The Cost of <str<strong>on</strong>g>Special</str<strong>on</strong>g>isati<strong>on</strong>: A C<strong>on</strong>servati<strong>on</strong> Challenge The apparently sterile Afroalpine steppes of Ethiopia support a rodent biomass which is spatially and temporally predictable, and comparable to o<strong>the</strong>r rodent-rich habitats elsewhere in Africa, which may explain why <strong>the</strong> Ethiopian wolf is <strong>the</strong> <strong>on</strong>ly canid to specialize so completely <strong>on</strong> rodents (Sillero- Zubiri et al. 1995a). The rodents’ distributi<strong>on</strong> and diurnal activity also c<strong>on</strong>cur with Ethiopian wolves’ diurnal and solitary foraging habits, and <strong>the</strong>ir c<strong>on</strong>finement to Afroalpine habitats over 3,000 m a.s.l.. Global warming during <strong>the</strong> last 10,000 years progressively c<strong>on</strong>fined <strong>the</strong> Afroalpine ecosystem to <strong>the</strong> highest mountains, and today 60% of all Ethiopian land above 3,000 m has been c<strong>on</strong>verted to farmland (Marino 2003a). Ethiopian wolves face threats that arise from <strong>the</strong>ir isolati<strong>on</strong>, small size, and <strong>the</strong> increasing c<strong>on</strong>tact with humans and disease transmissi<strong>on</strong> from domestic dogs (Sillero-Zubiri and Marino 2004). Transmissi<strong>on</strong> of rabies is <strong>the</strong> main threat for wolves in <strong>Bale</strong> populati<strong>on</strong> and can have serious c<strong>on</strong>sequences for small populati<strong>on</strong>s (Hayd<strong>on</strong> et al. 2002, 2006; Randall et al. 2004, 2006). Elsewhere habitat loss is ever increasing <strong>the</strong> risk of populati<strong>on</strong> extincti<strong>on</strong>s. Two small populati<strong>on</strong>s became extinct when suitable wolf range shrunk below 20 km² in recent years (Marino 2003a), but seven still survive in Afroalpine ranges across <strong>the</strong> country, with <strong>Bale</strong> <strong>the</strong> largest (Marino 2002a; Randall et al. this editi<strong>on</strong>). Aspects of <strong>the</strong> demography of wolves in <strong>Bale</strong>, particularly <strong>the</strong>ir high adult survivorship, also stress <strong>the</strong> resilience and stability of wolf populati<strong>on</strong>s (Marino 2003b; Marino et al 2006; Hayd<strong>on</strong> et al. 2002). Although <strong>the</strong>ir small, fragmented populati<strong>on</strong>s are a poor omen for Ethiopian wolves, <strong>the</strong>ir c<strong>on</strong>centrati<strong>on</strong> in a few clearly defined sites, <strong>the</strong>ir charisma and, we hope, a fair understanding of <strong>the</strong>ir biology, lend hope that with unwavering commitment from all c<strong>on</strong>cerned and adherence to a well-founded management plan (Sillero-Zubiri and Macd<strong>on</strong>ald 1997; Sillero- Zubiri et al. 2004) <strong>the</strong>y will survive. Protective measures require <strong>the</strong> c<strong>on</strong>solidati<strong>on</strong> of <strong>the</strong> General Management Plan for <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Nati<strong>on</strong>al Park (OARDB 2007) and o<strong>the</strong>r protected areas, and active efforts to m<strong>on</strong>itor and protect all remaining populati<strong>on</strong>s. Acknowledgements We thank <strong>the</strong> Ethiopian Wildlife C<strong>on</strong>servati<strong>on</strong> Authority and <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Nati<strong>on</strong>al Park for permissi<strong>on</strong> to undertake this research, and all <strong>the</strong> staff of <strong>the</strong> Ethiopian Wolf C<strong>on</strong>servati<strong>on</strong> Programme (EWCP) who assisted collecting data in <strong>the</strong> last 20 years. EWCP is a partnership between <strong>the</strong> Oxford University’s WildCRU and <strong>the</strong> Ethiopian authorities under <strong>the</strong> auspices of <strong>the</strong> IUCN/SSC Canid <str<strong>on</strong>g>Special</str<strong>on</strong>g>ist Group. We thank Born Free Foundati<strong>on</strong>, Frankfurt Zoological Society, Wildlife C<strong>on</strong>servati<strong>on</strong> Network, Wildlife C<strong>on</strong>servati<strong>on</strong> Society, Peoples’ Trust for Endangered Species and many o<strong>the</strong>rs for <strong>the</strong>ir financial support. <str<strong>on</strong>g>Walia</str<strong>on</strong>g>-<str<strong>on</strong>g>Special</str<strong>on</strong>g> <str<strong>on</strong>g>Editi<strong>on</strong></str<strong>on</strong>g> <strong>on</strong> <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> 76
References Ashenafi, Z.T. 2001. Comm<strong>on</strong> property resource management of an Afroalpine habitat: supporting a populati<strong>on</strong> of <strong>the</strong> critically endangered Ethiopian wolf (Canis simensis). DPhil Thesis. Durrel Institute of C<strong>on</strong>servati<strong>on</strong> and Ecology. University of Kent, UK. Ashenafi, Z.T., T. Couls<strong>on</strong>, Sillero-Zubiri, C. andLeader-Williams, N. 2005. Behaviour and ecology of <strong>the</strong> Ethiopian wolf in a human-dominated landscape outside protected areas. Animal C<strong>on</strong>servati<strong>on</strong>, 8: 113-121. Carb<strong>on</strong>e, C., Mace, G.M., Roberts S.C., and Macd<strong>on</strong>ald, D.W. 1999. Energetic c<strong>on</strong>straints <strong>on</strong> <strong>the</strong> diet of terrestrial carnivores. Nature, 402: 286-288 Dobs<strong>on</strong>, F.S. 1982. Competiti<strong>on</strong> for males and predominant juvenile male dispersal in mammals. 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(Sillero Zubiri, C. and & Macd<strong>on</strong>ald, D.W. (Eds)). IUCN, Gland, Switzerland & Cambridge, UK. Marino, J. 2003a. Threatened Ethiopian wolves persist in small isolated Afroalpine enclaves. Oryx, 37:62-71. Marino, J. 2003b. Spatial ecology of Ethiopian wolf evoluti<strong>on</strong>, populati<strong>on</strong> dynamics and territoriality. D.Phil. dissertati<strong>on</strong>. Oxford University, Oxford, UK. Marino, J., Sillero-Zubiri, C. and Macd<strong>on</strong>ald, D.W. 2006 Trends, dynamics and resilience of an Ethiopian wolf populati<strong>on</strong>. Animal C<strong>on</strong>servati<strong>on</strong>, 9: 49-58. Marino, J., R. Mitchell, and P.J. Johns<strong>on</strong>. 2010. Dietary specializati<strong>on</strong> and climatic-linked variati<strong>on</strong>s in extant populati<strong>on</strong>s of Ethiopian wolves. Journal of African Ecology, 48: 517-525 <str<strong>on</strong>g>Walia</str<strong>on</strong>g>-<str<strong>on</strong>g>Special</str<strong>on</strong>g> <str<strong>on</strong>g>Editi<strong>on</strong></str<strong>on</strong>g> <strong>on</strong> <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> 77
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Walia Spec
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This Special <stro
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Foreword The Bale Mountains are uni
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FACTORS AFFECTING FIRE ExTENT AND F
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Introduction This Special</
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Mammals of the Bale Mountains Natio
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History and Physical Features of th
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Name of Order Name of Family No of
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wolf is a rare canid endemic to the
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Hillman. J. C. 1993. Ethiopia: Comp
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Scientific name Common name Sources
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Structuring of the Birds of the Bal
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interactions? 2) Would such classif
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feeding habit and the related bill
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Table 1. Component loadings of fora
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Assemblage 1 Assemblage 2 Assemblag
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- Page 125 and 126: Miehe, G. and Miehe, S. 1994. Erica
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Table 5. Description of patchiness
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Acknowledgments This study was fund
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Characteristics and Origins of Glad
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Figure 1. Map with the approximate
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Table 1. Main characteristics of th
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Table 2. Soil Properties at two dep
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Total aboveground biomass ranged fr
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There might be some evidence for th
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Appendix 1. Attributes for soil pro
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Ogate (altitude 1753 m) Water Site
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the loss of natural forests due to
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Results Fire extent and frequency A
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Soil type Over 50% of the total num
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Distance to settlements The frequen
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than expected given there available
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MOA 2000. Ethiopian Forest Status R
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among seasons are usually only a fe
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In contrast to the northern highlan
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Table 1. The distribution, species
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it was absent from the central subz
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Figure 2. Population structure of t
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Fetene, M., Gashaw, M., Nauke, P. a
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Bale Mountain Lakes: Ecosystems Und
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occurrence above 4000 m. Rainfall i
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Table 1. List of the sampled waterb
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total nitrogen, chlorophyll a, cond
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Eggermont H., Russell, J.M.. Schett
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Direct Consumptive Use Value of Eco
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As more literature seeks to explore
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Table 1. Ecosystem goods and servic
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Figure 1. Map of the Bale Mountains
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2(a) Crop Production HH Crop Value
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3(a) Mean Household Annual Direct C
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accruing to households. Although no
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Acknowledgements This study was mad
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Livestock Grazing in Bale Mountains
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evidence that low levels of grazing
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wildlife, especially the mountain n
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and control sites (areas where live
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several of the Bale ecosystem compo
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Paine, R. T. and Vadas, R. L. 1969.
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their hives. Hive and tree types we
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HOROqqA (Bersama abyssinica, Melian
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Value Chain Analysis for Bamboo Ori
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data recorded by the Development Ag
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Amongst the interviewees, 80% of pe
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Producers As reported previously, b
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The above figure shows the various
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(6) BERSMP and all other stakeholde
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The Distribution, Properties and Us
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preliminary data. From the prelimin
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Figure 1. Map of the southern part
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Addeye All the 11 horas in Addeye a
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Tabalas are used for healing purpos
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Cultural value and history The use
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(Barrett-Lennard 2003). Finally, pr
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Appendix ph Colour Salinity (mS) Ta
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Villages using the hora Animals vis
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General Management Planning for the
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BMNP Management History Since its i
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effectively and efficiently impleme
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Problems and Issues A problems and
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understood threats were also identi
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Park Operations Programme This prog
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according to its core vision and pr
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People in National Parks - Joint Na
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pastoralists, as part of pastoral s
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of wild animals (Stephens et al. 20
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have experience in the implementati
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2004) or conservation and livelihoo
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• The redefinition of protected a
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Risk of Disease Transmission Betwee
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aspects of these factors, including
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ecorded as “point vegetation” f
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Table 1: Composition of 326 ungulat
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Table 3. Distance from road at whic
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Transmission risk Clearly, disease
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Dunn, A.M. 1968. The wild ruminant
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however continues to rise and in 19
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Tourism in the Bale Mountains Natio
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the past 5 years tourism activities
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assist with implementation of the t
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An increase in tourism investment i
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at a loss of approximately ETB 10,0
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Can Carbon Contribute to Conservati
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emains. The more recently coined RE
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Benefits The implementation of such
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or meet the minimum costs necessary
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Table 1. Financial forecast for 20
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across Africa. Biological Conservat
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sets, extract relevant bits of info
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What to Monitor? The question of wh
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scale as a balance where one side r
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through existing databases not only
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The moral of these stories are that
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anger based monitoring system is a
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spatial and temporal extent of the
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IUCN Red Listed Species Description
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Appendix 2: Metadata form A digital
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and climate data, AVHRR NDVI data,
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http://www.mentorsoftwareinc.com Me
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Individual Arrest Form Index No. Lo
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If for Commercial Market: □ in yo
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• Improve research work on wildli
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• Development Partners (donors) a
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Sustainable Development of the Prot
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I. Personal details Ethiopian Wildl
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Publication Financially Supported b