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
(1) Cost and time constraintsThe cost <strong>of</strong> and the time required to undertake a new CV study have increased, in particularif the study complies with the set <strong>of</strong> guidelines put forward by the NOAA panel in the US [Arrow etal. (1993)]. For these reasons there is an increased interest in benefit transfer, i.e. transferringestimates from previous valuation studies to value impacts <strong>of</strong> another project or policy. However, littleis known about the validity <strong>of</strong> these new estimates. One should be very careful when transferringestimates, particularly for complex goods, goods with a large non-use component, or both, for instancefor ecosystems and biodiversity. More work on the validity <strong>of</strong> benefit transfers is needed.(2) Methodological problemsMethodological problems due to the uncertainty both in the measurement <strong>of</strong> biodiversity andhow it is affected by a new project or policy, and the measurement <strong>of</strong> the economic value <strong>of</strong>biodiversity, may lead to invalid estimates. This is the most important obstacle to the wider use <strong>of</strong>benefits transfer. The validity <strong>of</strong> economic estimates from CV studies, especially for non-use values,has been questioned. The main question asked by policymakers is: “Can we trust the economicestimates <strong>of</strong> biodiversity and ecosystems - Will people actually pay the amounts they state they arewilling to pay in CV surveys?” Navrud and Veisten (1997) combined hypothetical donations from aCV study with actual donations to preserve biodiversity in old growth coniferous forests inOslomarka, Norway. The same respondents were asked to actually donate what they stated in the CVstudy to create an upper and lower bound, respectively, for the welfare measure, WTP to preservebiodiversity. Everybody had to pay, if, aggregated WTP for preservation exceeded the social costs <strong>of</strong>preservation. The bound proved to be sufficiently small (i.e. mean WTP <strong>of</strong> about 3-13euro/household/year) to be informative in a CBA <strong>of</strong> preserving 13 old growth forest areas. It would beuseful to have more studies comparing actual and hypothetical WTP for biodiversity preservation.(3) Information and communication problemsLack <strong>of</strong> information about valuation techniques among decision makers at different levelsmakes it difficult to defend the results <strong>of</strong> valuation studies against, <strong>of</strong>ten unjustified, critique fromaffected interest groups. Ethical concerns combined with scepticism towards neoclassical welfareeconomics, which is the foundation <strong>of</strong> CBA and environmental valuation methods, are the mostimportant reasons for such criticism. Increased and improved dissemination activities, and training <strong>of</strong>bureaucrats and decision-makers by valuation researchers, has proved effective in improvingacceptance <strong>of</strong> environmental valuation techniques in Norway.(4) Administrative constraintsThe lack <strong>of</strong> legal basis for doing CBAs, and the absence <strong>of</strong> environmental valuationtechniques in administrative guidelines for CBAs, discourages environmental benefit estimation. InNorway, a theoretical CBA manual, and practical CBA guidelines for evaluation <strong>of</strong> public projects andpolicies, have been prepared [NOU (1997:27) and NOU (1998:16)]. These manuals have specialsections on valuing environmental impacts. The previous CBA manual, issued in 1979, contained noinformation on environmental valuation techniques. The new CBA guidelines recommend usingenvironmental valuation techniques for local environmental problems, e.g. soiling and noise from roadtraffic and recreational areas. However, they raise caution on including non-use values in CBAsbecause <strong>of</strong> the uncertainty <strong>of</strong> CV studies for valuing non-use values (see also (2) above).66
- Page 1 and 2:
«ENVIRONMENTValuation ofBiodiversi
- Page 3 and 4:
ORGANISATION FOR ECONOMIC CO-OPERAT
- Page 5 and 6:
TABLE OF CONTENTSPART 1 ...........
- Page 7 and 8:
PART 4 ............................
- Page 10 and 11: Why value biodiversity?There are th
- Page 12 and 13: Figure 1.1 Total economic value: us
- Page 14 and 15: from biodiversity at the local leve
- Page 16 and 17: in the database and also for undert
- Page 18 and 19: in the policy context. This is high
- Page 20: Table 1.3 Policy Options for the Cl
- Page 23 and 24: Box 1.2 Value of Turkey’s Forests
- Page 25 and 26: of the most important implications
- Page 27 and 28: Additionally, valuation does not ju
- Page 29 and 30: value is the habitat, many differen
- Page 31 and 32: are very modest. More recently, new
- Page 33 and 34: Table 2.2 Estimates of the Medicina
- Page 35 and 36: The importance of indirect use valu
- Page 37 and 38: pharmaceutical use, although the li
- Page 39 and 40: McAllister, D., (1991). Estimating
- Page 41 and 42: Simpson, D and Craft, A.. (1996).
- Page 43 and 44: practice, the overlap between these
- Page 45 and 46: aimed at giving more precise quanti
- Page 47 and 48: structural values. There are a numb
- Page 49 and 50: Reid (forthcoming) discusses the po
- Page 51 and 52: Ecotourism as a Way to Generate Loc
- Page 53 and 54: endangered Indian rhino and other t
- Page 55 and 56: ReferencesBann, C., and M. Clemens
- Page 57 and 58: PART 261
- Page 59: many European countries, CBA has a
- Page 63 and 64: activity day, there is greater vari
- Page 65 and 66: added independent variable C s= cha
- Page 67 and 68: error in valuing respiratory sympto
- Page 69 and 70: ReferencesArrow, K.J., R. Solow, E.
- Page 71 and 72: OECD (1995). The Economic Appraisal
- Page 73 and 74: CHAPTER 5:by José Manuel LIMA E SA
- Page 75 and 76: linkages usually lead to diverse co
- Page 77 and 78: A discrete choice approach to quest
- Page 79 and 80: Table 5.2 Model-based point estimat
- Page 81 and 82: is potentially very large for multi
- Page 83 and 84: P3 is already in the mix is 2.51, s
- Page 85 and 86: PART 391
- Page 87 and 88: measures of value. An appendix to t
- Page 89 and 90: features (such as parks, beaches or
- Page 91 and 92: included in cost-benefit analysis o
- Page 93 and 94: A Discussion of Past Efforts to Dev
- Page 95 and 96: Satellite AccountsIn addition to th
- Page 97 and 98: which many people argue are associa
- Page 99 and 100: approach to competing uses of water
- Page 101 and 102: Figure 6.2 Trade-Off AnalysisEnviro
- Page 103 and 104: However, the farmers need not bear
- Page 105 and 106: Appendix 1: Theory and Application
- Page 107 and 108: iwhere C is the income adjustment n
- Page 109 and 110: complete. If there are more than on
- Page 111 and 112:
Horowitz, Joel. L. and Jordan. J. L
- Page 113 and 114:
CHAPTER 7:by Dennis M. KING and Lis
- Page 115 and 116:
Box 7.1 Definition of terms related
- Page 117 and 118:
Box 7.2 Categories of Ecosystem Ser
- Page 119 and 120:
Box 7.4 Dollar-based ecosystem valu
- Page 121 and 122:
Non-monetary indicators of ecosyste
- Page 123 and 124:
Figure 7.1 Effects of Wetland Locat
- Page 125 and 126:
description, and that the usefulnes
- Page 127 and 128:
2) Service capacity sub-indexIndica
- Page 129 and 130:
wetlands, for example, results in F
- Page 131 and 132:
(1) Functional CapacityIndexFigure
- Page 133 and 134:
constituents of runoff can be predi
- Page 135 and 136:
Service(on or off site)Recreational
- Page 137 and 138:
Table 7.3 Service Risk Sub-index De
- Page 139 and 140:
Measuring Service Preference Weight
- Page 141 and 142:
Table 7.4 Illustration of Paired Co
- Page 143 and 144:
PART 4151
- Page 145 and 146:
Ecological foundations for biodiver
- Page 147 and 148:
Phenotic diversity is a measure bas
- Page 149 and 150:
Operationalisation of the biotic-ri
- Page 151 and 152:
ten attributes that could score a m
- Page 153 and 154:
The choice of the scale relates to
- Page 155 and 156:
Nature measurement methodIn 1995, t
- Page 157 and 158:
Table 8.4 Value orientations and en
- Page 159 and 160:
Table 8.5 Identification of monetar
- Page 161 and 162:
Table 8.6 Valuation studiesSingle s
- Page 163 and 164:
in waterway systems for nine impact
- Page 165 and 166:
to other contexts, conditions, loca
- Page 167 and 168:
ReferencesAkcakaya, H.R. (1994).
- Page 169 and 170:
de Groot, R.S. (1994). “Environme
- Page 171 and 172:
Mace, G. M. & S. N. Stuart. (1994).
- Page 173 and 174:
Turner, R.K., Perrings, C. and Folk
- Page 175 and 176:
John A. DixonJohn A. Dixon is Lead
- Page 177 and 178:
Robert O’NeillDr. O’Neill recei
- Page 179 and 180:
Steven StewartSteven Stewart is Ass
- Page 181:
OECD PUBLICATIONS, 2, rue André-Pa