Determinants of the environmental conservation and poverty alleviation objectives of Payments for Ecosystem Services (PES) programs

2019 ◽  
Vol 35 ◽  
pp. 52-66 ◽  
Author(s):  
Oreoluwa Ola ◽  
Luisa Menapace ◽  
Emmanuel Benjamin ◽  
Hannes Lang
2015 ◽  
Vol 7 (4) ◽  
pp. 1-40 ◽  
Author(s):  
Jennifer M. Alix-Garcia ◽  
Katharine R. E. Sims ◽  
Patricia Yañez-Pagans

Environmental conditional cash transfers are popular but their impacts are not well understood. We evaluate land cover and wealth impacts of a federal program that pays landowners for protecting forest. Panel data for program beneficiaries and rejected applicants allow us to control for fixed differences and time trends affecting both groups. We find the program reduces the expected land cover loss by 40–51 percent and generates small but positive poverty alleviation. Environmental gains are higher where poverty is low while household gains are higher where deforestation risk is low, illustrating the difficulty of meeting multiple policy goals with one tool. (JEL I32, I38, O13, O15, Q23, Q28, Q56)


2009 ◽  
Vol 45 (3) ◽  
pp. 488-501 ◽  
Author(s):  
Crystal Gauvin ◽  
Emi Uchida ◽  
Scott Rozelle ◽  
Jintao Xu ◽  
Jinyan Zhan

2011 ◽  
Vol 38 (4) ◽  
pp. 370-379 ◽  
Author(s):  
TIM DAW ◽  
KATRINA BROWN ◽  
SERGIO ROSENDO ◽  
ROBERT POMEROY

SUMMARYThe concept of ecosystem services (ES), the benefits humans derive from ecosystems, is increasingly applied to environmental conservation, human well-being and poverty alleviation, and to inform the development of interventions. Payments for ecosystem services (PES) implicitly recognize the unequal distribution of the costs and benefits of maintaining ES, through monetary compensation from ‘winners’ to ‘losers’. Some research into PES has examined how such schemes affect poverty, while other literature addresses trade-offs between different ES. However, much evolving ES literature adopts an aggregated perspective of humans and their well-being, which can disregard critical issues for poverty alleviation. This paper identifies four issues with examples from coastal ES in developing countries. First, different groups derive well-being benefits from different ES, creating winners and losers as ES, change. Second, dynamic mechanisms of access determine who can benefit. Third, individuals' contexts and needs determine how ES contribute to well-being. Fourth, aggregated analyses may neglect crucial poverty alleviation mechanisms such as cash-based livelihoods. To inform the development of ES interventions that contribute to poverty alleviation, disaggregated analysis is needed that focuses on who derives which benefits from ecosystems, and how such benefits contribute to the well-being of the poor. These issues present challenges in data availability and selection of how and at which scales to disaggregate. Disaggregation can be applied spatially, but should also include social groupings, such as gender, age and ethnicity, and is most important where inequality is greatest. Existing tools, such as stakeholder analysis and equity weights, can improve the relevance of ES research to poverty alleviation.


1970 ◽  
Vol 16 (2) ◽  
pp. 45-49
Author(s):  
R Shakya ◽  
SK Baral ◽  
R Basukala ◽  
S Khanal

(Author of this paper, S Khanal was omitted in error - added on 29-3-2010)Leasehold forestry in Nepal has sought to address both poverty alleviation and environmental conservation. The major agroforestry practices observed in the leasehold forests were silvopasture, hortisilviculture and Non Timber Forest Product (NTFP) cultivation. The most prominent problem to the users in adopting agroforestry practices was the lack of technical information. Some successful insights observed suggest that agroforestry has a notable potential to address dual objectives of poverty alleviation and conservation. The need to evolve sustainable mechanism for promoting agrofrorestry in degraded lands through the dissemination of useful traditional knowledge, innovative practices and improved technologies was identified. Key words: Leasehold forest; agroforestry; silvopasture; hortisilviculture; NTFP Banko Janakari Vol.16(2) 2006 pp.45-49


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