perrot maitre

Upload: pwnkumar314

Post on 10-Apr-2018

237 views

Category:

Documents


0 download

TRANSCRIPT

  • 8/8/2019 Perrot Maitre

    1/40

  • 8/8/2019 Perrot Maitre

    2/40

  • 8/8/2019 Perrot Maitre

    3/40

  • 8/8/2019 Perrot Maitre

    4/40

  • 8/8/2019 Perrot Maitre

    5/40

  • 8/8/2019 Perrot Maitre

    6/40

  • 8/8/2019 Perrot Maitre

    7/40

  • 8/8/2019 Perrot Maitre

    8/40

  • 8/8/2019 Perrot Maitre

    9/40

  • 8/8/2019 Perrot Maitre

    10/40

  • 8/8/2019 Perrot Maitre

    11/40

  • 8/8/2019 Perrot Maitre

    12/40

  • 8/8/2019 Perrot Maitre

    13/40

  • 8/8/2019 Perrot Maitre

    14/40

  • 8/8/2019 Perrot Maitre

    15/40

  • 8/8/2019 Perrot Maitre

    16/40

  • 8/8/2019 Perrot Maitre

    17/40

  • 8/8/2019 Perrot Maitre

    18/40

  • 8/8/2019 Perrot Maitre

    19/40

    Limitations of Cost-Based Methods Provide only rough indicator of ecosystem value

    Replacement cost: often difficult to find perfect replacementsfor ecosystems goods and services, hence valuation results

    tend to undervalue ecosystem value

    Mitigation expenditures: often peoples perception of theeffect of ecosystem loss and what would be required tomitigate these effects do not always match those of experts.

    Damage cost method: estimated damages avoided remainhypothetical in most cases. Often difficult to relate damages tochanges in ecosystems

  • 8/8/2019 Perrot Maitre

    20/40

    CONTINGENT VALUATION

    The amount peoplewould pay/accept

    under the theoreticalcondition that

    biodiversity could bebought and sold

    Peoples statedwillingness to pay

    E.g. Doi Inthanon and SuthepPui National Parks, Thailand:Willingness to pay for park entryfees

    Doi Inthanon 40 Baht per personSuthep Pui 20 Baht per personTOTAL VALUE $1.2 million/year

  • 8/8/2019 Perrot Maitre

    21/40

    Advantages of CV

    + Very flexible. Can be used to estimate economicvalue of about anything but best to use it to estimatevalue of goods and services easily identified andunderstood by users

    + CV is the most widely accepted method for estimating TEV including non use, option and

    bequest values (only method to estimate option or existence values)

    + CV has been widely used and a great deal of researchis being conducted to improve the methodology,make results more valid and reliable and understandstrengths and limitations

  • 8/8/2019 Perrot Maitre

    22/40

    Limitations of CV Whether CV really measures WTP still controversial (most people unfamiliar making choices about ecosystem services)

    Results highly sensitive to design of choice scenarios and howsurvey conducted (psychological aspects)

    WTP sensitive to payment vehicle (WTA compensation)

    Strategic bias to influence outcome

    Non response bias

    Many people including jurists, policy makers, economists andothers do not believe the results of CV analysis

  • 8/8/2019 Perrot Maitre

    23/40

    LESS COMMON METHODS

    HedonicPricing

    Conjoint Analysis

    ChoiceExperiments

    Difference in (property or wage) prices thatcan be ascribed to the existence or level of nearby environmental goods and services.

    Obtains information on preferences betweenvarious alternatives of environmental goodsand services, at different price or cost.

    Present a series of alternative resource or use options, each of which are defined byvarious attributes including price.

  • 8/8/2019 Perrot Maitre

    24/40

    Application of economicvaluation to PES design

  • 8/8/2019 Perrot Maitre

    25/40

    Watershed services: supply and demand

    Supply of services:Upstream land uses affect the Q uantity ,Q uality , and Timing of water flows

    Demand for services:Possible downstreambeneficiaries:Domestic water useIrrigated agriculture

    Hydroelectric power FisheriesRecreationDownstream ecosystems

    Source: World Bank 2003

  • 8/8/2019 Perrot Maitre

    26/40

    A pplying ecosystem valuation to payment for ecosystem service: simple in theory

    Benefits toproducers

    Costs tooffsitepopulations

    Conventionalresource use:

    noconservation

    Conservationwith payment

    for service

    Payment

    Conservationwithout

    payment

    Minimum paymentwilling to receive tochange damagingbehaviour toecosystem

    Maximum paymentwilling to pay to reduceenvironmental damage

    Source: A dapted from World Bank 2002

  • 8/8/2019 Perrot Maitre

    27/40

    In practice, not so simple

  • 8/8/2019 Perrot Maitre

    28/40

    In practice not so simple

    Complex biophysical linkages (Brand 2003)

  • 8/8/2019 Perrot Maitre

    29/40

    In practice still not so simplevaluing effects of change

    in ecosystem conditions on agricultural production

    Impact on ecological function &service

    Physical impact of changein functions

    Socio-economic effectsof physical impact

    Overall impact of Socio-economic effects

    Intervention

    eduction in ater:floods &drought

    Increased erosion

    Increase in cropdamage ( in kg )

    ecrease in cropyield ( in US$)

    Increase use fertiliser &pesticides ( in kg )

    Increase productioncosts ( in US$)

    Increase in crop production ( in kg )

    Increase in cropyield ( in US$)eduction of forest cover

    educed pest-control &

    pollination

    eforestationhange in conomicalue of griculture

    (in US$)

    Impact on ecological function &service

    Physical impact of changein functions

    Socio-economic effectsof physical impact

    Overall impact of Socio-economic effects

    Intervention

    eduction in ater:floods &drought

    Increased erosion

    Increase in cropdamage ( in kg )

    ecrease in cropyield ( in US$)

    Increase use fertiliser &pesticides ( in kg )

    Increase productioncosts ( in US$)

    Increase in crop production ( in kg )

    Increase in cropyield ( in US$)eduction of forest cover

    educed pest-control &

    pollination

    eforestationhange in conomicalue of griculture

    (in US$)

  • 8/8/2019 Perrot Maitre

    30/40

    Use-and non use- of economic valuation todesign payments for ecosystem services

    Public payments

    Costa Rica : $20-44/ha/yr for forest conservation- based on oldsubsidy based on opportunity cost of land use change

    USA (Conservation Reserve Program): $50/ha/yr. Opportunity costand cost of conservation measures

    Ecuador : municipal water and electrical utility companies each donate1% of total revenues for watershed protaction (oroginally 5% had been

    proposed by TNC)

    Brazil a water utility in the city of Sao Paulo pays 1% of totalrevenues ($2,500 per month) for the restoration and conservation of theCorumbatai watershed. Funds are used to establish tree nurseries andfor reforestation along riverbanks. Payment is outcoem of politicalnegotiation.

  • 8/8/2019 Perrot Maitre

    31/40

    Use-and non use- of economic valuation todesign payments for ecosystem services

    Private payments

    France : US$320/ha/year for 7 years, equivalent to 75% of farm income Opportunity cost and actual cost of switching

    agricultural technology

    Costa Rica : a hydropower company pays US$10 per ha/year to a local conservation NGO for hydrological services in thePeas Blancas watershed

    Australia : Since 1999, farmers in the Murray Darlingwatershed pay $AUD 85/ha/yr for forest conservation for 10years or $AUD 17 per million liters of transpired water. Basedon increase in marginal benefits due to reduced soil salinityresulting of 100 ha of reforested area.

  • 8/8/2019 Perrot Maitre

    32/40

    Concluding remarks

  • 8/8/2019 Perrot Maitre

    33/40

  • 8/8/2019 Perrot Maitre

    34/40

    Applicability and limitations of

    economic valuationWhen ecosystem benefits that relate to attributes such as human life,cultural or religious significance, economic valuation raises serious ethicalquestions. Ecosystem valuation may be dangerous when it focuses only onfinancial or cash benefits at the expense of other types of values thatcannot-or should not-be valued.

    Results of ecosystem valuation studies are not definitive, and transferable between groups and locations. They are generally based on the perceptionof a particular group at one point in time and is not universally valid.

    There is no garantee that the findings of economic valuation will supportthe wise use and management of ecosystems and their services. In fact theuse of valuation studies to identify and promote new ways of capturingecosystem values through markets or PES, can be a double-edged sword.

  • 8/8/2019 Perrot Maitre

    35/40

    Key Messages

    It is easy to spend tons of money on valuation.

    It is easy to value everything, yet the results of valuation are not always useful or correct.

    Info on total benefit flows, even if correct, cannot provide guidance on specific conservation decisionswhich are about making incremental changes in theseflows.

  • 8/8/2019 Perrot Maitre

    36/40

    More key messages

    1st. step: ask yourself what is the purpose of theanalysis, who should take its results into account

    2nd. step: what is your budget, can it be adjusted, whatcapacity is available, which time frame?

    3rd. step: which process? Process may be asimportant as the result. Consider stakeholders,including policy makers, participation into the study.

  • 8/8/2019 Perrot Maitre

    37/40

    And moreIn designing PES, the most appropriate method tovalue an ecosystem service is the production functionanalysis-yet it is rarely done

    Be pragmatic, learn and adapt: most payments basedon OC to service provided, not on marginal benefit to beneficiary. Payments need not be cast in stone butadapted as more is learned about the system,especially biophysical relationships.

    Economic valuation will only address equity issue if this is designed into the valuation study from thestart. Hence back to step 1!

  • 8/8/2019 Perrot Maitre

    38/40

    For further information: IUCN economicFor further information: IUCN economicvaluation productsvaluation products

    Working Papers& Policy Briefs

    Toolkit

    Case Studies

  • 8/8/2019 Perrot Maitre

    39/40

    For further information

    Toolkit downloadable from:

    http://www.waterandnature.org/value /

    New revamped website:

    http://biodiversityeconomics.org

  • 8/8/2019 Perrot Maitre

    40/40

    Thank you!