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    Institutional

    Robustness: HowInstitutional ArrangementsFacilitate or Detract from

    Efforts to Sustain Ecological

    Systems

    Elinor OstromIndiana University

    Arizona State University

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    The Challenges we Face in

    Understanding Property

    Rights Overcoming the Panacea Trap

    Accepting -- rather than rejectingcomplexity

    Recognizing the benefits ofinstitutional diversity as well asbiodiversity

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    Challenge 1: The PanaceaTrap

    Panaceaspolicy advice for the

    best way to govern and manage

    CPRsassuming that there is onesimple cure-all for multiple

    ecological problems

    Scholars & policy makers fall into

    panacea traps even when theyassume an uncertain world

    Derived from basic failures to

    recognize the differences among

    CPRs in diverse sectors, at multiplespatial scales and over time

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    Tragedy of the

    Commons Debate One

    Source of Panaceas

    Hardin (1968) envisioned helplessresource users

    To prevent resource destructionmust imposegovernmentownership or private ownership

    Community control now proposedby some as a solution to resource

    destruction All 3 panaceasgovernment,

    private, or community control --work in some settings and fail inothers -- depend on the matchofthe specific institutionalarrangement and problem specificsas well as how implemented

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    Challenge 2: Accepting

    Rather than Rejecting

    Complexity Scientific progress involves

    understanding complex,

    decomposable, multi-tier systems Interactions are rarely linear

    additive

    Cannot assume away complexityand be successful in remedying

    problems Must dig into complex systems that

    are partially decomposable

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    Challenge 3: Recognize

    Value of Institutional

    Diversity

    Panacea thinking focuses onsimplified policy solutions

    Research finds vast numbersof specific rules used insustainable systems tied tospecific variables of a resource

    system & its units Need to value institutional

    diversity in addition tobiological diversity

    Lets review findings from ourmulti-country, multi-disciplinaryforestry research network

    First to Maya Biosphere Reserve

    in Guatemala

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    Maya Biosphere Reserve

    Four National Parks (NPs) inclose proximity

    Tikal NP has large budget to payfor extensive fences and guards

    El Mirador protected by nature Laguna del Tigre severely

    overharvested

    Sierra del Lacandn severelyoverharvested

    Same formal institution:

    Two are sustainable, but differentcausal process

    Two are vulnerable to massiveillegal harvesting

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    Maya Biosphere ReserveMultitemporal Color Composite (Dietz, Ostrom, Stern, 2003, Science SOM)

    B

    Multiple

    Use Zone

    Buffer Zone

    Laguna del

    Tigre NP

    El Mirador-

    Rio Azul NP

    Naachtun-

    Dos Laguna

    Biotope

    Tikal NP

    erra del

    acandn NP

    Laguna del

    Tigre Biotope

    El Zotz

    Biotope

    clouds

    N0 20 km10

    A

    B

    C D

    C

    D

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    To Rondnio, Brazil

    Two colonization projects assigned privateproperty & obligation to preserve half of theforested land

    Established side by side in 1980s

    Southern project laid out typical rectangular

    plots. Farmers obliged to preserve 50% of landassigned to them

    Northern project involved users in the plan

    Topographically sensitive layout

    Established separate forest reserves Private owners had full control of smaller

    plots

    Rubber tappers assigned to monitor theforest reserves (not government officials)

    Northern project is more sustainable than mosBrazilian colonization projects that assignfarmers responsibility to preserve 50% offorest on their own land

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    Contrasting Colonization Projects

    (Batistella, 2003)

    N 0 10 km5N0 10 km5

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    Now to India

    Todoba-Andhari Tiger Reserve

    An under-funded national wildlife

    reserve with multiple outcomes

    Stable forests in the core

    Park guards are not able tocontrol harvesting along sections

    of the borders

    Complementary field studies find

    Consistent harvesting of non-

    timber forest products

    Existence of considerable

    conflict between guards andlocal people Nagendra & Ostrom, PNAS, 2006

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    TADOBA-

    ANDHARI

    TIGER

    RESERVE

    Interior villages

    Multi-temporal Landsat color composite, 1972-1989-

    2001, landscape surrounding Tadoba-Andhari Tiger

    Reserve, India.

    Regrowth

    Clearing

    Regrowth

    Clearing

    Stable

    forest

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    Women harvesting thatch grass from within

    the TATR - while the forest ranger

    accompanying our research team looks on

    helplessly.

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    Cattle entering the TATR boundary (marked

    by the yellow topped pillar in the background)on their daily foraging beat.

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    Bicycles and trucks confiscated from

    timber poachers stealing large logs

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    Diversity of Institutions,

    Ecological Systems, and

    Results While some Protected Parks are

    successful in protecting forests,

    others are not.

    Depends on many factors re how

    established and relationships with

    local people.

    In a large cross-sectional IFRIstudy of 163 forests in 12 countries

    no difference in forest density

    (scale assigned by forester on

    team after doing forest plots) ismeasured for Protected Parks

    compared to allother institutional

    arrangements (Non-Parks)

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    Findings from Repeat

    Visits to IFRI Forests2ndtime research visit in 42 IFRI forests India5 forests

    Kenya3 forests

    Nepal10 forests

    Uganda18 forests USA6 forests

    Not a random sample of forests but basedon a random sample of plots inside each

    forestand

    first study of this type

    Can assess:

    Relative strength of formal institution onchanges in DBH, basal area, and stemcount

    Strength of regular involvement of usergroups in monitoring forests on same forestmeasures

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    Impact of Formally Designated Tenure and

    Forest Monitoring on Changes in Forest

    Condition: Assessment using ANOVA

    ndependent

    ariables

    Change in

    DBH

    Change in

    basal area

    Change in

    stem

    count

    Ownershipa F = 0.89 F = 2.52 F = 1.00

    nvolvement

    f user

    roups in

    monitoringulesb

    F = 0.28 F = 10.55** F = 4.66*

    a Government, community, private

    bAt least one user group is involved in regular monitoring of

    rules of forest use

    *Significant at .05 **Significant at .01

    Source:Ostrom, Elinor, & Harini Nagendra, Insights on Linking Forests,

    Trees, and People from the Air, on the Ground, and in the Laboratory.

    PNAS 103(51) (2006): 19230.

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    Importance of Local

    Monitoring

    An initially surprising finding but

    now supported by mutiple studies

    Monitoring by local forest users of

    the harvesting practices by otherusers is strongly associated with

    improved forest conditions

    Five recent studies find local

    monitoring to be very important Coleman JPAM (2009),

    Coleman & Steed in Ecol. Econ (2009);

    Chhatre & Agrawal PNAS(2008) &

    (2009)

    Van Laerhoven GEC(2010)

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    Study 100 forests in 14

    countriesIFRI over-time data

    Coleman & Steed found when local

    user groups have right to harvestfrom the forest, they are more likely

    to engage in M&S

    Considered counterintuitive to some

    policy makers that giving the right to

    harvest products from a forest may

    actually improve forest conditions

    But those who have long-term rightsto a flow of future benefits do monitor

    to see that rules are followed

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    Chhatre and Agrawal

    Recent analyses focusing on forests

    in 10 tropical countries examines

    tradeoffs and synergies between

    level of carbon storage in forests andtheir contributions to livelihoods.

    Larger forests more effective in

    enhancing carbon andlivelihoodsEven stronger when local

    communities have strong rule-making

    autonomy and incentives to monitor

    Keeping locals completely out offorests is NOT a panacea!!!!

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    A Puzzle from Field

    Research: Why Do Users

    Monitor Others?Voluntary effort to produce a public

    good of rule conformance

    Game theoretic predictionsno one

    will voluntarily contribute to provide a

    public good

    Earlier findings from field studies led

    to a series of laboratory experimentsat IU and now replicated by others

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    Harvesting Common-Pool

    Resources in the Lab

    Baseline experiment of completeanonymity and finitely repeated game Game theoretical prediction is substantial

    over-harvesting

    Prediction supported in the lab

    Adding the capacity to communicatedoes not change predictionin asocial dilemma communication is only

    CHEAP TALKSubjects make good use ofopportunity for cheap talkespeciallywhen repeated

    They use it to agree on jointharvesting strategy & for verbalrebukes of unknown over-harvesters

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    In the Lab

    Sanctioning design

    External rule established byexperimenters: participants may paya fee to fine others

    Game theory prediction: no one will

    sanction

    Results: relatively high levels ofsanctioningincreasescontributions but costly due to

    payment of fees & fines Self-determined sanctioning

    system

    Achieve 90% of optimal outcomes!

    Demonstrated capacity to self-organizewithout external enforcers

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    Replications

    Findings related to effect ofcommunication repeatedly

    replicated in other labs and in

    field experiments

    Very recent paper in Science

    reports on finding from a more

    complex experimental design

    where communication is againshown to be effective (and just

    having punishment capability is

    not effective) Janssen, Lee, Holahan, and Ostrom, Lab

    Experiments for the Study of Social-

    Ecological Systems. (April, 2010)

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    Initial Effort to Develop

    Design Principles of Robust

    CPR InstitutionsResult of my unsuccessful struggle

    to analyze multiple cases in our CPR

    database for specific rules thatappeared strongly related to long-

    term sustainable systems.

    Based on a close reading of a large

    number of case studies and

    checking with case authors re the

    accuracy of my speculations

    Thought I should share my strugglewith others in Governing the

    Commons as a step toward

    developing theory re what enhances

    robustness

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    New Findings re Design

    Principles

    Cox, Arnold & Villamayor A Reviewand Reassessment of Design

    Principles for Community-based

    Natural Resource Managementforthcoming Ecology & Society.

    Reviewed 96 studies from around the

    world (by other scholars of applicability

    of design principles across sites as

    well as case studies)Found substantial support for

    principles and have proposed a better

    framing of the principles so that one

    does not combine ecological factors(such as physical boundaries) with

    social factors (such as group

    membership)

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    Clarified Design Principles

    Boundariesnow distinguishclear boundaries between

    users & non-users and for the

    resource itself. Congruencenow distinguish

    rules congruent with local

    social & ecological conditionsfrom distribution of benefits

    and costs

    Monitoringincludedmonitoring resource conditions

    as well as user actions

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    Why Design Principles

    Enhance Robustness

    Assures participants that operational

    rules are being followed by others

    Those most knowledgeable abouteffects of rules are involved in

    making rules

    Resolves conflicts before they

    escalate

    Diversity of governance units

    stimulates learning and increased

    performanceLarge and small units backup each

    other

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    Threats to Robust CPR

    Institutions

    Mismatch of boundaries

    Only national or local authorities or

    only general purpose jurisdictions

    need polycentric institutions atmultiple domains

    Poor information about resource

    attributes especially when:

    Highly variable

    Complex interactions

    Very slow regeneration rate

    Imposed blueprint by outside

    authorities

    REDD+ could become such a threat

    Treating design pr incip lesas blue

    prints

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    To Study Robustness, Need

    to Change Social Sciences

    Dynamic to complement static

    models

    Multiple tiers of analysis

    PolycentricityHeterogeneous types of individuals

    Confront complexity rather than

    denying it (keeping theories as

    general as possible)

    Triangulate methods (theory, case

    studies, large N studies, lab

    experiments, ABMs)(Poteete, Janssen, and Ostrom. 2010. Work ingTogether: Col lect ive Ac t ion, the Commons, &

    Mult ip le Methods in Pract ice. Princeton University

    Press)

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    Basic Lessons

    No single idealized type of

    governance structures issuccessful in all ecological and

    social settings

    Institutional monocultures are notrobust

    Dangerous tendencies to impose

    uniform rules

    People living in or around aproject frequently not involved in

    design

    Few opportunities for

    experimentation and learning

    Rules-on-paper confused for rules-

    in-usedont really know what

    rules are being used in field

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    Thank You For Listening

    Thanks to many colleagues and

    co-authors, our International

    Forestry Resources andInstitutions (IFRI) colleagues,

    and to the many resource users

    in the field who have helped us

    greatly Questions?