Abstract
In this paper we analyze the economic effects of implementing EPA’s newly proposed regulations for carbon dioxide (\(\hbox {CO}_2\)) on existing U.S. coal-fired power plants using nonparametric methods on a sample of 144 electricity generating units. Moreover, we develop an approach for evaluating the economic gains from averaging emission intensities among the utilities’ generating units, compared to implementing unit-specific performance standards. Our results show that the implementation of flexible standards leads to up to 2.7 billion dollars larger profits compared to the uniform standards. Moreover, we find that by adopting best practices, current profits can be maintained even if an intensity standard of 0.88 tons of \(\hbox {CO}_2\) per MWh is implemented. However, our results also indicate a trade-off between environmental and profit gains, since aggregate \(\hbox {CO}_2\) emissions are higher with emission intensity averaging than with uniform standards.
Similar content being viewed by others
Notes
See Song et al. (2012) for a detailed review of the literature on nonparametric analysis of environmental efficiency.
Zhang and Choi (2014) provide a survey on the use of directional distance functions in environmental efficiency analysis.
In our analysis we refer to each generator located at coal-fired plants as a generating unit. Electric utilities are the companies which own the plants and may therefore be owning and operating multiple generating units.
Note that our theoretical discussion can be easily extended to the case of more than two inputs and two outputs. For the sake of notational simplicity we restrict this presentation to our empirical specification.
Emission (recuperation) factors indicate the amount of materials bound in one unit of inputs (outputs).
See e.g. Greene (2008) for a discussion on issues with parametric models containing multiple outputs.
A formal proof of that the equality constraint implies weak disposability of the technology can be found in Färe and Grosskopf (2004, pp. 49–51).
The estimated technologies only satisfy the inactivity axiom if an inactive unit is part of the dataset, which is rarely the case given empirical data.
See Welch and Barnum (2009) for a similar methodological approach to a cost and environmental analysis of power plants.
Moreover, due to an optimization approach which is not based on distance functions, the problems discussed by Chen (2014) for the JP model do not arise.
Note that if the ratio of averages is equal to s the average ratio can not be smaller than s since by Jensen’s inequality it follows that \(E(b/y)=E(b)\cdot E(1/y) \ge E(b)\cdot 1/E(y) =E(b)/E(y)\).
For more detailed discussions on network technologies modeling subunits see e.g. Färe and Grosskopf (2000).
Note that in line with the literature on profit efficiency we assume that the prices are not affected by the profit optimization. If demand and supply functions are known, endogenous models (see Johnson and Ruggiero 2011) could be estimated.
See Heshmati et al. (2012) for a discussion of the issues when estimating power plant efficiency with heterogeneous technology sets.
See Färe et al. (2013a) for a discussion on the reduction of the number of observations due to missing data from U.S. power plants.
See Hampf and Rødseth (2015) for more details on the data.
Note that the grid is evaluated for steps of 0.01 tons per MWh.
We define the profits of the generating units given their inefficiencies as the business-as-usual profits.
In principle, cost minimization implies allocating different standards to different fossil fuel types (that on average amount to the EPA standards), in order to equalize marginal abatement costs across different fuel types. Hence, if the fuel-specific abatement costs were known, it would be possible to assign fuel specific performance standards. The emission standard for coal will intuitively be higher than the EPA standard.
References
Ambec, S., & Barla, P. (2006). Can environmental regulations be good for business? An assessment of the Porter hypothesis. Energy Studies Review, 14, 42–62.
Ayers, R. U., & Kneese, A. V. (1969). Production, consumption, and externalities. American Economic Review, 59, 282–297.
Brännlund, R., Färe, R., & Grosskopf, S. (1995). Environmental regulation and profitability: An application to Swedish pulp and paper mills. Environmental and Resource Economics, 6, 23–36.
Brännlund, R., Chung, Y., Fre, R., & Grosskopf, S. (1998). Emission trading and profitability: The Swedish pulp and paper industry. Environmental and Resource Economics, 12, 345–356.
Chen, C.-M. (2014). Evaluating eco-efficiency with data envelopment analysis: An analytical reexamination. Annals of Operations Research, 214, 49–71.
Chung, Y. H., Fre, R., & Grosskopf, S. (1997). Productivity and undesirable outputs: A directional distance function approach. Journal of Environmental Management, 51, 229–240.
Deprins, D., Simar, L., & Tulkens, H. (1984). Measuring labor-efficiency in post offices. In M. Marchand, P. Prestieau, & H. Tulkens (Eds.), The performance of public enterprises: Concepts and measurement (pp. 243–268). Amsterdam: New-Holland.
Färe, R., & Grosskopf, S. (2000). Network DEA. Socio-Economic Planning Sciences, 34, 35–49.
Färe, R., & Grosskopf, S. (2003). Nonparametric productivity analysis with undesirable outputs: Comment. American Journal of Agricultural Economics, 85, 1070–1074.
Färe, R., & Grosskopf, S. (2004). New directions: Efficiency and productivity. Boston: Kluwer Academic.
Färe, R., & Primont, D. (1995). Multi-output production and duality: Theory and applications. Boston: Kluwer Academic.
Färe, R., Grosskopf, S., Lovell, C. A. K., & Pasurka, C. (1989). Multilateral productivity comparisons when some outputs are undesirable: A nonparametric approach. Review of Economics and Statistics, 71, 90–98.
Färe, R., Grosskopf, S., Noh, D.-W., & Weber, W. (2005). Characteristics of a polluting technology: Theory and practice. Journal of Econometrics, 126, 469–492.
Färe, R., Grosskopf, S., & Pasurka, C. (2007). Pollution abatement activities and traditional productivity. Ecological Economics, 62, 673–682.
Färe, R., Grosskopf, S., & Pasurka, C. (2013a). Joint production of good and bad outputs with a network application. In J. Shogren (Ed.), Encyclopedia of energy, natural resources and environmental economics (Vol. 2, pp. 109–118). Amsterdam: Elsevier.
Färe, R., Grosskopf, S., & Pasurka, C. (2013b). Tradeable permits and unrealized gains from trade. Energy Economics, 40, 416–424.
Färe, R., Grosskopf, S., & Pasurka, C. (2014). Potential gains from trading bad outputs: The case of U.S. electric power plants. Resource and Energy Economics, 36, 99–112.
Førsund, F. R. (2009). Good modelling of bad outputs: Pollution and multiple-output production. International Review of Environmental and Resource Economics, 3, 1–38.
Greene, W. H. (2008). The econometric approach to efficiency analysis. In H. O. Fried, C. A. K. Lovell, & S. S. Schmidt (Eds.), The measurement of productive efficiency and productivity growth (pp. 92–250). Oxford: Oxford University Press.
Gruenspecht, H. K., & Lave, L. B. (1989). The economics of health, safety, and environmental regulation. In R. Schmalensee & R. Willig (Eds.), Handbook of industrial organization (Vol. 2, pp. 1507–1550). Amsterdam: North-Holland.
Hampf, B. (2014). Separating environmental efficiency into production and abatement efficiency: A nonparametric model with application to US power plants. Journal of Productivity Analysis, 41, 457–473.
Hampf, B., & Rødseth, K. L. (2015). Carbon dioxide emission standards for U.S. power plants: An efficiency analysis perspective. Energy Economics, 50, 140–153.
Heshmati, A., Lee, S., & Hwang, W. (2012). Performance analysis of power plants under heterogenous technologies with meta frontier framework. International Journal of Economics and Management Engineering, 2, 5–14.
Jaffe, A. B., Newell, R. G., & Stavins, R. N. (2002). Environmental Policy and Technological Change. Environmental and Resource Economics, 22, 41–69.
Johnson, A. L., & Ruggiero, J. (2011). Allocative efficiency measurement with endogenous prices. Economics Letters, 111, 81–83.
Khodabakhshi, M., & Aryavash, K. (2014). The fair allocation of common fixed cost or revenue using DEA concept. Annals of Operations Research, 214, 187–194.
Kotchen, M. J., & Mansur, E. (2014). How stringent is the EPA’s proposed carbon pollution standard for new power plants? Review of Environmental Economics and Policy, 8(2), 290–306.
Lauwers, L. (2009). Justifying the incorporation of the materials balance principle into frontier-based eco-efficiency models. Ecological Economics, 68, 1605–1614.
Mekaroonreung, M., & Johnson, A. L. (2012). Estimating the shadow prices of SO2 and NOx for U.S. coal power plants: A convex nonparametric least-squares approach. Energy Economics, 34, 723–732.
Mohr, R. D. (2006). Environmental performance standards and the adoption of technology. Ecological Economics, 58, 238–248.
Nasrabadi, N., Dehnokhalaji, A., Kiani, N. A., Korhonen, P. J., & Wallenius, J. (2012). Resource allocation for performance improvement. Annals of Operations Research, 196, 459–468.
Nielsen, R. (2012). Introducing individual transferable quotas on nitrogen in Danish fresh water aqua-culture: Production and profitability gains. Ecological Economics, 75, 83–90.
Oude Lansink, A., & van der Vlist, A. (2008). Non-parametric modelling of CO2 emission quota. Journal of Agricultural Economics, 59, 487–497.
Porter, M. E., & van der Linde, C. (1995). Toward a new conception of the environment-competitiveness relationship. Journal of Economic Perspectives, 9, 97–118.
Ramli, N. A., Munisamy, S., & Arabi, B. (2013). Scale directional distance function and its application to the measurement of eco-efficiency in the manufacturing sector. Annals of Operations Research, 211, 381–398.
Rødseth, K. L. (2014). Axioms of a polluting technology: A materials balance approach. Working paper. Institute of Transport Economics - Norwegian Centre for Transport Research.
Rødseth, K. L., & Romstad, E. (2014). Environmental regulations, producer responses, and secondary benefits: Carbon dioxide reductions under the acid rain program. Environmental and Resource Economics, 59, 111–135.
Scheel, H. (2001). Undesirable outputs in efficiency valuations. European Journal of Operational Research, 132, 400–410.
Shephard, R. W. (1970). Theory of cost and production functions. Princeton: Princeton University Press.
Simar, L., & Wilson, P. W. (2011). Inference by the m out of n bootstrap in nonparametric frontier models. Journal of Productivity Analysis, 36, 33–53.
Song, M., An, Q., Zhang, W., Wang, Z., & Wu, J. (2012). Envionmental efficiency evaluation based on data envelopment analysis: A review. Renewable and Sustainable Energy Reviews, 16, 4465–4469.
Thanassoulis, E., Portela, M. C. A. S., & Despić, O. (2008). Data envelopment analysis: The mathematical programming approach to efficiency analysis. In H. O. Fried, C. A. K. Lovell, & S. S. Schmidt (Eds.), The measurement of productive efficiency and productivity growth (pp. 251–420). Oxford: Oxford University Press.
Tulkens, H., & Vanden Eeckaut, P. (1995). Non-parametric efficiency, progress and regress measures for panel data: Methodological aspects. European Journal of Operational Research, 80, 474–499.
Welch, E., & Barnum, D. (2009). Joint environmental and cost efficiency analysis of electricity generation. Ecological Economics, 68, 2336–2343.
Zhang, N., & Choi, Y. (2014). A note on the evolution of directional distance function and its development in energy and environmental studies 1997–2013. Renewable and Sustainable Energy Reviews, 33, 50–59.
Zhou, P., Ang, B. W., & Poh, K. L. (2008). A survey of data envelopment analysis in energy and environmental studies. European Journal of Operational Research, 189, 1–18.
Zofio, J. L., & Prieto, A. M. (2001). Environmental efficiency and regulatory standards: The case of CO2 emissions from OECD countries. Resource and Energy Economics, 23, 63–83.
Acknowledgments
We are grateful to Jens Krüger and two anonymous referees for valuable comments. Of course, all remaining errors are ours.
Author information
Authors and Affiliations
Corresponding author
Appendix
Appendix
Proof of the equivalence of the JP and the MB model:
To start consider the profit optimization subject to the non-convex JP model:
In the optimum \(x^P=\sum _{j=1}^n x_j^{P} \lambda _j\) and \(y = \sum _{j=1}^n y_j \lambda _j\theta \) hold since \(x^P\) and y can be freely chosen and \(b=\sum _{j=1}^n b_j \lambda _j\theta \) by construction. Moreover, \(\theta \) can be set equal to one since y and b can be freely chosen. Replacing the modified equalities in the objective function and the regulatory constraint leads to:
The optimization problem under the non-convex MB model is given by:
In this formulation the slack on the good output \(\epsilon _y\) is removed and the equality replaced by an inequality since the output in our analysis (electricity) does not contain any materials. In the optimum \(\epsilon _x=\epsilon _b=0\) since \(x^P\) and b can be freely chosen. Hence, \(x^P=\sum _{j=1}^n x_j^{P} \lambda _j\) and \(b=\sum _{j=1}^n b_j \lambda _j\). Moreover, \(y=\sum _{j=1}^n y_j \lambda _j\) since y can be freely chosen. Replacing these equalities in the objective function and the regulatory constraint leads to:
Therefore, the JP and the MB model lead to the same results for the profit maximization.
Rights and permissions
About this article
Cite this article
Hampf, B., Rødseth, K.L. Optimal profits under environmental regulation: the benefits from emission intensity averaging. Ann Oper Res 255, 367–390 (2017). https://doi.org/10.1007/s10479-015-2020-4
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10479-015-2020-4
Keywords
- Environmental regulation
- Profit maximization
- Emission intensity averaging
- Nonparametric efficiency analysis