Elsevier

Ecological Economics

Volume 64, Issue 2, 15 December 2007, Pages 374-385
Ecological Economics

Paying for the environmental services of silvopastoral practices in Nicaragua

https://doi.org/10.1016/j.ecolecon.2007.04.014Get rights and content

Abstract

Agricultural landscapes can provide many valuable ecosystem services, but many are externalities from the perspective of farmers and so tend to be under-produced. This paper examines an effort to make direct payments for ecosystem services (PES) in an agricultural landscape. The Regional Integrated Silvopastoral Ecosystem Management Project is piloting the use of PES to induce adoption of silvopastoral practices in the Matiguás–Río Blanco area in Nicaragua. Silvopastoral practices could substantially improve service provision while retaining agricultural production, but they have found only limited acceptance among farmers. The Silvopastoral Project seeks to increase their adoption by paying farmers for the expected increase in biodiversity conservation and carbon sequestration services that these practices would provide. The Project developed an ‘environmental services index’ (ESI) and pays participants for net increases in ESI points. Although the Silvopastoral Project is still underway, it already appears to have succeeded in inducing farmers to increase substantially the use of practices that generate higher levels of ecosystem services. In the project's first two years, over 24% of the total area experienced some form of land use change. The area of degraded pasture fell by two thirds, while pastures with high tree density increased substantially, as did fodder banks and live fences. On-going monitoring indicates that these land use changes are in fact generating the desired services. Questions remain about the long-term sustainability of the approach, however. To ensure sustainability, long-term payments are likely to be needed, raising the question of how they will be financed. Payments by water users and by carbon buyers provide a partial answer to this challenge, but still leave many gaps.

Introduction

Agricultural landscapes can provide many valuable ecosystem services. They can contain high levels of biodiversity, sequester substantial amounts of carbon, and affect downstream water supplies. Many of these services are externalities from the farmers' perspective, however, and so tend to be under-produced. Recent years have seen numerous efforts to devise innovative mechanisms to induce farmers to adopt practices that generate higher levels of services (Landell-Mills and Porras, 2002, Pagiola et al., 2002). An approach that has received increasing attention is to pay farmers directly to provide ecosystem services (Ferraro, 2001, Pagiola and Platais, 2007).

This paper examines one effort to make direct payments for ecosystem services (PES) in an agricultural landscape. The Regional Integrated Silvopastoral Ecosystem Management Project, financed by the Global Environment Facility (GEF), is piloting the use of PES to induce adoption of silvopastoral practices at sites in Nicaragua, Colombia, and Costa Rica (Pagiola et al., 2004). The extensive pastures that replaced the original forests in this area provide particularly low levels of services — with little biodiversity, low carbon sequestration, and adverse impacts on hydrological flows. Silvopastoral practices could substantially improve service provision while retaining agricultural production, but have found only limited acceptance among farmers. The Silvopastoral Project seeks to increase their adoption by paying farmers for the expected increase in biodiversity conservation and carbon sequestration services that these practices would provide.

This paper describes the Silvopastoral Project and its initial results at its Nicaragua site. We begin by describing the benefits of silvopastoral practices and the reasons for their limited adoption. We then discuss the PES approach, and how it is applied in this case. The first two years of the project have already resulted in substantial increases in service provision. Although this project is still underway, it is already generating important lessons for similar efforts.

Section snippets

Silvopastoral practices

Cattle production has long been an important cause of the loss of natural habitat and biodiversity in Central America (Downing et al., 1992, Kaimowitz, 1996). In addition to the environmental problems caused by the initial deforestation, extensive grazing often suffers from declining yields, diminishing grass cover, soil erosion, water supply contamination, air pollution, and landscape degradation. Declining producer income results in continuing poverty and can lead to pressure to clear

Barriers to adoption

Despite their many benefits, silvopastoral practices have seen limited adoption (Dagang and Nair, 2003). Large areas remain under extensive pasture with minimal tree cover.

The low profitability of silvopastoral practices from the farmers' perspective is an important constraint to their adoption. Establishment costs in Matiguás–Río Blanco range from US$180/ha for sowing improved pasture to about US$400/ha for planting trees at high density in pastures. Establishing fodder banks costs

Payments for environmental services

PES is a market-based approach to conservation based on the twin principles that those who benefit from environmental services (such as users of clean water) should pay for them, and that those who generate services should be compensated for providing them (Wunder, 2005, Pagiola and Platais, 2007). The approach seeks to create mechanisms to arrange transactions between service users and providers that are in both parties' interests, thus internalizing what would otherwise be an externality. In

Implementing PES in Matiguás–Río Blanco, Nicaragua

The Silvopastoral Project is piloting the use of PES to generate biodiversity conservation and carbon sequestration by encouraging the adoption of silvopastoral practices in degraded pastures in three areas: Quindío, in Colombia; Esparza, in Costa Rica; and Matiguás–Río Blanco, in Nicaragua (Pagiola et al., 2004). The project is financed by a US$4.5 million GEF grant with the World Bank as the implementing agency. It is being implemented in the field by local non-governmental organizations

Results

The Silvopastoral Project made its first payments, for baseline ESI points, in July 2003. After monitoring land use changes, it made its first payment for increases in ESI scores in May 2004, and a second payment in May 2005. Additional payments will be made in 2006 and 2007.

Three data sets are available to study the impact of PES in Matiguás–Río Blanco. A baseline survey conducted in late 2002, during project preparation, collected detailed information on household characteristics. A second

Sustainability and replicability

Initial results from the project suggest that PES can induce land use change, and that silvopastoral practices can generate environmental services. But are these changes sustainable? And can the approach be extended to other areas?

Conclusions

Because most ecosystem services are externalities from the farmers' perspective, they tend to be underproduced. PES approaches such as that being piloted in Matiguás–Río Blanco have considerable potential for helping to increase the generation of ecosystem services in agricultural landscapes. Although the Silvopastoral Project is still underway, it already appears to have succeeded in inducing farmers to increase substantially the use of practices that generate higher levels of ecosystem

Acknowledgements

The opinions expressed in this paper are the authors' own and do not necessarily reflect those of the World Bank, GEF, Nitlapan, CATIE, or CIPAV. We would like to thank two anonymous reviewers for their helpful comments and suggestions.

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    Prepared for submission to Special Issue of Ecological Economics on “Ecosystem Services and Agriculture”, edited by S.M. Swinton, F. Lupi, S.H. Hamilton, and G.P. Robertson.

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