ASSESSING THE IMPACTS OF ELECTRIC VEHICLES ON REGIONAL AIR QUALITY, PUBLIC HEALTH AND SOCIAL WELFARE IN CHINA Ou Xunmin, Tsinghua Univ, Phone +86 13910731708, E-mail: [email protected] Zhang Xu, Tsinghua Univ, Phone +86 13811268799, E-mail: [email protected] Yang Xi, Tsinghua Univ, Phone +86 18910602467, E-mail: [email protected] Zhang Xiliang, Tsinghua Univ, Phone +86 13911261226, E-mail: [email protected] Overview As an efficient measure to control oil consumption from transport sector, reduce carbon emissions and pollutant emissions, the development and expansion of electric vehicles (EVs) has been driving more and more concerns in China. This study conducts the integrated assessment of developing EVs in major regions and analyzes the comprehensive impacts on energy consumption, pollutant emissions, air quality, public health and social welfare using the China Regional Energy Emissions Air-quality Climate Health Model model. The emissions abatement effects of EV development goals on transport sector in 2030 in Jing-Jin-Ji (Beijing, Tianjin, Hebei), YRD (Yangtze River Delta, Shanghai, Jiangsu, Zhejiang) and PRD (Pearl River Delta, Guangdong) are well identified. Then we investigate the impacts of expanding EVs on improving regional air quality, public health and social welfare effects in the selected regions. The paper is organised as follows: After the introduction the second section gives a detailed description about the REACH comprehensive evaluation model and CREM-HE model which is extended from the standard version of CREM model using for health effects analysing. The third section addresses the data and assumptions, especially the provincial vehicle population and EVs development goal data. Results and discussion are provided in the section four and conclusions are given in the last section. Methods As Figure 1 shows, REACH Model is an advanced self-consistent integrated assessment model with the ability to capture the comprehensive impact of energy, environment and climate policy and to reflect the policy cost and benefit. REACH Model incorporates the energy and economy model, emission inventory model, atmospheric chemistry transport model and health effects evaluation model to implement the interdisciplinary and multi-system integration. REACH Model can be applied for policy cost-benefit analysis in the self-consistent framework by representing the provincial details of energy and economy systems and the spatial distribution information including emissions inventory and population to improve the spatial resolution. Figure 1. The theoretical framework of REACH model. The REACH model integrates the China Regional Energy-economic model (C-REM) used for energy and climate policy analysis with air quality impacts modeling system and the China-specific health effect module. As the cornerstone of the REACH, the C-REM is a multi-regional, multi-sector, computable general equilibrium (CGE) model used to analyze the impacts of existing and proposed energy and climate polices on technology, the environment and the economy. The C-REM describes thirty Chinese provinces individually with a consistent representation of energy markets, as well as detailed accounts of regional production and bilateral trade. The greatest merit of the REACH model is that it explicitly represents the pollution-health linkage within a larger economic system, and reduces the possibility of underestimation—the main limitation of conventional static approaches by developing the CREM-Health Effect Module (CREM-HE). For the purpose of reflecting the direct and indirect effects of air pollution on the health of the residents, we improved the traditional social accounting matrix(SAM) by adding in a production sector and a leisure time consumption sector in CREM-HE for responding to air pollution health services. On the basis of the above, we described the exposure-response functions of four chronic exposure deaths and five acute exposures to health outcomes using the latest epidemiological study of the health effects of air pollution, establishing correspondencse from the concentration to the incidence or death cases. Results Compared with no EV situation in 2030, the total emissions of NOX, PM2.5, BC and OC decrease by 7.9%(8.5%, 8.0%), 7.5%(8.3%, 8.2%), 7.1%(7.8%, 7.7%) and 13.2%(14.3%, 14.3%) in JJJ (YRD, PRD) with the EVs development goals are achieved. The average population weighted concentration of PM2.5 of JJJ, YRD and PRD reduces up to 5.3ug /m3, 4.8ug /m3 and 2.0ug /m3, respectively, with the EVs development in 2030. The accelerating popularization of EVs yields substantial public health benefits for selected regions, resulting in the reduction of excess mortality cases: the cumulative avoided mortality cases in JJJ, YRD and PRD reaches up to 50, 60 and 20 thousand from 2015 to 2030. Notably, provinces either facing severe air pollution or enhancing popularization of EV can enjoy more public health benefits. Conclusions The development and expansion of electric vehicles will be an efficient measure to reduce carbon emissions and pollutant emissions in transport sector in studied China’s major regions. The accelerating popularization of EV yields substantial public health benefits for selected regions, resulting in the reduction of excess mortality and morbidity cases. To some extent, the co-benefits of developing EVs can offset the policy costs, offering a new perspective to broaden the EVs consumer market. References [1] Zhang Xu. Development and Application of Regional Energy Emission Air-quality Climate Health Model(REACH) [D]. Tsinghua University, 2016. [2] Zhang D, Rausch S, Karplus V J, et al. Quantifying regional economic impacts of CO2 intensity targets in China. Energy Economics, 2013, 40: 687-701. [3] Zhang Da. Development and Application of China Regional Energy Model(C-REM) [D]. Tsinghua University, 2014. [4] Nam K, Selin N E, Reilly J M, et al. Measuring welfare loss caused by air pollution in Europe: A CGE analysis. Energy Policy, 2010, 38(9): 5059-5071. [5] Matus K, Nam K, Selin N E, et al. Health damages from air pollution in China. Global Environmental Change—Human and Policy Dimensions, 2012,22(1): 55-66. 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