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Global Environmental Change-human and Policy Dimensions | 2001

The causes of land-use and land-cover change: moving beyond the myths

Eric F. Lambin; Barry Turner; Helmut J. Geist; Samuel Babatunde Agbola; Arild Angelsen; John W. Bruce; Oliver T. Coomes; Rodolfo Dirzo; G. Fischer; Carl Folke; P.S. George; Katherine Homewood; Jacques Imbernon; Rik Leemans; Xiubin Li; Emilio F. Moran; Michael Mortimore; P.S. Ramakrishnan; John F. Richards; Helle Skånes; Will Steffen; Glenn Davis Stone; Uno Svedin; Tom Veldkamp; Coleen Vogel; Jianchu Xu

Common understanding of the causes of land-use and land-cover change is dominated by simplifications which, in turn, underlie many environment-development policies. This article tracks some of the major myths on driving forces of land-cover change and proposes alternative pathways of change that are better supported by case study evidence. Cases reviewed support the conclusion that neither population nor poverty alone constitute the sole and major underlying causes of land-cover change worldwide. Rather, peoples’ responses to economic opportunities, as mediated by institutional factors, drive land-cover changes. Opportunities and


Environmental Research Letters | 2012

An assessment of deforestation and forest degradation drivers in developing countries

Noriko Hosonuma; Martin Herold; Veronique De Sy; Ruth S De Fries; Maria Brockhaus; Louis Verchot; Arild Angelsen; Erika Romijn

Countries are encouraged to identify drivers of deforestation and forest degradation in the development of national strategies and action plans for REDDC. In this letter we provide an assessment of proximate drivers of deforestation and forest degradation by synthesizing empirical data reported by countries as part of their REDDC readiness activities, CIFOR country profiles, UNFCCC national communications and scientific literature. Based on deforestation rate and remaining forest cover 100 (sub)tropical non-Annex I countries were grouped into four forest transition phases. Driver data of 46 countries were summarized for each phase and by continent, and were used as a proxy to estimate drivers for the countries with missing data. The deforestation drivers are similar in Africa and Asia, while degradation drivers are more similar in Latin America and Asia. Commercial agriculture is the most important driver of deforestation, followed by subsistence agriculture. Timber extraction and logging drives most of the degradation, followed by fuelwood collection and charcoal production, uncontrolled fire and livestock grazing. The results reflect the most up to date and comprehensive overview of current national-level data availability on drivers, which is expected to improve over time within the frame of the UNFCCC REDDC process.


Journal of Development Economics | 1999

Agricultural expansion and deforestation: modelling the impact of population, market forces and property rights

Arild Angelsen

Abstract This paper compares four different modelling approaches to agricultural expansion and deforestation, and explores the implications of assumptions about the household objectives, the labour market, and the property rights regime. A major distinction is made between population and market based explanations. Many of the popular policy prescriptions are based on the population approach, assuming subsistence behaviour and limited market integration. Within a more realistic—particularly for the long term effects—market approach, well-intentioned policies such as agricultural intensification programmes may boost deforestation. Many forest frontier contexts are also characterized by forest clearing giving farmers land rights. Deforestation becomes an investment to the farmer and a title establishment strategy. Land titling and credit programmes may therefore increase deforestation.


World Development | 2014

Environmental Income and Rural Livelihoods: A Global-Comparative Analysis

Arild Angelsen; Pamela Jagger; Ronnie Babigumira; Brian Belcher; Nicholas Hogarth; Simone Bauch; Jan Börner; Carsten Smith-Hall; Sven Wunder

Summary This paper presents results from a comparative analysis of environmental income from approximately 8000 households in 24 developing countries collected by research partners in CIFOR’s Poverty Environment Network (PEN). Environmental income accounts for 28% of total household income, 77% of which comes from natural forests. Environmental income shares are higher for low-income households, but differences across income quintiles are less pronounced than previously thought. The poor rely more heavily on subsistence products such as wood fuels and wild foods, and on products harvested from natural areas other than forests. In absolute terms environmental income is approximately five times higher in the highest income quintile, compared to the two lowest quintiles.


Ecology and Society | 2008

Why Forests Are Important for Global Poverty Alleviation: a Spatial Explanation

William D. Sunderlin; Sonya Dewi; Atie Puntodewo; Daniel Müller; Arild Angelsen; Michael Epprecht

Forests have been declared important for the well-being of the poor because of the kinds of goods and services that they provide. We asked whether forests are important for the poor not only because of the kinds of goods and services they provide, but also because they tend to be located where the poor are. We conducted a spatial analysis to ascertain the degree of spatial association between poverty and forests in seven countries: Brazil, Honduras, Malawi, Mozambique, Uganda, Indonesia, and Vietnam. For most of these countries, there was a significant positive correlation between high natural forest cover and high poverty rate (the percentage of the population that is poor) and between high forest cover and low poverty density (the number of poor per unit area). We explain the findings and discuss policy implications and topics for future research.


Archive | 2007

Forest cover change in space and time: combining the von Thunen and forest transition theories

Arild Angelsen

This paper presents a framework for analyzing tropical deforestation and reforestation using the von Thunen model as its starting point: land is allocated to the use which yields the highest rent, and the rents of various land uses are determined by location. Forest cover change therefore becomes a question of changes in rent of forest versus non-forest use. While this is a simple and powerful starting point, more intriguing issues arise when this is applied to analyze real cases. An initial shift in the rent of one particular land use generates feedbacks which affect the rent of all land uses. For example, a new technology in extensive agriculture should make this land use more profitable and lead to more forest clearing, but general equilibrium effects (changes in prices and local wages) can modify or even reverse this conclusion. Another issue is how a policy change or a shift in broader market, technological, and institutional forces will affect various land use rents. The paper deals with three such areas: technological progress in agriculture, land tenure regimes, and community forest management. The second part of the paper links the von Thunen framework to the forest transition theory. The forest transition theory describes a sequence over time where a forested region goes through a period of deforestation before the forest cover eventually stabilizes and starts to increase. This sequence can be seen as a systematic pattern of change in the agricultural and forest land rents over time. Increasing agricultural rent leads to high rates of deforestation. The slow-down of deforestation and eventual reforestation is due to lower agricultural rents (the economic development path) and higher forest rent (the forest scarcity path). Various forces leading to these changes are discussed and supported by empirical evidence from different tropical regions.


Ecology and Society | 2013

Who Should Benefit from REDD+? Rationales and Realities

Cecilia Luttrell; Lasse Loft; M.F. Gebara; Demetrius Kweka; Maria Brockhaus; Arild Angelsen; William D. Sunderlin

Benefit-sharing mechanisms are a central design aspect of REDD+ because they help to create the necessary incentives to reduce carbon emissions. However, if stakeholders do not perceive the benefit sharing as fair, the legitimacy of REDD+, and support for the mechanism, will be weakened. In this paper, drawing on data from CIFOR’s Global Comparative Study on REDD+, we analyze national policy processes in 6 countries and incipient benefit-sharing arrangements in 21 REDD+ project sites. Through our analysis of current practices and debates, we identify six rationales that have been put forward to justify how benefits should be distributed and to whom. These rationales encompass a range of perspectives. Some hold that benefit sharing should be related to actual carbon emission reductions or to costs incurred in achieving the reduction of emissions; others emphasize the importance of a legal right to benefit, the need to consider aspects such as poverty reduction or the appropriateness of rewarding those with a history of protecting the forest. Each rationale has implications for the design of benefit-sharing mechanisms and the equity of their outcomes. We point out that, given the wide range of rationales and interests at play, the objectives of REDD+ and benefit sharing must be clearly established and the term “benefit” defined before effective benefit-sharing mechanisms can be designed. For stakeholders to support REDD+, the legitimacy of decision-making institutions, consideration of context, and attention to process are critical. Building legitimacy requires attention not only to fair distributional outcomes but also to consensus on relevant institutions’ authority to make decisions and to procedural equity.


Journal of Natural Resources Policy Research | 2010

Managing the Miombo Woodlands of Southern Africa: policies, incentives, and options for the rural poor

Peter A. Dewees; Bruce M. Campbell; Yemi Katerere; Almeida Sitoe; Anthony Cunningham; Arild Angelsen; Sven Wunder

Abstract Miombo woodlands cover vast areas of southern Africa. Of comparatively little interest for export-oriented commercial logging, they are part of a complex system of rural land use that integrates woodland management with crops and livestock. There is also evidence that woodland resources are extensively used for household consumption, greatly reducing the risk of households falling deeper into poverty as a result of environmental or economic stress. New opportunities for improving the management of miombo woodlands, with poverty mitigation in mind, suggest four policy options. First, communities are becoming more active in managing local natural resources, a result of decentralization and land reforms, which suggests that there may be good scope for strengthening related policy and legal frameworks and the measures to implement them. Second, new and integrated conservation-development approaches are emerging, which suggests possible scope for providing payments for environmental services to increase the value of managed woodlands. Third, markets throughout the region are developing and expanding, which suggests great scope for enhancing forest-based markets by removing restrictive legislation and by supporting local producers and forest enterprises. Fourth, all these opportunities suggest that public forest institutions can be revitalized by strengthening their service delivery orientations, with poverty mitigation as a main objective.


Review of Environmental Economics and Policy | 2013

Designing and Implementing Effective REDD + Policies: A Forest Transition Approach

Arild Angelsen; Thomas Rudel

Effective policies to halt deforestation depend critically on the forest context. This article uses a forest transition framework to discuss three forest contexts: remote (core) forest areas, frontier forests, and forest-agriculture mosaics. Just as the drivers and capabilities differ across these three contexts or stages, so too do the appropriate government policies. The first stage represents forests that are protected passively by their remote location, where the challenge is to maintain low deforestation rates. Thus high priority should be given to avoiding or redesigning infrastructure developments, resettlements, and other large-scale projects that can accelerate deforestation. Clarifying tenure and local forest rights and creating protected areas can also be helpful. In frontier forests, well-defined property rights, if present, provide a basis for using direct incentive and compensation schemes such as payments for environmental services. Avoiding perverse government policies, such as subsidized credit for deforesting activities, would also reduce the high deforestation rates that characterize this second stage. In largely settled forest-agriculture mosaics, government policies can augment emerging market-based incentives to plant trees. Improved agricultural technologies, which at early stages tend to stimulate agricultural land expansion, can also be important at later stages by increasing food production on existing agricultural land.


World Development | 2001

Economic Crisis, Small Farmer Well-Being, and Forest Cover Change in Indonesia

William D. Sunderlin; Arild Angelsen; Daju Pradnja Resosudarmo; Ahmad Dermawan; Edy Rianto

Field research was conducted on 1,050 Indonesian households to understand the effects of the Asian economic crisis on the well-being of small farmers outside of Java and on their forest-clearing practices. The main findings are: (a) most farmers perceived themselves as worse off during the crisis than before, challenging the claim that farmers with export income would be better off and (b) forest clearing by farmers increased significantly during the crisis to expand rubber holdings and other tree crops, with the aim of increasing future income security. Among the policy lessons are that crop diversification and targeted aid can minimize impoverishment and avert increased forest clearing following macroeconomic destabilization.

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Sven Wunder

Center for International Forestry Research

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David Kaimowitz

Center for International Forestry Research

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Maria Brockhaus

Center for International Forestry Research

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Martin Herold

Wageningen University and Research Centre

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Ronnie Babigumira

Norwegian University of Life Sciences

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John Herbert Ainembabazi

International Institute of Tropical Agriculture

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Charles Jumbe

University of Agriculture

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