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84 | Sub-Saharan Africa (SSA) Report
fuel wood and charcoal, and would also serve as an energy source for small and medium scale industries. Forests and agroforestry systems will become even more important for protecting watersheds as climate change effects become pronounced in the sub-region (IPCC, 2007). Forest biodiversity will continue to be important for the nutrition (e.g., bush meat as a source of protein), health (medicinal plants) and livelihoods of people in the sub-region. The economies of SSA countries would also be affected positively, as export of non-timber forest products (e.g., curios, bushmeat and medicinal plants), increases due to increased demand by the large number of sub-Saharan Africans in the diaspora. There have been various assessments on forests in SSA. The Millennium Ecosystem Assessment (MA) based on the Zambezi Basin case study predicts a continuing decline in forest diversity towards 2050, although the rates of decline vary among scenarios (MA, 2005abc). The main driver for the decline in forest genetic resources is expected to be habitat loss resulting from changes in land use. The causes attributed to future habitat loss include land expansion for agriculture and deforestation. A projection to 2020 in SSA shows that rates of deforestation
in East and West Africa will not change significantly
(FAO, 2003). In East Africa the continued deforestation
will be associated with population growth, intense land use
conflicts and poor economic growth. In West Africa continued
deforestation will also be associated with land use
conflicts. In both Central and Southern Africa deforestation
is expected to occur at a higher rate than now, causing a
rapid decline in forests. Deforestation in Central Africa will
be caused by increased logging, increased road construction
and land use conversion. In Southern Africa land reforms
in Zimbabwe and expansion of commercial agriculture in
Mozambique and Angola are projected to lead to rapid deforestation
(FAO, 2003). In the second Africa Environment
Outlook (AEO 2) projections on forest systems towards 2050
were based on forest assessments in Central Africa (UNEP,
2006a). Four scenarios resulted in different outcomes under
different policies. Under a Market Forces scenario, forests
will continue to decline but at a slower rate, due to policies
that promote afforestation and sustainable use and management
of forests. In the Policy Reform scenario, there is also
a decline in the rate of loss. This decline however, is due to
decreased demand in fuel wood and charcoal. The Fortress
World scenario predicts high rates of deforestation and degradation
of forest lands due to commercial over-exploitation
of resources and pressure from the rural poor. However, because
of international conventions, some forests remain. In
the Great Transitions scenario, there is an increase in forest
cover and improvement in forest quality. This increase will
be brought about by an appreciation of the value of forest
resources, improved forest management, sustainable use The move towards democratic decision making, transparency and participation of the populace in governance in countries of SSA will have an impact on the state of forest genetic resources towards 2050. For example, The New African initiative focusing primarily on African ownership and |
management is setting the agenda for renewal of the state of the continent (NEPAD, 2001). The initiative seeks to determine national and regional priorities and development plans through participatory processes involving the people. Some countries are already having a paradigm shift in the role of the public sector from control to policy formulation and support for community participation in the management of forest resources. National governments are involving communities in the management and sustainable use of forests and their resources. The case of the Communal Areas Management Programme for Indigenous Resources (CAMPFIRE) in Zimbabwe, and the successful management of the Duru-Haitemba and Mgori forests in southern Tanzania are examples of how community involvement in the management of forest resources could result in a win-win situation. East Africa, especially Kenya and Tanzania, have attempted similar efforts to integrate wildlife and livestock management. Involving local communities and ensuring equitable sharing of benefits with communities are essential to sustainable management of protected area (Box 4-1). The vigorous pursuance of these good practices across
SSA would reverse the trend of forest genetic decline and
enhance/improve the quality and quantity of forest genetic
resources and the services they provide for people. The future of non-wood forest products (NWFPs) is uncertain. Currently NWFP including plants used for food, drink, fodder, fuel and medicine and animals and their products, are important in all sub-regions of SSA for subsistence and income generation, and especially for rural livelihoods. NWFPs have potential value in local (Fondoun and Manga, 2000; Sonne, 2001; Adu-Anning, 2004; Ndam, 2004; Ngono and Ndoye, 2004), national (Russo et al., 1996; Tieguhong, 2003), regional (Ngono and Ndoye, 2004) and international trade (Ndam, 2004; Ndoye and Tieguhong, 2004). The discovery of more NWFPs of international value will improve incomes and livelihoods in the sub-region. Good examples include the Batanai Group in the Rushinga District of Zimbabwe, involved in the commercial extraction of marula oil, and the Mapanja Prunus Harvesters’ Union in Cameroon, who harvest and trade in Prunus africana on Mount Cameroon. The lack of regulatory frameworks has created an environment in which the informal sector and market forces dominate trade in NFWPs and therefore accurate data and projections on their trade are scarce (FAO, 2003). In the case of East Africa, it is expected that the provision of tax incentives would result in value addition to NWFPs by local communities and the private sector. |
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