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Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef van Vuuren 2 Bert de Vries 2 Arthur Beusen 2 Peter Heuberger 2 Serafin Corral Quintana 3 Silvio Funtowicz 3 Penny Kloprogge 1 David Nuijten 1 Arthur Petersen 5 Jerry Ravetz 4 1 UU-STS 2 RIVM 3 EC-JRC 4 RMC 5 VUA [email protected]

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Page 1: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Uncertainty assessment of the IMAGE/TIMER B1 CO2 emissions

scenario using the NUSAP method

Jeroen P. van der Sluijs1

Jose Potting1

James Risbey1

Detlef van Vuuren2

Bert de Vries2

Arthur Beusen2

Peter Heuberger2

Serafin Corral Quintana3

Silvio Funtowicz3

Penny Kloprogge1

David Nuijten1

Arthur Petersen5

Jerry Ravetz4

1UU-STS 2RIVM 3EC-JRC 4RMC 5VUA

[email protected]

Page 2: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Objective

Develop a framework for uncertainty assessment and management

addressing quantitative & qualitative dimensions

test & demonstrate usefulness in IA models

Page 3: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

IMAGE 2: Framework of models and Linkages

World Economy(WorldScan)

Population(Popher)

Change in GDP, population & others (i.e. scenario assumptions)

Land-useemissions

Energy demand & supply (TIMER)

Energy & industry emissions

Land demand, use & cover

Emissions & land-use changes

Carbon cycle

Atmospheric chemistry

Concentration changes

Climate (Zonal Climate Model or ECBilt)

Climatic changes

Naturalsystems

AgriculturalImpacts

Water Impacts

Land degradation

Sea levelrise

Feedbacks

Impacts

Page 4: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

TIMER Model : five submodelsEnergy

Demand (ED)

Liquid Fuel

supply (LF)

Gaseous Fuelsupply (GF)

Electric PowerGeneration (EPG)

Solid Fuelsupply (SF)

Population(POPHER)

Inputs: Population, GDP capita-1, activity in energy sectors, assumptions regarding technologicaldevelopment, depletion and others.

Outputs: End-use energy consumption, primary energyconsumption.

Fuel demand

Prices

Economy(WorldScan)

Electricitydemand

Page 5: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Main objectives TIMER

• To analyse the long-term dynamics of the energy system, and in particular changes in energy demand and the transition to non-fossil fuels within an integrated modeling framework;

• To construct and simulate greenhouse gas emission scenarios that are used in other submodels of IMAGE 2.2 or that are used in meta-models of IMAGE;

Page 6: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Key questions

What are key uncertainties in TIMER? What is the role of model structure

uncertainties in TIMER? Uncertainty in which input variables and

parameters dominate uncertainty in model outcome?

What is the strength of the sensitive parameters (pedigree)?

Page 7: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Location of uncertainty• Input data• Parameters• Technical model structure• Conceptual model sruct. /assumptions• Indicators• Problem framing• System boundary• Socio-political and institutional context

Page 8: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Sorts of uncertainty

• Inexactness

• Unreliability

• Value loading

• Ignorance

Page 9: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Inexactness

• Variability / heterogeneity

• Lack of knowledge

• Definitional vagueness

• Resolution error

• Aggregation error

Page 10: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Unreliability• Limited internal strength in:

– Use of proxies– Empirical basis– Theoretical understanding– Methodological rigour (incl. management of anomalies)– Validation

• Limited external strength in:– Exploration of rival problem framings– Management of dissent– Extended peer acceptance / stakeholder involvement– Transparency– Accessibility

• Future scope• Linguistic imprecision

Page 11: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Value loading• Bias

– In knowledge production– Motivational bias (interests, incentives)– Disciplinary bias– Cultural bias– Choice of (modelling) approach (e.g. bottom up, top down)– Subjective Judgement– In knowledge utilization– Strategic/selective knowledge use

• Disagreement– about knowledge – about values

Page 12: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Ignorance• System indeterminacy

– open endedness– chaotic behavior

• Active ignorance– Model fixes for reasons understood– limited domains of applicability of functional

relations– Surprise A

• Passive ignorance– Bugs (numerical / software / hardware error)– Model fixes for reasons not understood– Surprise B

Page 13: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Method Checklist for model quality assistance Meta-level analysis SRES scenarios to

explore model structure uncertainties Global sensitivity analysis (Morris) NUSAP expert elicitation workshop to assess

pedigree of sensitive model components Diagnostic diagram to prioritise uncertainties

by combination of criticality (Morris) and strength (pedigree)

Page 14: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Checklist

• Assist in quality control in complex models

• Not models are good or bad but ‘better’ and ‘worse’ forms of modelling practice

• Quality relates to fitness for function

• Help guard against poor practice

• Flag pittfalls

Page 15: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Checklist structure

• Screening questions

• Model & problem domain

• Internal strength

• Interface with users

• Use in policy process

• Overall assessment

Page 16: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Global CO2 emission from fossil fuels

0.00

5.00

10.00

15.00

20.00

25.00

30.00

35.00

40.00

1990 2000 2010 2020 2030 2040 2050 2060 2070 2080 2090 2100

Year

CO

2 E

mis

sio

n (

in G

tC)

Mar

iaM

essa

geA

imM

inic

amA

SFIm

age

(Van Vuuren et al. 2000)

(SRES scenarios reported to IPCC (2000) by six different modelling groups)

B1-marker

Page 17: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Morris (1991)

• facilitates global sensitivity analysis in minimum number of model runs

• covers entire range of possible values for each variable

• parameters varied one step at a time in such a way that if sensitivity of one parameter is contingent on the values that other parameters may take, Morris captures such dependencies

Page 18: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Most sensitive model components:

• Population levels and economic activity• Intra-sectoral structural change• Progress ratios for technological improvements• Size and cost supply curves of fossil fuels

resources• Autonomous and price-induced energy

efficiency improvement• Initial costs and depletion of renewables

Page 19: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

NUSAP: Pedigree

Evaluates the strength of the number by looking at:

• Background history by which the number was produced

• Underpinning and scientific status of the number

Page 20: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Parameter Pedigree

• Proxy

• Empirical basis

• Theoretical understanding

• Methodological rigour

• Validation

Page 21: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

ProxySometimes it is not possible to obtain direct

measurements or estimates of the parameter and so some form of proxy measure is used.

Proxy refers to how good or close a measure of the quantity which we model is to the actual quantity we represent. An exact measure of the quantity would score four. If the measured quantity is not clearly related to the desired quantity the score would be zero.

Page 22: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Empirical basisEmpirical quality typically refers to the degree to which

direct observations are used to estimate the parameter.

When the parameter is based upon good quality observational data, the pedigree score will be high. Sometimes directly observed data are not available and the parameter is estimated based on partial measurements or calculated from other quantities. Parameters determined by such indirect methods have a weaker empirical basis and will generally score lower than those based on direct observations.

Page 23: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Theoretical understandingThe parameter will have some basis in

theoretical understanding of the phenomenon it represents. This criterion refers to the extent en partiality of the theoretical understanding.

Parameters based on well established theory will score high on this metric, while parameters whose theoretical basis has the status of crude speculation will score low.

Page 24: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Methodological rigourSome method will be used to collect, check, and

revise the data used for making parameter estimates. Methodological quality refers to the norms for methodological rigour in this process applied by peers in the relevant disciplines.

Well established and respected methods for measuring and processing the data would score high on this metric, while untested or unreliable methods would tend to score lower.

Page 25: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

ValidationThis metric refers to the degree to which one has been able

to cross-check the data against independent sources.

When the parameter has been compared with appropriate sets of independent data to assess its reliability it will score high on this metric. In many cases, independent data for the same parameter over the same time period are not available and other datasets must be used for validation. This may require a compromise in the length or overlap of the datasets, or may require use of a related, but different, proxy variable, or perhaps use of data that has been aggregated on different scales. The more indirect or incomplete the validation, the lower it will score on this metric.

Page 26: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Code Proxy Empirical Theoretical basis Method Validation

4 Exactmeasure

Large sampledirect mmts

Well establishedtheory

Best availablepractice

Compared withindep. mmts ofsame variable

3 Good fit ormeasure

Small sampledirect mmts

Accepted theorypartial in nature

Reliable methodcommonlyaccepted

Compared withindep. mmts ofclosely relatedvariable

2 Wellcorrelated

Modeled/deriveddata

Partial theorylimitedconsensus onreliability

Acceptablemethod limitedconsensus onreliability

Compared withmmts notindependent

1 Weakcorrelation

Educated guesses/ rule of thumbest

Preliminarytheory

Preliminarymethodsunknownreliability

Weak / indirectvalidation

0 Not clearlyrelated

Crudespeculation

Crudespeculation

No discerniblerigour

No validation

Page 27: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Elicitation workshop

• 18 experts (in 3 parallel groups of 6) discussed parameters, one by one, using information & scoring cards

• Individual expert judgements, informed by group discussion

Page 28: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef
Page 29: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef
Page 30: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Example result gas depletion multiplier

Same data represented as kite diagram:Green = min. scores, Amber= max scores, Light green = min. scores if outliers omitted(Traffic light analogy)

Radar diagram:Each coloured line represents scores given by one expert

Page 31: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Average scores (0-4)• proxy 2½ ±½

• empirical 2 ±½

• theory 2 ±½

• method 2 ±½

• validation 1 ±½

• valueladeness 2½ ±1

• competence 2 ±½

Page 32: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef
Page 33: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Conclusions (1)

Model quality assurance checklist proves quick scan to flag major areas of concern and associated pitfalls in the complex mass uncertainties.

Meta-level intercomparison of TIMER with the other SRES models gave us some insight in the potential roles of model structure uncertainties.

Page 34: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Conclusions (2)

Global sensitivity analysis supplemented with expert elicitation constitutes an efficient selection mechanism to further focus the diagnosis of key uncertainties.

Our pedigree elicitation procedure yields a differentiated insight into parameter strength.

Page 35: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Conclusions (3)

The diagnostic diagram puts spread and strength together to provide guidance in prioritisation of key uncertainties.

Page 36: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

Conclusions (4)

NUSAP method:• can be applied to complex models in a

meaningful way• helps to focus research efforts on the

potentially most problematic model components

• pinpoints specific weaknesses in these components

Page 37: Uncertainty assessment of the IMAGE/TIMER B1 CO 2 emissions scenario using the NUSAP method Jeroen P. van der Sluijs 1 Jose Potting 1 James Risbey 1 Detlef

More information:

www.nusap.net