Annual Report
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Forest Cover and Change for the Eastern Arc Mountains and Coastal Forests of Tanzania and Kenya Circa 2000 to Circa 2010
Forest cover and change for the Eastern Arc Mountains and Coastal Forests of Tanzania and Kenya circa 2000 to circa 2010 Final report Karyn Tabor, Japhet J. Kashaigili, Boniface Mbilinyi, and Timothy M. Wright Table of Contents Introduction .................................................................................................................................................. 2 1.1 Biodiversity Values of the Eastern Arc Mountains and Coastal Forests ....................................... 2 1.2 The threats to the forests ............................................................................................................. 5 1.3 Trends in deforestation ................................................................................................................. 6 1.4 The importance of monitoring ...................................................................................................... 8 Methods ........................................................................................................................................................ 8 2.1 study area ............................................................................................................................................ 8 2.1 Mapping methodology ........................................................................................................................ 8 2.3 Habitat change statistics ..................................................................................................................... 9 2.4 Map validation -
Evaluating Support for Rangeland‐Restoration Practices by Rural Somalis
Animal Conservation. Print ISSN 1367-9430 Evaluating support for rangeland-restoration practices by rural Somalis: an unlikely win-win for local livelihoods and hirola antelope? A. H. Ali1,2,3 ,R.Amin4, J. S. Evans1,5, M. Fischer6, A. T. Ford7, A. Kibara3 & J. R. Goheen1 1 Department of Zoology and Physiology, University of Wyoming, Laramie, WY, USA 2 National Museums of Kenya, Nairobi, Kenya 3 Hirola Conservation Programme, Garissa, Kenya 4 Conservation Programmes, Zoological Society of London, London, UK 5 The Nature Conservancy, Fort Collins, CO, USA 6 Center for Conservation in the Horn of Africa, St. Louis Zoo, St. Louis, MO, USA 7 Department of Integrative Biology, University of Guelph, Guelph, ON, Canada Keywords Abstract Beatragus hunteri; elephant; endangered species; habitat degradation; rangeland; In developing countries, governments often lack the authority and resources to restoration; tree encroachment; antelope. implement conservation outside of protected areas. In such situations, the integra- tion of conservation with local livelihoods is crucial to species recovery and rein- Correspondence troduction efforts. The hirola Beatragus hunteri is the world’s most endangered Abdullahi H. Ali, Department of Zoology and antelope, with a population of <500 individuals that is restricted to <5% of its his- Physiology, University of Wyoming, Laramie, torical geographic range on the Kenya–Somali border. Long-term hirola declines WY, USA. have been attributed to a combination of disease and rangeland degradation. Tree Email: [email protected] encroachment—driven by some combination of extirpation of elephants, overgraz- ing by livestock, and perhaps fire suppression—is at least partly responsible for Editor: Darren Evans habitat loss and the decline of contemporary populations. -
Isolation of Tick and Mosquito-Borne Arboviruses from Ticks Sampled from Livestock and Wild Animal Hosts in Ijara District, Kenya
VECTOR-BORNE AND ZOONOTIC DISEASES Volume 13, Number X, 2013 ORIGINAL ARTICLE ª Mary Ann Liebert, Inc. DOI: 10.1089/vbz.2012.1190 Isolation of Tick and Mosquito-Borne Arboviruses from Ticks Sampled from Livestock and Wild Animal Hosts in Ijara District, Kenya Olivia Wesula Lwande,1,2 Joel Lutomiah,3 Vincent Obanda,4 Francis Gakuya,4 James Mutisya,3 Francis Mulwa,1 George Michuki,5 Edith Chepkorir,1 Anne Fischer,6 Marietjie Venter,2 and Rosemary Sang1,3 Abstract Tick-borne viruses infect humans through the bite of infected ticks during opportunistic feeding or through crushing of ticks by hand and, in some instances, through contact with infected viremic animals. The Ijara District, an arid to semiarid region in northern Kenya, is home to a pastoralist community for whom livestock keeping is a way of life. Part of the Ijara District lies within the boundaries of a Kenya Wildlife Service–protected conservation area. Arbovirus activity among mosquitoes, animals, and humans is reported in the region, mainly because prevailing conditions necessitate that people continuously move their animals in search of pasture, bringing them in contact with ongoing arbovirus transmission cycles. To identify the tick-borne viruses circulating among these communities, we analyzed ticks sampled from diverse animal hosts. A total of 10,488 ticks were sampled from both wildlife and livestock hosts and processed in 1520 pools of up to eight ticks per pool. The sampled ticks were classified to species, processed for virus screening by cell culture using Vero cells and RT-PCR (in the case of Hyalomma species), followed by amplicon sequencing. -
Biodiversity in Sub-Saharan Africa and Its Islands Conservation, Management and Sustainable Use
Biodiversity in Sub-Saharan Africa and its Islands Conservation, Management and Sustainable Use Occasional Papers of the IUCN Species Survival Commission No. 6 IUCN - The World Conservation Union IUCN Species Survival Commission Role of the SSC The Species Survival Commission (SSC) is IUCN's primary source of the 4. To provide advice, information, and expertise to the Secretariat of the scientific and technical information required for the maintenance of biologi- Convention on International Trade in Endangered Species of Wild Fauna cal diversity through the conservation of endangered and vulnerable species and Flora (CITES) and other international agreements affecting conser- of fauna and flora, whilst recommending and promoting measures for their vation of species or biological diversity. conservation, and for the management of other species of conservation con- cern. Its objective is to mobilize action to prevent the extinction of species, 5. To carry out specific tasks on behalf of the Union, including: sub-species and discrete populations of fauna and flora, thereby not only maintaining biological diversity but improving the status of endangered and • coordination of a programme of activities for the conservation of bio- vulnerable species. logical diversity within the framework of the IUCN Conservation Programme. Objectives of the SSC • promotion of the maintenance of biological diversity by monitoring 1. To participate in the further development, promotion and implementation the status of species and populations of conservation concern. of the World Conservation Strategy; to advise on the development of IUCN's Conservation Programme; to support the implementation of the • development and review of conservation action plans and priorities Programme' and to assist in the development, screening, and monitoring for species and their populations. -
Ali's Dissertation, 2016
To the University of Wyoming: The members of the Committee approve the dissertation of Abdullahi H. Ali presented on 4/13/2016. Jacob R. Goheeen, Chairperson Jeffrey L. Beck, External Department Member Matthew J. Kauffman Anna D. Chalfoun David McDonald APPROVED: Dr. Bob Hall: Director, Program In Ecology. Paula Lutz: College Dean Ali, Abdullahi H., Range Collapse, Demography and Conservation of the Critically Endangered Hirola Antelope in Kenya., Ph.D., Program in Ecology, May, 2016. The hirola (Beatragus hunteri) is one of the rarest antelopes on Earth, with a global population size of ca. 500 individuals restricted to 1500 km2 on the Kenya-Somalia border. Hirola has exhibited ongoing declines since the 1970s while the remaining populations occur almost solely on pastoral lands with no formal protection. Because of historical and political instability in the hirola’s native range, it has been difficult to clearly identify the reasons underlying hirola declines. Like many other globally endangered species, it is likely that more than one factor underlies the hirola problem. Therefore, I investigated, 1) the role of predation and range degradation in driving hirola declines, 2) mechanisms responsible for hirola range collapse and landscape change within hirola historical range, and 3) identified socially- acceptable strategies for habitat restoration and hirola recovery. I have used a combination of GPS telemetry, analysis of long-term satellite imagery, a large-scale predator exclusion zone, and structured questionnaires to address my objectives. Understanding the impacts of these factors can help determine the next steps necessary to maximize the chances of hirola persistence in the future. -
Ijara District Environment Action Plan 2009-2013
REPUBLIC OF KENYA MINISTRY OF ENVIRONMENT AND MINERAL RESOURCES IJARA DISTRICT ENVIRONMENT ACTIONi PLAN 2009-2013 EXECUTIVE SUMMARY The Environmental Management and Coordination Act (EMCA) 1999 provides for the preparation of District Environment Action Plans every five years. This is the first District Environment Action Plan (DEAP) for Ijara district. Preparation of this DEAP was done through a participatory process involving the civil society, private and public sectors. The document has incorporated salient issues from the divisions and it highlights priority themes and activities for the district towards attaining sustainable development. It is divided into eight chapters. Chapter one covers the preamble that highlights provisions for environmental planning as provided for under EMCA, Environmental Acton Planning process that discusses the methodology used in preparation of the DEAP. It also stipulates objectives, scope of this DEAP and challenges for environmental management in the district. It further describes district profile, climate and physical features, population size and distribution and social economic characteristics. Chapter two discusses the district’s environment and natural resources such as soils; land and land use changes; agriculture, livestock and fisheries; water sources; forest and wildlife resources and Biodiversity conservation. Chapter three addresses the human settlements and infrastructure. It covers human settlements and planning; human and environmental health; pollution and wastes generated from human settlements; communication networks; social economic services and infrastructure and energy supply. Chapter four discusses industry trade and services in the district. It highlights major industrial sector that covers agro-based industries, engineering, chemical and mineral industries; trade; service sector; tourism sector; mining and quarrying. Chapter five discusses environmental hazards and disasters. -
Conservation Outcomes Eastern Arc Mountains and Coastal Forests O U
Nairobi Arawale SOMALIA Conservation Outcomes Machakos Eastern Arc Mountains and Coastal Forests The CEPF Niche for Investment Boni National Reserve 20 0 20 40 60 80 100 40°E Boni Forest kilometers landscapes, representing discrete units along an ecological The five sites receiving more focused attention through The Critical Ecosystem Partnership Fund (CEPF) ecosystem Bondeni scale: 1/1,000,000 profile and five- year investment strategy for the Eastern Arc continuum, using a data-driven process and standardized Strategic Directions 1 and 2 are: Tana River Forests, Taita Lunghi projection: Lamberts Equal Area Azmuthial Hills, East Usambara Mountains, Udzungwa Mountains, and 38° east longitude 7° south latitude Mountains and Coastal Forests of Tanzania and Kenya was criteria. Species outcomes aim to avoid extinctions, and the developed based on stakeholder workshops and analyses by primary set of targets for species outcomes are those species Jozani National Park. The strategic directions that focus on a consortium of locally based conservation organizations that are globally threatened (Critically Endangered, these sites will aim to 1) increase the ability of local Dodori area of CEPF investment Biodiversity hotspots are regions coordinated by the International Centre of Insect Physiology Endangered and Vulnerable) according to the IUCN Red List. populations to benefit from and contribute to biodiversity Tana that harbor especially high conservation and 2) restore and increase connectivity among River and Ecology and Conservation International. Prima numbers of endemic species In the Eastern Arc Mountains and Coastal Forests, a total of fragmented forest patches in the hotspot. See the ecosystem te Kiunga Marine and, at the same time, have 333 species representing five taxonomic groups (mammals, profile for a full listing of the strategic directions. -
Management Effectiveness, Governance, and Social
Management Effectiveness, Governance, and Social Assessments of Protected and Conserved Areas in Eastern and Southern Africa A rapid inventory and analysis to support the BIOPAMA programme and partners August, 2019 The designation of geographical entities in this book, and the presentation of the material, do not imply the expression of any opinion whatsoever on the part of IUCN concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. This publication has been produced with support of the 11th EDF and does not necessarily reflect the views of European Union nor of the ACP Group of States. The views expressed in this publication do not necessarily reflect those of IUCN. Published by:BIOPAMA Programme, IUCN ESARO Copyright: © 2019 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorised without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale or other commercial purposes is prohibited without prior written permission of the copyright holder. Citation: Campese, J. & Sulle, E. (2019). Management Effectiveness, Governance, and Social Assessments of Protected and Conserved Areas in Eastern and Southern Africa: A rapid inventory and analysis to support the BIOPAMA programme and partners. BIOPAMA, IUCN ESARO. Layout by PENROSE CDB Photos: Christine Mentzel, free -
Class G Tables of Geographic Cutter Numbers: Maps -- by Region Or Country -- Eastern Hemisphere -- Africa
G8202 AFRICA. REGIONS, NATURAL FEATURES, ETC. G8202 .C5 Chad, Lake .N5 Nile River .N9 Nyasa, Lake .R8 Ruzizi River .S2 Sahara .S9 Sudan [Region] .T3 Tanganyika, Lake .T5 Tibesti Mountains .Z3 Zambezi River 2717 G8222 NORTH AFRICA. REGIONS, NATURAL FEATURES, G8222 ETC. .A8 Atlas Mountains 2718 G8232 MOROCCO. REGIONS, NATURAL FEATURES, ETC. G8232 .A5 Anti-Atlas Mountains .B3 Beni Amir .B4 Beni Mhammed .C5 Chaouia region .C6 Coasts .D7 Dra region .F48 Fezouata .G4 Gharb Plain .H5 High Atlas Mountains .I3 Ifni .K4 Kert Wadi .K82 Ktaoua .M5 Middle Atlas Mountains .M6 Mogador Bay .R5 Rif Mountains .S2 Sais Plain .S38 Sebou River .S4 Sehoul Forest .S59 Sidi Yahia az Za region .T2 Tafilalt .T27 Tangier, Bay of .T3 Tangier Peninsula .T47 Ternata .T6 Toubkal Mountain 2719 G8233 MOROCCO. PROVINCES G8233 .A2 Agadir .A3 Al-Homina .A4 Al-Jadida .B3 Beni-Mellal .F4 Fès .K6 Khouribga .K8 Ksar-es-Souk .M2 Marrakech .M4 Meknès .N2 Nador .O8 Ouarzazate .O9 Oujda .R2 Rabat .S2 Safi .S5 Settat .T2 Tangier Including the International Zone .T25 Tarfaya .T4 Taza .T5 Tetuan 2720 G8234 MOROCCO. CITIES AND TOWNS, ETC. G8234 .A2 Agadir .A3 Alcazarquivir .A5 Amizmiz .A7 Arzila .A75 Asilah .A8 Azemmour .A9 Azrou .B2 Ben Ahmet .B35 Ben Slimane .B37 Beni Mellal .B4 Berkane .B52 Berrechid .B6 Boujad .C3 Casablanca .C4 Ceuta .C5 Checkaouene [Tétouan] .D4 Demnate .E7 Erfond .E8 Essaouira .F3 Fedhala .F4 Fès .F5 Figurg .G8 Guercif .H3 Hajeb [Meknès] .H6 Hoceima .I3 Ifrane [Meknès] .J3 Jadida .K3 Kasba-Tadla .K37 Kelaa des Srarhna .K4 Kenitra .K43 Khenitra .K5 Khmissat .K6 Khouribga .L3 Larache .M2 Marrakech .M3 Mazagan .M38 Medina .M4 Meknès .M5 Melilla .M55 Midar .M7 Mogador .M75 Mohammedia .N3 Nador [Nador] .O7 Oued Zem .O9 Oujda .P4 Petitjean .P6 Port-Lyantey 2721 G8234 MOROCCO. -
Status and Behavioural Ecology of Sengis in the Boni-Dodori and Arabuko-Sokoke Forests, Kenya, Determined by Camera Traps
Journal of East African Natural History 105(2): 223–235 (2016) STATUS AND BEHAVIOURAL ECOLOGY OF SENGIS IN THE BONI-DODORI AND ARABUKO-SOKOKE FORESTS, KENYA, DETERMINED BY CAMERA TRAPS Rajan Amin Conservation Programmes, Zoological Society of London Regent's Park, London NW1 4RY, UK [email protected] Bernard Risky Agwanda Section of Mammalogy, National Museums of Kenya P.O. Box 40658, Nairobi, Kenya [email protected] Bernard Ogwoka Kenya Wildlife Service P.O. Box 40241-00100, Nairobi, Kenya [email protected] Tim Wacher Conservation Programmes, Zoological Society of London Regent's Park, London NW1 4RY, UK [email protected] ABSTRACT The biodiversity of northern coastal Kenya, east of the Tana River, is poorly understood because security problems and poor infrastructure have discouraged access to the area. However, the wooded areas in the region have great potential for harbouring endemic and rare species, including sengis or elephant-shrews (order Macroscelidea), especially giant sengis in the genus Rhynchocyon. Based on extensive camera-trap surveys of the Boni-Dodori forest, east of the Tana River near the Somalia border, and the Arabuko-Sokoke forest west of the Tana River, the golden- rumped sengi Rhynchocyon chrysopygus appears to be limited to the Arabuko-Sokoke area, while the giant sengi in the Boni-Dodori forest is different. The Boni-Dodori forest, the largest Kenyan coastal forest, with a potential forest and thicket area of at least 3000 km2 is likely to hold a significant number of Rhynchocyon, making it very important to sengi conservation. The study generated over 2700 images of giant sengi and 32 000 camera-trap images of soft-furred sengi in a total surveyed area of approximately 300 km2 providing the first detailed 24-hour behaviour data for the species. -
Saving Kenya's Last Coastal Wilderness by Defending
CONSERVATION BY KEVIN M. DOYLE n early January this year, a handful tempers flared. The surveyors packed up and contentious issues that the country of residents in the coastal Kenyan their gear and left. The beach regained and its people have faced: in December Ivillage of Mkokoni noticed land a measure of peace – temporarily. Shali 2009, a new national land policy was surveyors setting up equipment on a Mohamed, a Mkokoni resident, said: “We adopted which, if and when implemented, stretch of undeveloped dunes. Tension feel that if we didn’t show them that we will address historical inequities and in the community had been growing are prepared to fight for our land, then emphasize the rights of citizens to the use as outsiders brazenly acquired prime all of it will be taken right out from under of and access to land. beachfront property while, under Kenyan our feet.” Mkokoni is just one of many villages law, the villagers themselves were still The confrontation was a microcosm in the northernmost corner of the Kenyan considered “squatters” on land they of the pervasive land tenure issues facing coast, just south of the Somali border, in had lived on for generations. Villagers coastal residents of Kenya, as conflicts one of Kenya’s last wilderness areas. This attributed these new developments to intensify between traditional users region includes the Lamu archipelago, possible corruption and backroom deals. of land and outside speculators and home to a most unique and diverse On this occasion, the residents rushed developers. ecology on both land and sea. back to the village to spread the news. -
M.M. OKELLO: Threats and Their Relative Severity to Wildlife Protected
Kiringe – Okello: Threats and their relative severity to wildlife protected areas of Kenya - 49 - THREATS AND THEIR RELATIVE SEVERITY TO WILDLIFE PROTECTED AREAS OF KENYA J. W. KIRINGE * – M. M. OKELLO The School for Field Studies, Center for Wildlife Management Studies, P.O. Box 27743 – 00506, Nairobi, Kenya e-mail: [email protected] or [email protected] (Received 28 th Febuary 2006; accepted16 th July 2007) Abstract. Little information is available on the threats against biodiversity in Kenya. This is critical in prioritizing conservation strategies and instituting mitigation procedures to contain and or eliminate these threats for the survival of biodiversity in protected areas. This study aimed at documenting relative severity of threats and how serious protected parks are threatened. Two hundred protected area officers were interviewed. The most relatively severe threat factors were bush meat trade; poaching for trophies; human – wildlife conflicts; human population encroachment; loss of migration corridors and dispersal areas. Thirty-two (64%) protected areas were susceptible to over half of the threat factors, while over 70% of them were threatened by an index over 0.5. All marine and nearly all forested/montane protected areas were highly susceptible to the identified threat factors. Further, protected areas popular with tourists were also highly susceptible and threatened. Protected areas around urban/industrial and agricultural areas were threatened mostly by a variety of threat factors. These findings imply that threats to Kenya’s protected areas are serious. They are critical in helping the Kenya government to prioritize its strategies in protected areas management, rather than the current haphazard approach.