Abstract
Emission taxes are compared with emission quotas in a mixed and, after privatization, a pure duopoly. Previous studies have shown that in a mixed duopoly, direct regulation is superior to indirect regulation, regardless of the degree of partial privatization. These findings were reached on the basis that direct regulation was regarded as an emission standard in which the government sets the uniform abatement effort of each firm, and indirect regulation was regarded as an emission tax. This study considers another indirect regulation: an emission quota that the regulator sets for each firm uniformly or differentially. We show that in a mixed duopoly, a differentiated emission quota does more to improve welfare than an emission tax. In a comparison of the emission tax with a uniform emission quota, the superiority of environmental regulations in terms of social welfare depends on the parameters of the cost functions.
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Notes
Kato and Kiyono (2010) compare the three environmental regulations considered in Kiyono and Okuno-Fujiwara (2003) in several market structures: the competitive market, the monopoly, and the symmetric oligopoly. They show that the equilibrium outcomes are identical under the emission tax and emission quotas in these markets.
Note that as they analyze the welfare comparison under general demand, cost, and damage functions, they do not consider the second-best social optimum.
This type of emission standard is called design standard. For the properties of the design standard, see Besanko (1987).
One might consider why the cost of the production and that of the abatement effort are additively separable. We have three reasons. One is that this article examines the comparison of the equilibrium outcome and social welfare under emission quotas and emission taxes in the same framework of Naito and Ogawa (2009). Another is that it eases the calculation of the analyses. The third is that we can consider the following abatement effort, which is not related to production: planting trees or enclosing \({\hbox{CO}}_2\) in the ground. For other justifications of the additively separable cost function, see Bárcena-Ruiz and Garzón (2006).
The calculations can be obtained from the author upon request.
We set this assumption to eliminate the following cases. If c is small, the gross emission, which is not \(q_i-a_i\) but q i , is quite larger in the public firm than in the private firm. If an emission quota is imposed, there is a possibility that the quota is not binding on the private firm. If an emission tax is imposed, there is also a possibility that the pollution of the private firm e 1 is not positive.
Appendix 2 provides the results.
We omit the welfare comparison between \(W^{\rm S}\) and \(W^{\rm P}\).
With regard to Wang and Wang (2009), the objective of the public firm is slightly different: its objective is to maximize consumer surplus and its profit. However, because the public firm does not incorporate environmental damage and tax revenue into its objective in their setting, we follow Wang and Wang (2009). In Ohori (2006b), although the objective of the public firm is of this type, he considers the consumption externality. While his framework is different from ours, his model is the same as ours. Therefore, we model our work on Ohori (2006b) as well.
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I am grateful to Eiji Hosoda, the journal editor, and to two anonymous referees for their constructive comments and suggestions.
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Appendices
Appendix 1
Proof of Proposition 2. First, we compare welfare under the two emission quotas. By definition, the government can choose \(\bar{e}_0=\bar{e}_1=\bar{e}^{\rm UQ}\) under the differentiated emission quota. From the results, we know that \(\bar{e}_0 \neq \bar{e}_1 \neq \bar{e}^{\rm UQ}\). Therefore, \(W^{\rm DQ}>W^{\rm UQ}\).
Second, we compare welfare under a differentiated emission quota and emission tax. We obtain
Moreover, comparing \(W^{\rm UQ}\) and \(W^{\rm T}\) with \(W^{\rm P}\), we obtain
Finally, we compare welfare under a uniform emission quota and emission tax. We obtain
where \(\phi(c,k)=-1-2c-c^2-3k-4ck+c^2k-2k^2+ck^2\). We examine whether ϕ(c, k) is positive. When k = 1, we get ϕ(c,1) < 0. Suppose k > 1. Then, we obtain
where
We can easily find that \(\bar{c}>1\) and \(\underline {c}<0\). Moreover, we check the sign of \(d \bar{c}/ d k\). Calculating \(d \bar{c}/ d k\), we obtain
We find that the sign of the numerator determines the sign of \(d\bar{k}/dc\). With respect to the numerator, \(\{(k-1)^2+5\}\sqrt{k(k^3+16k+8)}\) is positive, while \(-k^4+2k^3+20k+4\) would be negative if k is slightly above 3.6. Thus, we calculate the value of the former squared minus the latter squared, and then we find
Therefore, \(d\bar{c}/d k<0\).\(\square\)
Appendix 2
2.1 Emission standard
We consider the differentiated emission standard under the framework of the basic model in Naito and Ogawa (2009). The government sets the abatement effort of each firm given by \(\bar{a}_i\). In this case, the firm only chooses its output level. The maximization problem of each firm is
The first-order conditions of the above maximization problem are
The government chooses \(\bar{a}_0\) and \(\bar{a}_1\) to maximize welfare, given the firms’ behavior. We obtain the following equilibrium outcome. The superscript \({\rm S}\) denotes the equilibrium outcome under the emission standard in a mixed duopoly.
where \(\Updelta^{\rm S}=(k+2)c^4+2(4k+7)c^3+4(5k+8)c^2+2(8k+13)c+4(k+1)>0\).
Appendix 3
We calculate equilibrium outcomes under four environmental regulations—uniform emission taxes and quotas and differentiated emission taxes and quotas—where the public firm is a CSPS maximizer. The superscripts \({\rm UT'}\), \({\rm DT'}\), \({\rm DQ'}\), and \({\rm UQ'}\) denote the equilibrium outcomes under the uniform emission tax, the differentiated emission tax, the differentiated emission quota, and the uniform emission quota, respectively.
3.1 Uniform emission tax
The maximization problem of each firm is given by
where \(\bar{W}(q_0,a_0,q_1,a_1)=\int_0^{Q} (\alpha-s)ds-\sum_{i=0}^{1}cq_i^2/2-\sum_{i=0}^{1}ka_i^2/2\). Here, \(\bar{W}^t(q_0,a_0,q_1,a_1)\) denotes \(\bar{W}(q_0,a_0,q_1,a_1)-t(e_0+e_1)\). We note that the term related to the emission tax appears in Eq. 14, which is different from the case where the public firm is a welfare maximizer. The first-order conditions of the above maximization problem are as follows:
The government chooses t to maximize welfare, given the firms’ behavior. We obtain the following equilibrium outcome.
where \(\Updelta^{\rm UT'}=2(k+2)c^4+2(k^2+10k+12)c^3+2(5 k^2+25 k+22)c^2+(9k^2+32k+24)c+2(k+1)(k+2)>0\).
3.2 Differentiated emission tax and differentiated emission quota
First, we consider the equilibrium under the differentiated emission tax. The maximization problem of each firm is given by
Here, \(\hat{W}^t(q_0,a_0,q_1,a_1)\) denotes \(\bar{W}(q_0,a_0,q_1,a_1)-t_0 e_0 - t_1 e_1\), and \(\hat{\pi}_1^t(q_0,q_1,a_1)\) denotes \(\pi_1(q_0,q_1,a_1)-t_1 e_1\). The first-order conditions of the above maximization problem are as follows:
The government chooses t 0 and t 1 to maximize welfare, given the firms’ behavior. We obtain the following equilibrium outcome.
where \(\Updelta^{\rm DT'}=(k+2)c^4+2(k^2+6 k+6)c^3+(k+1)(k+2)(k+11)c^2+(k+1)(4 k^2+17 k+12)c+2(k+1)^2>0\).
Next, we consider the equilibrium under the differentiated emission quota. The maximization problem of each firm is given by
Using the Lagrange undetermined multiplier and calculating the first-order condition of the Lagrangian function of each firm, we find that
where \(\hbox{LW}^{\rm DQ'}=\bar{W}+\lambda_0^{\rm DQ'} \{\bar{e}_0-(q_0-a_0)\}\), \(L\pi_1^{\rm DQ'}=\pi_1+\lambda_1^{\rm DQ'}\{\bar{e}_1-(q_1-a_1)\}\), and \(\lambda_i^{\rm DQ'}\) denotes the shadow price of the emission constraint of firm i. Given the above conditions, the government chooses \(\bar{e}_0\) and \(\bar{e}_1\) to maximize W. Calculating the equilibrium outcome, we find that they are the same as those under the differentiated emission tax in a mixed duopoly when the public firm is a CSPS maximizer; that is, \({\rm DQ'}={\rm DT'}\) holds with regard to the equilibrium outcome.
3.3 Uniform emission quota
The maximization problems of firm 0 and firm 1 are given by
Calculating the equilibrium outcome, we find that they are the same as those under the uniform emission quota in a mixed duopoly when the public firm is a welfare maximizer; that is, \({\rm UQ}={\rm UQ'}\) holds with regard to the equilibrium outcome.
Because the emission quota is binding on all firms, the environmental damage is constant, and therefore, the decision of the public firm is the same regardless of the public firm’s objective.
Appendix 4
Proof of\(d\bar{k}/d c>0\)in Proposition 3
where χ(c, k) is defined as \(c k^2-(c-1)^2 k-2(c^3+3 c^2+c+1)\).
If χ(c, k) < 0, we find that \(W^{\rm UT'}-W^{\rm P}>0\). We examine whether χ(c, k) is positive.
where
We can easily find that \(\bar{k}>1\) and \(\underline {k}<0\). When k = 1, we get χ(c,1) < 0. Therefore, we obtain Proposition 3.
We find that the sign of the numerator determines the sign of \(d\bar{k}/d c\). With respect to the numerator, both \((c-1)(c+1) \sqrt{9c^2+2c+1}\) and \(9c^3+c^2-c-1\) are positive. Therefore, \(d\bar{k}/d c>0\).
4.1 Comparison of QUT′ and QP
where \(\psi(c,k)=2(k+2)c^4+2(k^2+11 k+14)c^3+(13 k^2+66 k+64)c^2-(k^3-14 k^2-62 k-52)c+(k+2)(5 k+6)\). From the above, we find that QP could be larger than QUT' if k is extremely high and c is nearly equal to 1.
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Kato, K. Emission quota versus emission tax in a mixed duopoly. Environ Econ Policy Stud 13, 43–63 (2011). https://doi.org/10.1007/s10018-010-0003-x
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DOI: https://doi.org/10.1007/s10018-010-0003-x