Abstract
Without a comprehensive global climate agreement, carbon leakage remains a contentious issue. Consumption-based pricing of emissions—which could in practice be implemented with a full border tax adjustment (BTA)—has been forwarded as an option to increase the effectiveness of unilateral climate policy. This paper questions the economic rationale behind this approach, using a theoretical \(2 \times 2\) trade model in which leakage occurs through terms-of-trade effects. We show analytically, first, that consumption-based pricing of emissions does not necessarily result in less leakage than production-based policies. Second, the sign of the optimal unilateral carbon tariff depends on the carbon-intensity differential between the foreign country’s exporting and non-exporting sectors, and not on the differential between home’s and foreign’s exporting sectors, as implied by the full BTA approach. Third, based on empirical data for the year 2004, our model implies that full BTA applied by the European Union on e.g. imports from and exports to China would—by shifting China’s production from the export sector with a relatively low carbon-intensity towards the more carbon-intensive non-export sector—actually increase leakage.
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Notes
Throughout this paper, BTA always refers to full BTA, where a price is levied on imports according to their actual carbon content (embodied carbon), and a rebate is granted to exports to exempt them from the domestic carbon price. This corresponds to the definition given by (Ismer and Neuhoff (2007), p. 140): “exports from one region receive an export compensation based on the CO\(_2\) price level in the exporting region and pay an import tariff corresponding to CO\(_2\) price level in the importing region ”.
Of course, the specific leakage rates depend on how exactly the BTA is implemented and to which sectors it is applied, on model assumptions about the structure of international trade, and, perhaps most of all, on the considered policy scenario. E.g., Burniaux et al. (2010) show that the effectiveness of BTA rapidly declines when climate coalitions become large, as the relative importance of the energy-market (or supply-side) leakage channel—which is not targeted by BTA—becomes higher in that case.
Note that we assume throughout the paper that Home’s unilateral policies do not lead to an inversion of this specialization pattern, which seems reasonable as long as the imposed border-tax remains small in comparison to the price of goods.
We denote derivatives with respect to a certain variable by subscripts throughout the analysis.
This is equivalent to \(p^{*}E^{Yf} -M^{Xf} =0\) from Foreign’s point of view. Our two-region setting naturally implies market clearance on all markets such that \(E^{Yf} =M^{Yh} , E^{Xf} =M^{Xh} .\)
Imported and domestically produced goods are perfect substitutes from the consumer’s point of view.
Since we have adopted a non-cooperative setting and impacts of climate change in Foreign do not influence Home’s utility, we only specify a climate damage function for Home.
Leakage, when transmitted through a change in specialization patterns, occurs when a country with climate policy shifts away from the production of emission-intensive goods and, as a consequence, the world price of those goods increases and hence other countries without climate policy shift towards the production of those goods. Accordingly, the shifts of countries’ points of production highlighted in this paper should not be seen as a mere long-run phenomenon but as an essential ingredient of carbon leakage.
This is simply the equivalent of Markusen’s (1975) assumption of E\(_{1 }<\) 0.
Differently from e.g. Keen and Kotsogiannis (2011), we do not analyze policies aimed at global welfare.
Note that there is no need for a country index in the prices \(p\) or \(q\): they always refer to Home, since by assumption Foreign does not employ any policy, and hence all prices in Foreign are given by \(p\)*.
The latter condition can perhaps be better understood when written as \({\gamma ^{Yh} }/{p_Y}>{\gamma ^{Xh} }/{p_X}\).
We assume the cap to be binding but still being above the (technical) minimum emission level of the
economy, which is given by:
\(\mathop {\min }\limits _{Q^{Yh}} \left\{ {\gamma ^{Xh}T^{h}(Q^{Yh})+\gamma ^{Yh}Q^{Yh}} \right\} \).
That is, no single firm or consumer has influence on the world market price.
Negative leakage denotes an emission reduction in Foreign induced by an emission reduction in Home.
Their supplementary online material provides data for 95 countries. We aggregated the data of the 27 EU member countries contained in the dataset into one EU region. We also follow them in their use of GDP in market exchange rates to derive Table 1. This is compatible with our model, which does not feature non-traded goods. Note that the use of purchasing power parity GDP results in a higher relative carbon intensity of exports for China (Jakob and Marschinski 2013).
For example, the production of cement or steel is energy-intensive and thus carbon-intensive in all countries, whereas the provision of financial services has in general a rather low energy- and carbon-intensity.
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Acknowledgments
We are very grateful for receiving comments from Lydia Blaschtschak, Cameron Hepburn, and Philippe Quirion, two anonymous reviewers and the editor Hassan Benchekroun on earlier versions of this paper, which helped to considerably improve the manuscript. Funding from the German Federal Ministry of Education and Research (BMBF) within the Call ‘Ökonomie des Klimawandels’ (funding code 01LA1121A—‘CREW’ and funding code 01LA1105B—‘CliPoN’) is gratefully acknowledged.
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Appendix
Appendix
Proof of Lemma 2
The market clearing condition for the \(Y\) world market reads: \(M^{Yh} -E^{Yf} =0\), where both \(M^{Yh}\) and \(E^{Yf}\) depend upon the world market price \(p^{*}\). Moreover, the budget balance condition Eq. (2) implies: \(p^{*}M^{Yh} =E^{Xh} \). \(E^{Xh} \) depends upon \(p^{*}\) as well as \(\mu \), which translates into \(M^{Yh} \). This implies for the derivative of the market clearing condition with respect to a change in Home’s carbon tax \(\mu \) (equivalent to a change of the cap \(\bar{{Z}}^{h})\): \(M^{Yh} (p^{*},\mu )-E^{Yf} (p^{*})=0\) and thus
Under standard conditions, the denominator is unambiguously negative (note that in the present setting both Home and Foreign behave as price-takers). Hence, we only need to compute the sign of the numerator. Using the fact that consumers’ preferences are homothetic, Home’s imports, \(M^{Yh} = C^{Yh} -Q^{Yh} \), can be rewritten by inserting the standard expressions for the consumption of \(Y\) derived from utility maximizing given an income budget
where \(\eta (q)\) denotes the share of Home’s real income, \(I^{h}\), spent on good \(X\), and \(\overline{{\eta }}(q)=1-\eta (q)\) denotes the share of Home’s real income spent on good \(Y.\) Consumption of \(Y \) decreases in the relative consumer price of \(Y\), denoted by \(q\). Since for the moment there are no consumer taxes in place, it is \(q\) = \(p^{*}\). Since both goods, \(X \) and \(Y\), are traded internationally, total income is expressed by applying the world market price \(p^{*}\), i.e. as \(Q^{Xh}+ p^{*}Q^{Yh}\), implying:
Since in Eq. (32) only \(Q^{Yh}\) depends explicitly on the production tax, \(\mu \), we find
Differentiating the first and the second part of the producers’ efficiency condition in Eq. (19) with respect to \(\mu \) and solving for \(\frac{\partial Q^{Yh}}{\partial \mu }\) yields
Confronting the last equation with Eq. (14) shows that it will be negative when \(\gamma ^{Yh} >q \gamma ^{Xh} \). Therefore, Eq. (33) will be positive if and only if \(\gamma ^{Yh} >p^{*} \gamma ^{Xh} \), where \(p^{*}= q\). In this case, Eq. (30) will be positive as well.\(\square \)
Proof of Lemma 3
To determine the effect of \(\sigma \) on \(p^{*}\), we start by differentiating the market clearing condition, obtaining (cf. Eq. 30):
Again, the denominator is negative under standard conditions. To determine the sign of the numerator, we start by further specifying Home’s consumption. With homothetic preferences, we have:
where \(\bar{{\eta }}\equiv 1-\eta \) denotes the share of income spent on good \(Y\), as a function of the domestic consumer price \(q\). Since in equilibrium consumption must exhaust the total real income \(I^{h}\) of Home, i.e. \(C^{Xh}+ p^{*}C^{Yh}= I^{h}= Q^{Xh}+ p^{*}Q^{Yh}\), we obtain:
Using \(M^{Yh} = C^{Yh} -Q^{Yh} \), one can simplify \(M^{Yh}\) to
where the RHS can be expressed completely in terms of \(p^{*}\) and \(\sigma \), since \(q\) and \(p\) are dependent via Eqs. (28) and (29). Calculating the derivative \(\frac{\partial }{\partial \sigma }\) and collecting terms leads to:
The derivative of \(\eta \) with respect to \(q\) is connected to the elasticity of substitution \(\Sigma \) of \(U^{h}\) by \(\frac{\partial \eta }{\partial q}=\frac{\left( {\Sigma -1} \right) \eta \bar{{\eta }}}{q}\), leading to the final expression:
While the denominator is always positive, both terms of the numerator can be either positive or negative, depending on the sign of \(\frac{\partial p}{\partial \sigma }\) and \(\frac{\partial q}{\partial \sigma }\). Since \(\Sigma > 0\), and \(\frac{\partial Q^{Yh} }{\partial p}\) is positive as given by Eq. (14), we have the following three cases: (i) Eq. (40) and hence Eq. (35) for \(\frac{dp^{*}}{d\sigma }\) are positive, i.e. \(p^{*}\) increases when \(\sigma \) increases, if \(\frac{\partial p}{\partial \sigma }<\) 0 and \(\frac{\partial q}{\partial \sigma }<\) 0 (or if one term is negative and the other term is zero); likewise, Eq. (40) is negative and hence \(p^{*}\) decreases if \(\frac{\partial p}{\partial \sigma }\!>\! 0\) and \(\frac{\partial q}{\partial \sigma } > 0\) (or if one term is positive and the other term is zero); (ii) the impact of \(\sigma \) on \(p^{*}\) is ambiguous if \(\frac{\partial p}{\partial \sigma }\) and \(\frac{\partial q}{\partial \sigma }\) have different signs. To determine the signs of \(\frac{\partial p}{\partial \sigma }\) and \(\frac{\partial q}{\partial \sigma }\), we obtain from Eq. (29):
while combining Eqs. (28) and (29) yields for \(p\) and \(\frac{\partial p}{\partial \sigma }\):
Therefore, case (i) will hold if both of Home’s sectors are either more or less emission-intensive than Foreign’s export sector \(Y\), respectively, and case (ii) otherwise. In the symmetric case (iii), i.e. when \(\gamma ^{Xh} =\gamma ^{Xf} \text{ and } \gamma ^{Yh} =\gamma ^{Yf} \), \(\frac{\partial p}{\partial \sigma }\) will become zero and Eq. (40) will simplify so that the sign of \(\frac{dp^{*}}{d\sigma }\) only depends on Eq. (41) for \(\frac{\partial q}{\partial \sigma }\). Accordingly, \(\frac{dp^{*}}{d\sigma }\) will be positive if the \(Y\)-sector is less emission-intensive than the \(X\)-sector and negative if it is more emission-intensive.\(\square \)
Proof of Lemma 4
The proof proceeds analogously to the one of Lemma 3. Totally differentiating the market clearing condition \(M^{Yh} (p^{*},\phi )-E^{Yf} (p^{*})=0\) yields:
As in Eq. (38), Home’s imports can then again be expressed as:
with \(q\), \(p\), and \(p^{*}\) depending on \(\phi \). Using Eq. (21), to express \(p\) in terms of \(q\) (and \(\mu \), which is constant), and Eq. (29) to express \(q\) in terms in terms of \(p^{*}\) and \(\phi \) the RHS of Eq. (42) can be written as a function of \(p^{*}\) and \(\phi \).Footnote 19 Therefore, in analogy to Eq. (40), the sign of Eq. (43) is determined by the signs of \(\frac{\partial p}{\partial \phi }\) and \(\frac{\partial q}{\partial \phi }\):
As in Eq. (41), \(\frac{\partial q}{\partial \phi }\) follows directly from Eq. (29):
In order to determine \(\frac{\partial p}{\partial \phi }\), we use Eqs. (21) and (29) to obtain:
As the denominator of Eq. (47)—which represents the normalized price of good \(X\) minus the price of its ‘embodied’ emissions—is positive, \(\frac{\partial p}{\partial \phi }\) and \(\frac{\partial q}{\partial \phi }\) bear identical signs. Hence, if Home’s imports are more (less) carbon-intensive than its exports—i.e. it is a net importer (exporter) of emissions—Eq. (43) is negative (positive).\(\square \)
Proof of Lemma 5
The proof is basically identical to the one for Lemma 4. By substituting \(\gamma ^{Yh} \) for \(\gamma ^{Yf} \) in Eqs. (46) and (47), we obtain:
and
Therefore, under the best available technology approach, Eq. (43) will be negative (positive) if Home’s export sector is more carbon-intensive than its non-export sector.\(\square \)
Proof of Proposition 6
As demonstrated in Sect. 4, Home’s welfare is maximized by setting a domestic production tax \(\tau ^{opt}\) and a tariff \(\theta ^{opt,}\) and, according to Eq. (21), this optimal production tax is equivalent to a domestic carbon price \(\mu =-q^{Z}\). Therefore, given that \(\tau ^{opt}\) is in place, the optimal tariff \(\theta ^{opt }\) has to fulfill the following conditions:
Assuming the welfare maximum to be unique, it directly follows that for any two tariffs \(\theta ^{A},\, \theta ^{B}\) that deviate from the optimal tariff in the same direction—i.e. for which \(sgn (\theta ^{A},- \theta ^{opt}) = sgn (\theta ^{B},- \theta ^{opt})\)—the following has to hold:
Obviously, for the case in which the tariff \(\theta ^{cons}\) implied by consumption-based pricing of emissions (Eq. 29) has the opposite sign of the optimal tariff, and given that under production-based emission pricing the tariff \(\theta ^{prod}\) is zero (Eq. 20), Eq. (51) directly yields:
which proves the first part of the proposition.
The second part of the proposition results from the observation that without specific assumptions regarding the functional form of \(W ^{h}\), no general conclusions can be drawn for any two tariffs \(\theta ^{A}\,\text{ and }\,\theta ^{B}\) that deviate from the optimal tariff in different directions—i.e. for which \(sgn (\theta ^{A}- \theta ^{opt}) = -sgn (\theta ^{B}- \theta ^{opt})\).\(\square \)
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Jakob, M., Marschinski, R. & Hübler, M. Between a Rock and a Hard Place: A Trade-Theory Analysis of Leakage Under Production- and Consumption-Based Policies. Environ Resource Econ 56, 47–72 (2013). https://doi.org/10.1007/s10640-013-9638-y
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DOI: https://doi.org/10.1007/s10640-013-9638-y