Walia Special Edition on the Bale Mountains (2011) - Zoologische ...

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We derived class descriptions from the quantitative surveys of substrate, cover, vegetation height and plant species composition, supplemented by photos, qualitative descriptions of vegetation structure, and familiarity with easily identifiable plant communities. Results Landsat PCA Principal components (PCs) one to three captured over 95% of the variation in the Landsat pixel values, Table 1; see Tallents (2007) for factor loadings. PC1 isolated the factors which most strongly influenced reflectance in all wavelengths, contrasting water bodies and densely vegetated land with highly reflective bare soil. It was positively correlated with illumination (r = 0.44), separating heavily shaded from sun-facing slopes. PC2 had high values in cool, damp areas with high plant productivity such as drainage lines, and was lower in the arid Tullu Deemtu rain shadow and welldrained lava slopes. PC3 correlated strongly with altitude (r = -0.65), contrasting the Helichrysumdominated high plateaux with the lower-altitude grassy valleys. Table 1. Eigenvalues and variability captured by the Landsat image principal components. PC Eigenvalue Cumulative % 1 4.99 62.39 2 1.47 80.79 3 1.14 95.06 4 0.27 98.39 5 0.06 99.16 6 0.04 99.65 7 0.02 99.95 8 < 0.01 100.00 PC8 only described differences between the two highly correlated thermal bands, and appeared as spatially random speckle, with some striping characteristic of the scanning path. PC7 isolated speckle probably associated with the resampling undertaken during orthoregistration, and was discarded along with PC8. The remaining six PCS captured over 99% of the variability in the data (Table 1), and formed the input for the classification. PCs 4 to 6 were retained despite their relatively low information content because they highlighted features of interest and it was expected that they would allow discrimination between broadly similar land cover classes. The fact that components have low eigenvalues can simply indicate that the variability they encapsulate is very localized (Eastman and Fulk 1993), so they can help to distinguish rare habitat types or those which are spectrally similar despite being floristically distinct (Townshend and Justice 1980). Classification Several classifications fulfilled the criterion of spectral separability based on non-overlapping 80% ellipses. The one with 23 classes (here labelled A to W) was chosen because it adequately represented the full range of land cover types, and clearly delineated habitats of interest, such as wetlands, grass versus herbaceous pasture, lava flows and high-altitude Helichrysum meadows, Figure 1. <strong>Walia</strong>-<strong>Special</strong> <strong>Edition</strong> on the Bale Mountains 102
Figure 1. Afroalpine vegetation in the Bale Mountains. See legend for plant species abbreviations. <strong>Walia</strong>-<strong>Special</strong> <strong>Edition</strong> on the Bale Mountains 103
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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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of a community there must be a prem
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Hillman, J.C. 1986. The Bale Mounta
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1995a; Sillero-Zubiri et al. 2004,
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Monitoring Activities the Bale Moun
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Table 1. Packs monitored in the Bal
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long-term study areas. However, tot
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Creel, S., Spong, G., Sands, J.L.,
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Observations on the Status of the M
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The Bale Mountains Figure 1. The kn
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of the park’s interior, where hum
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The Ahmar (Chercher) Mountains The
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Casuarina equisetiflium lia, Hageni
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Threats Predictably, the main threa
Page 59 and 60: populations within hunting blocks a
Page 61 and 62: Population Estimates and Diet of St
Page 63 and 64: To identify the types and proportio
Page 65 and 66: Table 3. Coverage of plant species
Page 67 and 68: for eating grass species. During th
Page 69 and 70: Ecology and Reproductive Strategy o
Page 71 and 72: overall diet (36% of total prey occ
Page 73 and 74: Table 1. Ethiopian wolf density (in
Page 75 and 76: encounters between neighbouring wol
Page 77 and 78: No new packs were formed between 19
Page 79 and 80: Cooperative Breeding Role of helper
Page 81 and 82: Mean feeding rate (contributions/ho
Page 83 and 84: successful dispersal are very low,
Page 85 and 86: References Ashenafi, Z.T. 2001. Com
Page 87 and 88: Solomon, N. G., and French, J.A. Ed
Page 89 and 90: Figure 1. The Bale monkey (Cercopit
Page 91 and 92: Survey method - Dec 06-Jan 07 Line
Page 93 and 94: Table 3. Estimates of population de
Page 95 and 96: Monitoring and management prioritie
Page 97 and 98: Amphibians and Reptiles Recorded fr
Page 99 and 100: Lizards Agamidae Acanthocercus atri
Page 101 and 102: to just two montane sites in Harenn
Page 103 and 104: used for comparison. The study reve
Page 105 and 106: Mapping High-Altitude Vegetation in
Page 107 and 108: of the alpine vegetation have been
Page 109: Observers located each point by GPS
Page 113 and 114: other, and class N from O, because
Page 115 and 116: J. mima mounds and grazed mineral s
Page 117 and 118: Node Clusters Species in 1st cluste
Page 119 and 120: A. Arboreal heather/lake -E 64.6 +W
Page 121 and 122: A. Arboreal heather/lake 82 ± 176
Page 123 and 124: elevations of 4100-4200 m a.s.l. in
Page 125 and 126: Miehe, G. and Miehe, S. 1994. Erica
Page 127 and 128: and managing natural resources and
Page 129 and 130: The Bale Mountains National Park is
Page 131 and 132: The ground-truthing points made up
Page 133 and 134: Table 2. Table showing the area for
Page 135 and 136: Table 5. Description of patchiness
Page 137 and 138: Acknowledgments This study was fund
Page 139 and 140: Characteristics and Origins of Glad
Page 141 and 142: Figure 1. Map with the approximate
Page 143 and 144: Table 1. Main characteristics of th
Page 145 and 146: Table 2. Soil Properties at two dep
Page 147 and 148: Total aboveground biomass ranged fr
Page 149 and 150: There might be some evidence for th
Page 151 and 152: Appendix 1. Attributes for soil pro
Page 153 and 154: Ogate (altitude 1753 m) Water Site
Page 155 and 156: the loss of natural forests due to
Page 157 and 158: Results Fire extent and frequency A
Page 159 and 160: 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
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