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

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c<strong>on</strong>servati<strong>on</strong> and sustainable use of natural resources (Scherl, et al. 2004) Currently, approximately<br />

12% of <strong>the</strong> global land surface is protected (Emert<strong>on</strong> et al. 2006). This is a huge increase in PAs<br />

over <strong>the</strong> past four decades, with 2.4 milli<strong>on</strong> km2 being protected in 1962 and 20 milli<strong>on</strong> km2 in 2004<br />

(Emert<strong>on</strong> et al. 2006). Both internati<strong>on</strong>al and domestic funding has struggled to keep up with this<br />

increase in PAs and <strong>the</strong> relative global investment in biodiversity c<strong>on</strong>servati<strong>on</strong> has declined.<br />

Moore et al. (2004) found that $364/km2 and $574/km2 is needed for <strong>the</strong> effective management<br />

of Afro-m<strong>on</strong>tane forest and Alpine moorland respectively. In 2004 <strong>the</strong> Ethiopian government was<br />

providing approximately $30,000 including salaries ($8500 excluding) resulting in $13/km2 and $4/<br />

km2 respectively for park management to <strong>the</strong> <strong>Bale</strong> <strong>Mountains</strong> Nati<strong>on</strong>al Park (BMNP). In 2008 this<br />

increased to a total of approximately $50,000 including salaries ($18,000 excluding) resulting in $23/<br />

km2 and $8/km2 respectively for park management. In 2009, <strong>the</strong> newly established federal Ethiopian<br />

Wildlife C<strong>on</strong>servati<strong>on</strong> Authority (EWCA) took over <strong>the</strong> management of <strong>the</strong> park, and although it<br />

is thought that approximately ETB 1,000,000 (approximately $77,000) excluding salaries will be<br />

provided to <strong>the</strong> park for its management, equating to approximately $35/km2 , this is still below <strong>the</strong><br />

recommended amount. A detailed gap analysis was carried out for <strong>the</strong> BMNP (Kinahan 2010), and<br />

revealed that even with new improved government funds <strong>the</strong>re still remains a large gap between<br />

<strong>the</strong> funds needed and <strong>the</strong> funds available, with an 84% and 77% funding gap between optimal and<br />

critical requirements respectively or a 54% and 34% (optimal and critical) taking current external<br />

funds into account as well.<br />

In order to try and reduce <strong>the</strong>se gaps PA managers globally, including <strong>the</strong> BMNP, are now<br />

developing Business and Financial Management Plans. The emergence of markets and payments<br />

for ecosystem services is becoming an increasingly important potential financial strategy for PAs<br />

worldwide.<br />

Payment for ecosystem services and carb<strong>on</strong> trading<br />

Payments for ecosystem services (PES) are market mechanisms that can help finance c<strong>on</strong>servati<strong>on</strong><br />

efforts. They also have <strong>the</strong> potential to deliver socio-ec<strong>on</strong>omic co-benefits. They are voluntary<br />

schemes where well-defined ecosystem services are ‘bought’ from a ‘provider’ who secures <strong>the</strong><br />

supply of <strong>the</strong> ecosystem service such as clean water, soil protecti<strong>on</strong>, or carb<strong>on</strong> storage. PES are<br />

becoming an increasingly popular strategy to examine as a means of meeting c<strong>on</strong>servati<strong>on</strong> financing<br />

needs. Within <strong>the</strong>se, <strong>the</strong> carb<strong>on</strong> markets are unequivocally <strong>the</strong> most advanced and most investigated.<br />

Carb<strong>on</strong> markets use baseline-and-credit schemes whereby credits are generated by ei<strong>the</strong>r<br />

sequestering additi<strong>on</strong>al amounts of greenhouse gases from <strong>the</strong> atmosphere or by preventing <strong>the</strong>ir<br />

release into <strong>the</strong> atmosphere compared to a reference, or business-as-usual scenario. One potential<br />

way to achieve this that is directly in line with c<strong>on</strong>servati<strong>on</strong> management acti<strong>on</strong>s is through avoided<br />

deforestati<strong>on</strong> projects or REDD projects (Reduced Emissi<strong>on</strong>s from Deforestati<strong>on</strong> and Degradati<strong>on</strong>).<br />

REDD projects generate carb<strong>on</strong> credits by averting carb<strong>on</strong> dioxide (CO ) emissi<strong>on</strong>s into <strong>the</strong><br />

2<br />

atmosphere through <strong>the</strong> reducti<strong>on</strong> or preventi<strong>on</strong> of deforestati<strong>on</strong> and degradati<strong>on</strong> that o<strong>the</strong>rwise<br />

would occur in <strong>the</strong> absence of such a project. REDD is a means to realise <strong>the</strong> financial value for<br />

<strong>the</strong> carb<strong>on</strong> stored in forests particularly for developing countries where <strong>the</strong> majority of intact forest<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> 296

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