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Ferreira, L. Tools for Estimating the Cost of Carbon. Encyclopedia. Available online: https://encyclopedia.pub/entry/20229 (accessed on 01 July 2024).
Ferreira L. Tools for Estimating the Cost of Carbon. Encyclopedia. Available at: https://encyclopedia.pub/entry/20229. Accessed July 01, 2024.
Ferreira, Lurdes. "Tools for Estimating the Cost of Carbon" Encyclopedia, https://encyclopedia.pub/entry/20229 (accessed July 01, 2024).
Ferreira, L. (2022, March 04). Tools for Estimating the Cost of Carbon. In Encyclopedia. https://encyclopedia.pub/entry/20229
Ferreira, Lurdes. "Tools for Estimating the Cost of Carbon." Encyclopedia. Web. 04 March, 2022.
Tools for Estimating the Cost of Carbon
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Concepts and models of climate economics developed by researchers and modelers in recent decades have been suitable primarily for large scales of analysis and often in a top-down manner. The local dimension of climate policy is increasingly testing the adequacy of these concepts and models, as local governments begin to explore how to estimate the cost of carbon locally and thereby a local carbon price to formulate progressive climate policy. The question is what existing concepts, models, and methods can do for local climate governance and for incorporating local GHG emissions reduction into national targets. The cost of carbon is the value attributed to one unit of carbon (per ton) and the price of carbon is the explicit price for that unit of carbon for the market. In climate policy, the cost of carbon should inform the price of carbon. Carbon pricing embraces these concepts as the “polluter pays” principle and in practice, carbon tax and the carbon market (e.g., emissions trading, carbon credits) are the most well-known carbon pricing mechanisms that reflect this principle. The cost-benefit considerations and impact assessment of climate policies need to include carbon cost concepts such as the SCC or MAC, which also can influence the structure of a given IAM that analyzes the impacts and associated costs. SCC and MAC as concepts are different and complementary, while IAMs as tools operationalize these concepts inclusively. IAMs have been developed to expand and integrate additional components as scientific knowledge on the climate system and climate economics advances. Therefore, it is reasonable to expect that IAMs will include more features that take into account the increasing nuances required in carbon cost calculation and become more complex. The progresses of IAMs are expected to focus on microscales.

carbon pricing climate policy GHG emissions

1. Social Cost of Carbon and Marginal Abatement Cost

The concepts Social Cost of Carbon (SCC) and Marginal Abatement Cost (MAC) represent two mainstream approaches for estimating the carbon cost. The SCC represents the economic cost (damage value) that society incurs for emitting an additional ton of CO2 into the atmosphere for the time it will remain there (or the benefit for reducing it). SCC includes considerations of climate change damages to agriculture, human health, and property, and non-market damage such as the services that natural ecosystems provide to society [1]. SCC has been used primarily by national government agencies or international organizations to calculate the impact of climate policies based on a cost–benefit analysis. Researchers initially used the concept of SCC for the global scale and over time discussed it at large regional and national scales [2][3][4]. SCC is generally considered to have some major weaknesses, namely: complexity, subjectivity of discount rate, and the uncertainty of climate change impacts. Stern proposed that the discount rate should be zero as an attempt to solve this variability of the SCC and to avoid disproportionate burdens for the future caused by climate damage today due to overestimation of the present value of economic damage caused. The SCC approach to mitigate or explain the uncertainty elements results in a large variability of values, depending on the parameters, ranging from less than 0 to 1909 EUR/tCO2 (0 to 2300 USD/tCO2) [5] (assuming 1 US$ = 0.82 €; and CO2 and carbon are used here interchangeably), and with concentration of results between 8.3 and 166 EUR/tCO2 (10 and 200 USD/tCO2). Pindyck [6][7] proposed the average SCC from an elicitation with experts after criticism of the “pure guesswork” on critical matters of climate and social science that are themselves uncertain (e.g., tipping points). His large survey of climate economists and scientists showed that the highest average value (163 EUR/tCO2 (200 USD/tCO2)) for economists was the lowest value for climate scientists. Wang et al. [5] proposed a revised SCC calculation method, and Tian, Ye and Zhen [8] created a new simplified model for SCC calculation. When assessing the SCC at the country level, Ricke et al. [9] identified inequality in climate change impacts geographically as well as the contribution of each country to global emissions and the risk of unilateral climate action. Tol [10] estimated the national SCC and the penalty on the poorest and most populous countries. An important criticism also comes from the environmental science: SCC leads to an underestimation of fundamental costs of climate change such as ocean acidification and humanitarian and social impacts [11], which are not quantified in terms of GDP.
The other method for carbon cost estimation is the MAC—the cost of reducing an additional unit of emissions and the basis for measuring the capacity of an economy to support the cost of decarbonization, in relation to energy technology sectors. It is cost-effective-driven and does not consider the climate damage cost component. The MAC approach was developed following the oil shocks of the 1970s and the need to reduce energy consumption (fossil fuels and electricity) and air pollutants. Afterwards, researchers started to integrate carbon emissions and other sectors with strong climatic impacts into analyses using the MAC approach, such as agriculture and water.
Interest in MAC increased dramatically when the Paris Agreement in 2015 shifted the political focus from a carbon tax extracted from SCC to a committed timeframe, CO2 concentration, and temperature targets [6], and even more so when nations began to commit to carbon neutrality by mid-century. Carbon neutrality corresponds to a state of “balance between anthropogenic emissions by sources and removals by sinks of greenhouse gases” [12]. One MAC model that the International Energy Agency (IEA) has been developing is TIMES, in collaboration with member countries and academic institutions in open source and for several decades. Country members of the IEA use TIMES to simulate short-term average technology costs from the energy transition to carbon neutrality in 2050.
Pezzey [13] points out that it is preferable to estimate the carbon price closer to the target-based climate policies, while also recognizing uncertainties that remain in the MAC. The focus on reduction targets strengthens the adequacy of MAC to capture the effort of emissions reduction. Kaufman et al. [14] advocate for an alternative to the carbon price definition in a carbon-neutral horizon in 2050, based on a short-term MAC model (near-term to net-zero, or NT2NZ). The approach results in prices around 103.75 EUR/tCO2 (125 USD/tCO2) in 2030. Stern and Stiglitz [15] considered this approach as imperfect and transparent, as the SCC is uncertain and complex, proposing an alternative approach to the classic SCC that puts it at 83 EUR/tCO2 (100 USD/tCO2). They include the 2 °C increase limit as an additional constraint to the model, assuming that climate damage from the maximum limit drawn in the Paris Agreement costs more than 2% of GDP/year.
Much of the literature on the complexity, uncertainty, and subjectivity of the SCC and the limitations of the MAC shows that there is not an ideal approach, and policymakers should instead use a set of tools to assess climate policy. The problems pointed out with the SCC at the global or country levels are amplified when applied at a subnational level and smaller scales. As a global value harmonized to maximize efficiency, SCC is highly aggregated, and the smaller the scale (from global to regional, from regional to national, or from national to local), the greater the possible error margin. Although Pindyck [7] finds a general preference among economists for the SCC, the complexity of the estimates represents a barrier for policymakers and practitioners to understand [16][17].
As for the impacts of carbon pricing, Best, Burke and Jotzo [18] found evidence that in countries with carbon pricing, the average annual growth rate of CO2 emissions from fossil fuel consumption is 2% lower than in countries that do not have carbon pricing. Green [19] found that most studies concern Europe, and that the aggregate reductions range is modest, ranging from 0% to 2% per year. Lilliestam, Patt, and Bersalli [20] state that there is still no empirical evidence of carbon pricing effectiveness in promoting the technological change necessary for full decarbonization.
To summarize, both methods share the economic concept of marginal cost, and while the SCC is the marginal cost of damages associated with carbon emissions (when emitting less, the cost decreases), the MAC is the marginal cost of reducing emissions (when emitting less, the cost rises). Both have advantages and disadvantages. Comparing SCC and MAC, economists agree that MAC is not as sensitive to the discount rate as SCC is and does not use the damage function. MAC responds to how to decarbonize a sector in a given time constraint, and it allows for the modeling of regions/countries, as Ibrahim and Kennedy [21] as well as others have previously shown.

2. Integrated Assessment Models

Integrated Assessment Models (IAM) as a type of science and policymaking interface have been developed to estimate the cost of carbon, in the form of SCC or MAC. They simulate and calculate the optimal level of implementation of decisions/policies, while dealing with highly complex natural (climate) and social (economic) systems. Historically, an IAM includes key elements of the climate change mitigation and climate impacts systems in order to project alternative future climates with and without various types of policies [22]. When IAMs began to be increasingly used in climate policy analysis and policymaking in the 1990s, the rationale was to support policy on climate change mitigation and adaptation at the global level [23]. Today, IAMs are increasingly needing to be improved to suit analysis at the regional, national, or subnational levels, especially since the shift of focus of the Paris Agreement from global action to bottom-up initiatives and national mitigation policies [24]. An example of IAM adaptations to incorporate specific characteristics is the new single-region model—DEMETER-CCPE (previously a global IAM), which addresses regional climate policies from the perspective of cost–benefit efficiency [25]. The current diversity of IAM reflects different perspectives of analysis supporting climate policy decisions, such as cost-effectiveness, cost–benefit efficiency, and technology abatement contribution [26][27], which are useful to estimate the cost of carbon. The main limitations pointed out for IAM (assumptions uncertainty, transparency, replicability, and information) derive from the complexity of the climate puzzle (tipping points) and the policy decision (discount rate). Their detractors call them a “black box”. The strength of these newly adapted models is the systematic exploration of model, value, and parameter uncertainties, which improves the transparency of results and is thereby more useful for subnational decision makers [22].

References

  1. NASEM. Valuing Climate Damages: Updating Estimation of the Social Cost of Carbon Dioxide; The National Academies Press: Washington, DC, USA, 2017.
  2. Nordhaus, W.D.; Yang, Z. A Regional Dynamic General-Equilibrium Model of Alternative Climate-Change Strategies. Am. Econ. Rev. 1996, 86, 741–765.
  3. Nordhaus, W.D. Economic aspects of global warming in a post-Copenhagen environment. Proc. Natl. Acad. Sci. USA 2010, 26, 11721–11726.
  4. Nordhaus, W.D. Rolling the ‘DICE’: An Optimal Transition Path for Controlling Greenhouse Gases. Resour. Energy Econ. 1993, 15, 27–50.
  5. Wang, P.; Deng, X.; Zhou, H.; Yu, S. Estimates of the social cost of carbon: A review based on meta-analysis. J. Clean. Prod. 2018, 209, 1494–1507.
  6. Pindyck, R.S. The social cost of carbon revisited. J. Environ. Econ. Manag. 2019, 94, 140–160.
  7. Pindyck, R.S. Coase Lecture-Taxes, Targets and the Social Cost of Carbon. Economica 2017, 84, 345–364.
  8. Tian, L.; Ye, Q.; Zhen, Z. A new assessment model of social cost of carbon and its situation analysis in China. J. Clean. Prod. 2018, 211, 1434–1443.
  9. Ricke, K.; Drouet, L.; Caldeira, K.; Tavoni, M. Country-level social cost of carbon. Nat. Clim. Chang. 2018, 8, 895–900.
  10. Tol, l.R.S. A social cost of carbon for (almost) every country. Energy Econ. 2019, 83, 555–566.
  11. Snyder, B.F. Beyond the social cost of carbon: Negative emission technologies as a means for biophysically setting the price of carbon. Ambio 2019, 49, 1567–1580.
  12. IPCC. Global Warming of 1.5 °C. An IPCC Special Report on the Impacts of Global Warming of 1.5 °C Above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to Eradicate Poverty; Masson-Delmotte, V., Zhai, P., Pörtner, H.-O., Roberts, D., Skea, J., Shukla, P.R., Pirani, A., Moufouma-Okia, W., Péan, C., Pidcock, R., Eds.; IPPC: Geneva, Switzerland, 2018.
  13. Pezzey, J.C.V. Why the social cost of carbon will always be disputed. Wiley Interdiscip. Rev. Clim. Chang. 2018, 10, e558.
  14. Kaufman, N.; Barron, A.R.; Krawczyk, W.; Marsters, P.; McJeon, H. A near-term to net zero alternative to the social cost of carbon for setting carbon prices. Nat. Clim. Chang. 2020, 10, 1010–1014.
  15. Stern, N.; Stiglitz, J.E. The Social Cost of Carbon, Risk, Distribution, Market Failures: An Alternative Approach; NBER Working Paper; National Bureau of Economic Research: Cambridge, MA, USA, 2021.
  16. Van den Bijgaart, I.; Gerlagh, R.; Liski, M. A simple formula for the social cost of carbon. J. Environ. Econ. Manag. 2016, 77, 75–94.
  17. Craven, W.J. The Social Cost of Carbon. In Beyond One Health: From Recognition to Results; Wiley: Hoboken, NJ, USA, 2018; pp. 283–291.
  18. Best, R.; Burke, P.J.; Jotzo, F. Carbon Pricing Efficacy: Cross-Country Evidence. Environ. Resour. Econ. 2020, 77, 69–94.
  19. Green, J.F. Does carbon pricing reduce emissions? A review of ex-post analyses. Environ. Res. Lett. 2021, 16, 043004.
  20. Lilliestam, J.; Patt, A.; Bersalli, G. The effect of carbon pricing on technological change for full energy decarbonization: A review of empirical ex-post evidence. WIREs Clim. Chang. 2020, 12.
  21. Ibrahim, N.; Kennedy, C. A Methodology for Constructing Marginal Abatement Cost Curves for Climate Action in Cities. Energies 2016, 9, 227.
  22. Weyant, J. Some Contributions of Integrated Assessment Models of Global Climate Change. Rev. Environ. Econ. Policy 2022, 11, 115–137.
  23. Dowlatabadi, H. Integrated assessment models of climate change: An incomplete overview. Energy Policy 1995, 23, 289–296.
  24. Robertson, S. Transparency, trust, and integrated assessment models: An ethical consideration for the Intergovernmental Panel on Climate Change. WIREs Clim. Chang. 2020, 12, e679.
  25. Peng, P.; Zhu, L.; Fan, Y. Performance evaluation of climate policies in China: A study based on an integrated assessment model. J. Clean. Prod. 2017, 164, 1068–1080.
  26. Kojima, S.; Asakawa, K. Expectations for carbon pricing in Japan in the global climate policy context. In Economics, Law, and Institutions in Asia Pacific; Springer: Singapore, 2021; pp. 1–21.
  27. World Bank. State and Trends of Carbon Pricing 2021; World Bank: Washington, DC, USA, 2021.
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