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

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Discussi<strong>on</strong><br />

This study employed market value methods to estimate direct benefits accruing to rural communities<br />

of <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Eco-regi<strong>on</strong>. Using market prices a lower-limit estimate of <strong>the</strong> total value of<br />

envir<strong>on</strong>mental c<strong>on</strong>tributors to producti<strong>on</strong> are observed and c<strong>on</strong>sequentially, our value estimates<br />

are c<strong>on</strong>servative. This is beneficial in light of two key study limitati<strong>on</strong>s; <strong>the</strong> assumpti<strong>on</strong> that <strong>the</strong><br />

opportunity costs of labour are negligible and <strong>the</strong> omissi<strong>on</strong> of negative envir<strong>on</strong>mental externalities;<br />

<strong>the</strong> costs of envir<strong>on</strong>mental degradati<strong>on</strong> resulting from livelihood activities. Even with no employment<br />

prospects, an individual would have to fulfil no o<strong>the</strong>r useful household tasks to say that no output<br />

is forg<strong>on</strong>e in engaging in productive activity. However, with extremely limited job opportunities<br />

preventing an accurate measure of <strong>the</strong> minimum wage rate, <strong>the</strong> assumpti<strong>on</strong> that labour costs approach<br />

zero is justified. The omissi<strong>on</strong> of envir<strong>on</strong>mental externalities, in particular negative externalities,<br />

may mean that <strong>the</strong> direct c<strong>on</strong>sumptive value, though an underestimate from a private perspective,<br />

may be an overestimate from a social perspective. Negative externalities from crop cultivati<strong>on</strong> and<br />

livestock rearing are already observed in <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Eco-regi<strong>on</strong> as <strong>the</strong> destructi<strong>on</strong> of natural<br />

forest for arable and grazing land, with effects such as soil erosi<strong>on</strong>, changes in vegetati<strong>on</strong>, and<br />

<strong>the</strong> disappearance of wildlife (OARDB 2007). The harvest of forest products may also necessitate<br />

destructi<strong>on</strong> of natural areas and within <strong>the</strong> Nati<strong>on</strong>al Park commercial extracti<strong>on</strong> of bamboo poles and<br />

unregulated forest coffee extracti<strong>on</strong> affects natural habitats (pers<strong>on</strong>al observati<strong>on</strong>). The sustainability<br />

of <strong>the</strong>se principal livelihood strategies has implicati<strong>on</strong>s for future resource management. With <strong>the</strong><br />

Ethiopian government influencing <strong>the</strong> land use decisi<strong>on</strong>s of rural households through incentives,<br />

laws, infrastructure and instituti<strong>on</strong>al arrangements, this gap between private and social costs should<br />

be addressed. Despite limitati<strong>on</strong>s this study sufficiently allows <strong>the</strong> investigati<strong>on</strong> of present resource<br />

use from which we can infer <strong>the</strong> impact of declining benefits or restricti<strong>on</strong>s <strong>on</strong> use.<br />

Principal direct c<strong>on</strong>sumptive use values<br />

Envir<strong>on</strong>mental c<strong>on</strong>diti<strong>on</strong>s in <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> are favourable for crop cultivati<strong>on</strong> with multiple<br />

crop types meeting household needs. The mean direct c<strong>on</strong>sumptive use value derived from crop<br />

producti<strong>on</strong> is US$1157 ± 73 and differs significantly between kebeles with those at higher altitudes<br />

deriving higher value. Topographic variability of <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Eco-regi<strong>on</strong> climatically<br />

c<strong>on</strong>strains <strong>the</strong> type of crops that can be grown by households with maize, tef and fruits grown<br />

at lower altitudes and, barley and root crops at higher altitudes. Government development and<br />

poverty alleviati<strong>on</strong> schemes c<strong>on</strong>tinue to promote agricultural intensificati<strong>on</strong> and recommendati<strong>on</strong>s<br />

focus <strong>on</strong> better soil management and <strong>the</strong> use of fertiliser and improved crop varieties (Pender and<br />

Gebremedhin 2006). While intensificati<strong>on</strong> might reduce <strong>the</strong> encroachment of cropland into natural<br />

landscapes, <strong>the</strong> negative l<strong>on</strong>g-term envir<strong>on</strong>mental impacts should be assessed before fully endorsed.<br />

Livestock rearing is a comm<strong>on</strong> livelihood strategy in <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong>. In c<strong>on</strong>trast to<br />

previous findings livestock were not reported as being used for insurance, investment or social capital.<br />

Household income from livestock sales amount to US$228 ± 16 annually, but with livestock value<br />

in o<strong>the</strong>r studies comprising 57% from draught power al<strong>on</strong>e (Sco<strong>on</strong>es 1990), and value derived year<strong>on</strong>-year<br />

from animal reproducti<strong>on</strong> and milk, this study underestimates <strong>the</strong> private direct use value<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> 192

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