Abstract
Many developing countries are mixed economies in which public and private firms engage in Cournot competition. We show that some fundamental results in environmental economics fail to hold in these economies: more stringent environmental regulation does not necessarily reduce pollution levels, the equivalence between environmental taxes and standards breaks down, and not every emission level can be induced by emission taxes. These results are due to the endogeneity of the public firm CEO’s career choices. Instruments that can induce the CEO to choose a public career are most effective in reducing emissions and improving social welfare.
Similar content being viewed by others
Notes
For instance, the CEO at a national iron and steel corporation usually carries the rank at the vice minister level.
As another example, the “standard result” of market instruments dominating command-and-control approaches is also sensitive to the specific institutional settings. For instance, Endres (1997) and Endres and Finus (2002) show that when heterogeneous nations negotiate an international environmental agreement, an emission reduction standard agreed upon by the negotiating nations might dominate an emission tax.
One important caveat is that the nature of public firms might vary significantly across countries. For instance, Koppell (2007) argues that while SOEs in China compete with private firms, “hybrid” firms in the US typically do not compete with private firms performing similar functions.
This is not always true in developing countries with severe nepotism and corruption, where a group of collusive and interconnected elites control the governments and public firms.
Parameter \(\lambda \) also represents the partial privatization ratio in the literature on privatization in mixed oligopolies (Matsumura 1998).
The degree to which the CEO dominates firm decisions can also be determined by managerial discretion, or the CEO’s latitude of actions (Hambrick and Finkelstein 1987), and varies across industries (Hambrick and Abrahamson 1995). As long as CEO preferences substantially influence the firm’s behavior, our results are robust to varying the degree of managerial discretion.
Alternatively we can \(\hbox {interpret }\lambda \) as capturing the “residual” influence the CEO has over the firm’s objective function in a contract between the government and the CEO.
“Appendix” shows that when both firms abate only up to the standard and if \(\lambda <1\), the public firm’s output \(q_{0}\) is decreasing and the private firm’s output \(q_{1}\) is increasing in pollution damage \(\delta \): the public firm’s concern for social welfare means that it decreases its polluting output when pollution damage becomes higher, and correspondingly the private firm increases its output.
If the firms compete in prices, we have to go beyond the most basic Bertrand setup to capture the role of market power and public firms, e.g., by introducing capacity constraints or differentiated products. Once we do so, e.g., by introducing differentiated products, our main results still hold because discrete career choices will lead to jumps in equilibrium prices, similar to the Cournot setting.
References
Barros F (1995) Incentive schemes as strategic variables: an application to a mixed duopoly. Int J Ind Organ 13:373–386
Baumol WJ, Oates WE (1988) The theory of environmental policy, 2nd edn. Cambridge University Press, Cambridge
Bowles S (1998) Endogenous preferences: the cultural consequences of markets and other economic institutions. J Econ Lit XXXVI:75–111
Cao J, Karplus VJ (2014) Ownership and energy management in China’s Industrial Firms, working paper, Tsinghua University
Darnall N, Edwards D (2006) Predicting the cost of environmental management system adoption: the role of capabilities, resources and ownership structure. Strateg Manag J 27:301–320
DeFraja G, Delbono F (1989) Alternative strategies of a public enterprise in oligopoly. Oxf Econ Papers 41:302–311
Demski J, Sappington D (1987) Hierarchical regulatory control. Rand J Econ 18:369–383
Dewatripont M, Jewitt I, Tirole J (1999a) The economics of career concerns, part I: comparing information structures. Rev Econ Stud 66:183–198
Dewatripont M, Jewitt I, Tirole J (1999b) The economics of career concerns, part II: application to missions and accountability of government agencies. Rev Econ Stud 66:199–217
Du N, Heywood JS, Ye G (2013) Strategic delegation in an experimental mixed duopoly. J Econ Behav Organ 87:91–100
Earnhart D, Lizal L (2006) Effects of ownership and financial performance on corporate environmental performance. J Comp Econ 34:111–129
Endres A (1997) Negotiating a climate convention—the role of prices and quantities. Int Rev Law Econ 17:147–156
Endres A, Finus M (2002) Quotas may beat taxes in a global emission game. Int Tax Public Finance 9:687–707
Fjell K, Heywood JS (2004) Mixed oligopoly, subsidization and the order of firm’s moves: the relevance of privatization. Econ Lett 83:411–416
García JH, Afsah S, Sterner T (2009) Which firms are more sensitive to public disclosure schemes for pollution control? Evidence from Indonesia’s PROPER program. Environ Resour Econ 42:151–168
Gentry BS (1998) Private capital flows and the environment: lessons from latin America. Edward Elgar, Cheltenham
Hambrick DC, Abrahamson E (1995) Assessing managerial discretion across industries: a multimethod approach. Acad Manag J 38:1427–1441
Hambrick DC, Finkelstein S (1987) Managerial discretion: a bridge between polar views of organizational outcomes. Res Organ Behav 9:369–406
Hahn RW (2000) The impact of economics on environmental policy. J Environ Econ Manag 39:375–399
Hanley N, Shogren JF, White B (2007) Environmental economics in theory and practice, 2nd edn. Palgrave Macmillan,
Heywood JS, Ye G (2009) Mixed oligopoly, sequential entry and spatial price discrimination. Econ Inq 47:589–597
Jaffe AB, Stavins R (1995) Dynamic incentives of environmental regulations: the effects of alternative policy instruments on technology diffusion. J Environ Econ Manag 29:S43–S63
Jansen T, Lier AV, Witteloostuijn AV (2007) A note on strategic delegation: the market share case. Int J Ind Organ 25:531–539
Jung C, Krutilla K, Boyd R (1996) Incentives for advanced pollution abatement technology at the industry level: an evaluation of policy alternatives. J Environ Econ Manag 30:95–111
Katsoulacos Y, Xepapadeas A (1995) Environmental policy under oligopoly with endogenous market structure. Scand J Econ 97:411–420
Kikeri S, Nellis J, Shirley M (1992) Privatization: the lesson of experience. The World Bank, Washington
Kofman F, Lawarrée J (1993) Collusion in hierarchical agency. Econometrica 61:629–656
Koppell JG (2007) Political control for china’s state-owned enterprises: lessons from america’s experience with hybrid organizations. Governance 20:255–278
Mascarenhas B (1989) Domains of state-owned, privately held, and publicly traded firms in international corporations. Adm Sci Q 34:582–597
Matsumura T (1998) Partial privatization in mixed duopoly. J Public Econ 70:473–483
Matsumura T (2003) Endogenous role in mixed markets: a two production period model. South Econ J 70:403–413
Merrill WC, Schneider N (1966) Government firms in oligopoly industries: a short-run analysis. Quart J Econ 80:400–412
Montero JP (2002) Prices versus quantities with incomplete enforcement. J Public Econ 85:435–454
Pal D (1998) Endogenous timing in a mixed oligopoly. Econo Lett 61:181–185
Pargal S, Wheeler D (1996) Informal regulation of industrial pollution in developing countries: evidence from Indonesia. J Polit Econ 104:1314–1327
Requate T (2006) Environmental policy under imperfect competition. In: Tietenberg T, Folmer H (eds) International yearbook of environmental and resource economics 2006/2007, Edward Elgar
Shleifer A, Vishny R (1994) Politicians and firms. Quart J Econ 109:995–1025
Simpson RD (1995) Optimal Pollution taxation in a cournot duopoly. Environ Resour Econ 6:59–369
Stavins RN (2003) Experience with market-based environmental policy instruments. In: Maler KG, Vincent JR (eds). Handbook of environmental economics, vol 1, Chapter 9, pp 355–435
Talukdar D, Meisner CM (2001) Does the private sector help or hurt the environment? Evidence from carbon dioxide pollution in developing countries. World Dev 29:827–840
Tirole J (1986) Hierarchies and bureaucracies: on the role of collusion in organizations. J Law Econ Organ 2:181–214
Wang H, Jin Y (2007) Industrial ownership and environmental performance: evidence from China. Environ Resour Econ 36:255–273
White MD (2001) Managerial incentives and the decision to hire managers in markets with public and private firms. Eur J Polit Econ 17:877–896
White MD (2002) Political manipulation of a public firm’s objective function. J Econ Behav Organ 49:487–499
Wilson JQ (1989) Bureaucracy: what government agencies do and why they do it. Basic Books,
Zeckhauser RJ, Horn M (1989) The control and performance of state-owned enterprises. In: MacAvoy PW et al (eds) Privatization and state-owned enterprises: lessons from the United States, Great Britain and Canada. Kluwer Academic Publishers, Boston, pp 7–57
Zhao J (2003) Irreversible abatement investment under cost uncertainties: tradable emission permits and emissions charges. J Public Econ 87:2765–2789
Author information
Authors and Affiliations
Corresponding author
Additional information
Voice: 1-517-353-9935. We thank participants at the 2014 Shanghai international conference “China’s Environmental Challenges: A Global Perspective” and the 2015 AERE/ASSA conference in Boston, as well as two anonymous referees for their insightful comments. The usual disclaimer applies.
Appendix: Technical Details
Appendix: Technical Details
1.1 Emission taxes
Given the linear quadratic setup, we are able to obtain closed form solutions of the equilibrium output and abatement levels. It is straightforward to show that
-
(i)
If \(\tau \ge c\) , then \(\alpha _{0} =\alpha _{1} =1\) and
$$\begin{aligned} \left\{ {\begin{array}{l} q_{0} =\frac{a-k-c}{1+2\lambda } \\ q_{1} =\lambda \frac{a-k-c}{1+2\lambda } \\ \end{array}} \right. \end{aligned}$$(8) -
(ii)
If \(\tau <c\) and \(\lambda <\lambda ^{I}\) , then \(\alpha _{0} =1, \alpha _{1} =0 \) and
$$\begin{aligned} \left\{ {\begin{array}{l} q_{0} =\frac{\tau -2c+a-k}{1+2\lambda } \\ q_{1} =\frac{\lambda a-\lambda k-\lambda \tau -\tau +c}{1+2\lambda }\\ \end{array}} \right. \end{aligned}$$(9) -
(iii)
If \(\tau <c\) and \(\lambda \ge \lambda ^{I}\) , then \( \alpha _{0} =0, \alpha _{1} =0\) and
\(\hbox {When }\lambda <1\), the public firm differs from the private firm in two aspects due to the former’s concern about social welfare: it might abate, and it tends to produce more so as to raise consumer surplus. The two firms also respond differently to changes in exogenous parameters. Proposition A1, which can be easily derived from (10), highlights the differences for the case of (iii) above.
Proposition A1
Consider case (iii), i.e., \(\alpha _{0} =0, \alpha _{1} =0\) and \(q_{0}\) and \(q_{1}\) are given in (10).
-
(i)
Suppose \(\lambda <1\) , i.e., the public firm cares about the social welfare. As pollution damage \(\delta \) increases, the public firm’s output \(q_{0}\) decreases but the private firm’s output \(q_{1}\) increases.
-
(ii)
As pollution tax \(\tau \) increases, the public firms’ output \(q_{0}\) decreases if \(\lambda \ge 1/2\) and the private firms’ output \(q_{1}\) always decreases, and \(q_{1} \) decreases more than \(q_{0}\) does.
-
(iii)
As consumer demand parameter a increases, both firms’ outputs rise, but the public firm’s output rises more than that of the private firm.
-
(iv)
As the marginal cost k rises, both firms’ outputs decrease, but the public firm’s output decreases more than the private firm.
-
(v)
As \(\lambda \) increases, i.e., as the public firm cares more about its profit, the public firm’s output \(q_{0}\) decreases, and the private firm’s output \(q_{1}\) increases.
We omit the proof, which is straightforward utilizing (10). \(\hbox {When }\lambda <1\), the public firm cares about the social welfare. Thus, as the pollution damage \(\delta \) increases, the public firm reduces its \(\hbox {output }q_{0}\) but the private firm increases its output due to strategic substitution \(\hbox {between }q_{0}\,\hbox {and }q_{1}\). In general, the private firm produces less as tax increases, but the public firm might produce more since the tax revenue is part of the social welfare. It will produce less if it cares more about its profit than about social welfare, i.e., \(\hbox {if }\lambda \ge 1/2\). When demand increases, both firms produce more but since the marginal consumer surplus is higher, the public firm has incentive to increase its output more than the private firm. When cost k rises, the fact that social welfare includes both firms’ profits means that the public firm reduces its output more than the private firm. As \(\lambda \) increases, the public firm cares more about its profit and thus reduces its \(\hbox {output }q_{0}\), and the private firm increases its output \(q_{1}\hbox {in }\) response, mimicking results in the standard mixed oligopoly literature.
Proof of Proposition 1
Given \(\tau <c\), it is straightforward to show that (cf. Fig. 1) \((\hat{{\pi }}_{0} (\lambda ,\tau )-\hat{{\pi }}_{1} (\lambda ,\tau ))|_{\alpha _{0} =0,\alpha _{1} =0} >(\hat{{\pi }}_{0} (\lambda ,\tau )-\hat{{\pi }}_{1} (\lambda ,\tau ))|_{\alpha _{0} =1,\alpha _{1} =0} \): at any chosen \(\lambda \), the public firm obtains a higher profit when it does not abate. The definition of \(\lambda _{1}^{P}\) and \(\lambda _{2}^{P} \) then implies that \((\hat{{\pi }}_{0} (\lambda _{1}^{P} (\tau ),\tau )-\hat{{\pi }}_{1} (\lambda _{1}^{P} (\tau ),\tau ))|_{\alpha _{0} =0,\alpha _{1} =0} >(\hat{{\pi }}_{0} (\lambda _{2}^{P} (\tau ),\tau )-\hat{{\pi }}_{1} (\lambda _{2}^{P} (\tau ),\tau ))|_{\alpha _{0} =1,\alpha _{1} =0} \). Thus,
is the highest payoff the private career CEO can obtain when choosing \(\lambda \).
Under Case (i) of Proposition 1, \(\lambda _{1}^{P} (\tau )>\lambda ^{I}(\tau )\). By \(\hbox {setting }\lambda ^{P}=\lambda _{1}^{P} \), the CEO obtains the highest payoff in (11). Under Case (ii), the CEO has no incentive to choose \(\lambda <\lambda ^{I}\,\hbox {since }\) it induces full abatement (cf. Fig. 1b) and since \(\lambda ^{I} (\tau )<\lambda _{3}^{P}(\tau )\,\hbox {implies }\) that choosing \(\lambda \in [\lambda ^{I},\lambda _{3}^{P})\,\hbox {generates }\) a payoff that exceeds the maximum payoff obtainable under full abatement (cf. the definition of \(\lambda )\). Since \(f(\cdot )\) is concave by assumption and \((\hat{{\pi }}_{0} (\lambda ,\tau )-\hat{{\pi }}_{1} (\lambda ,\tau ))|_{\alpha _{0} =0,\alpha _{1} =0}\) is concave in \(\lambda \) (due to the linear quadratic setup), the optimal choice from \(\lambda \in [\lambda ^{I},\lambda _{3}^{P})\) is \(\lambda ^{P}=\lambda ^{I}\) . Under Case (iii), the definition of \(\lambda \) and the condition that \(\lambda ^{I} \ge \lambda _{3}^{P} \ge \lambda \,\hbox {imply }\) that the CEO can obtain a higher payoff by inducing full abatement and choosing \(\lambda ^{P}=\lambda _{2}^{P}\) . \(\square \)
Layout of Fig. 2. The layout of the threshold profit weight functions in Fig. 2 has the following properties: (i)\(\lambda _{1}^{P} (\tau )<\lambda _{2}^{P} (\tau )\le 1/4\) for all \(\tau \le c,\lambda _{2}^{P} (\tau =c)=1/4\), and \(\partial \lambda _{i}^{P} (\tau )/\partial \tau >0\), for \(i=1, 2,\) and \(\partial \lambda ^{I} (\tau )/\partial \tau >0\); (ii) \(\lambda ^{I}(\tau )\) crosses \(\lambda _{1}^{P} (\tau )\) only once and from below at point \(\tau _{1}\), defined as \(\tau _{1} \equiv \max \left\{ {\tau \ge 0,\hbox { s.t. }\lambda ^{I} (\tau )=\lambda _{1}^{P} (\tau )} \right\} \) if it exists and \(\tau _{1} =0\) otherwise; (iii) \(\lambda ^{I}(\tau )\) crosses \(\lambda _{3}^{P} (\tau )\) only once and from below at point \(\tau _{2}\), defined as \(\tau _{2} \equiv \max \left\{ {\tau \ge 0,\hbox { s.t. }\lambda ^{I} (\tau )=\lambda _{3}^{P} (\tau )} \right\} \) if it exists and \(\tau _{2} =0\) otherwise; and (iv) \(\tau _{1} <\tau _{2} <c\).
Property (i) can be established directly from Eqs. (5), (6) and (7). From (5) and (6), \(\lambda ^{I}(\tau )\) and \(\lambda _{1}^{P} (\tau )\) can cross at most twice. Figure 2 depicts a situation when they cross once where \(\lambda ^{I}(\tau )\) crosses from below. We can show that if \(\lambda ^{I} (\tau )\) ever crosses \(\lambda _{1}^{P} (\tau )\) from above, it will always cross \(\lambda _{1}^{P} (\tau )\) again from below because \(\frac{\partial \lambda _{1}^{P} (\tau )}{\partial \tau }=\frac{9(a-k-\delta )}{2(2a-2k-3\delta +\tau )^{2}}\) and is bounded above but \(\frac{\partial \lambda ^{I} (\tau )}{\partial \tau }=\frac{\delta -c}{(\delta -\tau )^{2}}\) and goes to infinity as \(\tau \) increases. That is, eventually the slope of \(\lambda ^{I} (\tau )\) will exceed that of \(\lambda _{1}^{P} (\tau )\) and they will cross again. A third possibility is when \(\lambda ^{I} (\tau )\) lies entirely above \(\lambda _{1}^{P} (\tau )\), in which case \(\tau _{1} =0\). Although we only analyze the situation when they cross only once, the same methods can be used to analyze the other two situations (crossing twice or never crossing) and our main results still hold. Property (iii) can be established in a similar fashion to Property (ii). In Property (iv), \(\tau _{1} <\tau _{2}\) follows from the fact \(\hbox {that }\lambda ^{I} (\tau )\) is increasing, \(\lambda ^{I} (\tau )\,\hbox {crosses } \lambda _{1}^{P} (\tau )\) from below, and \(\lambda _{1}^{P} (\tau )<\lambda _{2}^{P} (\tau )\). Since \(\lim _{\tau \rightarrow c} \lambda ^{I} (\tau )=1\) and \(\lambda _{3}^{P} (c)<1\), we know \(\tau _{2}<c\).
Proof of Proposition 2
When \(\tau >c\), both firms fully abate and thus pay no pollution tax. Their profits and the social welfare are independent of \(\tau \), establishing (i) of the Proposition. For (ii), we can establish that \(\partial W^{*}/\partial \tau -\partial (\pi _{0}^{*} -\pi _{1}^{*} )/\partial \tau =(\delta -c)-(a-k-\tau )/2\), which is negative from Assumption 2(ii), \(\tau <c\), and \(\delta >\tau \)(implied by Assumption 2(i)). For (iii) of the Proposition, we can show \(\hbox {that }\partial W^{*}/\partial \tau -\partial (\pi _{0}^{*} -\pi _{1}^{*})/\partial \tau =(\delta -c)+(a-k-\tau )/6\), which is positive from Assumption 1 and because \(\delta >c\)(Assumption 2(i)). \(\square \)
1.2 Emission standards
Given \(\hbox {standard }\bar{{\alpha }}\) and weight \(\lambda \), it is straightforward to show that in Stage 3 Nash equilibrium, the private firm always abates up to the standard. Further,
-
(i)
If \(\lambda <\tilde{\lambda }^{I}\) , the public firm fully abates (\(\alpha _0 =1\) ) and the outputs are given by
$$\begin{aligned} \left\{ {\begin{array}{l} q_{0} =\frac{c\overline{\alpha }-2c+a-k}{1+2\lambda } \\ q_{1} =\frac{\lambda a-\lambda k-\lambda c\overline{\alpha }-c\overline{\alpha }+c}{1+2\lambda } \\ \end{array}} \right. \end{aligned}$$(12) -
(ii)
If \(\lambda \ge \tilde{\lambda }^{I}, \alpha _{0} =\bar{{\alpha }}\) and the equilibrium outputs are
Similar to the case of taxes, when the public firm fully abates, further tightening of the standard (increasing \(\bar{{\alpha }})\) only hurts the private firm since it will have to abate more. Thus in (12), \(q_{0}\) is increasing while \(q_{1}\) is decreasing in \(\hbox {standard }\bar{{\alpha }}\). When both firms are constrained by the standard, the private firm’s output is always decreasing in the standard, again since it cares only about its profit and abatement is costly. Even though the standard is binding for the public firm, the public firm’s output can still be increasing in the standard as long as its profit weight is not too high: a sufficient condition for this to be true \(\hbox {is }\lambda \le 1/2\). Finally, we can show that in (13), \(q_{0}\) is decreasing while \(q_{1}\) is increasing in pollution damage \(\delta \): \(\partial q_{0} /\partial \delta \propto -(1-\bar{{\alpha }})(1-\lambda )\le 0\) and \(\partial q_{1} /\partial \delta \propto (1-\bar{{\alpha }})(1-\lambda )\ge 0\), where the inequalities follow from \(\lambda \le 1\) and \(\bar{{\alpha }}\le 1\).
Rights and permissions
About this article
Cite this article
Ye, G., Zhao, J. Environmental Regulation in a Mixed Economy. Environ Resource Econ 65, 273–295 (2016). https://doi.org/10.1007/s10640-015-9932-y
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10640-015-9932-y