Abstract
This paper examines the effect of environmental policy on economic growth in a small open economy in a neoclassical framework with pollution as an argument in both the utility and production functions. We show that environmental policy imposes a drag on long-run growth in both the open and closed economy cases. The effect of environmental policy on growth is stronger in the open economy case relative to the closed economy model if the country has strong aversion to pollution and thus serves as a net exporter of capital in the international capital market. On the other hand, if the agents in the economy have low aversion to pollution and thus import capital, the effect of environmental care on growth is stronger in the closed economy relative to the open economy. Thus, from our setup, environmental policy is harmful to growth but environmental sustainability need not be incompatible with continued economic growth.
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Notes
The idea behind this formulation is that “techniques of production are less costly in terms of capital inputs if more pollution is allowed”. To give the rationale for augmenting the aggregate production function as an input in a more formal way, suppose that gross output is produced with capital and effective labour and takes the following general form \( \tilde{Y} = F(K,LT) \). Suppose further that pollution is proportional to gross output according to the relation \( Z = f(\Upomega )\tilde{Y} \). A constant fraction of the gross output \( \Upomega \) is used as input for abatement. This leaves a net output of \( Y = (1 - \Upomega )\tilde{Y} \) which is available for consumption, investment and export. Assume that \( f(\Upomega ) = \left( {1 - \Upomega } \right)^{1/\alpha } \), where 0 < α < 1. This implies that \( Z = (1 - \Upomega )^{1/\alpha } F(K,LT) \Leftrightarrow 1 - \Upomega = Z^{\alpha } \left[ {F(K,LT)} \right]^{ - \alpha } \). This and the expression for net output gives \( Y = Z^{\alpha } \left[ {F(K,LT)} \right]^{1 - \alpha } \), which is constant returns in Z, K and L and can conveniently be written in the form of (1) as above without loss of generality. For a motivation of having Z as an input, see Chap. 2 of Copeland and Taylor (2003).
Here, r(t) is the net rate of return; R(t) is the gross return on capital and \( \delta \) is the rate of depreciation of capital. The reason why this relationship holds among these variables is that in the absence of uncertainty, capital and loans are perfect substitutes as stores of value and, as a result, they must deliver the same return in equilibrium (Barro and Sala-i-Martin 2004).
If \( \beta = 0 \), then g C = x + n, which is the growth rate in the standard model without environmental protection. Thus if pollution is useless (has zero partial elasticity) then environmental policy does not create drag on growth.
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Acknowledgments
I thank Dr. Clas Eriksson, Associate Professor of Economics, Malardalen University College, Sweden, Professor Yves Surry, Department of Economics, Swedish University of Agricultural Sciences, for their insightful comments on the earlier drafts of this paper. I also thank the two anonymous referees for useful comments and suggestions.
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Appendices
Appendix 1: decentralized solution
Then the objective of the household is to maximize
with respect to C, subject to
The current value Hamiltonian for the above dynamic optimization problem is
Note that the household cannot influence Z. It is therefore not a direct choice variable here. The associated optimality conditions for the representative household are
Note that (6) has been used in Eq. (52). It can conveniently be rewritten as
Taking logs of Eq. (51), differentiating both sides with respect to time and using condition (54), we obtain the familiar consumption Euler equation.
Appendix 2: equivalence between command and decentralized solutions
2.1 Optimal tax rule
From the optimality condition in (4), we obtain the following relationship among the growth rates of pollution tax, aggregate production and aggregate emissions as follows.
Imposing the planners steady state growth rate of aggregate production and pollution into the above condition for the growth rate of the pollution tax, we derived the socially optimal growth rate of the tax as follows.
2.2 Steady state growth rates of aggregate variables
Imposing the steady state condition that \( \dot{K}/K = \dot{Y}/Y \) on Eq. (9) we obtain the steady state growth rate of aggregate output as
Substituting Eq. (56) into this together with some simplifications, we have
Note that we have the same results as the one obtained under command allocation. Thus, we can conclude that with the Pigouvian tax optimally set, the command allocation and decentralized allocation are equivalent.
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Adu, G. Effects on growth of environmental policy in a small open economy. Environ Econ Policy Stud 15, 343–365 (2013). https://doi.org/10.1007/s10018-013-0065-7
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DOI: https://doi.org/10.1007/s10018-013-0065-7