What then is the economic value <strong>of</strong> diversity in this broader sense? If diversity is critical toecosystem functioning, albeit in an uncertain fashion, then reduced diversity reduces the probabilitythat the ecosystem will survive. Its functions will then be lost. Hence the value <strong>of</strong> diversity can beapproximated by the value <strong>of</strong> the functions <strong>of</strong> the ecosystem. The kinds <strong>of</strong> values estimated for theThai mangrove system would then be relevant: loss <strong>of</strong> local, indirect, and global values. If this iscorrect, analysing the value <strong>of</strong> the functions <strong>of</strong> ecosystems amounts to conferring a value on diversity.But, uncertainty makes it difficult to know if measuring the value <strong>of</strong> these functions amounts to acomplete coverage <strong>of</strong> the value <strong>of</strong> biodiversity. Given the context <strong>of</strong> uncertainty, conservation <strong>of</strong>diversity may have a value greater than the values that can be assigned to the ‘outputs’ that theecosystem produces. To some extent these additional values are captured in the idea <strong>of</strong> option value,the value <strong>of</strong> conserving diversity because we may wish to make use <strong>of</strong> its beneficial effects in thefuture, and quasi-option value, the value <strong>of</strong> any information that might accrue by maintaining diversityrather than sacrificing it now.The pervasiveness <strong>of</strong> the uncertainty about the value <strong>of</strong> diversity suggests two things:- First, that, while placing economic values on the functions that we can value is essential,that activity may not capture the ‘total’ or ‘true’ economic value <strong>of</strong> diversity. Unless wehave a better feel for option-type values, our valuation is incomplete; and- Second, we should be cautious about sacrificing diversity.The ‘precaution’ in the second implication needs further explanation. A traditionalcost-benefit analysis has the capacity to incorporate a good deal <strong>of</strong> our concerns about uncertainty. Forexample, it is possible to introduce probabilities, if they are known, and work with expected valuesrather than certain values. If probabilities are known, we can also build risk aversion into the picture,i.e. we can weight quite heavily the losses that might occur if diversity is lost. But the problem withthis expected value approach (or expected utility approach where risk aversion is incorporated) is thatthe probabilities tend not to be known. We have pure uncertainty. Cost-benefit analysis is lessadaptable in this case and some authors have argued for use <strong>of</strong> the safe minimum standards approach(SMS) in such contexts. Under SMS there is a presumption in favour <strong>of</strong> conservation unless theopportunity costs are ‘high’ [Bishop (1978)]. Arguably, as people are better and better informed aboutthe value <strong>of</strong> diversity, i.e. as we learn more and disseminate that learning, so the SMS approach willapproximate a cost-benefit approach, because people’s preferences will be better informed. In themeantime, SMS is intuitively attractive because it forces us to ask whether we are really sure that thebenefits <strong>of</strong> sacrificing diversity are ‘high’. The problem remains, <strong>of</strong> course, that we have to be clear onwhat we mean by ‘unacceptably high’ costs.Indirect global use values: ecosystem servicesThe kinds <strong>of</strong> services that ecosystems provide include the protection <strong>of</strong> watersheds, climateregulation, waste assimilation, and nutrient cycling. Many <strong>of</strong> the benefits <strong>of</strong> these ecosystem functionsaccrue locally, and do not therefore appear to be <strong>of</strong> global significance. But since all living organismsdepend on these functions, there is a real sense in which the local benefits contribute to an overallglobal benefit. Barbier (1994) classifies these ecosystem functions as regulation, production, carrier,and information functions. Regulatory functions include the regulation <strong>of</strong> climate, water flow, wasteflows, and nutrients. Production functions refer to the useful outputs <strong>of</strong> ecosystems, such as water andfuel. Carrier functions relate to the support roles that ecosystems have for recreation, industry, fishing,agriculture, etc. Finally, information functions relate to aesthetic, cultural and scientific benefits.37
The importance <strong>of</strong> indirect use value can be illustrated in the context <strong>of</strong> mangroves. Bann(1998) lists the potential benefits <strong>of</strong> a mangrove resource as shown in Table 2.3 (with slightmodifications). The table reveals the wide range <strong>of</strong> functions that can be served by any one ecosystem.In each case, the ecological functions have economic value.Table 2.3 Economic value <strong>of</strong> a mangrove resourceUse valuesDirect value Indirect value Option valueNon-usevaluesTimber, fuelwood,charcoalShoreline, riverbankstabilisationFuture direct andindirect valuesCultural,aestheticFisheriesForest products:food, medicine,wildlife etcAgriculturalresourcesWater supplyWater transportGroundwaterrecharge/dischargeFlood and flow controlWaste storage and recycling<strong>Biodiversity</strong> maintenanceProvision <strong>of</strong> migrationhabitatSpiritual,religiousGlobalexistencevalueGenetic resourcesTourism andrecreationNursery/breeding groundsfor fishNutrient retentionHuman habitatInformationSource: Bann (1998) (with modifications).Coral reef maintenance andprotectionPrevention <strong>of</strong> saline waterintrusionTable 2.4 provides monetary estimates for one mangrove system in Surat Thani in SouthThailand [Sathirathai (1998)]. The notable feature <strong>of</strong> these estimates is the dominant role played byindirect use values. Local use values relate to the use <strong>of</strong> the mangrove to supply fish, timber, andfuelwood. The <strong>of</strong>fshore fishery benefit relates to the benefit that the mangrove has for the productivity<strong>of</strong> the <strong>of</strong>fshore fishery. The coastal protection benefit is estimated by what it would cost to replace thebeneficial protection function produced by the mangrove, i.e. what it would cost in coastal defences.This ‘replacement cost’ approach assumes that if the mangrove was not there then the protectivefunction would have to be replaced, and this somewhat begs the question <strong>of</strong> the whether coastaldefence would be worthwhile. Nonetheless, the use <strong>of</strong> replacement costs is quite widespread in38
- Page 1 and 2: «ENVIRONMENTValuation ofBiodiversi
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- Page 31 and 32: are very modest. More recently, new
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- 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
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- Page 53 and 54: endangered Indian rhino and other t
- Page 55 and 56: ReferencesBann, C., and M. Clemens
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- Page 59 and 60: many European countries, CBA has a
- Page 61 and 62: (1) Cost and time constraintsThe co
- 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
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PART 391
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measures of value. An appendix to t
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features (such as parks, beaches or
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included in cost-benefit analysis o
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A Discussion of Past Efforts to Dev
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Satellite AccountsIn addition to th
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which many people argue are associa
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approach to competing uses of water
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Figure 6.2 Trade-Off AnalysisEnviro
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However, the farmers need not bear
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Appendix 1: Theory and Application
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iwhere C is the income adjustment n
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complete. If there are more than on
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Horowitz, Joel. L. and Jordan. J. L
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CHAPTER 7:by Dennis M. KING and Lis
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Box 7.1 Definition of terms related
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Box 7.2 Categories of Ecosystem Ser
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Box 7.4 Dollar-based ecosystem valu
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Non-monetary indicators of ecosyste
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Figure 7.1 Effects of Wetland Locat
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description, and that the usefulnes
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2) Service capacity sub-indexIndica
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wetlands, for example, results in F
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(1) Functional CapacityIndexFigure
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constituents of runoff can be predi
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Service(on or off site)Recreational
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Table 7.3 Service Risk Sub-index De
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Measuring Service Preference Weight
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Table 7.4 Illustration of Paired Co
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PART 4151
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Ecological foundations for biodiver
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Phenotic diversity is a measure bas
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Operationalisation of the biotic-ri
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ten attributes that could score a m
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The choice of the scale relates to
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Nature measurement methodIn 1995, t
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Table 8.4 Value orientations and en
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Table 8.5 Identification of monetar
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Table 8.6 Valuation studiesSingle s
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in waterway systems for nine impact
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to other contexts, conditions, loca
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ReferencesAkcakaya, H.R. (1994).
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de Groot, R.S. (1994). “Environme
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Mace, G. M. & S. N. Stuart. (1994).
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Turner, R.K., Perrings, C. and Folk
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John A. DixonJohn A. Dixon is Lead
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Robert O’NeillDr. O’Neill recei
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Steven StewartSteven Stewart is Ass
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