In response to global declines in biodiversity, some 190 countries have pledged, under the Convention on Biological Diversity (CBD), to reduce the rate of biodiversity loss by 2010. Moreover, this target has recently been incorporated into the Millennium Development Goals in recognition of the impact of biodiversity loss on human well-being. Timely information on where and in what ways the target has or has not been met, as well as the likely direction of future trends, depends on a rigorous, relevant, and comprehensive suite of biodiversity indicators with which to track changes over time, to assess the impacts of policy and management responses, and to identify priorities for action. How far have we come in meeting these needs, and is it sufficient?Resource Type: Journal Papers
Commercialization of non-timber forest products (NTFPs) has been widely promoted as a means of sustainably developing tropical forest resources, in a way that promotes forest conservation while supporting rural livelihoods. However, in practice, NTFP commercialization has often failed to deliver the expected benefits. Progress in analyzing the causes of such failure has been hindered by the lack of a suitable framework for the analysis of NTFP case studies, and by the lack of predictive theory.
We address these needs by developing a probabilistic model based on a livelihood framework, enabling the impact of NTFP commercialization on livelihoods to be predicted.Resource Type: Journal Papers
Moving beyond 2010, successful conservation approaches need to be reinforced and adequately financed. More radical changes are required that recognize biodiversity as a global public good, that integrate biodiversity conservation into policies and decision frameworks for resource production and consumption, and that focus on wider institutional and societal changes to enable more effective implementation of policy.Resource Type: Journal Papers
This briefing considers the implications for biodiversity conservation and local people’s livelihoods of the current discussion on reducing emissions from deforestation in developing countries (RED-DC, henceforth RED) under the UN Framework Convention on Climate Change (UNFCCC). The potential for RED to deliver multiple benefits for biodiversity conservation, livelihoods and other ecosystem services is well documented (UNEP-WCMC 2007). But it is important to note that RED could also have negative impacts on biodiversity and local livelihoods, for example as a result of the displacement of deforestation.Resource Type: Reports
Two recent analyses have measured protected area coverage for each of the world’s realms, biomes and ecoregions - UNEP-WCMC, 2008 and Jenkins and Joppa, 2009 Expansion of the global terrestrial protected area system, Biological Conservation 142 (2009), pp. 2166–2174, using the WWF Terrestrial Ecoregions of the World.
However, data handling procedures differ between these analyses, resulting in differences in the protection statistics reported. Here we outline differences in the use of datasets, present alternative analyses of the protected area coverage of WWF realms, biomes and ecoregions for 2009, and compare the two estimates of protected area coverage.
Marine conservation lags behind terrestrial in the establishment of protected areas. This was recognized by the Convention on Biological Diversity, whose members, in 2004, agreed to establish “comprehensive, effectively managed, and ecologically representative” systems of marine protected areas (MPAs) by 2012. Halfway toward this target date, we look at the coverage of the world’s 5045 MPAs from a biogeographic perspective.Resource Type: Journal Papers
The CBD target "to achieve by 2010 a significant reduction of the current rate of biodiversity loss" was incorporated into the Millennium Development Goals in 2002. Our lack of progress toward the 2010 target could undermine achievement of the MDGs and poverty reduction in the long term. With increasing global challenges, such as population growth, climate change, and overconsumption of ecosystem services, we need further integration of the poverty alleviation and biodiversity conservation agendas.
Climate change is expected to alter the distribution of habitats and thus the distribution of species connected with these habitats in the terrestrial Barents Sea region. It was hypothesised that wild species connected with the tundra and open-land biome may be particularly at risk as forest area expands. Fourteen species of birds were identified as useful indicators for the biodiversity dependent upon this biome.Resource Type: Journal Papers
Entrepreneurship and innovation by actors in the market for non-timber forest products (NTFPs) cannot be fully understood without a proper understanding of the position and behaviour of actors in the value chain of NTFPs. This paper places the market for NTFPs in the emerging literature on value chains which has, so far, lacked a detailed analysis of NTFPs. Our analysis reveals that certain key entrepreneurs are a driving force of success throughout several NTFP value chains in both Bolivia and Mexico. Where market information is scarce, e.g. where producers are distant from consumers, key entrepreneurs often govern entire value chains.
Rather than criticising the monopolistic position of individuals, it is important to understand how the activity of key entrepreneurs can be supported in spreading successful commercialisation further and where necessary control negative impacts of their role. Our analysis indicates that policies to support commercialisation of the case study NTFPs would also need to be tailored to each value chain.Resource Type: Journal Papers
Assessments of forest biodiversity - the diversity within forest species, between species and of forest ecosystems - are essential if forest resources are to be effectively conserved and sustainably managed (Hunter, 1999). Assessments are needed to provide information necessary to support biodiversity-related decision-making in forest policy and management. However, assessment of forest biodiversity presents a number of challenges. First, because of the complexity of biodiversity, information about it needs to be assembled and expressed based on simplified variables, typically in the form of indicators (Noss, 1990, 1999). Second, since decisions relating to forests are made at a variety of scales, biodiversity data and indicators need to be aggregated across different scales for monitoring and reporting purposes (Noss, 1990; Turner, 1995).Resource Type: Journal Papers
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