Abstract
This paper analyzes governments’ strategic regulations in an imperfectly competitive market of international emissions trading (IET). Whether and how governments intervene in IET is explored. If regulations are decided, it is optimal for price-influencing countries to subsidize but for price-taking countries to tax permit trading. Conducting simulations of the Annex-1 emissions trading, we discover that no-intervention of all countries cannot be supported by any equilibrium. In contrast, all or some countries would regulate at equilibrium. In the latter case, price-influencing countries would not regulate but price-taking countries would. This justifies the necessity of considering no-intervention as a policy choice, and shows that a country’s decisions about strategically regulating IET may be affected by other countries’ intervention resolutions.
Similar content being viewed by others
Notes
Strategic trade policy is an important topic in international economics. Relevant literature usually focuses on governments’ intervention policy that could affect firms’ interactions in an international oligopolistic market. The policy’s central idea is to shift profits from foreign to domestic firms, i.e., a strategic profit-shifting policy. Early contributors in this field include Brander and Spencer (1981, 1985), Spencer and Brander (1983), Dixit (1984), Brander (1986), Eaton and Grossman (1986), etc.
In other words, in each stage of our game, acting governments or firms adopt the Cournot–Nash equilibrium by solving the first-order-condition systems simultaneously. We thank the referee for pointing out this issue, so that our game structure becomes more clearly.
According to the numerical results from the GTAP-E model, the rest of the Annex-1 countries account for small portion of permit purchase.
Countries’ statuses of being price setters or price takers depend on their permit trading amounts, instead of their emission levels. This fact can be justified by Eqs. (9) and (10), which show that price-influencing countries will consider marginal price effect due to market power, \( (\frac{\partial \, p}{{\partial \, e_{m} }})(e_{m}^{*} - \bar{w}_{m} ) \), in determining their respective optimal permit trading amounts. Because the EU and Japan are two major permit buyers under the Kyoto Protocol framework, we consider cases of the EU having market power in group B and Japan having market power in group C.
References
Böhringer C, Löschel A (2003) Market power and hot air in international emissions trading: the impacts of US withdrawal from the Kyoto protocol. Appl Econ 35:651–663
Böhringer C, Moslener U, Sturm B (2007) Hot air for sale: a quantitative assessment of Russia’s near-term climate policy options. Environ Resour Econ 38:545–572
Brander J (1986) Rationales for strategic trade and industrial policy. In: Krugman P (ed) Strategic trade policy and the new international economics. MIT Press, Cambridge, pp 23–46
Brander J, Spencer B (1981) Tax and the extraction of foreign monopoly rent under potential entry. Can J Econ 14:371–389
Brander J, Spencer B (1985) Export subsidies and international market share rivalry. J Int Econ 18:83–100
Burniaux JM, Truong TP (2002) GTAP-E: an energy-environmental version of the GTAP Model. GTAP Technical Paper, No. 16
Criqui P, Mima S, Viguier L (1999) Marginal abatement costs of CO2 emission reductions, geographical flexibility and concrete ceilings: an assessment using the POLES model. Energy Policy 27:585–601
Dixit A (1984) International trade policy for oligopolistic industries. Econ J 94(Suppl):1–16
Eaton J, Grossman G (1986) Optimal trade and industrial policy under oligopoly. Q J Econ 101:383–406
Evans M (2003) Emissions trading in transition economies: the link between international and domestic policy. Energy Policy 31:879–886
Hwang HS, Schulman CT (1993) Strategic non-intervention and the choice of trade policy for international oligopoly. J Int Econ 34:73–93
Kainuma M, Matsuoka Y, Mortia T (1999) Analysis of post-Kyoto scenarios: the Asian-Pacific integrated model. Energy J Spec Issue 20:207–220
Klepper G, Peterson S (2005) Trading hot-air: the influence of permit allocation rules, market power and the US withdrawal from the Kyoto protocol. Environ Resour Econ 32:205–228
OECD (1999) Action against climate change: the Kyoto protocol and beyond. Organization for Economic Co-operation and Development, Paris
Persson TA, Azar C (2003) The cost of meeting the Kyoto protocol: dealing with the carbon surplus in Russia and the Ukraine. Manag Environ Qual Int J 14:488–507
Rehdanz K, Tol R (2005) Unilateral regulation of bilateral trade in greenhouse gas emission permits. Ecol Econ 54:397–416
Rose A, Stevens B (1993) The efficiency and equity of marketable permits for CO2 Emissions. Resour Energy Econ 15:117–146
Sager J (2003) An Analysis with the CERT Model of the FSU market power in the carbon emissions trading market. Environ Model Assess 8:219–238
Spencer B, Brander J (1983) International R&D rivalry and industrial strategy. Rev Econ Stud 50:707–722
Westskog H (1996) Market power in a system of tradeable CO2 quotas. Energy J 17:95–103
Acknowledgments
We would like to thank Editor Ken-Ichi Akao and an anonymous referee for their helpful comments and suggestions. Funding from the National Science Council of Taiwan, ROC (Project No.: NSC 99-2410-H-305-078) is gratefully acknowledged by Tsung-Chen Lee.
Author information
Authors and Affiliations
Corresponding author
Appendix
Appendix
Proof of Eq. (11)
Denote H the Hessian matrix of L equations in Eqs. (9) and (10) with
where \( A = \frac{\partial \, p}{{\partial \, e_{m} }} = \frac{ - 1}{{\sum\nolimits_{n = L + 1}^{N} {(\partial \, e_{n}^{*} /\partial \, p)} }} > 0 \) and \( K_{m} = \frac{{C^{\prime\prime}_{m} (e_{m}^{*} ) + 2A}}{A} \) with K m > 2 given \( C^{\prime\prime}_{m} (e_{m}^{*} ) > 0 \), m = 1, …, L.
Letting \( \hat{H} = \, \left[ {\begin{array}{*{20}c} {K_{1} } & 1 & \cdots & 1 \\ 1 & {K_{2} } & \cdots & 1 \\ \vdots & \vdots & \cdots & \vdots \\ 1 & 1 & \cdots & {K_{L} } \\ \end{array} } \right] \), we can show \( \left| {\hat{H}} \right| = [\prod\nolimits_{m = 1}^{L} {(K_{m} - 1} ][1 + \sum\nolimits_{m = 1}^{L} { \, \frac{1}{{K_{m} - 1}}} ] > 1 \) by K m > 2. Applying Cramer’s rule, we acquire
where \( C_{r\,r} = ( - 1)^{r + r} [\prod\nolimits_{m \ne r}^{L} {(K_{m} - 1)} ][1 + \sum\nolimits_{m \ne r}^{L} { \, \frac{1}{{K_{m} - 1}}} ] > 0 \) is the (r, r)th cofactor of \( \hat{H} \).
On the other hand, the market-clearing condition for the IET system at equilibrium is
Differentiating this equation with respect to t r yields
Rearranging the above equation gives \( \frac{{\partial p^{*} }}{{\partial t_{r} }} = - (\sum\nolimits_{n = L + 1}^{N} {\frac{{\partial e_{n}^{*} }}{\partial p}} )^{ - 1} (\sum\nolimits_{m = 1}^{L} { \, \frac{{\partial e_{m}^{*} }}{{\partial t_{r} }}} ) \). Substituting Eq. (8), i.e., \( \frac{\partial p}{{\partial e_{r} }} = \frac{ - 1}{{\sum\nolimits_{n = L + 1}^{N} {(\partial e_{n}^{*} /\partial p)} }} > 0 \), into this equation produces
Proof of Eq. (12)
Differentiating the market-clearing condition with respect to t u and rearranging it yields
Since \( - 1 < A{ (}\frac{{\partial e_{u}^{*} }}{\partial p} )< 0 \), we have \( - 1 < \frac{{\partial p^{*} }}{{\partial t_{u} }} < 0 \). Differentiating Eq. (4) with respect to t u gives
Proof of Eq. (19)
Following the proof of Eq. (11), we have \( \frac{{\partial p^{*} }}{{\partial t_{r} }} = (\frac{\partial p}{{\partial e_{r} }})(\sum\nolimits_{m = 1}^{L} {\frac{{\partial e_{m}^{*} }}{{\partial t_{r} }}} ) \). Thus,
due to \( (\frac{\partial p}{{\partial e_{r} }}) > 0 \) and \( \frac{{\partial e_{m}^{*} }}{{\partial t_{r} }} = \frac{ - 1}{{A\left| {\hat{H}} \right|}}C_{r\,m} > 0 \) for m = 1, …, L, r = 1, …, L′, and m ≠ r, where \( C_{r\,m} = ( - 1)^{2(r + m) - 3} [\prod\nolimits_{t \ne m,r}^{L} {(K_{t} - 1)} ] < 0 \) is the (r, m)th cofactor of \( \hat{H} \). Combining these results with Eq. (11), Eq. (19) is obvious.
About this article
Cite this article
Lee, TC., Chen, HC. & Liu, SM. Optimal strategic regulations in international emissions trading under imperfect competition. Environ Econ Policy Stud 15, 39–57 (2013). https://doi.org/10.1007/s10018-012-0033-7
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10018-012-0033-7