Abstract
In the meta-modeling approach, one builds a numerically tractable dynamic optimization or game model in which the parameters are identified through statistical emulation of a detailed large scale numerical simulation model. In this paper, we show how this approach can be used to assess the economic impacts of possible climate policies compatible with the Paris Agreement. One indicates why it is appropriate to assume that an international carbon market, with emission rights given to different groups of countries will exist. One discusses the approach to evaluate correctly abatement costs and welfare losses incurred by different groups of countries when implementing climate policies. Finally, using a recently proposed meta-model of game with a coupled constraint on a cumulative CO2 emissions budget, we assess several new scenarios for possible fair burden sharing in climate policies compatible with the Paris Agreement.
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Notes
The GEMINI-E3 model is continuously improved to better represent future possibilities of energy substitution. The model focuses on assessing the incremental capital cost of restructuring the economy, i.e., new investments in the production sectors and in housing aimed at improving energy efficiency. From a comprehensive survey, one has identified in each sector the technologies that can significantly increase energy efficiency. One assumes that these new technologies induce more capitalistic equipment and more energy-efficient production. These new technologies are introduced into the model through technical progress (positive for energy and negative for capital). In order to be accepted by the industrial sectors, the change must be profitable, which means that the discounted savings in operating costs over the lifespan of the investment must be greater or equal to their price increase. This methodology has been implemented in housing, industry, and transportation sectors. In the model, one offers the possibility to use carbon capture and sequestration (CCS) technology only for coal-fired power plant. When the total cost of the CCS technology is lower than the carbon price, one assumes that all investments in power plants using coal are done with CCS. Simulation is based on a CCS cost of US$100 by ton of CO2.
In a paper published in 1999 [26], the energy taxation in the USA and European countries was compared and a gap equivalent to US$100 by ton of carbon (around US$25 by ton of CO2) was found. The authors concluded that the USA should start implementing a carbon tax of this level before the European countries start taxing GHG emissions.
This behavior is known in the economic literature as “greasing.”
This mechanism of a world carbon market under distortions, i.e. in a second-best setting à la Boiteux [27], has been theorized in a 1999 paper [28] presented at the Paris 1999-IEW conference with numerical simulations displayed in another paper presented at the same conference and also in [25]. An important issue is the efficiency of the market, according to the Pareto criterion. In second-best problems, in particular in the present one where the issue is to determine the equilibrium (in the markets of goods and in the market of permits) between countries implementing each a second-best policy, Pareto efficiency is not in general strictly obtained when there are not simplifying assumptions such as in the Diamond and Mirrlees paradigm [29] (where the firms profits are totally taxed). In the present case, Pareto efficiency can be shown to turn up under separability conditions which are not exactly verified in the real world. Nevertheless it is permitted to consider that the equilibrium is not far from Pareto-efficiency, and the eventual gap to efficiency can be assessed through numerical simulations of macroeconomic models.
This is for the mitigation issue and does not preclude others transfers under the adaptation issue, with tools such as the Green Climate Fund.
The unconditional target refers to an initial objective of GHG emissions for a reference year or period. The target, called conditional, provides additional GHG abatement efforts conditional on some circumstances or events (e.g., actions of other parties, contingent on broader mitigation efforts of other countries, the provision of financial transfers by other countries, and technology or capacity building support).
Without US participation to the Paris Agreement, the permit price is equal to US$16.
IPCC, 2013. Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Cli-mate Change, Stocker, T.F., D. Qin, G.-K. Plattner, M. Tignor, S.K. Allen, J. Boschung, A. Nauels, Y. Xia, V. Bex and P.M. Midgley Eds. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.
It appears that for a given level of cumulative CO2 emissions, the planet experiences about the same level of warming irrespective of whether that CO2 is emitted fast or slow [6]. The safety cumulative emissions budget for the entire anthropocene, i.e. since the beginning of industrial era, compatible with a 2 °C target at the end of twenty-first century is estimated at one trillion tonnes of carbon (3.7 trillion tonnes of CO2), half of which had already been emitted by 2015.
As shown in [38], one should expect a manifold of equilibria indexed over a weighting of the players. Here, we show the results for the equilibrium corresponding to an equal weight given to all players.
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This research is supported by the Qatar National Research Fund under Grant Agreement No. NPRP10-0212-170447.
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Appendix: Mathematical Description of the Meta-models
Appendix: Mathematical Description of the Meta-models
1.1 Appendix 1: The Game Design Problem.
Design variables
θj, share of the safety emission budget given to group of country j. These variables define the key element of the negotiations, namely the sharing of the safety emission budget.
Strategic variables
ωj(t), supply of quotas by coalition j during period t. We assume that once a player (group of countries) has been given a share of the emission budget, it can supply this amount of quotas (emission rights) on the emissions trading markets organized at each period of the planning horizon. These supplies are strategic variables. They influence the market structure, determining price of carbon, then emission levels by each player, and, finally the transfers (buying and selling of permits) and the net surplus variations.
Secondary (passive) variables
These are variables that will be computed from the values given to the strategic variables. They will be used to describe the permits market functioning. Using statistical emulation an abatement cost is estimated as a function of the abatement realized w.r.t. the BaU scenario.
- ej(t):
-
emission level for group of countries j in period t;
- qj(t):
-
abatement level for player j in period t;
- p(t):
-
carbon price in period t;
- ACtj(qj(t)):
-
abatement cost for player j in period t;
- MACtj(qj(t)):
-
marginal abatement cost for player j in period t;
- GTTj(t):
-
gains from the terms of trade for player j in period t;
- ν j :
-
multiplier associated with the share of budget given to group of countries j.
Parameters
- Bud:
-
safety budget: global safety emission budget;
- bcej(t):
-
BaU emissions for group of countries j in period t;
- α0j(t), α2j(t), α2j(t), α3j(t), α4j j(t)):
-
coefficients in the abatement cost function;
- μ0j(t), μ1j(t):
-
coefficients in the gain from the terms of trade function;
- β :
-
periodic discount factor;
- hcj:
-
discounted household consumption in BaU scenario over the planning horizon.
Payoffs for the game of quotas supply
The players (groups of countries) try to minimize (resp. maximize) the discounted sum of net surplus losses (resp. gains). The payoff is therefore defined as the discounted sum of the gains from the terms of trade plus the gains from the permit trading (can be negative) minus the abatement cost, given the actions taken by the other players.
where qj(t) = bcej(t) − ej(t)
Functions estimated by statistical emulation of GEMINI-E3: They are the abatement cost
and the gains in the terms of trade
The statistical emulation of GEMINI-E3 is based on a sample of 200 scenarios that simulate different possible world climate change policies.
Objective of the game design problem
One applies a Rawlsian criterion of fairness [39].
where \( {\mathrm{W}}_j^{\ast } \) is the Nash equilibrium payoff for the game designed by the choice of the θ’s. So we select the sharing which, in the Nash equilibrium solution of the game of quotas supply, maximizes the worst surplus gain among the players.
We describe now how to characterize the Nash equilibrium in the game of quotas supply. There are m players (groups of countries) indexed j = 1, …, m, that generate emissions ej (t) on periods t ∈ {0, 1, …, T − 1}. Let Ω (t) = \( {\sum}_{j=1}^m{\omega}_j(t) \) denote the total supply of permits on the market at period t and p(t, Ω(t)) the clearing permit price at period t.
We assume a competitive market for emissions permits, which clears at each period. Given a price p(t), each player chooses emissions so as to (5)
where \( {\pi}_j^t\left({e}_j(t)\right)=-{AC}_j^t\left({\mathrm{bce}}_j(t)-{e}_j(t)\right) \) is the economic benefit associated with emission level ej (t) at period t. The equilibrium conditions of profit maximization and market clearing are then
These conditions define after-trade equilibrium emissions, ej (t, Ω(t)), and the permit price p(t, Ω(t, t). Differentiating (5) and (6), we can compute the derivatives
Applying standard Kuhn-Tucker multiplier method, with multipliers νj, and exploiting the equality (5), we obtain the following first order necessary conditions for a Nash equilibrium
1.2 Appendix 2: Imposing the Benchmark Abatement Scenario
To obtain in the game the same global abatement schedule as in the benchmark scenario, it suffices to add, for the periods 2020, 2030, and 2040, new coupled constraints imposing the global supply of permits on the world market to be greater than or equal to the corresponding emissions level in the benchmark scenario. More formally, we introduce the new parameters
and the new constraints
The NOCs will be modified in an obvious way.
1.3 Appendix 3: Full Optimization vs. Equilibrium
To find the fully optimal solution, one solves the following problem:
where, as defined above, bcej (t) denotes the BaU emissions and qj (t) the abatement level for group of countries j in period t; Let q∗(·) denotes the optimal abatement path for all countries. The optimal emissions levels are determined by
We form the Lagrangian
where π is the multiplier (dual variable) associated with the global emissions budget constraint.
The optimality conditions are
These are also the market clearing conditions for an international emissions trading scheme. The carbon price at t will thus be p⋆(t) = π⋆β−t.
1.3.1 Fair Allocation of Emission Permits
We consider that fairness is obtained when the net costs relative to the respective consumption levels in the BaU scenarios are equalized. The balance in net cost per unit of consumption is obtained at period t if the following relation holds true
where
and W⋆(t) with Hc (t) are world level values. The fair allocation of permits at period t would then be
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Babonneau, F., Bernard, A., Haurie, A. et al. Meta-Modeling to Assess the Possible Future of Paris Agreement. Environ Model Assess 23, 611–626 (2018). https://doi.org/10.1007/s10666-018-9630-6
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DOI: https://doi.org/10.1007/s10666-018-9630-6