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Impact and distribution of climatic damages: a methodological proposal with a dynamic CGE model applied to global climate negotiations

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Abstract

The UNFCCC Paris Agreement, entered into force on 4 November 2016, represents a step forward in involving all countries in mitigation actions, even though it is based on a voluntary approach and lacks the active participation of some major polluting countries. The underinvestment in mitigation actions depends on market and policy failures and the absence of price signals internalizing the economic losses due to climatic damage. This contributes to underestimating potential benefits from global action. In this paper we discuss how crucial is the assessment of the vulnerability of a country to climate change in defining the threat and action strategies. A dynamic climate-economy CGE model is developed that includes a monetary evaluation of regional damages associated with climate change. By considering alternative damage profiles, results show that internalizing climatic costs might change the bargaining position of countries in climate negotiations. Consequently, damage costs should be given greater importance when defining the implementation of a global climate agreement.

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Notes

  1. Source: http://www4.unfccc.int/submissions/indc/Submission%20Pages/submissions.aspx.

  2. The GCF, discussed and approved during the COP16 held in Cancun in 2010 and officially launched the following year at COP17, is explicitly individuated as a key mechanism for international support by several developing and emerging countries in their NDCs, such as China, Gabon, Morocco, Sudan, among the others.

  3. The Climate Vulnerable Forum (CVF) is an international cooperation group founded in 2009 by the Maldives, that now includes 20 countries that face significant insecurity due to climate change.

  4. DICE (RICE) is the (regional) Dynamic Integrated model of Climate and the Economy model.

  5. These impacts are derived from specific applied models. In particular, the impact on coastal land loss due to the sea level rise is driven by results from the DIVA (Dynamic Integrated Vulnerability Assessment) model (Vafeidis et al. 2008). The ClimateCrop model (Iglesias et al. 2009, 2010) is used for changes in the average productivity of crops in agriculture sector, while data on for the energy sector, as the changes in residential energy demand due to increasing temperatures, are derived from the POLES (Prospective Outlook on Long-term Energy Systems) model (Criqui 2001; Criqui et al. 2009).

  6. An example is the CIRCLE project “Costs of Inaction and Resource Scarcity: Consequences for Long-term Economic Growth Project”, where the dynamic general equilibrium ENV-linkages model is used to express climate impacts in monetary term and links them to GDP. In this case, the impacts covered are: loss of land and capital due to sea level rise, capital damages from hurricanes, changes in crop yields, fisheries catches, labour productivity, tourism flows, health care expenditures due to diseases and heat stress and energy demand for cooling and heating.

  7. For an extensive review on sectoral impacts see Markandya et al. (2017).

  8. The included electricity generating technologies are Coal, Gas, Oil, Hydro, Wind, Solar, Nuclear and Other Base Load Power sources, while Gas, Oil, Hydro and Solar generating technologies are further divided between Base and Peak Load. All details on the aggregation choice for this GDynEP model version are reported in “Appendix”. In order to merge GDynE and GTAP-Power, it is worth mentioning that in this model version we have adopted two simplifying assumptions. First, the transmission and distribution sector for electricity is included in the service sector and it is not taken as a distinguished one. This implies that there is no technical difference between renewables and the other energy sources in the transmission of electricity. This conservative assumption is adopted because we have no region-based data on distinguished institutional and technical features for the electricity transmission and distribution. Second, given that GDynEP is not a bottom up technical model, it deserves specific exogenous behavioral parameters for each stage of the production function. By introducing the renewable electricity sector, it is necessary to add a specific substitution elasticity parameter between fossil-based and renewable electricity. Given that there is not a specific value provided in the GTAP database, we have derived it from calibrating the BAU scenario in order to have a dynamic trend in renewable electricity production up to 2050 in line with BAU provided by IEA Outlook (IEA 2015). We acknowledge that this is an extremely conservative hypothesis, especially when carbon mitigation scenarios are considered. Nonetheless, in this paper we test only the emission trading policy option without exploring the role of public support to clean technologies, and this allows taking this substitution parameter as constant. Future research lines would require specific efforts in empirically estimating substitution elasticities at least at the country level as well shaping the evolution of such parameter over time.

  9. NOAA estimates the concentration of CO2 in the atmosphere at 404.06 PPM in 2011.

  10. The stock of GHG concentrated in the atmosphere used for the calculation of the average damage cost is taken from the PPM concentration measure available from IPCC (2014) and expressed in ton of CO2-eq by applying the conversion criteria used by IPCC: 1 PPM CO2 = 2.12 Gton Carbon; 1 ton Carbon = 3.66 ton CO2; 1 PPM of CO2 rise in the atmosphere is equal to 2.12 × 3.66 Gton CO2 emission.

  11. For a comparison of alternative damage functions used in other IAM and CGE models, see Markandya et al. (2017).

  12. The Vulnerability Index measures a country’s exposure, sensitivity and adaptive capacity (components) to the negative effects of climate change. It considers six life-supporting sectors: food, water, health, ecosystem service, human habitat, and infrastructure. 36 indicators (two per component in each sector) contribute to the measure of vulnerability, obtained as a simple mean of the sector scores, which are the average scores of component indicators. Readiness measures the ability of a country’s private and public sectors to absorb investment resources and successfully apply them to reduce climate change vulnerability. Readiness includes indicators for three components (social, economic and governance indicators) not weighted equally (Economic Readiness is 50% of the readiness score while governance and social readiness are 25%).

  13. The ratio between the vulnerability and readiness indices has been normalized (min = 0; max = 2) and then it is kept constant over time, as there is not information about future projections, especially because of uncertainties with regard to readiness issues. Thus, the variation in the regional distribution of damage cost is due to variations in population dynamics data. Population data do not take into account deaths caused by climate change since the vulnerability measure provided by ND-GAIN already includes number of deaths. In particular, the health component captures a country’s vulnerability of public health to climate change, including projected change of deaths from climate change induced diseases.

  14. Although Farmer et al. (2015) emphasize the role of uncertainty in shaping the cost of climate change into IAMs, for the sake of simplicity in this work we ignore this factor that will be part of future work. By considering country vulnerability to climate change fixed over time in physical term, our modelling choice underestimates future damages that could be larger if vulnerability raises with increasing temperatures.

  15. Equation (8) provides a stylized description of how damage cost is considered into the capital stock function of GDynEP. More precisely, GDynEP adopts the same capital accumulation function structure of GDyn (Ianchovichina and McDougall 2000) in which international capital mobility is allowed. Accordingly, the cost of climate change can be considered as a negative component of the available net investments at the regional level (that derive from national and foreign savings). To this purpose, the adoption of a weak sustainability approach allows including all forms of capital (economic, natural and ecologic) into a unique total capital stock measures assuming full substitutability of different forms of capital (Hamilton 1996; Neumayer 2003). This allows treating the damage cost as a negative component of capital accumulation whatever form of capital is considered. Given that in GDynEP, economic capital (\(K_{r,t}\)) is the only form of capital that is dynamically modelled and changes over time according to market mechanisms, we have modelled the cost of climatic damage within the economic capital accumulation function.

  16. Asian developing and emerging countries have also been distinguished in Rest of South Asia and South East Asian representing, respectively, developing and emerging countries according to their level of development.

  17. See Tables 4, 5, 6 and 7 in “Appendix” for a detailed description of regional and sectoral aggregates.

  18. We acknowledge that the burden sharing adopted for the policy scenario is compatible with technological capabilities of regions but is not chosen on the basis of real policy feasibility (for instance strongly affected by the US defection). The exclusion of the US from mitigation actions would force to recalculate the burden sharing for all the other regions if the final goal is to reach anyway a 450 PPM concentration. This modelling choice will reduce comparability across scenarios selected for this specific paper. Further work could be done in the future to evaluate the effect of alternative burden sharing options.

  19. In this paper we have not modeled the relation between the value adopted for parameter α and the level of risk-aversion of the social planner since we consider a common and univocal mitigation path that is driven by the IPCC and IEA bottom up climate-energy models. In the case of mitigation efforts endogenously decided according to the risk aversion of the policy maker, the value for parameter α would also influence timing profiles for mitigation actions. We will develop this relation in our future research agenda.

  20. In order to obtain accurate results, the discount rate should be both differentiated by region and declining over time (Philibert 2003). However, in order to reduce uncertainty and facilitate the interpretability of results, we apply a single discount rate equal to 3%. This value is the most commonly used in SCC calculations and corresponds to the intermediate value applied by the US Government in its latest SCC computation (US Government 2015).

  21. More specific targets are expressed in terms of use of renewable sources, afforestation and emission intensity.

  22. Further research work on this specific issue will be part of the next agenda on modelling climatic damage in GDynEP for assessing climate policy optimality under different uncertainty conditions.

  23. We gratefully acknowledge Francesco Onufrio for inspiring us the combination of the different pictures of welfare aspects into a single graph as represented in Figs. 4 and 5.

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Acknowledgements

We acknowledge financial support received by the EU D.G. Research (research project “CECILIA2050—Choosing efficient combinations of policy instruments for low-carbon development and innovation to achieve Europe’s 2050 climate targets”, Grant agreement no. 308680), the Italian Ministry of Education, University and Research (Scientific Research Program of National Relevance 2010 on “Climate change in the Mediterranean area: scenarios, economic impacts, mitigation policies and technological innovation”), the Regione Lazio (research project SMART ENVIRONMENTS) and the Department of Economics and the Centro Rossi-Doria of Roma Tre University. We are also indebted to the research group of the National Consortium CREA-ENEA-ROMATRE for the continuous scientific support in CGE modelling. We thank Dr. Mariangela Zoli for her review and highly appreciate the comments and suggestions that contributed to improving the quality of the publication. We also thank the journal Reviewers for several suggestions that have improved the paper. Errors and omissions are of course ours alone.

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Correspondence to Valeria Costantini.

Appendix

Appendix

See Tables 3, 4, 5, 6, 7, 8 and 9.

Table 3 DARA indicators.
Table 4 ND-GAIN vulnerability indicators.
Table 5 ND-GAIN readiness indicators.
Table 6 List of GDYnEP Region aggregates
Table 7 List of GDYnEP Sector aggregates
Table 8 List of GDynEP countries and regions
Table 9 List of GDYnEP commodities and aggregates

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Costantini, V., Markandya, A., Paglialunga, E. et al. Impact and distribution of climatic damages: a methodological proposal with a dynamic CGE model applied to global climate negotiations. Econ Polit 35, 809–843 (2018). https://doi.org/10.1007/s40888-018-0129-z

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