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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front Envir Sci Eng    2012, Vol. 6 Issue (6) : 849-859    https://doi.org/10.1007/s11783-012-0432-9
RESEARCH ARTICLE
An assessment of China-Japan-Korea Free Trade Agreement’s economic and environmental impacts on China
Zhaoyang LIU1, Xianqiang MAO1(), Wei TANG1, Tao HU2, Peng SONG1
1. School of Environment, Beijing Normal University, Beijing 100875, China; 2. Policy Research Center of Environment and Economy, Ministry of Environmental Protection, Beijing 100029, China
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Abstract

Recently, China, Japan, and the Republic of Korea (Korea) are conducting a government-commissioned feasibility study on the Free Trade Agreement among the three countries (CJKFTA) to form a regional free trade zone in East Asia. Considering that freer trade can cause unexpected impact on domestic environment, there is a need to evaluate the environmental impact of such a trade policy. This move should be made to help negotiators understand and pay more attention to environmental issues during CJKFTA negotiations, and to help lobby with the government to carry out appropriate policy instruments for adaptation or mitigation. Following the Chain Reaction Assessment Method that integrates and links the elements of trade, production, and environment, the present research aims to quantitatively assess CJKFTA’s possible impact on China’s environment. This is done by estimating the variations of China’s major conventional pollutants and greenhouse gases (GHGs) emission in two policy scenarios to represent CJKFTA’s scale and composition effects on China’s environment. Estimating the variations is based on a static Computable General Equilibrium model, working with Global Trade Analysis Project (GTAP) 7 database and China’s energy-environment statistics. Based on these assessments, CJKFTA is predicted to lead to notable environmental impact, including increased emissions of agricultural total nitrogen, agricultural total phosphorus, chemical oxygen demand, and GHGs. On the other hand, decreased emissions of industrial SO2 and dust are also expected to happen. Suitable policies need to be made to combat negative effects and amplify positive ones, while aiming at a more sustainable regional freer trade system.

Keywords Free Trade Agreement      Strategic Environmental Assessment      Chain Reaction Assessment Method      Computable General Equilibrium model      Global Trade Analysis Project     
Corresponding Author(s): MAO Xianqiang,Email:maoxq@bnu.edu.cn   
Issue Date: 01 December 2012
 Cite this article:   
Zhaoyang LIU,Xianqiang MAO,Wei TANG, et al. An assessment of China-Japan-Korea Free Trade Agreement’s economic and environmental impacts on China[J]. Front Envir Sci Eng, 2012, 6(6): 849-859.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-012-0432-9
https://academic.hep.com.cn/fese/EN/Y2012/V6/I6/849
Fig.1  CRAM
regionChina (CHN), Japan (JPN), Korea (KOR), rest of the world (ROW)
sectorgrain crop (GRC), other crop (OTC), livestock and poultry (LPR), forestry (FRS), fishing (FSH), coal (COL), crude oil (CRU), gas (GAS), other minerals (OMN), food (FOD), beverage and tobacco (B_T), textiles (TEX), apparels (WAP), leather product (LEA), wood product (LUM), paper product and publishing (PPP), petroleum and coal product (REF), chemical rubber plastics (CRP), non-mineral product (NMM), iron and steel (I_S), non-ferrous metal (NFM), metal product (FMP), transport equipment (TRE), electronic equipment (ELE), machinery (OME), other manufactures (OMF), electricity (ELC), water (WTR), service (SEV)
Tab.1  Region and sector abbreviations in the CGE model
policy scenariocommodityservice
full liberalization scenarioall tariff and quota eliminatedall barrier eliminated
GTA protection scenario(grains, textile and apparel protection)tariff on grains, textile and apparel product unchanged; other tariff eliminated; all quota eliminatedall barrier eliminated
Tab.2  CJKFTA policy scenarios in this research
policy scenariosChina’s exportsChina’s imports
to Japanto Koreafrom Japanfrom Korea
full liberalization scenario10.7238.1734.6235.91
GTA protection scenario5.0314.6214.2416.52
Tab.3  Variation rates of china’s exports and imports in two policy scenarios/%
sectorfull liberalization scenarioGTA protection scenariosectorfull liberalization scenarioGTA protection scenario
WAP8.62-0.30ELC0.11-0.33
GRC7.681.72FRS0.01-0.26
FOD6.896.90REF-0.40-0.67
LEA3.833.89FMP-0.48-0.46
OTC2.772.18COL-0.51-0.59
ELE2.663.11OMF-0.57-0.74
TEX2.34-0.55OMN-0.70-0.65
FSH1.240.90CRP-0.98-1.20
B_T1.160.26NFM-1.21-0.72
LPR1.110.62I_S-1.27-1.26
WTR0.680.03OME-1.45-1.30
SEV0.520.11GAS-2.06-1.37
PPP0.27-0.11CRU-3.02-1.83
LUM0.140.10TRE-3.40-3.48
NMM0.13-0.13
Tab.4  Variation rates of production sectors’ outputs in china/%
policy scenariosvariation rates of real GDP/%EV/(million USD)
ChinaJapanKoreaChinaJapanKorea
full liberalization scenario0.540.040.509093.507886.764078.73
GTA protection scenario0.200.030.27699.507886.763059.05
Tab.5  CJKFTA’s impacts on macro-economy for the three countries
Fig.2  Variations of pollutant emissions in “full liberalization scenario” and “GTA protection scenario”
policy scenariosGHGs emission (CO2 equivalent) by different sources
energy combustionagricultural processindustrial processtotal
full liberalization scenario0.044.40-0.700.83
GTA protection scenario-0.361.20-0.90-0.10
Tab.6  Variation rates of GHGs emission in China/%
policy scenariosCODindustrial SO2GHGs/(CO2 equivalent)
full liberalization scenario0.57-0.560.29
GTA protection scenario0.43-0.57-0.30
Tab.7  Variation rates of emission intensity (emissions per unit GDP) index of 3 pollutants under different scenarios in China/%
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