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Carbon border adjustment: a unilateral solution to the multilateral problem?

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Abstract

This study investigates whether the rationales for introducing carbon border adjustments (CBA) are consistent with theoretical predictions. Specifically, it addresses the following questions. When CBA is theoretically modelled for a level playing field in international trade, does it encourage climate efforts in developing countries, and does it improve global climate effectiveness? What are the implications for international environmental cooperation? The study highlights how the strategic interdependence between countries changes with the introduction of CBA by using a model that incorporates CBA into the two-stage reciprocal-markets model originated by Brander and Spencer (1984). Recognising that CBA is unidirectional, whereby only a country with a more stringent climate policy can impose CBA on imports, the results demonstrate that introducing CBA creates an incentive discrepancy between developed and developing countries; the former (the latter) may adopt a more aggressive (defensive) domestic climate policy.

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Notes

  1. The firstly embodied but unrealised example of a policy was the American Clean Energy and Security Act of 2009 (H.R. 2454) in the USA. The European Union is recently materialising one under the EU Green Deal.

  2. This result is consistent with Balistreri et al. (2019), which shows Pigouvian-based CBAs are likely to be too aggressive. Focusing on how this property of CBA relates to the countries’ best responses of climate policy in an oligopolistic model, this study enables us to directly observe the effect of CBA introduction on IEA stability later.

  3. In theory, export subsidy is another type of CBA. However, in practice export subsidy is prohibited according to Article III in the WTO Agreement on Subsidies and Countervailing Measures. Reflecting the fact, all Carbon Border Adjustment schemes proposed to date are tax-type.

  4. In case the of the European Union (EU), carbon border adjustment mechanism is discussed as a part of the EU Green Deal. See EC (2019) for details.

  5. According to the WTO National Treatment principle, CBA should not discriminate between domestic producers and foreign producers of like products. Hence, I concentrate on a case where the domestic and the foreign goods are homogeneous.

  6. Although I do not explicitly consider inter-industry relationship in trade context, it is known that this oligopolistic model can be extended to have a general equilibrium treating other industries almost independently when a quasi-linear utility function is used as Eq. (2) (Neary 2003). More detailed survey on the general oligopolistic equilibrium, see Colacicco (2015).

  7. To ensure the existence of a pure equilibrium, I introduce the product differentiation parameter. For details, please see the Appendix.

  8. Remember that λ, which is close to 0 (1), indicates a larger (smaller) environmental sensitivity gap.

  9. A corner solution is found when the lagger’s climate effort is set to zero, \(({\bar{\mathbf{\tau }}}_{i},{\underset{\_}{\mathbf{\tau }}}_{j})=\left(\frac{9{\alpha }_{i}{d}_{i}-1}{10{\alpha }_{i}},0\right),\) which describes a situation where the leader completely discourages the follower’s climate effort. The existence condition for the corner solution is \({\bar{\tau }}_{j}(0)=\frac{9{\alpha }_{j}{d}_{j}-1}{10{\alpha }_{j}}>{\widehat{\tau }}_{j}=\frac{2{\alpha }_{i}-{\alpha }_{j}}{{\alpha }_{j}}{d}_{i}\) such that \({\underset{\_}{\tau }}_{i}({\widehat{\tau }}_{j})=0\iff (9+10{\lambda }_{ij}-20{\beta }_{ij}{\lambda }_{ij}){\alpha }_{i}{d}_{i}>1\). It holds when \({\lambda }_{ij}<\frac{9}{10(2{\beta }_{ij}-1)}$$. Since$$\frac{9}{4(2{\beta }_{ij}-1)}>\frac{9}{10(2{\beta }_{ij}-1)}\) for any \({\beta }_{ij}$$such that$$9+10{\lambda }_{ij}-20{\beta }_{ij}{\lambda }_{ij}>0.\) The existence condition for the corner solution is higher than that for the interior solution. When the North is the lead country, the equilibrium becomes a corner solution if λ is small enough. When the South is a leader, the corner solution is found if λ is large enough.

  10. In case of a corner solution, \({\bar{\mathbf{\tau }}}_{i}>{\stackrel{\sim }{\mathbf{\tau }}}_{i}\iff \frac{9{\alpha }_{i}{d}_{i}-1}{10}>\frac{6(2{\alpha }_{i}-{\alpha }_{j}){d}_{i}-4}{7}\iff (60{\beta }_{ij}-57){\alpha }_{i}{d}_{i}+33>0,\) which holds if \({\beta }_{ij}>\frac{57}{60}.\) For the lead country, especially when it is the North, it is always \({\bar{\mathbf{\tau }}}_{N}>{\stackrel{\sim }{\mathbf{\tau }}}_{N}$$, since$$\beta >1>\frac{57}{60}\) in this case. Notice, in a case of corner solution, there is no difference in climate efforts for the lagging country by definition, \({\underset{\_}{\mathbf{\tau }}}_{S}={\stackrel{\sim }{\mathbf{\tau }}}_{S}=0.\).

  11. Since \(({\bar{\mathbf{\tau }}}_{i},{\underset{\_}{\mathbf{\tau }}}_{j})=\left(\frac{\left(9+2(2\beta -1)\lambda \right){\alpha }_{i}{d}_{i}-1}{12{\alpha }_{i}},\frac{(10(2\beta -1)\lambda -9){\alpha }_{i}{d}_{i}+1}{12\beta {\alpha }_{i}}\right),\) then \(\frac{\partial {\bar{\mathbf{\tau }}}_{N}}{\partial {\alpha }_{N}{d}_{N}},\frac{\partial {\underset{\_}{\mathbf{\tau }}}_{S}}{\partial {\alpha }_{N}{d}_{N}}>0.\) It holds that \(\frac{\partial {\bar{\mathbf{\tau }}}_{N}}{\partial {\alpha }_{N}{d}_{N}}>\frac{\partial {\underset{\_}{\mathbf{\tau }}}_{S}}{\partial {\alpha }_{N}{d}_{N}}\) if and only if \(9+2(2\beta -1)\lambda >\frac{1}{\beta }\left[10(2\beta -1)\lambda -9\right]\iff \lambda <\frac{9(1+\beta )}{2(2\beta -1)(5-\beta )}.\) Since \(\frac{9(1+\beta )}{2(2\beta -1)(5-\beta )}>1\) for any β ≥ 1, the condition holds for any \(\lambda \in (\mathrm{0,1}].\)

  12. For an intensive discussion on the relationship between a unilateral trade measure and multilateral international agreements, see He (2019).

References

  • Balistreri, E. J., Kaffine, D. T., & Yonezawa, H. (2019). Optimal environmental border adjustments under the General Agreement on Tariffs and Trade. Environmental and Resource Economics, 74(3), 1037–1075.

    Article  Google Scholar 

  • Barrett, S. (1994). Strategic environmental policy and international trade. Journal of Public Economics, 54, 325–338.

    Article  Google Scholar 

  • Böhringer, C., Carbone, J. C., & Rutherford, T. F. (2016). The strategic value of carbon tariffs. American Economic Journal: Economic Policy, 8(1), 28–51.

    Google Scholar 

  • Brander, J. A., & Spencer, B. J. (1984). Trade warfare: Tariffs and cartels. Journal of International Economics, 16, 227–234.

    Article  Google Scholar 

  • Carraro, C., & Siniscalco, D. (1993). Strategies for the international protection of the environment. Journal of Public Economics, pp 309–328.

  • Colacicco, R. (2015). Ten years of general oligopolistic equilibrium: A survey. Journal of Economic Surveys, 29(5), 965–992.

    Article  Google Scholar 

  • Copeland, B. R. (1996). Pollution content tariffs environmental rent shifting and the control of cross-border pollution. Journal of International Economics, 40(3–4), 459–476. https://doi.org/10.1016/0022-1996(95)01415-2.

    Article  Google Scholar 

  • Cosbey, A. (2008). Border Carbon Adjustment, Sustainable China Trade: A Conceptual Framework. Winnipeg: International Institute for Sustainable Development.

  • European Commission. (2019). The European Green Deal, COM/2019/640 final. Brussels., 11(12), 2019.

  • Gros, D. (2009). Global welfare implications of carbon border taxes. No. 2790. CESifo Group Munich

  • He, J. (2019). Do unilateral trade measures really catalyze multilateral environmental agreements? International Environmental Agreements, 19(577), 593.

    Google Scholar 

  • Hoel, M. (1992). International environment conventions: The case of uniform reductions of emissions. Environmental and Resource Economics, 2(2), 141–159.

    Google Scholar 

  • Jakob, M., Marschinski, R., & Hübler, M. (2013). Between a rock and a hard place: A trade-theory analysis of leakage under production-and consumption-based policies. Environmental and Resource Economics, 56(1), 47–72.

    Article  Google Scholar 

  • Keen, M., & Kotsogiannis, C. (2014). Coordinating climate and trade policies: Pareto efficiency and the role of border tax adjustments. Journal of International Economics, 94(1), 119–128.

    Article  Google Scholar 

  • Markusen, J. R. (1975). International externalities and optimal tax structures. Journal of International Economics, 5(1), 15–29. https://doi.org/10.1016/0022-1996(75)90025-2.

    Article  Google Scholar 

  • Neary, J. P. (2003). Globalization and market structure. Journal of the European Economic Association, 1(2–3), 245–271.

    Article  Google Scholar 

  • Sanctuary, M. (2017). Border carbon adjustments and unilateral incentives to regulate the climate. Review of International Economics, 26(4), 1–26.

    Google Scholar 

  • Ulph, A. (1992). The choice of environmental policy instruments and strategic international trade. In Pethig, R. (Editor) Conflicts and cooperation in managing environmental resources. Springer.

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Appendix

Appendix

1.1 Proof of Proposition 2

Proposition 2

For each \(i\in \{N,S\}\) , there exists the \(i\) -lead equilibrium \(({\overline{{\varvec{\uptau}}}}_{i},{\underset{\_}{{\varvec{\uptau}}}}_{j})\) if \({\alpha }_{i}{d}_{i}>\frac{1}{9-8{\beta }_{ij}{\lambda }_{ij}+4{\lambda }_{ij}}\) .

Proof.

Since \({\overline{\tau }}_{i}(\cdot )\) is strictly increasing in \({\tau }_{j}\) and \({\overline{\tau }}_{i}({\tau }_{j})>{\tau }_{j}\) for any \({\tau }_{j}\in \left[0,\frac{9{\alpha }_{i}{d}_{i}-1}{8{\alpha }_{j}}\right]\), \({\underset{\_}{\tau }}_{j}(\cdot )\) is decreasing in \({\tau }_{i}\) and \({\underset{\_}{\tau }}_{j}({\tau }_{i})<{\tau }_{i}\) for any \({\tau }_{i}>\frac{2{\alpha }_{j}-{\alpha }_{i}}{2{\alpha }_{i}}{d}_{j}\), \({\overline{\tau }}_{i}(\cdot )\) intersects \({\underset{\_}{\tau }}_{j}(\cdot )\) only once if \(\frac{9{\alpha }_{i}{d}_{i}-1}{8{\alpha }_{i}}>\frac{2{\alpha }_{j}-{\alpha }_{i}}{2{\alpha }_{i}}{d}_{j}\), which is \((9-8{\beta }_{ij}{\lambda }_{ij}+4{\lambda }_{ij}){\alpha }_{i}{d}_{i}>1\).

1.2 Proof of Proposition 4

Proposition 4

For a given \((\beta ,\lambda )\) , there exists \(\widehat{\alpha d}\) such that (i) \(\Omega ({\overline{{\varvec{\uptau}}}}_{N},{\underset{\_}{{\varvec{\uptau}}}}_{S})<\stackrel{\sim }{\Omega }({\stackrel{\sim }{{\varvec{\uptau}}}}_{N},{\stackrel{\sim }{{\varvec{\uptau}}}}_{S})\) if and only if \({\alpha }_{N}{d}_{N}<\widehat{\alpha d}\) .

Proof.

When the equilibrium is an interior solution, \(\Omega ({\overline{{\varvec{\uptau}}}}_{N},{\underset{\_}{{\varvec{\uptau}}}}_{S})<\stackrel{\sim }{\Omega }({\stackrel{\sim }{{\varvec{\uptau}}}}_{N},{\stackrel{\sim }{{\varvec{\uptau}}}}_{S})\iff {\alpha }_{N}{d}_{N}<\widehat{\alpha d}=\frac{8+14\beta }{63-108\beta +45{\beta }^{2}+\left(23-71\beta +50{\beta }^{2}\right)\lambda }\). Since \(\widehat{\alpha d}\) \(>\frac{1}{9-8\beta \lambda +4\lambda },\frac{1}{9\beta \lambda +4\beta -8}\) for any \(\beta\) and \(\lambda\), there exists such \(\widehat{\alpha d}\) whenever the North-lead equilibrium exists. When the equilibrium is a corner solution, the threshold is \({\widehat{\alpha d}}_{0}=\frac{14+20\beta }{96-165\beta +45{\beta }^{2}+15\left(3-11\beta +10{\beta }^{2}\right)\lambda }\). One may check that \(\widehat{\alpha d}>{\widehat{\alpha d}}_{0}\) and \({\widehat{\alpha d}}_{0}<\frac{1}{9+10\lambda -20\beta \lambda }\). Thus, once the North-lead equilibrium exists, \(\Omega ({\overline{{\varvec{\uptau}}}}_{N},{\underset{\_}{{\varvec{\uptau}}}}_{S})\le \stackrel{\sim }{\Omega }({\stackrel{\sim }{{\varvec{\uptau}}}}_{N},{\stackrel{\sim }{{\varvec{\uptau}}}}_{S})\) in the case of a corner solution.

1.3 Bertrand case

Define the consumer’s utility:

$$U_{i} = q_{i}^{i} + q_{j}^{i} - \frac{1}{2}\left[ {\left( {q_{i}^{i} } \right)^{2} + \left( {q_{j}^{i} } \right)^{2} + 2bq_{i}^{i} q_{j}^{i} } \right] + y,$$

where the parameter \(b\in \mathrm{0,1}]\) is a measure of the degree of product differentiation and \(b=1\) implies that the goods are homogenous. With fixed income, utility maximisation yields the following inverse demand functions:

$$p_{i}^{i} = 1 - q_{i}^{i} - bq_{j}^{i} {\text{ and }}p_{j}^{i} = 1 - q_{j}^{i} - bq_{i}^{i} .$$

From these, I derive the demand functions \({q}_{i}^{i}=\frac{\left(1-b\right)-{p}_{i}^{i}+b{p}_{j}^{i}}{1-{b}^{2}}\) and \({q}_{i}^{j}=\frac{\left(1-b\right)-{p}_{i}^{j}+b{p}_{j}^{j}}{1-{b}^{2}}\). For a given \((B,\tau )\), a firm chooses its price to maximise profit, yielding the following best responses:

$$p_{i}^{i} (p_{j}^{i} ) = \frac{{(1 - b) + \alpha_{i} \tau_{i} + bp_{j}^{i} }}{2},$$
$${\mathbf{p}}_{i}^{j} \left( {p_{j}^{j} } \right) = \frac{{\left( {1 - b} \right) + \left( {\alpha_{i} \tau_{i} + B_{j} } \right) + bp_{j}^{j} }}{2}.$$

At Nash equilibrium,

$${\mathbf{p}}_{i}^{i} = \frac{{\left( {2 + b} \right)\left( {1 - b} \right) + 2\alpha_{i} \tau_{i} + b\left( {\alpha_{j} \tau_{j} + B_{i} } \right)}}{{4 - b^{2} }}$$
$${\mathbf{p}}_{i}^{j} = \frac{{\left( {2 + b} \right)\left( {1 - b} \right) + b\alpha_{j} \tau_{j} + 2\left( {\alpha_{i} \tau_{i} + B_{j} } \right)}}{{4 - b^{2} }}.$$

Plugging in these equilibrium prices provides the equilibrium production level:

$${\mathbf{q}}_{i}^{i} = \frac{{\left( {2 - b - b^{2} } \right) - \left( {2 - b^{2} } \right)\alpha_{i} \tau_{i} + b\alpha_{j} \tau_{j} - b\left( {1 - b} \right)B_{i} }}{{\left( {4 - b^{2} } \right)\left( {1 - b^{2} } \right)}}$$
$${\mathbf{q}}_{i}^{j} = \frac{{\left( {2 - b - b^{2} } \right) - \left( {2 - b^{2} } \right)\alpha_{i} \tau_{i} + b\alpha_{j} \tau_{j} - b\left( {1 - b} \right)B_{j} }}{{\left( {4 - b^{2} } \right)\left( {1 - b^{2} } \right)}}.$$

Given a firm’s behaviour, each government chooses a domestic carbon tax to maximise social welfare. Following a similar progression for the Cournot case, the best response of carbon tax is

$${\overline{\mathbf{\tau }}}_{i} \left( {\tau_{j} } \right) = \frac{{\rho_{j} \tau_{j} + \rho_{d} d_{i} + \rho_{c} }}{\rho },$$

where \(\rho ={\alpha }_{i}\left(12-4b-8{b}^{2}+{b}^{3}+{b}^{4}\right)>0\), \({\rho }_{j}={\alpha }_{j}\left(8-4b-6{b}^{2}+2{b}^{3}+{b}^{4}\right)>0\), \({\rho }_{d}={\alpha }_{j}\left(8-8b-6{b}^{2}+2{b}^{3}+{b}^{4}\right)+{\alpha }_{i}\left(16-4b-12{b}^{2}+{b}^{3}+2{b}^{4}\right)\) and \({\rho }_{c}=2{b}^{2}-{b}^{3}-{b}^{4}\).

Since \(\rho >0\) and \({\rho }_{j}>0\) for any \(b\in [\mathrm{0,1})\),

$$\frac{{\partial {\overline{\mathbf{\tau }}}_{i} \left( {\tau_{j} } \right)}}{{\partial \tau_{j} }} = \frac{{\rho_{j} }}{\rho } > 0,$$

which is a strategic complement to the leading case. Next, the best response in the lagging case is given by

$${\mathbf{\underline {\tau } }}_{i} \left( {\tau_{j} } \right) = \frac{{ - \left( {2 - b - b^{2} } \right)\tau_{j} + \theta d_{i} + 1 - b}}{{\alpha_{i} }},$$

where \(\theta =(2-{b}^{2}){\alpha }_{i}-b{\alpha }_{j}\).

$$\frac{{\partial {\mathbf{\underline {\tau } }}_{i} \left( {\tau_{j} } \right)}}{{\partial \tau_{j} }} = - \left( {2 - b - b^{2} } \right) < 0,$$

since \(b\in [\mathrm{0,1})\), which is a strategic substitute for a lagging country. These results are similar to the Cournot case, as the carbon tax of a leading country strategically complements that of its opponent, while that of the lagging country strategically substitutes it. This result shows that the strategic relationships between home and foreign carbon taxes depend on the relative stringency of carbon tax rates and the design of the CBA; hence, the issue of whether competition is about price or quantity is largely irrelevant.

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Suh, J. Carbon border adjustment: a unilateral solution to the multilateral problem?. Int Environ Agreements 22, 715–733 (2022). https://doi.org/10.1007/s10784-022-09578-3

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