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Intergenerational Equality: Quantitatively Analyzing Ethical
Philosophy With Integrated Assessment Modeling
1,2Alex Pusch, 2Gregory Garner
INTRODUCTION
MODELING
MODEL OUTCOMES
STATISTICALANALYSIS CONCLUSIONS
IntegratedAssessment Modeling combines and evaluates economic and
ecological parameters to inform climate policy decisions. Among these
parameters are discount rates, which serve as intertemporal weightings
between generations and often carry underlying utilitarian assumptions.
This study aims to:
1. Determine the complexities and tradeoffs introduced in modeling
between ideologies and opinions.
2. Evaluate the implications and outcomes of diverse stakeholder
preferences.
After running the model through the multiple seed
experiment, results were evaluated using 3 criteria that
describe the optimization process at a given function
evaluation.
1. Fit:
• Generational Distance is a measure of how well
the pareto-front “fits” the reference set by
measuring mean squared error.A pareto set
with perfect fit would have a generational
distance equal to zero.
2. Continuity:
• The Epsilon Indicator measures how many gaps
there are in a set of solutions. A perfectly
continuous pareto-front would have an epsilon
indicator value equal to zero.
3. Convergence:
• Hypervolume measures the ratio of the volume
that a solution set occupies relative to its
reference set. Ideally, a pareto-front will achieve
a hypervolume of 1, meaning it is identical to its
reference set.
0.0
0.2
0.4
0.6
0.8
1.0
1.2
Emissions Control Rate
Year
ControlRate[FractionofGHG]
2010 2035 2060 2085 2110 2135 2160
Nordhaus
Stern
Prioritarian 1
Prioritarian 2
Compromise 1
Compromise 2
Compromise 3
0
2
4
6
8
Net Present Value of Abatement Costs
Year
Cost[trillions2005USD]
2010 2035 2060 2085 2110 2135 2160
Nordhaus
Stern
Prioritarian 1
Prioritarian 2
Compromise 1
Compromise 2
Compromise 3
0
50
100
150
200
250
300
Social Cost of Carbon
Year
Cost[2005USDpertonCO2]
2010 2035 2060 2085 2110 2135 2160
Nordhaus
Stern
Prioritarian 1
Prioritarian 2
Compromise 1
Compromise 2
Compromise 3
1.0
1.5
2.0
2.5
3.0
Temperature Change
Year
TemperatureChange[degCsince1900]
2010 2035 2060 2085 2110 2135 2160
Nordhaus
Stern
Prioritarian 1
Prioritarian 2
Compromise 1
Compromise 2
Compromise 3
0
2
4
6
8
10
12
14
Damages
Year
Cost[trillions2005USD]
2010 2035 2060 2085 2110 2135 2160
Nordhaus
Stern
Prioritarian 1
Prioritarian 2
Compromise 1
Compromise 2
Compromise 3
Objectives were projected out to 2160. After analysis, we found:
• Prioritarian outcomes lie between utilitarian outcomes.
• Stern and Nordhaus both prescribe immediate action, whereas
prioritarian frameworks prescribe steadier emissions control.
• All policy approaches exceed the 2° C limit established by the Paris
conference.
ACKNOWLEDGEMENTS
This work was supported by the National Science Foundation through the Network forSustainable Climate Risk Management (SCRiM) under NSF cooperative
agreement GEO-1240507.Anyopinions, findings, and conclusions or recommendations expressed in this material are those ofthe author(s) and do not necessarily
reflect the views ofthe National Science Foundation.
References:
1. Adler, Matthew D., and Nicolas Treich. "Prioritarianism and Climate Change." Environmental and Resource Economics Environ Resource Econ 62.2 (2015): 279-
308.Springer. Web. 1 July 2016.
2. Garner, Gregory, Patrick Reed, and Klaus Keller. "Climate Risk Management Requires Explicit Representation ofSocietal Trade-offs." Climatic Change134.4
(2016): 713-23.Web. 25May 2016.
3. Hadka, David, and Patrick Reed. "Borg: AnAuto-Adaptive Many-Objective Evolutionary Computing Framework." EvolutionaryComputation 21.2 (2013):231-
59.Web. 25May 2016.
4. Reed, P.m., D.Hadka, J.d. Herman, J.r.Kasprzyk, and J.b. Kollat. "Evolutionary Multiobjective Optimization in Water Resources:The Past, Present, and
Future." Advancesin WaterResources 51 (2013):438-56.Web. 25May 2016.
5. Ward, Victoria L., Riddhi Singh, Patrick M. Reed, and Klaus Keller. "ConfrontingTipping Points: Can Multi-objective Evolutionary Algorithms Discover Pollution
ControlTradeoffs given Environmental Thresholds?” Environmental Modelling& Software 73 (2015): 27-43.Web. 25May 2016.
• Prioritarianism is more ethically and possibly quantitatively
defensible. It is also more conducive to capturing threshold climate
impacts such as melting of major ice sheets.
• The Stern objective did not perform well relative to any of the others.
This is demonstrated by the blue line in the figure below.
• Prioritarianism presents a need for better understanding of future
damages as outcomes are heavily reliant on damages.
FutureWork:
• Further modeling with prioritarianism
• Statistical analysis of each policy
approach
• Experiments across alternative damage
functions
1Pomona College (contact: awp02014@mymail.pomona.edu), 2Pennsylvania State University
Preference
Stern Nordhaus Prioritarian 1 Prioritarian 2
η=1.5, δ=.001 η=1.45, δ=.015 γ=1.5 γ=2.5

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Analyzing Climate Policies with Integrated Assessment Modeling

  • 1. Intergenerational Equality: Quantitatively Analyzing Ethical Philosophy With Integrated Assessment Modeling 1,2Alex Pusch, 2Gregory Garner INTRODUCTION MODELING MODEL OUTCOMES STATISTICALANALYSIS CONCLUSIONS IntegratedAssessment Modeling combines and evaluates economic and ecological parameters to inform climate policy decisions. Among these parameters are discount rates, which serve as intertemporal weightings between generations and often carry underlying utilitarian assumptions. This study aims to: 1. Determine the complexities and tradeoffs introduced in modeling between ideologies and opinions. 2. Evaluate the implications and outcomes of diverse stakeholder preferences. After running the model through the multiple seed experiment, results were evaluated using 3 criteria that describe the optimization process at a given function evaluation. 1. Fit: • Generational Distance is a measure of how well the pareto-front “fits” the reference set by measuring mean squared error.A pareto set with perfect fit would have a generational distance equal to zero. 2. Continuity: • The Epsilon Indicator measures how many gaps there are in a set of solutions. A perfectly continuous pareto-front would have an epsilon indicator value equal to zero. 3. Convergence: • Hypervolume measures the ratio of the volume that a solution set occupies relative to its reference set. Ideally, a pareto-front will achieve a hypervolume of 1, meaning it is identical to its reference set. 0.0 0.2 0.4 0.6 0.8 1.0 1.2 Emissions Control Rate Year ControlRate[FractionofGHG] 2010 2035 2060 2085 2110 2135 2160 Nordhaus Stern Prioritarian 1 Prioritarian 2 Compromise 1 Compromise 2 Compromise 3 0 2 4 6 8 Net Present Value of Abatement Costs Year Cost[trillions2005USD] 2010 2035 2060 2085 2110 2135 2160 Nordhaus Stern Prioritarian 1 Prioritarian 2 Compromise 1 Compromise 2 Compromise 3 0 50 100 150 200 250 300 Social Cost of Carbon Year Cost[2005USDpertonCO2] 2010 2035 2060 2085 2110 2135 2160 Nordhaus Stern Prioritarian 1 Prioritarian 2 Compromise 1 Compromise 2 Compromise 3 1.0 1.5 2.0 2.5 3.0 Temperature Change Year TemperatureChange[degCsince1900] 2010 2035 2060 2085 2110 2135 2160 Nordhaus Stern Prioritarian 1 Prioritarian 2 Compromise 1 Compromise 2 Compromise 3 0 2 4 6 8 10 12 14 Damages Year Cost[trillions2005USD] 2010 2035 2060 2085 2110 2135 2160 Nordhaus Stern Prioritarian 1 Prioritarian 2 Compromise 1 Compromise 2 Compromise 3 Objectives were projected out to 2160. After analysis, we found: • Prioritarian outcomes lie between utilitarian outcomes. • Stern and Nordhaus both prescribe immediate action, whereas prioritarian frameworks prescribe steadier emissions control. • All policy approaches exceed the 2° C limit established by the Paris conference. ACKNOWLEDGEMENTS This work was supported by the National Science Foundation through the Network forSustainable Climate Risk Management (SCRiM) under NSF cooperative agreement GEO-1240507.Anyopinions, findings, and conclusions or recommendations expressed in this material are those ofthe author(s) and do not necessarily reflect the views ofthe National Science Foundation. References: 1. Adler, Matthew D., and Nicolas Treich. "Prioritarianism and Climate Change." Environmental and Resource Economics Environ Resource Econ 62.2 (2015): 279- 308.Springer. Web. 1 July 2016. 2. Garner, Gregory, Patrick Reed, and Klaus Keller. "Climate Risk Management Requires Explicit Representation ofSocietal Trade-offs." Climatic Change134.4 (2016): 713-23.Web. 25May 2016. 3. Hadka, David, and Patrick Reed. "Borg: AnAuto-Adaptive Many-Objective Evolutionary Computing Framework." EvolutionaryComputation 21.2 (2013):231- 59.Web. 25May 2016. 4. Reed, P.m., D.Hadka, J.d. Herman, J.r.Kasprzyk, and J.b. Kollat. "Evolutionary Multiobjective Optimization in Water Resources:The Past, Present, and Future." Advancesin WaterResources 51 (2013):438-56.Web. 25May 2016. 5. Ward, Victoria L., Riddhi Singh, Patrick M. Reed, and Klaus Keller. "ConfrontingTipping Points: Can Multi-objective Evolutionary Algorithms Discover Pollution ControlTradeoffs given Environmental Thresholds?” Environmental Modelling& Software 73 (2015): 27-43.Web. 25May 2016. • Prioritarianism is more ethically and possibly quantitatively defensible. It is also more conducive to capturing threshold climate impacts such as melting of major ice sheets. • The Stern objective did not perform well relative to any of the others. This is demonstrated by the blue line in the figure below. • Prioritarianism presents a need for better understanding of future damages as outcomes are heavily reliant on damages. FutureWork: • Further modeling with prioritarianism • Statistical analysis of each policy approach • Experiments across alternative damage functions 1Pomona College (contact: awp02014@mymail.pomona.edu), 2Pennsylvania State University Preference Stern Nordhaus Prioritarian 1 Prioritarian 2 η=1.5, δ=.001 η=1.45, δ=.015 γ=1.5 γ=2.5