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Environmental Policy Making in a Second-Best Setting

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This paper uses analytically tractable and numerically solved general equilibrium models to examine the significance of pre-existing distortions in factor markets for revenue-neutral environmental tax reforms and for various policies involving pollution quotas and permits. Results indicate that pre-existing factor taxes generally raise the costs of these environmental policies. This reflects a tax-interaction effect: the lowering of real factor returns resulting from the higher output prices occasioned by environmental taxes and other regulations. The revenue-recycling effect - stemming from the use of environmental tax revenues to finance cuts in pre-existing factor taxes - helps reduce policy costs, but under plausible assumptions does not eliminate the costs of such policies: the double dividend does not materialize. Even if it does not produce a double dividend, the revenue-recycling effect is important for reducing policy costs. Policies that fail to exploit the revenue-recycling effect suffer significant disadvantages in terms of efficiency. Like environmental taxes, freely allocated (or grandfathered) pollution quotas or permits, for example, produce a costly tax-interaction effect, yet such quotas or permits do not enjoy the offsetting revenue-recycling effect. Auctioning the permits or quotas makes possible the revenue-recycling effect and allows given pollution-abatement targets to be achieved at lower cost. The failure to exploit the revenue-recycling effect can alter the sign of overall efficiency impact. Indeed, if marginal environmental benefits from pollution reductions are below a certain threshold value, then any level of pollution abatement through freely allocated quotas or permits is efficiency-reducing. The tax-interaction effect is relevant to government regulation outside the environmental area. To the extent that regulations on international trade or agricultural production raise output prices and thereby reduce real factor returns, these regulations exacerbate the factor-market distortions from pre-existing taxes and thus involve higher social costs than would be indicated by partial equilibrium analyses.

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  • Lawrence H. Goulder, 1998. "Environmental Policy Making in a Second-Best Setting," Journal of Applied Economics, Universidad del CEMA, vol. 1, pages 279-328, November.
  • Handle: RePEc:cem:jaecon:v:1:y:1998:n:2:p:279-328
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    9. Jesse D. Jenkins & Valerie J. Karplus, 2016. "Carbon pricing under binding political constraints," WIDER Working Paper Series 044, World Institute for Development Economic Research (UNU-WIDER).
    10. Homma, Takashi & Akimoto, Keigo & Tomoda, Toshimasa, 2009. "Evaluation of CO2 emissions based on the consumption-based measurement under CO2 reduction scenarios of different reduction levels," Conference papers 331871, Purdue University, Center for Global Trade Analysis, Global Trade Analysis Project.
    11. Gonzalez, Fidel, 2012. "Distributional effects of carbon taxes: The case of Mexico," Energy Economics, Elsevier, vol. 34(6), pages 2102-2115.
    12. Sobieralski, Joseph B., 2013. "The optimal aviation gasoline tax for U.S. general aviation," Transport Policy, Elsevier, vol. 29(C), pages 186-191.
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    14. Devarajan Shantayanan & Go Delfin S & Robinson Sherman & Thierfelder Karen, 2011. "Tax Policy to Reduce Carbon Emissions in a Distorted Economy: Illustrations from a South Africa CGE Model," The B.E. Journal of Economic Analysis & Policy, De Gruyter, vol. 11(1), pages 1-24, February.
    15. Lynn Mainwaring & Richard Jones & David Blackaby, 2006. "Devolution, sustainability and GDP convergence: Is the Welsh agenda achievable?," Regional Studies, Taylor & Francis Journals, vol. 40(6), pages 679-689.
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