Abstract
This paper investigates how a tax revenue allocation rule determines the level of environmental taxation influenced by interest groups. A model of special interest politics is modified to incorporate environmental taxation. Two groups of agents exist. The first group earns wage income, has negative utility derived from pollution generated by energy consumption, and earns a profit share of the energy industry. The second group earns wages and has negative utility from pollution, but does not own shares. The government imposes an ad-valorem pollution tax and spends a proportion of its revenue as compensation for the tax burden on the first group and the remainder on public abatement. Two regimes are considered. First, a resource-rent group lobbies the government to protect its income source. Second, an environmentally conscious group lobbies the government to spend the revenue for pollution reduction. The critical proportion of transfer to tax revenue is derived to achieve the socially optimal rate of environmental taxation, even when the tax rate is subject to the influence of interest groups.
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Notes
Millock and Nauges (2006) mentioned that in the case of the Swedish emission tax on \(NO_{x}\), the revenue is rebated to industries based on their energy consumption. Additionally, carbon tax rates are often reduced for energy-intensive industries in EU countries and in Japan. These options can be considered as tax burden compensation that could benefit energy-rent holders.
In this model, lobby formation is exogenous to focus on the impact of tax revenue allocation on environmental policy. Those who are interested in the relationship between environmental policy and endogenous lobby formation should consult studies, such as Damania and Fredriksson (2003) and Kawahara (2014).
Following Gulati (2008), we assume that, if one group of agents is unorganized, the other group of agents are perfectly organized. However, we could assume that the group of agents is partially organized. Let the share of agents in each group organized as a lobby be \(\theta ^{j}\in [0,1]\) and assume that \(\theta ^{-j}=0\text { if }\theta ^{j}>0\). The welfare function without contribution for organized members of the group \(\omega _{j}^{\theta }(\tau )\) is provided by multiplying the share of the organized group \(\theta ^{j}\) by the gross welfare function for all the members of the group without contribution \(\omega _{j}(\tau )\), that is, \(\omega _{j}^{\theta }(\tau )=\theta ^{j}\omega _{j}(\tau )\). The problem of the government could be \(\tilde{G_{j}}=\beta ^{j}\omega _{j}(\tau )+\beta \omega _{-j}(\tau )\), where \(\beta ^{j}=(1-\beta )\theta ^{j}+\beta <1\). In this setting, under the regime with lobbying by agents in the resource-rent group, the difference between the optimal and the equilibrium tax rates with lobbying by the resource-rent group could be derived as \({\tilde{\Theta }}_{R}\equiv \tilde{\tau ^{o}}-\tilde{\tau _{R}^{*}}=(1-{\tilde{\lambda }}_{R})\Omega\), where \({\tilde{\lambda }}_{R}=[(1-\beta )\theta ^{R}+\beta ]r+\beta n(<1)\) and \(\Omega\) is the same as in the original model. This equation implies that our results are not qualitatively changed if some of the agents in the organized group are unorganized.
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Acknowledgements
The author is grateful to Marko Köthenbürger (co-editor) for his informative advice and thanks to two anonymous referees for their constructive comments and suggestions. This work is supported by a Grant-in-Aid for Scientific Research(C)17K03682 from the Japan Society for the Promotion of Science. Any errors are the sole responsibility of the author.
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Appendices
Appendix A: Comparison between Optimal And Equilibrium Tax Rates
Consider regime (1) wherein the resource-rent group contributes. Let the difference between the optimal and the equilibrium tax rates be
where
and \(0<\lambda _{R}=r+\beta n<1\). To ensure that the equilibrium tax rate \(\tau _{R}^{*}\) is equal to the optimum \(\tau ^{o}\) (consequently, \(\Theta _{R}=0\)), let the critical proportion of transfer to tax revenue be
\(\Omega \gtreqless 0\) if \(\phi \lesseqgtr {\bar{\phi }}\). Since \(\beta <1\), we have \(\tau ^{o}>\tau _{R}^{*}\) if \(\phi <{\bar{\phi }}\) or \(\tau ^{o}<\tau _{R}^{*}\) if \(\phi >{\bar{\phi }}\). Next, consider regime (2) wherein the environmentally conscious group contributes. Let the difference between the equilibrium and the optimal tax rates be
where \(\lambda _{N}=\beta r+n=\beta -n(\beta -1)>\beta\). Similarly, we have \(\tau _{N}^{*}>\tau ^{o}\) if \(\phi <{\bar{\phi }}\) or \(\tau _{N}^{*}<\tau ^{o}\) if \(\phi >{\bar{\phi }}\). Finally, in result (3), \(\Omega =0\) if \(\phi ={\bar{\phi }}\): then, we find \(\Theta _{R}=\Theta _{N}=0\) and \(\tau ^{o}=\tau _{R}^{*}=\tau _{N}^{*}\).
Appendix B: Effects of changes in the proportion of transfer to tax revenue on convergence
As for result (1), consider the regime with lobbying by the resource-rent group. We differentiate the difference between the optimal and equilibrium tax rates (18) with respect to the proportion of transfer to revenue parameter \(\phi\) as follows:
if the curly brackets are positive or \(H=\frac{1}{1-\eta }<2(1-\alpha )\frac{\alpha v_{p}}{\alpha (v_{p}+1)-1}\) as long as \(v_{p}>\frac{1-\alpha }{\alpha }\). The above inequality indicates that an increase in \(\phi\) makes the divergence between the optimum and the equilibrium smaller when the energy resource sector is fairly concentrated and the marginal damage of pollution is sufficiently high. Similarly, for result (2) under the regime with lobbying by the environmentally conscious group, if we differentiate (19) with respect to \(\phi\), we have
and find the same result as in result (1).
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Nakada, M. The impact of environmental tax revenue allocation on the consequence of lobbying activities. Econ Gov 21, 335–349 (2020). https://doi.org/10.1007/s10101-020-00243-6
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DOI: https://doi.org/10.1007/s10101-020-00243-6