Serengeti: Nature's Living Laboratory Transcript
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Serengeti National Park
Serengeti • National Park A Guide Published by Tanzania National Parks Illustrated by Eliot Noyes ~~J /?ookH<~t:t;~ 2:J . /1.). lf31 SERENGETI NATIONAL PARK A Guide to your increased enjoyment As the Serengeti National Park is nearly as big as Kuwait or Northern Ireland no-one, in a single visit, can hope to see Introduction more than a small part of it. If time is limited a trip round The Serengeti National Park covers a very large area : the Seronera valley, with opportunities to see lion and leopard, 13,000 square kilometres of country stretching from the edge is probably the most enjoyable. of the Ngorongoro Conservation Unit in the south to the Kenya border in the north, and from the shores of Lake Victoria in the If more time is available journeys can be made farther afield, west to the Loliondo Game Controlled Area in the east. depending upon the season of the year and the whereabouts of The name "Serengeti" is derived from the Maasai language the wildlife. but has undergone various changes. In Maasai the name would be "Siringet" meaning "an extended area" but English has Visitors are welcome to get out of their cars in open areas, but replaced the i's with e's and Swahili has added a final i. should not do so near thick cover, as potentially dangerous For all its size, the Serengeti is not, of itself, a complete animals may be nearby. ecological unit, despite efforts of conservationists to make it so. Much of the wildlife· which inhabits the area moves freely across Please remember that travelling in the Park between the hours the Park boundaries at certain seasons of the year in search of 7 p.m. -
Influence of Common Eland (Taurotragus Oryx) Meat Composition on Its Further Technological Processing
CZECH UNIVERSITY OF LIFE SCIENCES PRAGUE Faculty of Tropical AgriSciences Department of Animal Science and Food Processing Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing DISSERTATION THESIS Prague 2018 Author: Supervisor: Ing. et Ing. Petr Kolbábek prof. MVDr. Daniela Lukešová, CSc. Co-supervisors: Ing. Radim Kotrba, Ph.D. Ing. Ludmila Prokůpková, Ph.D. Declaration I hereby declare that I have done this thesis entitled “Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing” independently, all texts in this thesis are original, and all the sources have been quoted and acknowledged by means of complete references and according to Citation rules of the FTA. In Prague 5th October 2018 ………..………………… Acknowledgements I would like to express my deep gratitude to prof. MVDr. Daniela Lukešová CSc., Ing. Radim Kotrba, Ph.D. and Ing. Ludmila Prokůpková, Ph.D., and doc. Ing. Lenka Kouřimská, Ph.D., my research supervisors, for their patient guidance, enthusiastic encouragement and useful critiques of this research work. I am very gratefull to Ing. Petra Maxová and Ing. Eva Kůtová for their valuable help during the research. I am also gratefull to Mr. Petr Beluš, who works as a keeper of elands in Lány, Mrs. Blanka Dvořáková, technician in the laboratory of meat science. My deep acknowledgement belongs to Ing. Radek Stibor and Mr. Josef Hora, skilled butchers from the slaughterhouse in Prague – Uhříněves and to JUDr. Pavel Jirkovský, expert marksman, who shot the animals. I am very gratefull to the experts from the Natura Food Additives, joint-stock company and from the Alimpex-maso, Inc. -
Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions
Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions An Analysis of Illegal Hunting of Wildlife in Serengeti National Park, Tanzania Ken Campbell, Valerie Nelson and Martin Loibooki June 2001 Main Report This report should be cited as: Campbell, K. L. I., Nelson, V. and Loibooki, M. (2001). Sustainable use of wildland resources, ecological, economic and social interactions: An analysis of illegal hunting of wildlife in Serengeti National Park, Tanzania. Department for International Development (DFID) Animal Health Programme and Livestock Production Programmes, Final Technical Report, Project R7050. Natural Resources Institute (NRI), Chatham, Kent, UK. 56 pp. 2 Sustainable Use of Wildland Resources: Ecological, Economic and Social Interactions An Analysis of Illegal Hunting of wildlife in Serengeti National Park, Tanzania FINAL TECHNICAL REPORT, 2001 DFID Animal Health and Livestock Production Programmes, Project R7050 Ken Campbell1, Valerie Nelson2 Natural Resources Institute, University of Greenwich, Chatham, ME4 4TB, UK and Martin Loibooki Tanzania National Parks, P.O. Box 3134, Arusha, Tanzania Executive Summary A common problem for protected area managers is illegal or unsustainable extraction of natural resources. Similarly, lack of access to an often decreasing resource base may also be a problem for rural communities living adjacent to protected areas. In Tanzania, illegal hunting of both resident and migratory wildlife is a significant problem for the management of Serengeti National Park. Poaching has already reduced populations of resident wildlife, whilst over-harvesting of the migratory herbivores may ultimately threaten the integrity of the Serengeti ecosystem. Reduced wildlife populations may in turn undermine local livelihoods that depend partly on this resource. This project examined illegal hunting from the twin perspectives of conservation and the livelihoods of people surrounding the protected area. -
Serengeti National Park Tanzania
SERENGETI NATIONAL PARK TANZANIA Twice a year ungulate herds of unrivalled size pour across the immense savanna plains of Serengeti on their annual migrations between grazing grounds. The river of wildebeests, zebras and gazelles, closely followed by predators are a sight from another age: one of the most impressive in the world. COUNTRY Tanzania NAME Serengeti National Park NATURAL WORLD HERITAGE SITE 1981: Inscribed on the World Heritage List under Natural Criteria vii and x. STATEMENT OF OUTSTANDING UNIVERSAL VALUE [pending] INTERNATIONAL DESIGNATION 1981: Serengeti-Ngorongoro recognised as a Biosphere Reserve under the UNESCO Man & Biosphere Programme (2,305,100 ha, 1,476,300 ha being in Serengeti National Park). IUCN MANAGEMENT CATEGORY II National Park BIOGEOGRAPHICAL PROVINCE East African Woodland/Savanna (3.05.04) GEOGRAPHICAL LOCATION In the far north of Tanzania 200 km west of Arusha, adjoining the Ngorongoro Conservation Area, between 1° 30' to 3° 20'S and 34° 00' to 35°15'E. DATES AND HISTORY OF ESTABLISHMENT 1929: Serengeti Game Reserve declared (228,600 ha) to preserve lions, previously seen as vermin; 1940: Declared a Protected Area; 1951: Serengeti National Park created, including Ngorongoro; boundaries were modified in 1959; 1981: Recognised as part of the Serengeti-Ngorongoro UNESCO Biosphere Reserve. LAND TENURE State, in Mara, Arusha and Shinyanga provinces. Administered by the Tanzanian National Parks Authority. AREA 1,476,300ha. It is contiguous in the southeast with Ngorongoro Conservation Area (809,440ha), in the southwest with Maswa Game Reserve (220,000ha), in the west with the Ikorongo-Grumeti Game Reserves (500,000ha), in the north with the Maasai-Mara National Reserve (151,000ha) in Kenya and in the northeast with the Loliondo Game Controlled Area (400,000ha). -
Connochaetes Gnou – Black Wildebeest
Connochaetes gnou – Black Wildebeest Blue Wildebeest (C. taurinus) (Grobler et al. 2005 and ongoing work at the University of the Free State and the National Zoological Gardens), which is most likely due to the historic bottlenecks experienced by C. gnou in the late 1800s. The evolution of a distinct southern endemic Black Wildebeest in the Pleistocene was associated with, and possibly driven by, a shift towards a more specialised kind of territorial breeding behaviour, which can only function in open habitat. Thus, the evolution of the Black Wildebeest was directly associated with the emergence of Highveld-type open grasslands in the central interior of South Africa (Ackermann et al. 2010). Andre Botha Assessment Rationale Regional Red List status (2016) Least Concern*† This is an endemic species occurring in open grasslands in the central interior of the assessment region. There are National Red List status (2004) Least Concern at least an estimated 16,260 individuals (counts Reasons for change No change conducted between 2012 and 2015) on protected areas across the Free State, Gauteng, North West, Northern Global Red List status (2008) Least Concern Cape, Eastern Cape, Mpumalanga and KwaZulu-Natal TOPS listing (NEMBA) (2007) Protected (KZN) provinces (mostly within the natural distribution range). This yields a total mature population size of 9,765– CITES listing None 11,382 (using a 60–70% mature population structure). This Endemic Yes is an underestimate as there are many more subpopulations on wildlife ranches for which comprehensive data are *Watch-list Threat †Conservation Dependent unavailable. Most subpopulations in protected areas are stable or increasing. -
IUCN Briefing Paper
BRIEFING PAPER September 2016 Contact information updated April 2019 Informing decisions on trophy hunting A Briefing Paper regarding issues to be taken into account when considering restriction of imports of hunting trophies For more information: SUMMARY Dilys Roe Trophy hunting is currently the subject of intense debate, with moves IUCN CEESP/SSC Sustainable Use at various levels to end or restrict it, including through increased bans and Livelihoods or restrictions on carriage or import of trophies. This paper seeks to inform SpecialistGroup these discussions. [email protected] Patricia Cremona IUCN Global Species (such as large antlers), and overlaps with widely practiced hunting for meat. Programme It is clear that there have been, and continue to be, cases of poorly conducted [email protected] and poorly regulated hunting. While “Cecil the Lion” is perhaps the most highly publicised controversial case, there are examples of weak governance, corruption, lack of transparency, excessive quotas, illegal hunting, poor monitoring and other problems in a number of countries. This poor practice requires urgent action and reform. However, legal, well regulated trophy Habitat loss and degradation is a primary hunting programmes can, and do, play driver of declines in populations an important role in delivering benefits of terrestrial species. Demographic change for both wildlife conservation and for and corresponding demands for land for the livelihoods and wellbeing of indigenous development are increasing in biodiversity- and local communities living with wildlife. rich parts of the globe, exacerbating this pressure on wildlife and making the need for viable conservation incentives more urgent. © James Warwick RECOMMENDATIONS and the rights and livelihoods of indigenous and local communities, IUCN calls on relevant decision- makers at all levels to ensure that any decisions that could restrict or end trophy hunting programmes: i. -
The Effect of Species Associations on the Diversity and Coexistence of African Ungulates
The effect of species associations on the diversity and coexistence of African ungulates. By Nancy Barker For Professor Kolasa BIO306H1 – Tropical Ecology University of Toronto Wednesday, August 24th, 2005 Abstract: The effects of species associations on species diversity and coexistence were investigated in East Africa. The frequency and group sizes of African ungulates were observed and analyzed to determine for differences in species associations based on their density and distribution, as well as their associations with other species. Associations between species were determined to be nonrandom and seen to affect the demographics of associating herds. Such associations mirrored in other studies were shown to be the result of interspecific competition, habitat preferences and predation pressure which increases the potential for coexistence between species. This suggests a potentially important role in the regulation of species diversity by ecological dynamics in species rich communities. In the face of today’s biodiversity crisis, such understanding of species associations and how they are regulated may have huge implications for conservation. Introduction: known with the famous Darwin’s finches of the Galapagos Islands. However, there are many other Sympatric coexistence of organisms within a guilds with what seems to be extensive community poses several questions for ecologists. overlapping in their resources, such as the grazing High levels of species association occur with high herds in Africa which eat common and widely species packing, as is seen within the Selous game dispersed foods. Sinclair (Sinclair, 1979 as cited in reserve of Tanzania in east Africa. Sinclair (1985) Sinclair, 1985) has found that this seemingly notes that mixed herds are frequently seen in east extensive overlap among these herds have also Africa and Connor and Simberloff (1979) have undergone niche separation. -
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.). -
Mammal Species Richness at a Catena and Nearby Waterholes During a Drought, Kruger National Park, South Africa
diversity Article Mammal Species Richness at a Catena and Nearby Waterholes during a Drought, Kruger National Park, South Africa Beanélri B. Janecke Animal, Wildlife & Grassland Sciences, University of the Free State, 205 Nelson Mandela Road, Park West, Bloemfontein 9301, South Africa; [email protected]; Tel.: +27-51-401-9030 Abstract: Catenas are undulating hillslopes on a granite geology characterised by different soil types that create an environmental gradient from crest to bottom. The main aim was to determine mammal species (>mongoose) present on one catenal slope and its waterholes and group them by feeding guild and body size. Species richness was highest at waterholes (21 species), followed by midslope (19) and sodic patch (16) on the catena. Small differences observed in species presence between zones and waterholes and between survey periods were not significant (p = 0.5267 and p = 0.9139). In total, 33 species were observed with camera traps: 18 herbivore species, 10 carnivores, two insectivores and three omnivores. Eight small mammal species, two dwarf antelopes, 11 medium, six large and six mega-sized mammals were observed. Some species might not have been recorded because of drought, seasonal movement or because they travelled outside the view of cameras. Mammal presence is determined by food availability and accessibility, space, competition, distance to water, habitat preferences, predators, body size, social behaviour, bound to territories, etc. The variety in body size and feeding guilds possibly indicates a functioning catenal ecosystem. This knowledge can be beneficial in monitoring and conservation of species in the park. Keywords: catena ecosystem; ephemeral mud wallows; habitat use; mammal variety; Skukuza area; Citation: Janecke, B.B. -
First Enhancing Our Heritage Assessment at Ngorongoro Conservation Area
2010-2011 First Enhancing our Heritage Assessment at Ngorongoro Conservation Area i Compiled by: Krissie Clark and Wayne Lotter of the PAMS Foundation, Dr Victor Runyoro, Hillary Mushi, Robert Mande, Henry Sweddy and Donatus Gadiye of Ngorongoro Conservation Area Authority (NCAA), and Sue Stolton (Equilibrium Research) Acknowledgements: The authors would like to thank the Chief Conservator, Mr. Amiyo Amiyo, Dr Justice Muumba, NCAA, UNESCO and all Workshop Participants Photographs by: Krissie Clark & Wayne Lotter i Table of Contents Introduction to the project area, Ngorongoro Conservation Area ........................................................................................................ 1 Project Background ............................................................................................................................................................................. 1 The Project Workbook and Tool Kits............................................................................................................................................... 2 How the Project was carried out .......................................................................................................................................................... 3 Compilation of EoH Project Report...................................................................................................................................................... 6 Tools completed during the NCA assessment ................................................................................................................................... -
Tanzania Wildlife Migration Safari Specially Designed for the Cincinnati Zoo
TANZANIA WILDLIFE MIGRATION SAFARI SPECIALLY DESIGNED FOR THE CINCINNATI ZOO 13 - DAY WILDLIFE SAFARI DEPARTS JUNE, 19, 2011 ESCORTED BY DOUG FEIST, $4775 PER PERSON, DOUBLE OCCUPANCY ALL INCLUSIVE FROM THE KILIMANJARO AIRPORT TANZANIA WILDLIFE MIGRATION SAFARI SPECIALLY DESIGNED FOR THE CINCINNATI ZOO DESTINATION: Tanzania TRIP TO BE OPERATED: June 19 – July 1, 2011 NUMBER OF DAYS: 13 NUMBER OF PASSENGERS: 10 DEPARTURE CITY: Arusha, Tanzania COST: $4775 PER PERSON, DOUBLE OCCUPANCY SINGLE SUPPLEMENT: $450 Price includes: full board & accommodations while in Tanzania, park fees, all activities at each location as detailed in the safari itinerary, airport transfers, a maximum of 6 passengers per 4x4 safari vehicle, tips for porters and waiters and mineral water in the vehicles during game drives and temporary Flying Doctor’s membership. The price also includes informational booklets, luggage tags, passport wallets, and the services of World Discovery Safaris. Please see the INCLUDED and NOT INCLUDED statements in the Safari Registration form. WILDLIFE SAFARI TO TANZANIA About this safari: This wildlife safari is specifically designed to take full advantage of the wildlife migration and visit a variety of East Africa’s wildlife habitats, each with its unique community of birds and mammals, scenic attractions, and cultural components. Your means of transportation is in customized 4-wheel drive safari vehicles with a guaranteed window seat and access to the roof hatch for all participants. Physical activities: The pace of this safari is “moderate” and should not be excessively demanding for most. Stays at most locations are of more than one night, which allows time to experience the place, relax and even sit out a game drive or two. -
Final Project Completion Report
CEPF SMALL GRANT FINAL PROJECT COMPLETION REPORT Organization Legal Name: Indigenous Heartland Organization (IHO) Developing tools and methods for community participation to protect the Ngorongoro crater rim from inappropriate tourism Project Title: development Date of Report: June 2017 Report Author and Contact Naini Oleshweel Tel+ 255 786 662 500 Information Email. [email protected] CEPF Region: THE EASTERN AFROMONTANE BIODIVERSITY HOTSPOT Strategic Direction: Strategic Direction 2; to improve the protection and management of the network of KBAs (Key Biodiversity Areas / high conservation value areas) throughout the hotspot Grant Amount: 10,000 USD Project Dates: 1st October 2015 to 30th September 2016, and extended on request to April 2017 Implementation Partners for this Project (please explain the level of involvement for each partner): The Ngorongoro Conservation Area Authority (NCAA) . Geographical Coordinates: 3o 15‟S, 35o 30‟E . Date of Inscription on the World Heritage List: 1979 as Natural World Heritage and 2010 as Mixed World Heritage Site The Ngorongoro Conservation Area (NCA) covers 8,292 square kilometres. It is one of the three divisions that comprise Ngorongoro District in Arusha Region. NCA was established in 1959 by the NCA Ordinance No 413 of 1959 as a multiple land use area, designated to promote the conservation of natural resources, safeguard the interests of NCA indigenous residents and promote tourism. NCA is a unique protected area in the whole of Africa where conservation of natural resources is integrated with human development. The main features of the NCA include the Ngorongoro Crater, the Serengeti Plains that support about 2.0 million migratory wildlife species of the Serengeti-Mara ecosystem (TAWIRI, 2003) and the catchment forest; the Northern Highland Forest Reserve (NHFR) known as „Entim Olturot‟ in Maa language.