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Tradable Permit Systems: Considering Uncertainty in Emission Estimates

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Water, Air, & Soil Pollution: Focus

Abstract

We simulate the market for emission permits by considering uncertainty in emission inventory reports. The approach taken in this analysis is to enhance the emissions reported in each region by a certain part of their uncertainty when compliance with the Kyoto targets is being proved. While this formulation is not new in the literature, we define the uncertainty component in a way that enables comparison with the approach of effective permits presented in Nahorski, Horabik, and Jonas (2007) Compliance and emissions trading under the Kyoto protocol: Rules for uncertain inventories, (this issue). We show and explain that the transformation to effective permits bears additional costs apart from those resulting from shifting the Kyoto targets.

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Notes

  1. More information at http://www.ibspan.waw.pl/GHGUncert2004/prezent/Nahorski_prezentacja.pdf.

References

  • Babiker, M. H., Reilly, J. M., Mayer, M., Eckaus, R. S., Wing, I. S., & Hyman, R. C. (2001). The MIT emissions prediction and policy analysis (EPPA) model: Revisions, sensitivities, and comparisons of results. MIT Report No. 70, (Internet edition).

  • Bartoszczuk, P. (2004). Tradable emission permits as efficient strategy for achieving environmental goals. In Proceedings of the international workshop on uncertainty in greenhouse gas inventories: Verification, compliance and trading, held 24–25 September in Warsaw, Poland, pp. 143–150. Available at http://www.ibspan.waw.pl/ GHGUncert2004/papers.

  • Brandes, L. J., Olivier, J. G. J., & van Oorschot, M. M. P. (2004). Validation, verification and uncertainty assessment for the Netherlands. Emission inventory. In Proceedings of the international workshop on uncertainty in greenhouse gas inventories: Verification, compliance and trading, held 24–25 September in Warsaw, Poland, pp.19–33. Available at http://www.ibspan.waw.pl/ GHGUncert2004/papers.

  • EEA (2006). Annual European community greenhouse gas inventory 1990–2004 and inventory report 2006. Technical report no. 6, European Environment Agency, Copenhagen, Denmark. Available at: http://reports.eea.europa.eu/technical_report_2006_6/en.

  • Ellerman, A. D., & Decaux, A. (1998). Analysis of post-Kyoto CO2 emissions trading using marginal abatement curves, emission and ambient permits: A dynamic approach. Report No. 40, MIT Joint program on the science and policy of global change. Massachusetts Institute of Technology, Cambridge, MA, USA, 15, 39–56.

  • Ellerman, A. D., Jacoby, H. D., & Decaux, A. (1998). The effects on developing countries of the Kyoto protocol, and analysis of CO2 emissions trading. Report of the joint program on the science and policy of global change Massachusetts Institute of Technology. Cambridge, MA, USA.

  • Field, B. C., & Field, M. K. (2002). Environmental Economics, An Introduction. New York: McGraw-Hill.

    Google Scholar 

  • Gillenwater, M., Sussman, F., & Cohen, J. (2007). Practical applications of uncertainty analysis for national greenhouse gas inventories (this issue).

  • Godal, O. (2000). Simulating the carbon permit market with imperfect observations of emissions: Approaching equilibrium through sequential bilateral trade. Interim Report IR-00-060, International institute for applied systems analysis (IIASA), Laxenburg, Austria.

  • Godal, O., Ermoliev, Y., Klaassen, G., & Obersteiner, M. (2003). Carbon trading with imperfectly observable emisssions. Environmental and Resource Economics, 25, 151–169.

    Article  Google Scholar 

  • Hill, M., & Kriström, B. (2002). Sectoral EU trading and other climate policy options: Impacts on the Swedish economy, Stockholm School of Economics, Stockholm, Sweden. See http://www.sekon.slu.se/~bkr/hk2.pdf, 23.08.2004.

  • Holtsmark, B., Maestad, O. (2002). Emission trading under the Kyoto protocol-effects on fossil fuels markets under alternative regimes. Energy Policy, 30, 207–218.

    Article  Google Scholar 

  • IPCC (2000). Good practice guidance and uncertainty managment in national greenhouse gas inventories. Japan: IPCC-TSU NGGIP.

    Google Scholar 

  • Monni, S., Syri, S., Pipatti, & Savolainen, I. (2007). Extension of Eu emissions trading scheme to other sectors and gases: Consequences for uncertainty of total tradable amount (this issue).

  • Nahorski, Z., Jęda, W. (2007). Processing national CO2 inventory emissions data and their total uncertainty estimates (this issue).

  • Nahorski, Z., Horabik, J., & Jonas M. (2007). Compliance and emissions trading under the Kyoto protocol: Rules for uncertain inventories (this issue).

  • Nilsson, S., Shvidenko, A., & Jonas, M. (2007). Uncertainties of the regional terrsetial biota full carbon account: A systems analysis (this issue).

  • Paltsev, S., Reilly, J. M., Jacoby, H. D., Richard, S. E., McFarland, J., Sarofirm, M., et al. (2005). The MIT emissions prediction and policy analysis (EPPA) model: Version 4, Report No 125. (Internet Edition).

  • Rousse, O., & Sévi, B. (2004). Portfolio managment of emission permits and prudence behaviour uncertainties of the regional terrestial biota full carbon account: A systems analysis. In Proceedings of the international workshop on uncertainty in greenhouse gas inventories: Verification, compliance and trading, held 24–25 September in Warsaw, Poland, pp. 135–142. Available at http://www.ibspan.waw.pl/ GHGUncert2004/papers.

  • Sterner, T. (2003). Policy Instruments for Environmental and Natural Resource Management, Resources for the future. Washington, D.C., USA.

  • Tietenberg, T. (1985). Emissions Trading, An Exercise in Reforming Pollution Policy, Resources for the future. Washington, D.C., USA.

  • Tietenberg, T. (1998). Environmental economics and policy. Reading, MA: Addison-Wesley.

    Google Scholar 

  • Winiwarter, W. (2007). National greenhouse gas inventories: Understanding uncertainties versus potential for improving reliability (this issue).

  • Yang, Z., Eckaus, R. S., Ellerman, A. D., & Jacoby, H. D. (1996). The MIT emission prediction and policy analysis (EPPA) model. Report No. 6, MIT joint program on science and policy of global change, Cambridge, MA, USA.

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Correspondence to Paweł Bartoszczuk.

Appendix

Appendix

1.1 Emissions Trading and Marginal Abatement Cost Curves

Below we present the economic bases of the emissions trading mechanism. It introduces a new type of property right that allows a specified amount of pollutant to be emitted. Thus, the total number of permits held by all sources puts a limit on the total quantity of emissions. Permits can be sold to anyone participating in the permit market. The system is initialized by central decision makers who decide on the number of permits to be put into circulation. As the total number of permits is usually lower than current total emissions, some emitters will receive fewer permits than their current emissions would normally allow.

Regional purchase or sale of permits until their marginal costs are equalized:

$$ MAC_{1} = MAC_{2} = P_{2} $$

This way the aggregate emission reduction is reached at the least cost for the whole market. The difference between the market price and the marginal cost in the absence of trade creates a potential gain that is shared between the two trading regions. This is illustrated in Fig. 1.

Fig. 1
figure 1

Marginal abatements cost curves for two regions: MAC1 and MAC2

The origin of the marginal cost of control for the first source (MAC1) is the left-hand axis and the origin of the marginal cost of control for the second source (MAC2) is the right-hand axis. The diagram represents all possible allocations of the reduction between the two sources. The left-hand axis represents an allocation of the entire control responsibility to the second region, while the right-hand axis represents a situation in which the first source bears responsibility (Tietenberg, 1985). Initially region “1” must reduce hq amount of pollution, while region “2” tq amounts of pollution (looking from the right side of the axis). Total abatement cost is given by the area below the marginal abatement cost curves MAC1 and MAC2, respectively. Before trading, the total abatement cost for region “1” is the field “A”, and for region “2” is the sum of the areas B+C+D+E. Region “2” buys permits to emit more than is allowed (in other words, it reduces only the amount (tr) instead of the amount (tq), while region “1” abates more than it is obliged to do (hr), simultaneously selling (qr) permits.

After exchange of permits, costs for both sources is represented by the area (A + B + C ). The sum of the area A and B is the cost of control for the first source, while the area C is the cost of control for the second. The area D + E represents the amount saved by emissions trading. The costs of emission reduction is minimized, as the marginal costs are equalized across the emitters. Both regions have incentives to trade, as the marginal cost of control for the second region is higher than that for the first region. The second region will lower its costs as long as it can buy permits from the first region at a price lower than p 3. When the price equals p 2, neither region would have any further incentive to trade.

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Bartoszczuk, P., Horabik, J. Tradable Permit Systems: Considering Uncertainty in Emission Estimates. Water Air Soil Pollut: Focus 7, 573–579 (2007). https://doi.org/10.1007/s11267-006-9110-x

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