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Environmental taxation and mergers in oligopoly markets with product differentiation

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Abstract

We analyze the effect of mergers on optimal environmental taxation in a Cournot oligopoly market with product differentiation. Our result indicates that the adjustment in emission tax crucially depends on the post-merger output distortion and pollution intensities. Specifically, we find that the optimal emission tax increases post-merger as long as pollution intensity of firms is higher and output distortion smaller post-merger than pre-merger. Furthermore, our result suggests that there is no need to revise environmental policy in markets where pollution intensity of firms does not change post-merger and (i) products are completely differentiated, or (ii) there are many firms for any degree of product differentiation.

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Notes

  1. Source: http://www.carbontax.org/where-carbon-is-taxed/

  2. This ratio arises from differentiation of \(C_{e}(q,e)\); that is, \(dC_{e}=C_{eq}dq+C_{ee} de=0\Rightarrow -C_{eq}/C_{ee}\).

  3. Notice that for (i) the pollution intensities, \(\delta _{m}\) and \(\delta \), are the terms associated with emissions, and for (ii) the pollution intensities are associated with the output distortion.

  4. An analogous condition to (27) can be derived from (28).

  5. We use the fact that at \(\gamma =1\): \(2q_{1}=\tilde{q}\) and \(2\partial q_{1}/\partial t_{m} = \partial \tilde{q}/\partial t_{m}\).

  6. This expression is analogous to (23).

  7. It is noteworthy that in (30) the tax \(t_{m}\) is a function of \(\delta _{m}\) and thus \(t_{m}\) may rise/fall as \(\delta _{m}\) rises. There are two possibilities. First, the tax may rise as \(\delta _{m}\) rises. In this case the increase in the tax post-merger compensates the increase in \(\delta _{m}\): the numerator in the left-hand-side of (30) becomes smaller via the tax and also via the pollution intensity (for given tax). The left-hand-side term of (30) becomes smaller faster than the right-hand-side because of three factors: a larger denominator and a smaller numerator both through a reduction in \(\delta _{m}\) and \(t_{m}\). The right-hand-side term becomes smaller just via a reduction in the tax. Second, the tax post-merger may fall as \(\delta _{m}\) rises thus having an ambiguous effect on the numerator of the left-hand-side term of (30). We are interested in the first case (i.e., where \(t_{m}\) rises with \(\delta _{m}\)) since this case yields a clear-cut result which illustrates the factors leading to a larger tax post-merger even in the presence of restricted output due to the merger. The case where \(t_{m}\) rises (falls) with an increase in \(\delta _{m}\) can be interpreted as a situation where the government puts more (less) weight on addressing higher pollution.

  8. The role of commitment in policy making is important. For instance, Dixit et al. (1997) emphasizes the importance of commitment in government policy making. Likewise, Aidt (1998) presents factors that cause governments to adopt taxes that considerably differ from the Pigovian rule. These aspects are key, but in this paper we assume governments will adopt optimal policies and there are no commitment issues on the side of the government.

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Correspondence to Mahelet G. Fikru.

Appendix

Appendix

We examine the comparative static effects of the tax, \(t_{m}\), in the post-merger equilibrium. Differentiation of (13)–(16) yields the following system

$$\begin{aligned}&\left[ { \begin{array} [c]{cccc} -2(\beta +\gamma )-C_{q_{1}q_{1}} &{}\quad -\gamma (n-2) &{}\quad -C_{q_{1}e_{1}} &{}\quad 0\\ -C_{e_{1}q_{1}} &{}\quad 0 &{} \quad -C_{e_{1}e_{1}} &{}\quad 0\\ -2\gamma &{}\quad -2\beta -\gamma (n-3)-C_{\tilde{q}\tilde{q}} &{} \quad 0 &{}\quad -C_{\tilde{q}\tilde{e}}\\ 0 &{} \quad -C_{\tilde{e}\tilde{q}} &{} \quad 0 &{}\quad -C_{\tilde{e}\tilde{e}}\\ &{} &{} &{} \end{array} }\right] \left[ { \begin{array} [c]{c} dq_{1}\\ d\tilde{q}\\ de_{1}\\ d\tilde{e}\end{array} }\right] \\&\quad =\left[ { \begin{array} [c]{c} 0\\ dt_{m}\\ 0\\ dt_{m}\\ \end{array} }\right] \end{aligned}$$

where the determinant of the coefficient matrix \(\eta <0\):

$$\begin{aligned} \eta= & {} -C_{\tilde{e}\tilde{e}}C_{e_{1}e_{1}}\left[ \left( 2\beta +\gamma (n-3) +\frac{C_{\tilde{q}\tilde{q}} C_{\tilde{e}\tilde{e}}-C^{2}_{\tilde{e}\tilde{q}}}{C_{\tilde{e}\tilde{e}}}\right) \right. \\&\left. \times \left( 2(\beta +\gamma ) +\frac{C_{q_{1}q_{1}}C_{e_{1}e_{1}} - C^{2}_{e_{1}q_{1}}}{C_{e_{1}e_{1}}} \right) - 2\gamma ^{2} (n-2)\right] \end{aligned}$$

We follow Lahiri and Symeonidis (2007) in the definition of pollution intensity, \(-C_{qe}/C_{ee}>0\), where subscripts denote partial derivatives. When deriving the comparative statics analysis we assume identical pollution intensity within firms in the post-merger market; this is to facilitate the comparison with the pre-merger market. That is, \(-C_{q_{1}e_{1}} /C_{e_{1}e_{1}}=-C_{\tilde{q}\tilde{e}}/C_{\tilde{e}\tilde{e}}>0\).

Using the above system the effect of the tax post-merger on output, \(q_{1}\) and \(\tilde{q}\) is given by

$$\begin{aligned} \frac{\eta }{C_{e_{1}e_{1}}C_{\tilde{e}\tilde{e}}} dq_{1}&= \frac{-C_{e_{1}q_{1}}}{C_{e_{1}e_{1}} }\left[ 2\beta -\gamma +\frac{\left( C_{\tilde{e}\tilde{e}}C_{\tilde{q}\tilde{q}}-C_{\tilde{e}\tilde{q}}^{2}\right) }{C_{\tilde{e}\tilde{e}} }\right] dt_{m}\end{aligned}$$
(32)
$$\begin{aligned} \frac{\eta }{C_{e_{1}e_{1}}C_{\tilde{e}\tilde{e}}} d\tilde{q}&= \frac{-C_{\tilde{e}\tilde{q}}}{C_{\tilde{e}\tilde{e}} }\left[ 2\beta +\frac{\left( C_{e_{1}e_{1}}C_{q_{1}q_{1}}-C_{e_{1}q_{1}}^{2}\right) }{C_{e_{1}e_{1}}}\right] dt_{m}\end{aligned}$$
(33)

where \(2\beta -\gamma >0\), and \(C_{qq}C_{ee}-C_{eq}^{2}>0\), \(C_{ee}>0\) by the properties of the cost function. Hence, output falls with the tax, i.e., \(\eta <0\) and \(dq_{1}>0\), \(d\tilde{q}>0\).

The effects of the tax post-merger on emissions are given by:

$$\begin{aligned} \eta de_{1}&=-\frac{C_{e_{1}q_{1}}}{C_{e_{1}e_{1}}} \left[ -C_{e_{1}e_{1}} C_{\tilde{e}\tilde{e}}\frac{C_{e_{1}q_{1}}}{C_{e_{1}e_{1}}}\left( 2\beta -\gamma +\frac{\left( C_{\tilde{e}\tilde{e}} C_{\tilde{q}\tilde{q}}-C_{\tilde{e}\tilde{q}}^{2}\right) }{C_{\tilde{e}\tilde{e}}}\right) + \eta /C_{e_{1}q_{1}} \right] dt_{m}\end{aligned}$$
(34)
$$\begin{aligned} \eta d\tilde{e}&=-\frac{C_{\tilde{e}\tilde{q}}}{C_{\tilde{e}\tilde{e}}} \left[ -C_{e_{1}e_{1}} C_{\tilde{e}\tilde{e}}\frac{C_{\tilde{e}\tilde{q}}}{C_{\tilde{e}\tilde{e}}}\left( 2\beta +\frac{\left( C_{e_{1}e_{1}} C_{q_{1}q_{1}}-C_{e_{1}q_{1}}^{2}\right) }{C_{e_{1}e_{1}}}\right) + \eta /C_{\tilde{e}\tilde{q}} \right] dt_{m}\end{aligned}$$
(35)

The expressions in (32)–(35) reduce to the following in the special case of the end-of-pipe-type cost function \(C(q,e)=cq+(\delta q-e)^{2}/2\), where \(C_{qq}C_{ee}-C_{eq}^{2}=0\), \(C_{ee}=1\), \(-C_{q_{1}e_{1}} /C_{e_{1}e_{1}}=-C_{\tilde{q}\tilde{e}}/C_{\tilde{e}\tilde{e}}=\delta \), where \(\delta \) is a constant pollution intensity of firms:

See Table 1.

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Fikru, M.G., Gautier, L. Environmental taxation and mergers in oligopoly markets with product differentiation. J Econ 122, 45–65 (2017). https://doi.org/10.1007/s00712-017-0531-y

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