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Proceedings of the Workshop - Georg-August-Universität Göttingen

Proceedings of the Workshop - Georg-August-Universität Göttingen

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Based upon <strong>the</strong> critical state in which <strong>the</strong> TDF ecosystems are found in<br />

Colombia, it is urgent to devote efforts so as to implement strategies focused on<br />

restoration processes in <strong>the</strong>se ecosystems. And in this context, it should be noted that<br />

it will in no way be possible to perform a restoration against <strong>the</strong> will <strong>of</strong> <strong>the</strong> affected<br />

population that is conscious <strong>of</strong> only being kept afloat by a dependence on land<br />

resources (Andres 2009; Galmez & Komett 2009, Barnsley 2009).<br />

Due to drought conditions experienced by dry forests, seed recruitment and<br />

growth rates are affected and are lower than those <strong>of</strong> tropical rainforests. Also, some <strong>of</strong><br />

<strong>the</strong> dry forests are subject to large-scale forest fires due to <strong>the</strong> accumulation <strong>of</strong> not<br />

decomposed, dry organic matter, although <strong>the</strong>re is evidence that <strong>the</strong>se forests are less<br />

prone to such events due to <strong>the</strong> plant adaptations (Vieira & Scariot 2006).<br />

In this sense, ecological restoration aims to restore an ecosystem that has been<br />

degraded, damaged or destroyed, through <strong>the</strong> stimulation and acceleration <strong>of</strong> natural<br />

succession in order to restore <strong>the</strong> forests' ability <strong>of</strong> self-regulation (Rodriguez 2009)<br />

and finally, to allow not only <strong>the</strong> establishment <strong>of</strong> core conservation, but also <strong>the</strong><br />

recovery <strong>of</strong> <strong>the</strong> functionality and environmental services a previously degraded<br />

ecosystem provides or may provide.<br />

This gives great importance to each existing remnant when seeking to preserve a<br />

representative sample <strong>of</strong> TDF in Colombia. Particularly <strong>the</strong> San Sebastian hacienda<br />

has almost 200 hectares <strong>of</strong> forests that have not been touched in at least 40 years;<br />

<strong>the</strong>reby exists a great opportunity in contributing to <strong>the</strong> study and conservation <strong>of</strong> this<br />

type <strong>of</strong> ecosystem.<br />

Given <strong>the</strong> significant emissions from deforestation and forest degradation,<br />

especially in developing countries, several parties have focused <strong>the</strong>ir attention on<br />

creating positive incentives for those countries, so as to reduce <strong>the</strong>ir deforestation rates<br />

and forest degradation (Barnsley 2009). In this sense, emissions from deforestation<br />

and forest degradation in developing countries account for about 20 percent <strong>of</strong> total<br />

emissions <strong>of</strong> greenhouse gases (GHG) annually, and it is precisely in this context that<br />

<strong>the</strong> initiative <strong>of</strong> reducing emissions from deforestation and forest degradation in<br />

developing countries (REDD) is a must (Angelsen 2009). The basic idea behind REDD<br />

is <strong>the</strong> creation <strong>of</strong> a system <strong>of</strong> positive incentives that will persuade developing countries<br />

with tropical forests to reduce deforestation rates, by financially rewarding <strong>the</strong>m<br />

(Barnsley 2009).<br />

Colombian TDF are included in <strong>the</strong> Andean forest ecosystems (EFA) which<br />

according to Etter & Villa (2000) are <strong>the</strong> most diverse and threatened terrestrial<br />

ecosystems, recognized as a major global hotspot and representing a priority for<br />

conservation because <strong>of</strong> <strong>the</strong>ir extraordinary richness and endemism, as well as several<br />

<strong>of</strong> its constituent species being severely threatened (Miles, et al. 2006). In addition to<br />

be a priority for biodiversity conservation in <strong>the</strong> great hosting, EFAs are <strong>the</strong> living basis<br />

<strong>of</strong> populations in surrounding areas, due to <strong>the</strong> multiple social, economic and<br />

environmental resources <strong>the</strong>y provide (Quesada, et al. 2009).<br />

Forestry activities <strong>of</strong>fer an attractive potential for climate change adaptation and<br />

mitigation <strong>of</strong> adverse effects. By promoting conservation <strong>of</strong> forest through management<br />

practices, forest carbon emissions into <strong>the</strong> atmosphere are reduced, helping to mitigate<br />

climate change and its impacts (Galmez & Komett 2009).<br />

In this sense <strong>the</strong> REDD systems have great potential to generate collateral<br />

benefits for <strong>the</strong> conservation <strong>of</strong> biodiversity and o<strong>the</strong>r ecosystem services (in addition<br />

to carbon sequestration). It is considered that tropical forest conservation has been<br />

underfunded in recent decades, both in terms <strong>of</strong> scale and duration <strong>of</strong> <strong>the</strong> funding cycle<br />

(Galmez & Komett 2009). In this sense, <strong>the</strong> financial flows related to REDD <strong>of</strong>fer new<br />

possibilities providing collateral benefits in terms <strong>of</strong> conservation. The ecological<br />

importance <strong>of</strong> <strong>the</strong>se ecosystems is becoming obvious as a source <strong>of</strong> storage and water<br />

sources regulation, since <strong>the</strong>y are a determining factor for soil protection and<br />

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