has a brown pelt with up to twelve stripes. Tragelaphus o. oryx (Pallas 1766; Cape Eland): also called alces, barbatus, canna and oreas. This subspecies is found south of the Zambezi river (South Africa, Botswana and Namibia). The fur is tawny, and adults lose their stripes. Regional Red List status (2016) Least Concern Tragelaphus o. pattersonianus (Lydekker 1906; East National Red List status (2004) Least Concern African Eland or Patterson's Eland): also called Reasons for change No change billingae. It is found in east Africa extending into the Somali arid areas, hence its common name. Its coat Global Red List status (2008) Least concern can have up to 12 stripes. TOPS listing (NEMBA) None Tragelaphus o. oryx occurs throughout the larger part of South Africa, but the far northern Limpopo Province CITES listing None bordering Zimbabwe is regarded as a transitional zone Endemic No between T. o. oryx and T. o. livingstonii or an area where they overlap. This argues the case that they should rather During drought conditions Eland roam extensively be described as ecotypes (in ecotypes, it is common for in order to meet forage and water requirements; in continuous, gradual geographic variation to impose the southern Kalahari during abnormally dry analogous phenotypic and/or genetic variation; this conditions, Eland were found to cover more than situation is called cline.). -
Copy of Roan Antelope Project
Roan Antelope Project Roan Antelope (Hippotragus equines) are Africa’s second largest antelope after the eland. Historically they were widely distributed in small herds over a large part of Swaziland. They became locally extinct when Swaziland’s very last freeranging roan antelope was poached at Maphiveni in 1961. Roan have become extremely rare across their entire natural range. The reason for their demise is probably a combination of factors which include poaching, diminishing range, stressinduced disease, predation, and competition by high density species. A small group of 4 roan (3 females, 1 bull) reintroduced to Mkhaya from Namibia perished because, we now believe, the animals were naïve to tickborne diseases in a densely tick hostile environment where mortalities overwhelmed recruitment. It is likely that the tickborne Theileria hippotragi disease played a large role. Theileria is a protozoal disease which is fatal to roan and sable antelope. The expertise of Dr Johan Steyl under the supervision of Prof. Leon Prozesky of the Onderstepoort Veterinary Faculty of the University of Pretoria has helped enormously with this project. The vector is the redlegged tick Rhipicephalus evertsi, which is abundant in Swaziland, but little was known about its impact on wildlife at the time of the Namibian introduction. Our Roan Antelope project got underway in 2002 after Dr Hamish Currie, founder and chief executive of Back to Africa, very generously committed to assist in restoring a viable population of roan antelope to Swaziland. Dr Hamish Currie wisely harnessed the expertise of Dr Johan Steyl whose guidance has without doubt been pivotal to the success of the project so far. -
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. -
Transboundary Species Project
TRANSBOUNDARY SPECIES PROJECT ROAN, SABLE AND TSESSEBE Rowan B. Martin Species Report for Roan, Sable and Tsessebe in support of The Transboundary Mammal Project of the Ministry of Environment and Tourism, Namibia facilitated by The Namibia Nature Foundation and World Wildlife Fund Living in a Finite Environment (LIFE) Programme Cover picture adapted from the illustrations by Clare Abbott in The Mammals of the Southern African Subregion by Reay H.N. Smithers Published by the University of Pretoria Republic of South Africa 1983 Transboundary Species Project – Background Study Roan, Sable and Tsessebe CONTENTS 1. BIOLOGICAL INFORMATION ...................................... 1 a. Taxonomy ..................................................... 1 b. Physical description .............................................. 3 c. Habitat ....................................................... 6 d. Reproduction and Population Dynamics ............................. 12 e. Distribution ................................................... 14 f. Numbers ..................................................... 24 g. Behaviour .................................................... 38 h. Limiting Factors ............................................... 40 2. SIGNIFICANCE OF THE THREE SPECIES ........................... 43 a. Conservation Significance ........................................ 43 b. Economic Significance ........................................... 44 3. STAKEHOLDING ................................................. 48 a. Stakeholders .................................................