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Valuation of Biodiversity Benefits (OECD)

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original studies. Section 4 concludes with the main challenges for benefit transfer and some policyimplications.Policy use <strong>of</strong> biodiversity valuation estimates in NorwayIn Norway about 30 empirical environmental valuation studies <strong>of</strong> biodiversity have beencarried out since the early 1980s. Many <strong>of</strong> these studies have been initiated and funded by the Ministry<strong>of</strong> Environment and its affiliated institutions: the State Pollution Control Authority (SFT) and theDirectorate <strong>of</strong> Nature Management (DN). Both Travel Cost (TC) and Contingent <strong>Valuation</strong> (CV)methods have been used to estimate the use value <strong>of</strong> freshwater fish (recreational fishing) and wildlife(hunting and viewing). There have also been CV studies <strong>of</strong> the non-use value (and some use value) <strong>of</strong>endangered species, such as the three big carnivores in Norway (brown bear, wolverine, and wolf);insects, fungi and lichens growing in old growth coniferous forests; and the genetic diversity <strong>of</strong> localtrout and salmon stocks threatened by acidification.Benefit estimates from CV studies on the impacts from improved water and air quality havebeen utilised by SFT in a CBA <strong>of</strong> measures to reduce air and water pollution on the local, regional andnational level since the mid-80s. During the past 5 years SFT has funded new CV studies to create anupdated list <strong>of</strong> values to use in CBA evaluations. In the early 1990s the Directorate <strong>of</strong> Public Roads(DPR) also funded new CV studies on valuations for noise, local air pollution, and soiling from roadtraffic. The DPR has included these valuations in their new manual and s<strong>of</strong>tware package forundertaking CBAs <strong>of</strong> road projects. A CBA is required for all new road projects in Norway. Both theSFT and DPR analyses plays an important administrative role. The SFT analyses have also had a largeinfluence on policy decisions, while the DPR analyses play a relatively minor role in the politicaldecision making on road projects.The administrative and political use <strong>of</strong> benefit estimates <strong>of</strong> biodiversity is much less regular.In most cases the economic estimates <strong>of</strong> biodiversity and a CBA are used to support decisions, butthey are seldom decisive. However, there are also examples where the valuation estimates have playedan important role in the decision making process.Three case studies are discussed [Navrud (1993)]:a) CBA <strong>of</strong> preservation <strong>of</strong> the brown bear, wolf, and wolverine;b) CBA <strong>of</strong> liming acidified lakes and rivers to preserve the genetic diversity <strong>of</strong> local salmonand trout stocks; andc) CBA <strong>of</strong> the preservation <strong>of</strong> biodiversity in old growth coniferous forestsIn case A the benefit estimate was used to support the policy decision, in case B the benefitestimate played a much more decisive role, while in case C the benefit estimates had little or no effecton the decision taken.Obstacles to the wider use <strong>of</strong> environmental valuationFive main categories <strong>of</strong> potential obstacles for wider use <strong>of</strong> environmental valuation can beidentified.65

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