uncertainty and quality in scientific policy assessment -introductory remarks-

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Uncertainty and quality Uncertainty and quality in scientific policy in scientific policy assessment assessment -introductory remarks- -introductory remarks- Martin Krayer von Krauss, WHO/EEA Integrated Assessment of Health Risks of Environmental Stressors in Europe INTARES E

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Integrated Assessment of Health Risks of Environmental Stressors in Europe. INTA RESE. Uncertainty and quality in scientific policy assessment -introductory remarks-. Martin Krayer von Krauss, WHO/EEA. Introductions. Intarese contingent National public institutes Academia - PowerPoint PPT Presentation

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Page 1: Uncertainty and quality in scientific policy assessment -introductory remarks-

Uncertainty and qualityUncertainty and qualityin scientific policy assessmentin scientific policy assessment

-introductory remarks--introductory remarks-

Martin Krayer von Krauss, WHO/EEA

Integrated Assessment of Health Risks of Environmental Stressors in EuropeINTARES

E

Page 2: Uncertainty and quality in scientific policy assessment -introductory remarks-

IntroductionsIntroductions Intarese contingent

– National public institutes– Academia– Other: WHO, CEFIC, etc…

EEA contingent Others Marco Martuzzi & David Gee Jeroen van der Sluijs & Arthur Petersen Jerry Ravetz and Andrea Saltelli Jacqueline McGlade

Page 3: Uncertainty and quality in scientific policy assessment -introductory remarks-

ContextContext

Science with a twist!

Page 4: Uncertainty and quality in scientific policy assessment -introductory remarks-
Page 5: Uncertainty and quality in scientific policy assessment -introductory remarks-
Page 6: Uncertainty and quality in scientific policy assessment -introductory remarks-

ContextContext Stakes are high; Values are in dispute; Facts are uncertain.

In a situation where very few of our assessments can truly be “validated”, and where the consequences of error could be far reaching, how do we ensure the quality of our work?

Page 7: Uncertainty and quality in scientific policy assessment -introductory remarks-

Workshop ObjectiveWorkshop ObjectiveProvide you with an understanding of: The context within which science for policy is conducted; The rational for the interest in uncertainty and quality in policy assessments; Qualitative as well as quantitative conceptions of uncertainty; Qualitative and quantitative approaches to managing uncertainty and quality; The relationship between uncertainty, quality and stakeholder participation.

Page 8: Uncertainty and quality in scientific policy assessment -introductory remarks-

Dynamic learningDynamic learningLecturingDiscussionsExercise

Workshop dinner!

Page 9: Uncertainty and quality in scientific policy assessment -introductory remarks-

Setting the scene: Setting the scene: The RIVM credibility crisis of 1999 The RIVM credibility crisis of 1999

and the subsequent responseand the subsequent response Chair: Gordon McInnes, Deputy Director, EEA Presentations:

– Arthur Petersen, Director of the Methodology and Modelling Programme, MNP

– Jeannette Beck, Program Leader on Air Quality, MNP – Jan Wijmenga, Netherlands Ministry of Housing,

Spatial Planning and the Environment Discussion: Quality and uncertainty management

needs in science for policy– Sigfus Bjarnason, Head of group, EEA

Page 10: Uncertainty and quality in scientific policy assessment -introductory remarks-

Session 2: the contextSession 2: the context 13.00-14.00 13.00-14.00

Lecturing (30 minutes)– Introduction by Jerry Ravetz– Reflexivity and the Reflexive Practitioner (AP)– Levels of uncertainty (mkvk)

Discussion (30 minutes)

Page 11: Uncertainty and quality in scientific policy assessment -introductory remarks-

Uncertainty: a 3 dimensional Uncertainty: a 3 dimensional conceptconcept

Location

Level

Nature

See: Walker et al., (2003). J. of Integrated Assessment, 4 (1): 5-17.

Page 12: Uncertainty and quality in scientific policy assessment -introductory remarks-

Location of UncertaintyLocation of Uncertainty(1(1stst dimension) dimension)

Refers to the location at which the uncertainty manifests itself in the model

Examples of common assessment models:– Risk Assessment:

Risk = Probability x Consequence– Environmental & Health assessment of chemicals:

Risk = Exposure x Effect

Generic model locations: – Context (e.g. boundaries, framing) – Input data– Model uncertainty– Calibration data– Parameter uncertainty– Model output (conclusion)

Page 13: Uncertainty and quality in scientific policy assessment -introductory remarks-

Level of Uncertainty Level of Uncertainty (2(2ndnd dimension) dimension)

StatisticalUncertainty

ScenarioUncertainty

RecognisedIgnorance

TotalIgnorance

e.g. see Knight, 1921; Smithson, 1988; Funtowicz and Ravetz, 1990; Faber et al., 1992; Wynne, 1992; Schneider & Turner, 1994; ESTO, 2001.

Location

Level

Nature

Page 14: Uncertainty and quality in scientific policy assessment -introductory remarks-

Statistical Statistical UncertaintyUncertainty

Normal Distribution

-1.9

-1.6

-1.3 -1

-0.7

-0.4

-0.1 0.2

0.5

0.8

1.1

1.4

1.7 2

= 0

= .5

•There exist solid grounds for the assignment of a discrete probability to each of a well-defined set of outcomes.

•We have a well known functional relationship

•We have an adequate combination of: (i) number of parameters and (ii) amount and character of data.

Page 15: Uncertainty and quality in scientific policy assessment -introductory remarks-

-1.9

-1.6

-1.3 -1

-0.7

-0.4

-0.1 0.2

0.5

0.8

1.1

1.4

1.7 2

Scenario UncertaintyScenario UncertaintyWe can describe a set of outcomes to be expected, but we cannot associate probabilities very well. Assumptions; various plausible scenarios; unverified “what if ?” questions; Ambiguous results.

?

?

?

? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ? ?

Page 16: Uncertainty and quality in scientific policy assessment -introductory remarks-

Example of scenario uncertainty:Example of scenario uncertainty: Antibiotics in animal feedstuffAntibiotics in animal feedstuff

Scenario: resistance to antibiotics The widespread use of the antibiotics could lead to the development of

resistant bacterial strains; In the long run, antibiotics would no longer be effective in the

treatment of disease in humans.

• Scientific evidence: the development of bacterial resistance can take place. • How quickly and to what extent will it become a problem?

The outcome is clear, the probability of it occurring is unknown.

Page 17: Uncertainty and quality in scientific policy assessment -introductory remarks-

IgnoranceIgnoranceWe do not know the essential functional

relationships. There exist neither grounds for the assignment

of probabilities, nor even the basis for the definition of a complete set of outcomes.

More information may become known later through research, but little is known for the time being.

Recognized ignorance: We know that we don’t know!

Location

Level

Nature

StatisticalUncertainty

ScenarioUncertainty

RecognisedIgnorance

TotalIgnorance

Page 18: Uncertainty and quality in scientific policy assessment -introductory remarks-

Consider the case of a scientist asked to assess the risks or the costs of BSE at the time of its discovery in 1986.

No historical data on BSE was available and scientific understanding of how the disease is contracted was limited.

The extent of the public outcry that would eventually occur remained unknown, as did the extent of the loss of exports and the drop in domestic demand that ensued.

Knowledge on the relationship between BSE and CJD would not become available for another 10 years.

Any assessment would necessarily rely on a large number of assumptions, there would be no credible basis for the assignment of probabilities.

There would not even be a credible basis to claim that all

of the potential outcomes of the BSE epidemic had been thought of.

Example of ignorance: Example of ignorance: Mad cow disease & CJDMad cow disease & CJD

Page 19: Uncertainty and quality in scientific policy assessment -introductory remarks-

Different levels of uncertainty call for different approaches to uncertainty assessment and management!

StatisticalUncertainty

ScenarioUncertainty

RecognisedIgnorance

TotalIgnorance

Page 20: Uncertainty and quality in scientific policy assessment -introductory remarks-

Session 3: Basic conceptsSession 3: Basic concepts 14.00-15.30 14.00-15.30

Lecturing (45 minutes): Jeroen van der Sluijs – Knowledge quality assessment– Problem framing and context– Indicators– Intro: approaches to uncertainty management

Coffee break (10 minutes) Discussion (30 minutes) Comfort break (5 minutes)

Page 21: Uncertainty and quality in scientific policy assessment -introductory remarks-

Session 4: Approaches to Session 4: Approaches to managing uncertaintymanaging uncertainty

15.30-17.00 15.30-17.00 Lecturing (45 minutes)

– Quantitative approaches by Andrea Saltelli– Qualitative approaches (JvdS)– Procedural approaches (JvdS)

Comfort break (5 minutes)Discussion (40 minutes)

Page 22: Uncertainty and quality in scientific policy assessment -introductory remarks-

Session 5: ExerciseSession 5: Exercise09.30-14.20 09.30-14.20

Presentation (15 minutes) (JvdS/AP/MKvK)– Intro to case study – Intro to assignment

Facilitated group work 12.00-13.00 Lunch 13.00-14.20 Session 5 Continued

– Presentation & discussion of results (60 minutes)– Presentation of assignment for interim period (15

minutes) Coffee break (10 minutes)

Page 23: Uncertainty and quality in scientific policy assessment -introductory remarks-

Session 6: stakeholder participationSession 6: stakeholder participation 14.30-15.30 14.30-15.30

Presentation (40 minutes) (JvdS)– Why participation?– Introduction to approaches.

Discussion (40 minutes)

15.30-16.00 Discussion and evaluation of course