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Game of Regional Environmental Policy: Europe and US

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Abstract

We analyse a different timing implementation of environmental regulation and compare the effects on the markets from a policy innovation perspective. The paper addresses the question: Should a regulator try to commit to a policy (ex-ante regulation) or rather adapt its policy to a firm’s decisions (ex-post)? The findings are of interest towards improving regulatory effectiveness and economics efficiencies, e.g. for the transatlantic regional relationship between EU and USA. Our findings highlight differences in policy timing between markets may be harmful. The transatlantic regulators should consider the timing of the policy innovation for the achievement of mutual benefits.

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Notes

  1. A possible extension could be the case of the emission permits. For the case of environmental taxes see Innes and Bial (2002).

  2. For examples of innovation policy instruments see Borras and Edquist (2013).

  3. A similar approach is followed by Khan et al. (2014) under an informal analysis and for the case of the renewable energy in a monopoly market. In our case we focus on the case of the environmental anti-pollution technology and we analyse a formal model under monopoly and oligopoly markets.

  4. The set up of the technology is adopted from Asproudis and Gil-Molto (2014, 2015).

  5. For similar damage function see Kennedy (1999), Kennedy and Laplante (1999) and Requate (2005a).

  6. The trade-off between the two (regulator’s) priorities is close to the reality and represents this case where one could be better off if someone else will be worst off. Furthermore we assume b ∈ (0, 1), thus there are not extreme priorities.

  7. In our paper and contrary to Asproudis and Gil-Moltó (2015) we assume decreasing returns to scale. The “Quadratic cost functions reflect decreasing returns to scale or diseconomies of scale and are frequently met in applications, for instance in the modeling of renewable resources exploitation” Dubiel-Teleszynski (2011). Also the decreasing returns to scale could represent the “limited supply of industrial land and buildings” like in the case of Singapore’s manufacturing sector (Kee 2002).

  8. Following Asproudis and Gil-Moltó (2015), the technological cost is not connected directly with the production level but with the anti-pollution technology. For example, this could be the case of the number of the filters in the smokestack or the number of catalysts in the cars (for similar cases see Keohane 2002,Chao and Wilson 1993,Srivastava et al. 2001).

  9. All the steps of the two models and the analogous calculations are available to the reader and are included in the Appendix.

  10. See the Appendix for the proof of Lemma 1.

  11. See Appendix for the proof of Lemma 2.

  12. We set \(\frac { \partial \bar {SW}_{1}}{ \partial b} = 0\) and we solve with respect to b, Then, the quadratic form will give two possible solutions. \(b_{1} = 1 -\frac {a e^{2}}{\sqrt {a e^{2} (8 (1 +c) e +a (2 + 4 c +e^{2}))}}\) and \(b_{2} = 1 +\frac {a e^{2}}{\sqrt {a e^{2} (8 (1 +c) e +a (2 + 4 c +e^{2}))}}\), the second solutions is rejected because b < 1.

  13. \(\frac {\partial \bar {q}_{2}}{ \partial b} =\frac {4 a (b -1) b e^{2}}{(4 (b -1)^{2} (1 +c) +b^{2} e^{2})^{2}} <0\), where numerator < 0 and denominator > 0, ∀b < 1. Also, \(\frac { \partial \bar {k}_{2}}{ \partial b} =\frac { -4 a (b -1)^{2} (1 +c) e +a b^{2} e^{3}}{(4 (b -1)^{2} (1 +c) +b^{2} e^{2})^{2}}\) where denominator > 0 and numerator\( \lessgtr 0\), ∀b < 1.

  14. There are two possible solutions; \(e_{1} = -\frac {2 (b -1) \sqrt {1 +c}}{b}\) accepted, \(e_{2} =\frac {2 (b -1) \sqrt {1 +c}}{b}\) rejected ∀e > 0.

  15. In order to guarantee a real number for the ecvwe set − 1 + 2ci − 2cj(3 + 2cj) > 0 or \(c_{i} >\frac {1}{2} (1 + 6 c_{j} + 4 {c_{j}^{2}})\).

  16. The Second Order Conditions (SOC) are satisfied \(\frac { \partial ^{2}{\Pi } }{ \partial q^{2}} = -2 (1 +c) <0\).

  17. The SOC is \(\frac { \partial ^{2}S W^{ \ast }}{ \partial k^{2}} = 2 (b -1)\), which is negative since b < 1.

  18. The SOC is negative so, it guaranties the optimum value of \(k_{2}^{ \ast }\).

  19. The SOC is negative and equal to \(\frac { \partial ^{2}{\Pi }_{2}}{ \partial q^{2}} = -2 -2 c -\frac {b^{2} e^{2}}{2 (-1 +b)^{2}}\).

  20. The Second Order Condition (SOC) is satisfied \(\frac { \partial ^{2}{\Pi }_{i}}{ \partial {q_{i}^{2}}} = -2 (1 +c_{i}) <0\).

  21. The SOC is \(\frac { \partial ^{2}S W^{ \ast }}{ \partial k^{2}} = 2 (b -1) <0\), ∀b < 1.

  22. The SOC is negative (2(b-1)) so, it guaranties the optimum value of k.

  23. The SOC is \(\frac { \partial ^{2}{\Pi }_{i}}{ \partial {q_{i}^{2}}} = -2 -2 c_{i} <0\).

References

  • Aguilera RV, Jackson G (2003) The cross national diversity of corporate governance: dimensions and determinants. Acad Manage Rev 28:447–465

    Article  Google Scholar 

  • Asproudis E, Gil-Moltó MJ (2014) Pollution and environmentalists participation in emissions trading systems. Strategic Behavior and the Environment 4:59–87

    Article  Google Scholar 

  • Asproudis E, Gil-Moltó MJ (2015) Green trade unions: structure, wages and environmental technology. Environ Resource Econ 60:165–189

    Article  Google Scholar 

  • Baldwin R (2011) 21st century regionalism: filling the gap between 21st century trade and 20th century trade rules, staff working paper ERSD, no. 2011–08

  • Bandyopadhyay S, Lahiri S, Wall HJ (2012) Cross-border lobbying in preferential trading agreements: implications for external tariffs and welfare. Rev Int Econ 20:1034–1045

    Article  Google Scholar 

  • Barron A (2011) Exploring national culture’s consequences on international business lobbying. J World Bus 46:320–327

    Article  Google Scholar 

  • Berman E, Bui LT (2001) Environmental regulation and productivity: evidence from oil refineries. Rev Econ Stat 83:498–510

    Article  Google Scholar 

  • Bernheim D, Whinston M (1986) Menu auctions, resource allocation, and economic influence. Q J Econ 101:1–31

    Article  Google Scholar 

  • Bibas R, Mejean A, Hamdi-Cherif M (2015) Energy efficiency policies and the timing of action: an assessment of climate mitigation costs. Technol Forecast Soc Chang 90:137–152

    Article  Google Scholar 

  • Borras S, Edquist C (2013) The choice of innovation policy instruments. Technol Forecast Soc Chang 80:1513–1522

    Article  Google Scholar 

  • Borzel T, Risse T (2000) When Europe hits home: Europeanisation and domestic change. Paper available at: European Integration online Papers (EIoP) Vol. 4, N15. http://eiop.or.at/eiop/texte/2000-015a.htm

  • Chao H-P, Wilson R (1993) Option value of emission allowances. J Regul Econ 5:233–249

    Article  Google Scholar 

  • Coen D (1999) The impact of U.S. lobbying practice on the European business–government relationships. Calif Manage Rev 41:27–44

    Article  Google Scholar 

  • Conyon M, Judge WQ, Useem M (2011) Corporate governance and the 2008–09 financial crisis. Corporate Governance: An International Review 19:399–404

    Article  Google Scholar 

  • Damania R, Fredriksson PG (2000) On the formation of industry lobby groups. J Econ Behav Organ 41:315–336

    Article  Google Scholar 

  • Denicolo V (1999) Pollution-reducing innovations under taxes or permits. Oxf Econ Pap 51:184–199

    Article  Google Scholar 

  • Dubiel-Teleszynski T (2011) Nonlinear dynamics in a heterogeneous duopoly game with adjusting players and diseconomies of scale. Commun Nonlinear Sci Numer Simul 16:296–308

    Article  Google Scholar 

  • Elliott ED, Ackerman BA, Millian JC (1985) Toward a theory of statutory evolution: the federalization of environmental law. J Law Econ Org 1:313–340

    Google Scholar 

  • Farazmand A (1999) Globalization and public administration. Public Adm Rev 59:509–522

    Article  Google Scholar 

  • Flores R, Aguilera RV, Mahdian, Vaaler PM (2013) How well do supranational regional grouping schemes fit international business research models and quest. J Int Bus Stud 44:451–474

    Article  Google Scholar 

  • Freeman RE, Martin K, Parmar B (2007) Stakeholder capitalism. J Bus Ethics 74:303–314

    Article  Google Scholar 

  • Friedman M (1962) Capitalism and freedom. University of Chicago Press, Chicago

    Google Scholar 

  • Goulder LH, Mathai K (2000) Optimal CO2 abatement in the presence of induced technological change. J Environ Econ Manag 39:1–38

    Article  Google Scholar 

  • Groll T, Ellis CJ (2013) A simple model of the commercial lobbying industry (No 4110). CESifo working paper: public finance

  • Grossman G, Helpman E (1994) Protection for sale. Am Econ Rev 84:833–850

    Google Scholar 

  • Grossman G. M., Helpman E. (2002) Interest groups and trade policy. Princeton University Press, Princeton, NJ

    Google Scholar 

  • Hamilton DS, Quinlan JP (2011) The transatlantic economy: annual survey of jobs, trade and investment between the United States and Europe. Centre for transatlantic relations, the Paul H. Nitze school of advanced international studies, Johns Hopkins University. Washington. Available at http://transatlantic.sais-jhu.edu/publications/books/transatlantic_economy_2011/te_2011.pdf

  • Hay C, Rosamond B (2002) Globalisation, European integration and the discursive construction of economic imperatives. J Eur Publ Policy 9:147–167

    Article  Google Scholar 

  • Henning CR, Kessler M (2012) Fiscal federalism: U.S. history for architects of Europe’s fiscal union (January 10, 2012). Peterson Institute for International Economics Working Paper No. 2012-1. Available at SSRN: http://ssrn.com/abstract=1982709 or https://doi.org/10.2139/ssrn.1982709

  • Helfand GE (1991) Standards versus standards: the effects of different pollution restrictions. Am Econ Rev 81:622–634

    Google Scholar 

  • Hillman AJ (2003) Determinants of political strategies in U.S. multinationals. Business and Society Journal 42:455–484

    Article  Google Scholar 

  • Hiriart Y, Martimort D, Pouyet J (2004) On the optimal use of ex ante regulation and ex post liability. Econ Lett 84:231–235

    Article  Google Scholar 

  • Holman C (2009) Lobbying reform in the United States and the european union: progress on two continents. Interest groups and lobbying, citizen.org (Public citizen), pp 267–296

  • Holzinger K, Knill C, Sommerer T (2008) Environmental policy convergence: the impact of international harmonization, transnational communication, and regulatory competition. Int Organ 62:553–587

    Article  Google Scholar 

  • Innes R, Bial JJ (2002) Inducing innovation in the environmental technology of oligopolistic firms. J Ind Econ 50:265–287

    Article  Google Scholar 

  • Jaffe AB, Stavins RN (1995) Dynamic incentives of environmental regulations: the effects of alternative policy instruments on technology diffusion. J Environ Econ Manag 29:43–63

    Article  Google Scholar 

  • Kakabadse AP, Kakabadse NK (2012) Beyond lobbying: analysis of european wide corporate/government relations. Report funded by academy of business in society

  • Kakabadse NK, Kakabadse A, Kouzmin A, Pesqueux Y (2013) Rethinking the ontology of the shareholder model of the corporation. Soc Bus Rev 8:55–70

    Article  Google Scholar 

  • Kee HL (2002) Markups, returns to scale, and productivity: a case study of Singapore’s manufacturing sector. World Bank Policy Research Working Paper 2857

  • Keohane NO (2002) Environmental policy and the choice of abatement technique: evidence from coal-fired power plants. Paper presented at 2nd world congress of environmental and resource economists, June 2002, Monterrey, CA

  • Kennedy PW (1999) Learning about environment damage: implications for emissions trading. Can J Econ 32:1313–1327

    Article  Google Scholar 

  • Kennedy P, Laplante B (1999) Environmental policy and time consistency: emission taxes and emissions trading. In: Petrakis E, Sartzetakis ES, Xepapadeas A (eds) Environmental regulation and market power. U.K, Edward Elgar

  • Khan N, Asproudis E, Kakabadse NK (2014) Transatlantic regulatory timing of policy innovations: the case of renewable energy. In: Kakabadse A, Schepers S (eds) Rethinking the future of europe: a challenge of governance. Palgrave Macmillan

  • Kolstad C, Ulen T, Johnson G (1990) Ex post liability for harm vs. ex ante safety regulation: substitutes or complements? Am Econ Rev 80:888–901

    Google Scholar 

  • Magee SP, Brock WA, Young L (1989) Black hole tariffs and endogenous policy theory: political economy in general equilibrium. Cambridge University Press, Cambridge

    Google Scholar 

  • Matten D, Moon J (2008) “Implicit” and “explicit” CSR: a conceptual framework for a comparative understanding of corporate social responsibility. Acad Manage Rev 33:404–424

    Article  Google Scholar 

  • Marusca L, Irimies C (2013) Models of lobby in Europe. Journal of Media Research – Revista de Studii Media 1:56–62

    Google Scholar 

  • Montero JP (2002) Permits, standards, and technology innovation. J Environ Econ Manag 44:23–44

    Article  Google Scholar 

  • Onetti A, Zucchella A, Jones MV, McDougall-Covin (2012) Internationalization, innovation and entrepreneurship: business models for new technology-based firms. J Manag Gov 16:337–368

    Article  Google Scholar 

  • Parry IW, Pizer WA, Fischer C (2003) How large are the welfare gains from technological innovation induced by environmental policies?. J Regul Econ 23:237–255

    Article  Google Scholar 

  • Puller S (2006) The strategic use of innovation to influence regulatory standards. J Environ Econ Manag 52:690–706

    Article  Google Scholar 

  • Requate T (2005a) Dynamic incentives by environmental policy instruments - a survey. Ecol Econ 54:175–195

  • Requate T (2005b) Timing and commitment of environmental policy, adoption of new technology, and repercussions on R&D. Environ Resource Econ 31:175–199

  • Schepers S (2010) Business-government relations: beyond lobbying. Corp Gov 10:475–483

    Article  Google Scholar 

  • Shadbegian RJ, Gray WB (2006) Assessing multi-dimensional performance: environmental and economic outcomes. J Prod Anal 26:213–234

    Article  Google Scholar 

  • Shaffer B (1995) Firm-level responses to government regulation: theoretical and research approaches. J Manag 21:495–514

    Google Scholar 

  • Shavell S (1984) A model of the optimal use of liability and safety regulation. RAND J Econ 15:271–280

    Article  Google Scholar 

  • Soltani B (2013) The anatomy of corporate fraud: a comparative analysis of high profile american and european corporate scandals. J Bus Ethics 120:1–24

    Google Scholar 

  • Spar DL, La Mure LT (2003) The power of activism: assessing the impact of NGOs on global business. Calif Manage Rev 45:78–101

    Article  Google Scholar 

  • Srivastava RK, Jozewicz W, Singer C (2001) SO2 scrubbing technologies: a review. Environmental Progress 20:219–227

    Article  Google Scholar 

  • Tobey JA (1990) The effects of domestic environmental policies on patterns of world trade: an empirical test. Kyklos 43:191–209

    Article  Google Scholar 

  • United Nations (2012) World economic situation and prospects 2012. A join t report produced by UNDESA and UNTAD, New York, NY available at United Nations (2012a). World Economic Situation and Prospects 2012, United Nations

  • Van den Bergh JCJM (2013) Environmental and climate innovation: limitations, policies and prices. Technol Forecast Soc Chang 80:11–23

    Article  Google Scholar 

  • van Essen M, Engelen PJ, Carney M (2013) Does “good” corporate governance help in a crisis? The impact of country- and firm-level governance mechanisms in the European financial crisis. Corporate Governance: An International Review 21:201–224

    Article  Google Scholar 

  • Vogel D (2003) The hare and the tortoise revisited: the new politics of consumer and environmental regulation in Europe. Br J Polit Sci 33:557–580

    Article  Google Scholar 

  • Weymouth S (2011) The microeconomic determinants of lobbying and political influence: a multilevel approach. Working paper. George Town University

  • Yackee JW, Yackee SW (2006) A bias towards business? Assessing interest group influence on the US bureaucracy. J Polit 68:128–139

    Article  Google Scholar 

Download references

Acknowledgments

We would like to thank the editor and the anonymous referee for the constructive com- ments for the improvement of this paper. Also, we would like to thank participants at the EAERE 2016 and ASSET 2014 for comments and suggestions on previous versions of the paper. The usual disclaimer applies.

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Correspondence to Elias Asproudis.

Appendix

Appendix

1.1 Ex-ante Scenario - Monopoly

1.1.1 Stage 2: Firm Decides on Output

We calculate the First Order Conditions (FOC)Footnote 16

$$ \frac{ \partial {\Pi}_{1}}{ \partial q} =a -2 q (1 +c) = 0 $$
(14)

and solving with respect to q the firm’s level of production and the analogous profits are

$$ \bar{q}_{1} =\frac{a}{2 (1 +c)} $$
(15)
$$ {\Pi}_{1}^{ \ast } =\bar{q}_{1}^{2} (1 +c) -(k -1)^{2} $$
(16)

where the subscript 1 indicates the first scenario (ex-ante).

1.1.2 Stage 1: Regulator Decides for Technology

After the substitution of Eq. 6 into Eq. 1 we have

$$ S W_{1}^{ \ast } =(b -1) \left[(k -1)^{2} -\frac{a^{2}}{4 (1 +c)} \right] +\frac{a b (a -4 (1 +c) e k)}{8 (1 +c)^{2}} $$
(17)

and from the FOC we obtainFootnote 17

$$ \frac{\partial S W_{1}^{ \ast }}{ \partial k} = 2 (b -1) (k -1) -\frac{a b e}{2 (1 +c)} = 0 $$
(18)

yielding the optimum technology

$$ \bar{k}_{1} = 1 -\frac{a b e}{4 (1 -b) (1 +c)} $$
(19)

where \(\frac { \partial \bar {k}_{1}}{ \partial b} <0\) thus, the technological choice is reducing in b or the higher the value of the parameter b the less polluting the technological choice k is. We substitute all the results to the initial equations and therefore we have the results for the ex-ante case. Particularly, the profits are given by

$$ \bar{{\Pi} }_{1} =\frac{a^{2} \left( 1 -\frac{b^{2} e^{2}}{4 (b -1)^{2} (1 +c)}\right)}{4 (1 +c)} $$
(20)

and the price of good in the market is

$$ \bar{p}_{1} =a -\frac{a}{2 (1 +c)} $$
(21)

After substituting the technology to the Social Welfare (8) we obtain:

$$ \bar{SW}_{1} =\frac{ -a A +a^{2} b^{2} e^{2}}{16 (b -1) (1 +c)^{2}} $$
(22)

where A = (b − 1)(2a(2c(b − 1) + b − 2) + 8b(1 + c)e).

Also, the firm’s emissions are

$$ \bar{y}_{1} =\frac{a (4 (b -1) (1 +c) +a b e)}{8 (b -1) (1 +c)^{2}} $$
(23)

where \(\frac { \partial \bar {y}_{1}}{ \partial b} <0\) thus, emissions’ level is decreasing in b. Finally, the damage to the environment is equal to \(\bar {DF}_{1} =e \bar {y}_{1}\).

1.2 Ex-post Scenario - Monopoly

1.2.1 Stage 2: Regulator Decides for Technology

The regulator decides on the technological level in order to maximize the social welfare. The FOC is equal to:Footnote 18

$$ \frac{ \partial S W}{ \partial k} = 2 (1 -b) (1 -k) -b e q = 0 $$
(24)

and solving with respect to k we have

$$ k_{2}^{ \ast } = 1 -\frac{b e q}{2 (1 -b)} $$
(25)

where the subscript 2 indicated the ex-post case.

1.2.2 Stage 1: Firm Decides on Output

After the substitution of k into the profit’s equation we have \({\Pi }_{2} =(a -q) q -c q^{2} -\frac {b^{2} e^{2} q^{2}}{(2 b -2)^{2}}\). As usual we calculate the FOC which isFootnote 19

$$ \frac{ \partial {\Pi}_{2}}{ \partial q} =a +\frac{1}{2} \left( -4 -4 c -\frac{b^{2} e^{2}}{(b -1)^{2}}\right) = 0 $$
(26)

and solving for q we calculate the optimum level of output

$$ \bar{q}_{2} =\frac{2 a}{4 + 4 c +\frac{b^{2} e^{2}}{(b -1)^{2}}} $$
(27)

We substitute \(\bar {q}_{2}\) into \(k_{2}^{ \ast }\) and then we have the optimum technology for this model

$$ \bar{k}_{2} = 1 -\frac{a (1 -b) b e}{4 (b -1)^{2} (1 +c) +b^{2} e^{2}} $$
(28)

Hence, the final results for the ex post model are; profits equals

$$ \bar{{\Pi} }_{2} =\frac{a^{2} (b -1)^{2}}{4 (b -1)^{2} (1 +c) +b^{2} e^{2}} $$
(29)

and price of the good is

$$ \bar{p}_{2} =a -\frac{2 a}{4 + 4 c +\frac{b^{2} e^{2}}{(b -1)^{2}}} $$
(30)

After the necessary substitutions and calculation we get the Social welfare

$$ \bar{SW}_{2} =\frac{a (b -1)^{2} (X +Y)}{(4 (b -1)^{2} (1 +c) +b^{2} e^{2})^{2}} $$
(31)

where X = − 8(b − 1)2b(1 + c) − 2b3e3 and Y = a(b − 1)(− 2(b − 1)(b − 2 + 2(b − 1)c) − 3b2e2).

The level of the emissions are given by

$$ \bar{y}_{2} = 2 a (b -1)^{2} \left( \frac{1}{L} +\frac{a (b -1) b e}{L^{2}}\right) $$
(32)

where L = 4(b − 1)2(1 + c) + b2e2. So, the analogous damage function is \(\bar {DF}_{2} =e \bar {y}_{2}\).

1.3 Proof of Lemma 1

From the calculation of the difference we take \(\bar {\mathbf {p}}_{1} -\bar {\mathbf {p}}_{2} = -\frac {\mathbf {a} \mathbf {b}^{2} \mathbf {e}^{2}}{2 (1 +\mathbf {c})(4 (\mathbf {b} -1)^{2} (1 +\mathbf {c}) +\mathbf {b}^{2} \mathbf {e}^{2}}\) and it is straightforward that it is a negative result since the numerator and the denominator is positive. Thus, the price is lower under the ex-ante case. Also, we calculate \(\bar {\mathbf {q}}_{1} -\bar {\mathbf {q}}_{2} =\frac {\mathbf {a} \mathbf {b}^{2} \mathbf {e}^{2}}{2 (1 +\mathbf {c})(4 (\mathbf {b} -1)^{2} (1 +\mathbf {c}) +\mathbf {b}^{2} \mathbf {e}^{2}}\) which is positive since both numerator and denominator are positive.

1.4 Proof of Lemma 2

We calculate \(\bar {k}_{1} -\bar {k}_{2} =\frac {a b^{3} e^{3}}{4 (b -1) (1 +c) (4 (b -1)^{2} (1 +c) +b^{2} e^{2})}\) where the denominator is negative since b ∈ (0, 1), thus the technology is “greener” or less polluting under the ex-ante case. Furthermore, \(\bar {{\Pi } }_{1} -\bar {{\Pi } }_{2} = -\frac {a^{2} b^{4} e^{4}}{16 (b -1)^{2} (1 +c)^{2} (4 (b -1)^{2} (1 +c) +b^{2} e^{2})}\) which is negative (both numerator and denominator are positive) since there is a negative sing in front of the ratio. Hence, the level of the profitsis lower under the ex-ante case.

1.5 Ex-ante Scenario - Oligopoly

1.5.1 Stage 2: Firms Decide on Output

We calculate the First Order Conditions (FOCs)Footnote 20\(\frac { \partial {\Pi }_{i}}{ \partial q_{i}^{ \ast }} =a -2 q_{i} (1 +c_{i}) -q_{j} = 0\) and solving simultaneously with respect to qi we take

$$ \bar{q}_{i}^{E A} =\frac{a (1 + 2 c_{j})}{3 + 4 c_{j} + 4 c_{i} (1 +c_{j})} $$
(33)
$$ {\Pi}_{i}^{E A} =(\bar{q}_{i}^{E A})^{2} (1 +c_{i}) -(k_{i} -1)^{2} $$
(34)

where the superscript EA indicates the first scenario (ex-ante).

1.5.2 Stage 1: Regulator Decides for Technology

The Social Welfare is given by SWEA = b(CSEADFEA) + (1 − b)PSEA where \(C S^{E A} =\frac {1}{2} \overset {2}{ \sum _{i = 1}} \bar {q}_{i}^{E A}\), \(D F^{E A} =e (k_{i} \bar {q}_{i}^{E A} +k_{j} \bar {q}_{j}^{E A})\) and \(P S^{E A} =\overset {2}{ \sum _{i = 1}} {\Pi }_{i}^{E A}\) and from the FOC we obtainFootnote 21

$$ \frac{ \partial S W^{E A}}{ \partial k_{i}} = 2 (b -1) (k_{i} -1) -\frac{b (a + 2 a c_{j}) e}{3 + 4 c_{j} + 4 c_{i} (1 +c_{j})} = 0 $$
(35)

yielding the optimum technology

$$ \bar{k}_{i}^{E A} = 1 +\frac{a b (1 + 2 c_{j}) e}{2 (b -1) (3 + 4 c_{j} + 4 c_{i} (1 +c_{j}))} $$
(36)

After the necessary substitutions the profits are

$$ \bar{{\Pi} }_{i}^{E A} =(\bar{q}_{i}^{E A})^{2} \left( \left( \frac{4 (b -1)^{2} (1 +c_{i}) -b^{2} e^{2}}{4 (b -1)^{2}}\right)\right) $$
(37)

and the price is

$$ \bar{p}_{i}^{E A} =\frac{a (1 + 2 c_{i}) (1 + 2 c_{j})}{3 + 4 c_{j} + 4 c_{i} (1 +c_{j})} $$
(38)

The emissions are given by \(\bar {y}_{i}^{E A} =\bar {q}_{i}^{E A} \bar {k}_{i}^{E A}\) and \(D F^{E A} =e \bar {y}_{i}^{E A}\). As usual we substitute the above equation into the SWEA and we take the final \(\bar {SW}^{EA}\).

1.6 Ex-post Scenario

1.6.1 Stage 2: Regulator Decides for Technology - Oligopoly

Like in the basic model, the regulator will decide on the level of the technology which maximises the social welfare. The FOC is equal to:Footnote 22

$$\begin{array}{@{}rcl@{}} \frac{ \partial S W}{ \partial k_{i}} & = & 2 (b -1) (k_{i} -1) -b e q_{i} = 0 , \\ \frac{ \partial S W}{ \partial k_{j}} & = & 2 (b -1) (k_{j} -1) -b e q_{j} = 0, \end{array} $$
(39)

and solving simultaneously we have

$$ k_{i}^{E P} = 1 +\frac{b e q_{i}}{2 (b -1)} ,k_{j}^{E P} = 1 +\frac{b e q_{j}}{2 (b -1)} $$
(40)

where the superscript EP indicates the ex-post case.

1.6.2 Stage 1: Firms decide on output

After the substitution of \(k_{i}^{E P}\) into the profit’s equation we have \({\Pi }_{i}^{E P} =q_{i} (a +(-1 -c_{i} -\frac {b^{2} e^{2}}{4 (b -1)^{2}}) q_{i} -q_{j})\) and the FOCs areFootnote 23

$$ \frac{\partial {\Pi}_{i}^{E P}}{ \partial q_{i}} =a +\left( -2 -2 c_{i} -\frac{b^{2} e^{2}}{(b -1)^{2}}\right) q_{i} -q_{j} = 0 $$
(41)

where the optimum level of output is

$$ \bar{q}_{i}^{E P} =\frac{4 a G^{4} (1 + 2 c_{j}) + 2 a G^{2} b^{2} e^{2}}{4 G^{4} F + 4 G^{2} b^{2} (2 +c_{i} +c_{j}) e^{2} +b^{4} e^{4}} $$
(42)

where G = b − 1, F = 3 + 4cj + 4ci(1 + cj). Moreover, the optimum level of technology (after the substitution) equals \(\bar {k}_{i}^{E P} =\frac {2 a G^{3} b (1 + 2 c_{j}) e +a G b^{3} e^{3}}{4 G^{4} F + 4 G^{2} b^{2} (2 +c_{i} +c_{j}) e^{2} +b^{4} e^{4}}\) and similar we take the level of the emissions \(\bar {y}_{i}^{E P} =\bar {q}_{i}^{E P} \bar {k}_{i}^{E P}\), the damage equation \(D F^{E P} =e \bar {y}_{i}^{E P}\), the price \(\bar {p}_{i}^{E P} =a -\bar {q}_{i}^{E P} -\bar {q}_{j}^{E P}\), the profits \({\Pi }_{i}^{E P} =\bar {q}_{i}^{E P} (a +(-1 -c_{i} -\frac {b^{2} e^{2}}{4 (b -1)^{2}}) \bar {q}_{i}^{E P} -\bar {q}_{j}^{E P})\) and the social welfare \(\bar {SW}^{EP}\) (the last results are characterised by complex and long equations).

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Asproudis, E., Khan, N. & Korac-Kakabadse, N. Game of Regional Environmental Policy: Europe and US. J Ind Compet Trade 19, 1–20 (2019). https://doi.org/10.1007/s10842-018-0274-7

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  • DOI: https://doi.org/10.1007/s10842-018-0274-7

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