SNR Skunkwor ks 1 Trick or treatment? Evaluating the quality of structured risk management decisions...

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1 SNR Skunkwor ks Trick or treatment? Evaluating the quality of structured risk management decisions Joe Arvai The Ohio State University Decision Research
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Transcript of SNR Skunkwor ks 1 Trick or treatment? Evaluating the quality of structured risk management decisions...

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SNR

Skunkworks

Trick or treatment?Evaluating the quality of structured

risk management decisions

Joe ArvaiThe Ohio State University

Decision Research

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Outline

Structured DM in briefA practical example

Questions of quality (3 experiments)Parting thoughts

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SDM In Brief

• Structured decision approaches have their roots in…

– …the observation that people tend to have tremendous difficulty with making decisions that involve multiple objectives and, therefore, tradeoffs.

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SDM In Brief

• Structured decision approaches have their roots in…

– …studies of the constructive nature of preferences in response to available cues.

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SDM In Brief

• Structured decision approaches are designed based on…

– …“value focused thinking.”

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SDM In Brief

• Structured decision approaches are designed based on…

– …the literature dealing with normative decision making, specifically the steps required for a complete analysis of a given decision

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SDM In Brief

• Structured decision approaches are designed based on…

– …methods for decreasing the cognitive burden associated with complex choices.

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The Case of Water Use Planningin British Columbia

• Work with B.C. Hydro on a comprehensive, stakeholder-based development of revised operating plans at all major hydroelectric facilities.

• In response to increasing, competing demands on provincial water resources

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Scale of Study

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The Case of Water Use Planningin British Columbia

• Multiple Objectives:1. Electricity generation/trade2. Environmental quality

• Water, land, & air

3. Recreation opportunities4. Cultural values 5. Learn over time; reduce uncertainty

http://www.bchydro.com/wup/

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Water Use Planning in B.C.The Basic Steps

• The approach is based on work with stakeholders on:

1. Eliciting objectives from various stakeholders.

2. Identifying a series of workable options for management.

3. Establishing attributes of/measures for each objective.

4. Generating a matrix across these objectives and options and addressing the tradeoffs that selecting one option over another entails.

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Water Use Planning in B.C.Participants

• BC Hydro (Crown Corporation)• Federal Government• Provincial Government• Local Government• First Nations• Community Stakeholders

– Home owners, business operators, etc.

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Water Use Planning in B.C.Objectives, Attributes, Measures

Objectives AttributesRecreation e.g., Weighted User Days

Erosion e.g., Weighted Erosion Days

Flooding e.g., Weighted Flood Days (flow level)

Fish e.g., % Available Habitat, IBI

Water Supply e.g., Water Quality Impact Rating

Cultural Heritage e.g., Consistency Rating

Financial e.g., Annual Revenues M$ / Year

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Water Use Planning in B.C.e.g., Financial Objectives &

Attributes

M A R K E T V A LU EO F P O W E R

TOTAL FINANCIALVALUE

C O S T O F M O N ITO R IN GA N D M IT IG A T IO N P G M S

M O N ITO R IN G A N DM IT IG A T IO N P G M S

TH E R M A L P O W E RP R O D U C E D

GHG EMISSIONS

N E W C A P ITA L W O R K S C A P ITA L C O S TS TO TA L C O S TS

TO TA L R E V E N U E S

O P E R A TIN G C O S TS

W A TE R M A N A G E M E N T:

R ESER VO IR LEVELS FLO W R AT ES D IVER SIO N FLO W S R AM PIN G R AT ES

P O W E R G E N E R A TIO N :

AM O U N T O FG EN ER AT IO N

T IM E O F G EN ER AT IO N

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Water Use Planning in B.C.e.g., Recreation Objectives &

AttributesRESERVOIR

LEVELS

FLO A TIN GD E B R IS

RECREATION

OPPORTUNITIES QUALITY

DEBRISMANAGEMENT

V IS U A LQ U A LITY

B O A TIN G &S W IM M IN G C O N D IT IO N S SAFET Y

DIVERSIONFLOW S

TOURISMFLOW RATES

K A YA K & C A N O E IN GC O N D IT IO N S

A C C E S S TO : BEAC H BO AT LAU N C H SH O R ELIN E

S TA N D IN GD E B R IS

S H O R E LIN EE R O S IO N

N O N -C O N FO R M IN GP A R K U S E

N A TU R A L H IS TO R Y

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Water Use Planning in B.C.Assessing Value

Objectives Attributes Mimic Natural Hydrograph

Enhanced Summer Releases

Enhanced Winter Releases

EnvironmentConserve Salmon

% Viable Spawning Habitat

50 20 25

EconomicRevenue Generation

NPV ($) $60 Million $80 Million $65 Million

SocialRecreation Opportunities

Number of User-Days 1400 1200 1500

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Objectives AttributesMimic

Natural Hydrograph

Enhanced Summer Releases

Enhanced Winter

Releases

EnvironmentConserve Salmon

% Viable Spawning Habitat

50 20 30

EconomicRevenue Generation

NPV ($$)

$ 60 M $ 80 M $ 65 M

SocialRecreation Opportunities

# of user days

1400 1200 1500

Range of Values

Nat

6040

100

ExpectedLowHigh

Sum

8010140

RISK PROFILES

1.0

0.8

0.6

0.4

0.2

20 60 100 140

Pro

bab

ilit

y

Expected Value

Nat Sum

Water Use Planning in B.C.Risk & Uncertainty

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Water Use Planning in B.C.

AlternativesObjective Attribute E F G H I J

Upper Campbell / Buttle LakeErosion - Days / Year weighted days (220 and 221 m) 37 13 4 3 3 3Recreation - Days / Year weighted days (217.5, 218.5, 200m by season)43 40 106 158 158 158Effective Littoral Zone hectares 91 107 93 214 215 220

Lower Campbell / McIvor / FryErosion - Days / Year weighted days (177.4 and 178.3 m) 3 27 13 0 0 0Recreation - Days / Year weighted days (175.75 - 177.8 by season) 115 43 83 167 170 167Spawning Habitat - Cutthroat % Available Habitat 78 18 95 79 79 78Spawning Habitat - Rainbow % Available Habitat 26 3 49 49 47 50

Campbell RiverFlooding - Total Days weighted days (300, 453, 530 cms) 34 48 24 59 59 59Recreation - Days / Year weighted days (28 cms - 80 cms) 66 83 51 81 79 81Total Spill Days - All Species days (Q>340cms, Sept 22 - April 15) 118 214 102 176 177 176Spawning Habitat - All Species % successful redds (Chum as indicator) 55 89 78 59 59 59Rearing Habitat - All Species "Average" risk index (scale 0 - 1) 0.53 0.48 0.53 0.50 0.49 0.49

Salmon RiverCanoe Route - Days / Year days (Q<6cms, April 1 - Oct 22) 162 167 153 204 183 204All Habitat - All Species "Average" risk index (scale 0 - 1) 0.54 0.47 0.44 0.48 0.47 0.47

System-WidePower / Financial Annual Revenue M $ / Year 68.5 64.6 68.6 65.1 65.3 64.1

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Moving From Alternative:E

To Alternative:G

Results In:

Upper Campbell / Buttle LakeG A decrease in Erosion - Days / Year of 33 weighted daysG An increase in Recreation - Days / Year of 63 weighted daysY An increase in Effective Littoral Zone of 2 hectares

Lower Campbell / McIvor / FryR An increase in Erosion - Days / Year of 10 weighted daysR A decrease in Recreation - Days / Year of 32 weighted daysG An increase in Spawning Habitat - Cutthroat of 17 %

Campbell RiverG A decrease in Flooding - Total Days of 10 weighted daysR A decrease in Recreation - Days / Year of 16 weighted daysG An increase in Spawning Habitat - All Species of 23 %Y No change in Rearing Habitat - All Species of 0 in average risk

Salmon RiverY A decrease in Canoe Route - Days / Year of 9 daysG A decrease in All Habitat - All Species of 0.1 in average risk

System-WideY An increase in Power / Financial of 0.1 M $ / Year

Denotes an improvement in the PM greater than the significant difference.Denotes a worsening in the PM greater than the significant difference.Denotes a change in the PM that is less than the significant differencfe.

Water Use Planning in B.C.

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A High Quality Process?

1. Government Support• Approach originally conceived as a pilot project at a

single site• Now implemented at 23 sites province wide (18 Water

Use Plans completed to date)

2. Cost-effective• Original budget to complete all 23 plans = $25 Million• Revised budget = Approx. $14 Million

3. Participant Satisfaction• Historically adversarial groups work together• BC Hydro has a clear mandate• Consensus plans often achieved

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• Designed to compare two approaches for involving stakeholders in water use planning in B.C…– …small groups (7-10)– …both conditions provided with the

same information– …“Structured” vs. “Unstructured”

process

Experiment 1Quantitative Measures of Quality

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UNSTRUCTURED1. Self-rating questions2. Technical Information

• newspaper article• informative booklet• audio-documentary

3. Group Discussion4. Evaluation of policy

alternatives• referendum• willingness to pay

5. Self-rating questions

STRUCTURED

1. Self-rating questions2. Technical Information

– newspaper article– informative booklet– audio-documentary

3. Decision structuring– characterize values & objectives– group discussion about values

and objectives.– objectives ranking/tradeoffs

4. Evaluation of policy alternatives

– referendum– willingness to pay

5. Self-rating questions

Experiment 1Quantitative Measures of Quality

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UNSTRUCTURED STRUCTUREDSelf-rating Item

x Start sStart

x End sEnd p

x Start sStart

x End sEnd p

Knowledge about power 3.71 1.34 4.23 1.10 <0.0001 3.58 1.34 4.39 1.13 <0.0001

Knowledge about salmon 3.84 1.58 4.21 1.41 <0.01 3.63 1.48 4.30 1.30 <0.0001

Amount of information onwhich to base an informedanswer

3.23 1.54 3.52* 1.28 0.08 3.11 1.59 3.93* 1.46<0.001*<0.01

Comfort with giving policyadvice

4.34 1.48 4.47* 1.30 0.06 4.44 1.69 4.88* 1.75<0.01*<0.01

Choices reflect whatmatters

5.45 1.15 5.88 1.13 <0.05

Experiment 1Results

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0

0.1

0.2

0.3

0.4

0.5

Costs TechnicalIssues

SocialIssues

CulturalIssues

UnstructuredStructured

F

Experiment 1Results

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• Based on participants’ self-ratings and an analysis of deliberation periods, we conclude that the the structured approach leads to higher quality decisions.

• Arvai, J. L., R. Gregory, and T. McDaniels. 2001. Testing a structured decision approach: Value-focused thinking for deliberative risk communication. Risk Analysis, 21: 1065-1076.

Experiment 1Conclusions

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• Decision structuring to alleviate embedding in environmental valuation

– …when a good is assigned a higher value on its own vs. when it’s part of a more inclusive set.

• e.g., 5:1 differences in WTP for a single vs. a set of disaster preparedness services

Experiment 2Analyzing Choices

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• Providing much-needed structure may help to overcome the embedding problem by helping decision makers to think about the components of a valuation problem.

Experiment 2Analyzing Choices

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VERSION A

1. Technical Information– newspaper article– informative booklet– audio-documentary

2. Decision structuring– characterize values & objectives– group discussion about values and

objectives.– objectives ranking/tradeoffs

3. WTP 1 Rivers

4. WTP 10 River

VERSION B

1. Technical Information– newspaper article– informative booklet– audio-documentary

2. Decision structuring– characterize values & objectives– group discussion about values and

objectives.– objectives ranking/tradeoffs

3. WTP 10 Rivers

4. WTP 1 River

Experiment 2Analyzing Choices

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Experiment 2Analyzing Choices

CHOICE 1 CHOICE 2

VERSION AWTP 1 River

W

WTP 10 Rivers

X

VERSION BWTP 10 Rivers

Z

WTP 1 RiverY

W > YZ<XNo Embedding

W/X = Y/Z0.42 0.25

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• Based on participants’ mean WTP judgments, embedding was not alleviated (according to the ratio standard).

• McDaniels, T., R. Gregory, J. L. Arvai, and R. Chuenpagdee. 2003. Decision structuring as a means of alleviating embedding in environmental valuation. Ecological Economics, 44: 33-46.

Experiment 2Conclusions

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• An experiment that would measure both self-ratings of quality and subjects’ choices…

Experiment 32-Part Evaluation

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UNSTRUCTURED

1. Self-rating questions2. Technical Information3. Choice Task

• Funding allocations across three risk problems

4. Self-rating questions

STRUCTURED

1. Self-rating questions2. Technical Information3. Decision Structuring

• Objectives ranking, tradeoffs

• Linking objectives with management problems

4. Choice Task• Funding allocations

across three risk problems

5. Self-rating questions

Experiment 32-Part Evaluation

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Problem Affect RatingCorresponding Objective

Wildlife Disease Affect Rich

Human Health

Deer Overpopulation

Affect Neutral

Environmental Health

Damaged TrailsAffect

NeutralRecreation

Experiment 3Three Risk Problems

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Unstructured Structured

Self-rating item

x Start SEStart

x End SEEnd p

x Start SEStart

x End SEEnd p

Knowledge(Trails)

3.1 0.25 4.1 0.22 <0.001* 3.7 0.21 4.4 0.23 <0.001*

Knowledge(DOP)

3.8 0.24 4.4 0.22 <0.001* 3.7 0.22 4.4 0.17 0.001*

Knowledge(Disease)

3.3 0.20 4.1 0.22 <0.001* 3.7 0.21 4.3 0.21 0.005*

Comfort withproviding input

4.5 0.25 5.1 0.23 <0.05

Choices reflectwhat matters -- -- 4.9 0.21 -- -- -- 5.5 0.17 <0.05

Satisfactionwith choice -- -- 4.5 0.25 -- -- -- 5.1 0.23 <0.05

Experiment 3Self-Rating Results

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OBJECTIVE RANK

Environmental Health 1

Human Health 2Recreation 3

Experiment 3Ranked Objectives

1=Overpopulation

2=Disease

3=Trails

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Overpop Disease Trails0

110000

135000

160000

185000

210000

235000 A

Ranked Management Problems(Descending Order)

1 2 3 4 5 6 70

110000

135000

160000

185000

210000

235000 B Wildlife Disease

DeerOverpopulation

DamagedTrails

Mean Affect Rating

Experiment 3Funding Allocations

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• Appears to be a disconnect between self-ratings of quality and actual funding choices

• Wilson, R.S. and J. L. Arvai. 2004. Evaluating the quality of structured risk management decisions. In Review.

Experiment 3Conclusions

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Parting Thoughts

• Level of facilitation, time for deliberation, increased attention to tradeoffs, etc. all seem to be critical.

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Parting Thoughts

• Anecdotal observations or evaluations based on self-reports alone are likely insufficient for evaluating the quality of structured decision approaches.

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Parting Thoughts

• Affective responses to stimuli exert powerful influences on risk judgments

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Parting Thoughts

• Not suggesting that the outcomes of all structured decision making approaches are suspect.

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Thanks

Tim McDanielsRobin Gregory

Ying ChuenpagdeeRobyn WilsonLouie RiversDan Ohlsen

SSHRCNSF

OARDCEPI