Abstract
This paper compares the performance of two allowance allocation rules in an international climate change treaty. I construct a model in which countries differ according to both GDP and an idiosyncratic damage parameter that links global emissions to damage for an individual country. Allowances are allocated to treaty members according to an allocation rule based on a single allocation parameter. The model can be solved analytically to determine upper and lower bounds on this allocation parameter that ensure that a treaty of any given composition is internally and externally stable. I focus on grand coalition treaties. The first treaty examined uses a simple proportional rule in which allocations are set as some fraction of emissions in the non-cooperative equilibrium. The second treaty adds a coverage-contingent element to the allocation rule such that the emissions reduction required of each treaty member is weighted by the fraction of global emissions that treaty members as a whole emit in the non-cooperative equilibrium. I show that the coverage-contingent treaty outperforms the simpler treaty except when all countries have the same emissions intensity in the non-cooperative equilibrium (in which case neither treaty can reduce emissions).
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Notes
Based on emissions data from World Resources Institute, Climate Analysis Indicators Tool (Version 9), 2012.
It should be noted that more sophisticated outcome-based schemes can support treaties that may Pareto-dominate treaties supported by allocation-based schemes (Nagashima et al. 2009).
For example, in a simulation model with 12 regions (and hence 4084 possible non-singleton coalitions), Altamirano-Cabrera and Finus (2006) find stable coalitions only when pragmatic schemes are used.
It should be noted that in the absence of emissions-related damage, all countries would choose \(x=0\), and therefore have the same emissions intensity. This is a strong assumption; it ignores other important country-specific determinants of emissions intensity, such as natural capital endowments and historical factors.
Andreoni and Levinson (2001) derive a technique effect based on increasing returns to abatement. Copeland and Taylor (1994) derive an effect motivated by preferences over environmental quality. The latter typically yields an EKC between per-capita income and per-capita emissions, and it is this form of the EKC that has attracted most attention in empirical work. See Dinda (2004) for a useful survey of the literature.
Note in particular that country \(j\) correctly anticipates how total emissions from the expanded coalition will change if it joins. This is important to country \(j\) because this total determines the price at which its allocation can be traded if it joins. Note too that emissions from the expanded coalition do not necessarily increase by the allocation awarded to country \(j\); we need to allow for the possibility that allocations are coverage-contingent, which means that all allocations may change if country \(j\) joins the treaty.
Note that (28) is stated as a strict inequality while (25) is stated as a weak inequality. This implies that an indifferent member-country always chooses to remain in the treaty while an indifferent non-member country always chooses to join the treaty. Thus, all non-member countries strictly prefer to remain outside the treaty. I have not explored the possibility that an indifferent country instead plays a mixed strategy.
GDP data is from International Monetary Fund, World Economic Outlook Database, October 2012. GDP is calculated at purchasing power parity. Emissions data is from World Resources Institute, Climate Analysis Indicators Tool (Version 9), 2012.
References
Altamirano-Cabrera JC, Finus M (2006) Permit trading and stability of international climate agreements. J Appl Econ 9(1):19–47
Andreoni J, Levinson A (2001) The simple analytics of the environmental Kuznets curve. J Public Econ 80:269–286
Barrett S (1992) International environmental agreements as games. In: Carraro C (ed) International environmental negotiations. Edward Elgar, Cheltenham
Barrett S (1994) Self-enforcing international environmental agreements. Oxf Econ Pap 46:878–894
Barrett S (2001) International cooperation for sale. Eur Econ Rev 45:1835–1850
Carraro C, Siniscalco D (1993) Strategies for the international protection of the environment. J Public Econ 52:309–328
Carraro C, Eyckmans J, Finus M (2006) Optimal transfers and participation decisions in international environmental agreements. Rev Int Organ 1:379–396
Copeland B, Taylor MS (1994) North-South trade and the environment. Q J Econ 109:755–787
d’Aspremont C, Jacquemin A, Gabszewicz JJ, Weymark J (1983) On the stability of collusive price leadership. Can J Econ 16:17–25
Dinda S (2004) Environmental Kuznets curve hypothesis: a survey. Ecol Econ 49:431–455
Endres A, Finus M (2002) Quotas may beat taxes in a global emission game. Int Tax Public Financ 9:687–707
Eyckmans J (1999) Strategy-proof uniform effort sharing schemes for transfrontier pollution problems. Environ Resour Econ 14:165–189
Hoel M (1992) International environmental conventions: the case of uniform reductions of emissions. Environ Resour Econ 2:141–159
Hoel M, Schneider K (1997) Incentives to participate in an international environmental agreement. Environ Resour Econ 9:153–170
McGinty M (2007) International environmental agreements among asymmetric nations. Oxf Econ Pap 59(1):45–62
McGinty M, Milam G, Gelves A (2012) Coalition stability in public goods provision: testing an optimal allocation rule. Environ Resour Econ 53:327–345
Nagashima M, Dellink R, van Ierland E, Weikard HP (2009) Stability of international climate coalitions—a comparison of transfer schemes. Ecol Econ 68(5):1476–1487
Rose A, Stevens B, Edmonds J, Wise M (1998) International equity and differentiation in global warming policy. Environ Resour Econ 12:25–51
Weikard HP, Finus M, Altamirano-Cabrera JC (2006) The impact of surplus sharing on the stability of international climate agreements. Oxf Econ Pap 58:209–232
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Appendix
Appendix
1.1 Derivation of (10)
Set \(Z_{-i} =Z-z_{i}\) in (9) and cross-multiply to obtain
Collect terms to obtain
and then sum across \(i\) to obtain
which then yields (10).
1.2 Analysis of (41)
Rewrite condition (41) as
The RHS can be written as
since \(w_{CL} +\sum _{i\ne L} {w_{Ci}} =1\). Thus, the condition (41) becomes
This can never hold since \(v_{L}=\mathop {\hbox {min}}\nolimits _{i\in C} \{v_{i}\}\) and \(v_{i}\ge 0 \,\forall i\).
1.3 Proof of Proposition 2
We know from (20) that demand for allowances by member country \(i\) is
where
The emissions allowance for country \(i\) under the EPR treaty is
where \(v_{i}=\delta _{i}y_{i}\). Thus, allowance sales by country \(i\) are
where
It follows that \(s_{i}(\beta )>0\) if and only if \(v_{i}<\tilde{v}_{C}\), and \(s_{i}(\beta )<0\) if and only if \(v_{i}>\tilde{v}_{C}\).
1.4 Sketch Proof of Proposition 3
Setting \(\pi _{i}^{C}(\beta )=0\) and solving for \(\beta \) yields two roots for each value of \(v_{i}\) as a function of \(Y_{C}\) and \(S_{C}\). As noted in the text, these solutions are too complicated to report usefully here but they are easily generated using Maple (Version 15). The solutions are much simpler when \(Y_{C}=Y\) and \(S_{C}=S\), and reduce to the roots reported in the text. Note that these two roots are symmetric around a common intercept at \(v_{i}=\tilde{v}\).
1.5 Proof of Proposition 4
Setting \(Y=Y_{C}\) and \(S=S_{C}\) in \(\pi _{i}^{C}(\theta )=0\), and solving for \(\theta \) using Maple (Version 15), yields the solution for \(\bar{{\theta }}_{i}^{GC}\) as a function of \(y_{i}\) and \(\delta _{i}\) (too complicated to report here). From Proposition 3, let \(\bar{{\beta }}_{Li}^{GC}\) denote the solution for \(\bar{{\beta }}_{i}^{GC}\) when \(v_{i}<\tilde{v}\), and let \(\bar{{\beta }}_{Hi}^{GC}\) denote the solution for \(\bar{{\beta }}_{i}^{GC}\) when \(v_{i}>\tilde{v}\). Setting \(\bar{{\theta }}_{i}^{GC} =\bar{{\beta }}_{Li}^{GC}\) and solving for \(y_{i}\) yields a single real root, at \(y_{i}=0\), for any \(\delta _{i}\). Thus, \(\bar{{\theta }}_{i}^{GC}\) lies either everywhere above or everywhere below \(\bar{{\beta }}_{LI}^{GC}\) for \(y_{i}>0\). At \(y_{i}=0\), \(\partial (\bar{{\theta }}_{i}^{GC} -\bar{{\beta }}_{Li}^{GC})/\partial y_{i}=\delta _{i}Y(1+S)/(1+2S)^{2}>0\) for any \(\delta _{i}>0\). Thus, \(\bar{{\theta }}_{i}^{GC}\) must lie everywhere above \(\bar{{\beta }}_{LI}^{GC}\) for \(y_{i}>0\) and \(\delta _{i}>0\).
Setting \(\bar{{\theta }}_{i}^{GC} =\bar{{\beta }}_{Hi}^{GC}\) and solving for \(y_{i}\) also yields a single real root, at \(y_{i}=(1+S)/(\delta _{i}Y)\). This is an iso-\(v\) contour in \((y_{i},\delta _{i})\) space, along which \(v_{i}=v^{*}\equiv (1+S)/Y\). Crucially, along this contour, \(z_{i}^{*}=0\); see (12) in the text. If \(z_{i}^{*}>0 \,\forall i\) (all countries have positive emissions in the NCE), then \(v_{i}<v^{*} \,\forall i\). Thus, if \(z_{i}^{*}>0 \,\forall i\) then \(\bar{{\theta }}_{i}^{GC}\) lies either everywhere above or everywhere below \(\bar{{\beta }}_{Hi}^{GC}\). At \(y_{i}=(1+S)/(\delta _{i}Y)\), \(\partial (\bar{{\theta }}_{i}^{GC} -\bar{{\beta }}_{Hi}^{GC})/\partial y_{i}\) and \(\partial (\bar{{\theta }}_{i}^{GC} -\bar{{\beta }}_{Hi}^{GC})/\partial \delta _{i}\) are both complicated expressions but they are both negative if
This holds for any \(\delta _{i}\ge 0\). Thus, \(\bar{{\theta }}_{i}^{GC}\) must lie everywhere above \(\bar{{\beta }}_{Hi}^{GC}\) for \(v_{i}<v^{*}.\)
Since \(\bar{{\theta }}_{i}^{GC}\) lies everywhere above \(\bar{{\beta }}_{LI}^{GC}\) for \(y_{i}>0\) and \(\delta _{i}>0\), and \(\bar{{\theta }}_{i}^{GC}\) lies everywhere above \(\bar{{\beta }}_{Hi}^{GC}\) for \(v_{i}<v^{*}\), it follows that \(\mathop {\hbox {min}}\nolimits _{i\in GC} \{\bar{{\theta }}_{i}^{GC} \}>\mathop {\hbox {min}}\nolimits _{i\in GC} \{\bar{{\beta }}_{i}^{GC}\}\) if all countries have positive emissions in the NCE, except when \(v_{i}\) is the same for all countries. In that special case, \(\bar{{\theta }}_{i}^{GC} =\bar{{\beta }}_{Li}^{GC} =\bar{{\beta }}_{Hi}^{GC} =0 \,\forall i\).
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Kennedy, P. Cooperative Action on Greenhouse Gas Emissions and the Distribution of Global Output and damage. Environ Resource Econ 63, 147–166 (2016). https://doi.org/10.1007/s10640-014-9845-1
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DOI: https://doi.org/10.1007/s10640-014-9845-1