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Key messages The REDD+ policy process in the Democratic Republic of Congo (DRC) over the past decade has diverged from the initial government planning due to political changes at the international and national levels. While participation is perceived by government and international actors as one of the biggest achievements of REDD+ in the DRC, non-state actors – particularly civil society organizations and Indigenous groups – are skeptical about inclusiveness within the decision-making process. Social inequalities and local power relations may hinder the implementation of participation instruments and the involvement of local and Indigenous communities, impeding their ability to achieve reduced deforestation and poverty alleviation. The political economy and the lack of data on deforestation and forest degradation – and on the recently discovered large swamp in the DRC – make it challenging to monitor, report and verify a reduction in forest emissions within a multilevel setting. The experience of REDD+ tested at scale in the DRC through the Mai-Ndombe jurisdictional project highlights the cost challenges of generating timely and accurate data. Supporting REDD+ finance in the DRC is difficult since the country relies entirely on international funding to fight climate change. A benefits-sharing mechanism remains unclear. Consequently, there is a lack of flexibility in addressing unanticipated costs that may result from the implementation of the process. This jeopardizes the success of the process and raises uncertainty about the expected results. Emerging issues, such as community forestry and the discovery of large swamp areas, make the DRC more attractive for the REDD+ program. The first issue offers a workaround to the problem of securing communal rights, while the second issue provides additional opportunities for REDD+ activities.
DRC has committed to reduce its emissions effectively, efficiently, and equitably from deforestation and degradation (REDD+). The country experiences complex relationships between drivers, agents, and institutions of deforestation nationally. The REDD+ policy arena is influenced by both governmental and non-governmental actors whose number have increased in the policy arena over the years; however, weak coordination among these actors remains an issue. Since 2009, the DRC has announced several reforms relating to land tenure, land-use planning and agricultural policy, to create an institutional environment that motivates the implementation of REDD+ in the DRC. By 2019, none of these reforms had materialized, due to both political changes and a lack of finance, capacity, and political will. Between 2013 and 2019, little progress has been made on REDD+ in the DRC, as a result of conflicting interests among actors both at national and decentralized levels; information asymmetry; elite capture and corruption; and the pre- and post-election situation. To date, the effectiveness of REDD+ activities in the DRC remain unclear, due to the absence of rigorous impact assessment. However, efforts can be observed on the field where there is increased number of participants to forest policy process compared to REDD+ early years; and several ongoing projects are testing policy options within and across levels. If these efforts are sustained, they can contribute in putting in place conditions to achieve REDD+ objectives.
REDD+ must be transformational. REDD+ requires broad institutional and governance reforms, such as tenure, decentralisation, and corruption control. These reforms will enable departures from business as usual, and involve communities and forest users in making and implementing policies that a ect them. Policies must go beyond forestry. REDD+ strategies must include policies outside the forestry sector narrowly de ned, such as agriculture and energy, and better coordinate across sectors to deal with non-forest drivers of deforestation and degradation. Performance-based payments are key, yet limited. Payments based on performance directly incentivise and compensate forest owners and users. But schemes such as payments for environmental services (PES) depend on conditions, such as secure tenure, solid carbon data and transparent governance, that are often lacking and take time to change. This constraint reinforces the need for broad institutional and policy reforms. We must learn from the past. Many approaches to REDD+ now being considered are similar to previous e orts to conserve and better manage forests, often with limited success. Taking on board lessons learned from past experience will improve the prospects of REDD+ e ectiveness. National circumstances and uncertainty must be factored in. Di erent country contexts will create a variety of REDD+ models with di erent institutional and policy mixes. Uncertainties about the shape of the future global REDD+ system, national readiness and political consensus require  exibility and a phased approach to REDD+ implementation.
Integration of peatlands into land-use monitoring systems is central to the conservation of their carbon storage – be they conserved, degraded or restored. Healthy peatlands mitigate climate change, enhance adaptive capacity and maintain ecosystem services and biodiversity. Albeit peatlands are starting to receive a high level of attention and the scientific basis for their monitoring has quickly developed over the last few years. Robust and practical approaches and tools for developing and integrating peatland-monitoring into national monitoring and reporting frameworks is an important opportunity for countries to limit global warming to 2 °C.
Key messagesIndonesia and Peru harbor some of the largest lowland tropical peatland areas. Indonesian peatlands are subject to much greater anthropogenic activity than Peru's resulting in high GHG and particulate emissions.We explored patterns of impact in both countries and compared predisposing factors. Impacts differ greatly among Indonesian regions and the Peruvian Amazon in the order: Sumatra > Kalimantan > Papua > Peru.All impacts, except fire, are positively related to population density.Current peatland integrity in Peru arises from a confluence of factors that has slowed development, with no absolute barriers protecting Peruvian peatlands from a similar fate to Indonesia's.If the goal is to maintain the integrity of Peruvian peatlands, government policies recognizing unique peatland functions and sensitivities will be necessary.
Constructive critique. This book provides a critical, evidence-based analysis of REDD+ implementation so far, without losing sight of the urgent need to reduce forest-based emissions to prevent catastrophic climate change. REDD+ as envisioned
The Congo Basin comprises Cameroon, Central African Republic, the Democratic Republic of Congo, the Republic of Congo, Equatorial Guinea and Gabon. It covers close to 70% of the forestlands of Africa. Of the 530 million hectares in the Congo Basin, 300 million are composed of forests: 99% of these are primary or naturally regenerated forests, as opposed to plantations.
Cambridge, UK : Cambridge University Press, 1998.
Tropical peatlands are found mostly in South East Asia, but also in Africa and in Central and South America. They and peat-swamp forests store large amounts of carbon and their destruction, particularly through the development of plantations for oil palm and other forms of agriculture, releases large quantities of greenhouse gases which contribute to climate change. They are also complex and vulnerable ecosystems, home to great biodiversity and a number of endangered species such as the orang utan.The aim of this book is to introduce this little known but important and vulnerable ecosystem in a way that explains its long standing interaction with the global carbon cycle and how it is being destroyed by deforestation and inappropriate development. The authors describe the origin and formation of peat in the tropics, its current location, extent and amount of carbon stored in it, its biodiversity and natural resource functions and key ecological functions and processes. Appropriate hydrology is the key to the development and maintenance of peatlands and the unique aspects of tropical peatland water supply and management are also explored. In the same vein the nutrient dynamics and budgets of this ecosystem are explained in order to show how complex habitats can be maintained mainly by rainwater containing very low concentrations of essential chemical elements. Past and present impacts on tropical peatlands in SE Asia are discussed and the need for restoration and wise use highlighted. Finally, projections are made about the future of this ecosystem as a result of continuing human impacts and climate change.