英文摘要: | The China–Russia gas deal will play an important role in reducing greenhouse-gas emissions and air pollution in China.
China is the world's largest greenhouse-gas emitter and is also facing severe air pollution. In response, China is transforming its energy sector to be more efficient and cleaner. On 21 May 2014, China and Russia finally, after 10 years of negotiations, signed a historic gas deal that will provide 38 billion m3 of natural gas per year to China for 30 years starting in 2018. The deal is an important milestone for improving Chinese energy structure. It will account for 16–29% of natural gas imports and will reduce coal usage by 50 million tons yr−1. This will mean 46 million tons yr−1 less CO2 emissions, which is comparable to the 2020 CO2 reductions targets of many individual developed countries. Moreover, it will reduce the emissions of SO2, a major air pollutant, by 1.11 million tons yr−1 (equivalent to 5.4% of 2011 emissions in China). The rippling environmental effects of the deal open the door to broader cooperation between China and Russia, and exemplify the significance of cross-boundary energy treaties in mitigating climate change and air pollution. As the largest developing country, China has achieved spectacular economic development in the past three decades, propelled by increasing energy consumption. China's energy consumption accounted for 22% of global primary energy consumption in 20121 and 28% of global CO2 emissions in 20112. China is especially dependent on coal for its primary source of energy, burning 50% of the global coal consumed in 20121. Enormous coal consumption is largely responsible for high levels of air pollution in China. In 2013, 92% of Chinese cities failed to meet national ambient air-quality standards, and three major megalopolises (that is, the Yangtze River Delta, Pearl River Delta and Beijing–Tianjin–Hebei) suffered more than 100 days with PM2.5 (particles with an aerodynamic diameter less than 2.5 μm) concentrations at least twice the World Health Organization maximum exposure guidelines3. Hence, China has pledged to optimize its energy structure by reducing coal consumption. In 2009, China's State Council announced that the country will cut the carbon intensity — carbon emissions per unit of gross domestic product (GDP) — by 40–45% from 2005 levels by 2020, and this target is included in the long-term planning of China's socio-economic development. Last September, China's State Council released an Airborne Pollution Prevention and Control Action Plan pledging the Chinese government to make significant reductions in coal consumption. The plan details actions needed at the provincial level and includes ambitious coal consumption caps and specific responsibilities for named individuals. The huge challenge has been how to replace coal with alternative energy in China. The China–Russia gas deal is therefore expected to play a critical role in transforming the energy consumption structure of China for the next 30 years. However, its impacts on climate change mitigation and air pollution are unknown.
On 21 May 2014, Gazprom and the China National Petroleum Corporation signed a 30-year contract stipulating gas supplies of 38 billion m3 yr−1 of natural gas from Russia to China's populous northeast region. Gazprom will start pre-developing the gas deposit in the Chayandinskoye field, constructing the first string of the Power of Siberia gas transmission system and creating gas processing facilities in the Amur Region in 2015. Gas production from the Chayandinskoye field will begin in late 2018. Infrastructure investment from both sides will amount to more than US$70 billion and become the world's largest construction project, with Russia providing US$55 billion upfront and China US$22 billion for pipelines on their respective territories.
Coal accounts for the vast majority (66–71%) of China's total energy consumption with oil in second place (18–22%), and natural gas (2–5%) and renewable energy (6–9%) accounting for relatively modest shares (Fig. 1; ref. 4). Emissions of CO2 and SO2 from coal burning are, respectively, 70% and 130% more than those of natural gas5. The Chinese economic reliance on coal, along with its high emissions factors, explains why China's greenhouse-gas emissions are proportionately high.
- British Petroleum BP Statistical Review of World Energy 2014 (BP, 2014); www.bp.com/statisticalreview
- Peters, G. P. et al. Nature Clim. Change 3, 4–6 (2012).
- Greenpeace Dangerous Breathing: PM2.5, Measuring the Human Health and Economic Impacts on China's Largest Cities (Greenpeace, 2013); http://go.nature.com/ws72ju
- National Bureau of Statistics of the People's Republic of China China Energy Statistical Yearbook (China Statistics Press, 2001–2013).
- US Environmental Protection Agency Compilation of Air Pollutant Emission Factors (EPA, 1995); www.epa.gov/ttn/chief/ap42
- United Nations Framework Convention on Climate Change Quantified Economy-Wide Emission Reduction Targets by Developed Country Parties to the Convention: Assumptions, Conditions, Commonalities and Differences in Approaches and Comparison of the Level of Emission Reduction Efforts FCCC/TP/2012/5 (UNFCCC, 2012); http://unfccc.int/resource/docs/2012/tp/05.pdf
- World Bank Cost of Pollution in China: Economic Estimates of Physical Damages (World Bank, 2007).
- International Energy Agency World Energy Outlook 2012 (IEA, 2013); www.worldenergyoutlook.org/publications/weo-2012/
- Tu, H. & Liu, C. Coal Quality Tech. 2, 54–60 (2014).
- Wei, T. et al. Proc. Natl Acad. Sci. USA 109, 12911–12915 (2012).
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We greatly appreciate insightful comments and support from D. Qin and Y. Liu. This study was supported by the National Key Program for Global Change Research of China (2010CB950504), the State Key Program of National Natural Science of China (41330527) and the Fund for Creative Research Groups of National Natural Science Foundation of China (41321001).
Affiliations
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State Key Laboratory of Earth Surface Processes and Resource Ecology, Beijing Normal University, Beijing 100875/Zhuhai 519087, China
- Wenjie Dong,
- Wenping Yuan,
- Peijun Shi &
- Jieming Chou
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State Key Laboratory of Cryospheric Sciences, Cold and Arid Regions Environmental and Engineering Research Institute, CAS, Lanzhou 730000, China
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State Engineering Laboratory of Southern Forestry Applied Ecology and Technology, Central South University of Forestry and Technology, Changsha, Hunan 410004, China
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College of Global Change and Earth System Science, Beijing Normal University, Beijing 100875, China
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Energy Research Institute, National Development and Reform Commission, Beijing 100038, China
- Shengbo Feng &
- Kejun Jiang
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