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

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The <strong>Bale</strong> <strong>Mountains</strong> Nati<strong>on</strong>al Park is part of C<strong>on</strong>servati<strong>on</strong> Internati<strong>on</strong>al’s Eastern<br />

Afrom<strong>on</strong>tane Biodiversity Hotspot and is <strong>on</strong> <strong>the</strong> tentative nominati<strong>on</strong> for World Heritage Site<br />

Listing. The park houses a number of rare and endemic species (Asefa this editi<strong>on</strong>), such as <strong>the</strong><br />

mountain nyala Tragelaphus buxt<strong>on</strong>i (Malcolm and Evangelista this editi<strong>on</strong>), <strong>the</strong> Ethiopian wolf<br />

Canis simensis (Randall et al. this editi<strong>on</strong>; Sillero-Zubiri et al. this editi<strong>on</strong>), <strong>the</strong> giant mole rat<br />

Tachyoryctes macrocephalus and <strong>the</strong> giant lobelia Lobelia rhynchopetalum.<br />

Generally, <strong>the</strong> study area is characterized by five distinct vegetati<strong>on</strong> z<strong>on</strong>es each of which<br />

harbor its own fauna and flora. The Gaysay valley grasslands are situated within a broad flat valley<br />

at an altitude of 2600-3000 m a.s.l. These grasslands, which are part of <strong>the</strong> nor<strong>the</strong>rn projecti<strong>on</strong> of <strong>the</strong><br />

BMNP boundary, are dominated by Artemisia afra, Ferula communis, Kniphofia foliosa, grasses and<br />

sedges, interspersed with wetlands (Hillman 1986; AAU 2004). The dry evergreen m<strong>on</strong>tane forest (or<br />

Gaysay woodland) is also at <strong>the</strong> nor<strong>the</strong>rn end of <strong>the</strong> park and situated 2600 and 3800 m a.s.l. The<br />

lower altitudes are dominated ei<strong>the</strong>r by Juniperus procera or Hagenia abyssinica with <strong>the</strong> two species<br />

sometimes co-dominating <strong>on</strong> slopes. O<strong>the</strong>r species that are not dominant but of significance include<br />

Hypericum revolutum, Myrsine melanophloeos, Erica arborea and Discopodium eremanthum. The<br />

higher altitudes dominated by Hypericum revolutum, Erica arborea between, and Helichrysum<br />

citrispinum and H. splendidum moorland (Hillman 1986; AAU 2004). The central massif of <strong>the</strong> park<br />

c<strong>on</strong>sists of an Afroalpine plateau between about 3200 and 4377 m a.s.l. The area between 3550 and<br />

4000 m a.s.l is covered by Erica shrub <strong>on</strong> ridges and Helichrysum moorland in <strong>the</strong> valleys (Assefa<br />

et al. this editi<strong>on</strong>). The highest plateau areas are characterized by H. citrispinum and H. splendidum<br />

while <strong>the</strong> endemic giant lobelia is scattered across <strong>the</strong> landscape. At lower altitudes (3200 – 3500<br />

m a.s.l.) such as in <strong>the</strong> Web Valley and Morebawa, <strong>the</strong> Afroalpine habitat is characterized by short,<br />

herbaceous plant communities dominated by Alchemilla (A. abyssinica, A. rothii, A. cyclophylla)<br />

pasture, Helichrysum (H. citrispinum, H. cyosum, H. gofense, H. splendidum) shrubs and Artemesia<br />

afra shrubs (Hillman 1986; Sillero-Zubiri 1994; AAU 2004). The Ericaceous belt, composed mainly<br />

of Erica arborea and E. trimera, is located between 3200-3800 m a.s.l. and forms an important<br />

vegetati<strong>on</strong> belt between <strong>the</strong> high altitude Afroalpine plateau and <strong>the</strong> lower Harenna forest (Assefa<br />

et al. this editi<strong>on</strong>). Both shrub and tree forms are present, as well as <strong>the</strong> remnants of ancient forests<br />

of giant heath (Erica arborea) in areas spared from excessive fire (Miehe and Miehe 1994). The<br />

Harenna moist m<strong>on</strong>tane forest, rising from 1450 to 3200 m a.s.l. within a distance of <strong>on</strong>ly 8 km, is <strong>on</strong>e<br />

of <strong>the</strong> most extensive and largely natural forests remaining in Ethiopia. It is subdivided into a number<br />

of altitudinal belts based <strong>on</strong> differences in tree species compositi<strong>on</strong> across <strong>the</strong> altitudinal gradient (Friis<br />

1986; Woldu et al. 1989).<br />

Satellite image acquisiti<strong>on</strong> and preparati<strong>on</strong><br />

We used three types of satellite images in <strong>the</strong> study; Landsat MSS, Landsat ETM+ and ASTER (see<br />

Table 1 for specificati<strong>on</strong>s). The Landsat images were acquired from <strong>the</strong> Global Land Cover Facility<br />

(GLCF; www.glcf.org) through <strong>the</strong>ir Earth Science Data Interface (ESDI), whereas <strong>the</strong> ASTER was<br />

downloaded from <strong>the</strong> USGS <strong>on</strong>line data provisi<strong>on</strong> interface (http://edc.usgs.gov/products/satellite/<br />

aster.html).<br />

<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> 121

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