Our goal is to learn about the Costa Rican experience from the inside, working closely with FONAFIFO staff to understand how they have sought to improve efficiency and to explore options for setting payment levels and targeting to increase efficiency, without missing the myriad of norms, rules, and other obstacles that program managers might face in the implementation of, for example, procurement auctions.
Our hypothesis base on previous studies’ findings (see literature review section) suggest that so far PES are being assigned to big and relatively wealthy landowners, and that most landowners use the payment for investments within the property.
The adoption of good practices for the economic valuation of environmental services (ES) has strong implications in the evaluation and design of a Payment for Environmental Services program.
This study was carried to find out the impact of PES (Payment for Environmental Services) on the welfare of the communities in the Uluguru Mountains. The aim of the study is to assess the main objectives of the PES project which is to conserve the environment (forest) and reduce poverty. The assessment of the project is done by looking on the difference between the treatment group (those who participate in PES) and control group (households who do not participate).
Because the effectiveness of payment for ecosystem services (PES) programs depends on landowners’ engagement, understanding the relationship between the type of payment and participation is a key issue. This paper reports on a choice experiment that quantifies landowners’ preferences for cash and educational in-kind payment. The main results indicate a positive correlation between participation in a PES contract and the magnitude of the cash payment, while participation seems uncorrelated with the magnitude of the educational in-kind payment.
The People’s Republic of China-Global Environment Facility Partnership to Combat Land Degradation in Dryland Ecosystems promotes an integrated ecosystem management (IEM) approach to restore, sustain and enhance the productive capacity of dryland ecosystems.
Monetary contributions might not be an appropriate welfare measure in Contingent Valuation (CV) when household incomes are very low. In such cases, willingness to pay (WTP) is restricted by household's ability to reduce the consumption of other goods in order to pay for the environmental good under valuation. Beneficiaries, however, may be willing to contribute their time to work on the project instead of paying money.
A critical issue in the design of incentive mechanisms is the choice of whom to target. For forests, the leading schemes: [i] target locations with high ecosystem-service density; [ii] target additionality, i.e., locations where conservation would not occur without the incentive; or, at least effectively, [iii] reward previous private choices to conserve forest. We use a field experiment to examine the changes in contributions to forest conservation when we introduce each of those three selection rules.
This study was carried out to find out the impact of PES on the welfare of the communities in the Uluguru Mountains. The objective is to assess PES project which aims at conserving the environment (forest) and reducing poverty level.