BORIS M. HILLMANN, JAN BARKMANN, RAINER MARGGRAF
Georg-August-Universität Göttingen, Department of Agricultural Economics and Rural Development, Germany
Recent estimates of the economic value of ecosystem conservation imply that conservation of primary ecosystems is up to 100 times as beneficial than ecosystem conversion to agriculture or silviculture. A substantial share of these benefits stem from indirect use and non-use values stated by OECD citizens. These `willingness"=to-pay' (WTP) figures are then applied to conservation areas in developing countries.
The southern Ecuadorian Andes, e.g., the area of the Biosphere Reserve Podocapus-El Cóndor (BRPC), are a hotspot of biodiversity. The remaining primary forests are threatened by smallholder encroachment in the northern part of BRPC. Here, forested land is converted to pasture to raise cattle. At a net profit of about 100USDyr-1ha-1, cattle farming is the most profitable smallholder land-use option. Selective logging (10USDyr-1ha-1) or alder plantations (90USDyr-1ha-1) are economically not attractive without external financial support. Does international non"=use WTP for the conservation of biological diversity suffice to compensate farmers for lost profits from the non"=conversion of BRPC forests?
Menzel (2003) estimated an average WTP of 108 yr-1 for German citizens for avoiding the projected loss of a half of 50.000 endangered species in developing countries. Assuming that this figure represents the maximum WTP for additional international biodiversity conservation by each of the 290 million OECD households, roughly 31.6 billon yr-1 could be generated. The total area of remaining primary vegetation in the 25 global biodiversity hotspots amounts to 2.123 million km2 resulting in a WTP for additional conservation of 150 ha-1yr-1. At current /USD exchange rates, this appears sufficient to compensate losses from any agricultural or silvicultural development restrictions.
Among other issues in the application of stated preference studies, the `benefit transfer' necessary to apply international WTP estimates to local conservation problems poses multiple conceptual challenges. Strictly speaking, none of the currently available WTP studies can directly be applied to the BRPC case as the Ecuadorian Andes (or their species) are not explicitly addressed in any of the studies. To improve the situation, new systematically surveyed data are necessary that allow for a flexible spatial reference across multiple scales.
Keywords: Benefit transfer, biodiversity conservation, economic valuation, willingness-to-pay, Zamora
Poster (pdf-Format): http://www.tropentag.de/2008/abstracts/posters/651.pdf