globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2377
论文题名:
China's hydrofluorocarbon challenge
作者: Junjie Zhang
刊名: Nature Climate Change
ISSN: 1758-1115X
EISSN: 1758-7235
出版年: 2014-10-29
卷: Volume:4, 页码:Pages:943;945 (2014)
语种: 英语
英文关键词: Climate-change policy
英文摘要:

China should take more active participation in a prospective agreement on the global phase-down of hydrofluorocarbons.

China has recently agreed to work towards limiting the production and consumption of the climate-damaging hydrofluorocarbons (HFCs). In the scenario of HFC regulation proposed by the North American countries, China has to reduce its annual growth rate of HFC emissions from 40% in 2005–2009 to 13% in 2010–2018. Although Chinese leaders face obstruction from the domestic industrial lobbies, we argue that a phase-down of HFCs is aligned with China's self-interest while contributing to global climate mitigation.

HFCs are used as replacements for ozone-depleting substances; however, many of them are potent greenhouse gases1. Owing to the rapid growth of demand for air conditioning and refrigeration, the use and release of HFCs, and hence their contribution to climate forcing, are projected to increase significantly under the business-as-usual scenario2. The situation has been exacerbated by the accelerated phase-out of hydrochlorofluorocarbons (HCFCs) in accordance with the 2007 Montreal Protocol3.

China is a major HFC producer and consumer. From 2005 to 2010, its HFC production tripled to about 180 thousand metric tons. On a global-warming potential (GWP)-weighted basis, China's HFC production in 2010 that would eventually be emitted into the atmosphere was 230 million metric tons (MMT) of carbon dioxide equivalent (MMT CO2e), of which 150 MMT CO2e was for domestic HFC consumption. In comparison, China's fossil-fuel CO2 emissions have grown 38% since 2005, hitting 7.03 billion metric tons in 2010 (ref. 4). Although HFC emissions are still small compared with those from energy use, they are increasing much more rapidly.

China only recently shifted its stance by joining the United States and other countries in finding ways to limit HFCs. In the 2013 US–China Sunnylands Summit, presidents Obama and Xi signed a landmark agreement on working together to cut HFC consumption and production. This commitment was confirmed again later in the St Petersburg's G20 meeting. These moves have been widely applauded as a positive step towards implementing a meaningful HFC agreement to combat global climate change.

Although the Chinese top leadership has agreed to limit HFCs, it is not yet clear how the proposal will be implemented or what its impact on the nation's HFC industry is likely to be. To project China's degree of participation, it is therefore necessary to understand the dynamics of the HFC industry.

After a decade of rapid growth, China has become one of the most important players in the production and use of HFCs. Among the 11 categories of HFCs produced in China, data are available for the eight most commonly used substances: HFC-32, HFC-125, HFC-134a, HFC-143a, HFC-152a, HFC-227ea, HFC-236fa and HFC-245fa. The omitted three substances, HFC-23 (as substitute for ozone-depleting substances), HFC-161, and HFC-365mfc, account for only a small share of HFC production. In addition, HFC-23 by-product emissions are discussed separately because of the different generation and abatement processes. China's HFC production and consumption on a GWP-weighted basis in 2005–2009 is shown in Fig. 1.

Figure 1: Carbon dioxide equivalent (CO2e) emissions of HFC production and consumption in China (2005–2009).
Carbon dioxide equivalent (CO2e) emissions of HFC production and consumption in China (2005-2009).

The calculations are based on the data in Supplementary Tables 1 and 2. As HFC data reporting is not required by either the United Nations Framework Convention on Climate Change or the Montreal Protocol, data were collected mainly from industrial surveys and supplemented with data from international organizations, government reports, trade associations and firm disclosures. The 100-yr global warming potential was used to convert HFC emissions to CO2e.

To preserve the climate benefits of the ozone treaty, the United States, Canada and Mexico have proposed since 2009 to use the Montreal Protocol to control climate-damaging HFCs5. As of 2013, the so-called North American Proposal (NAP) has gained support from 112 countries, including major emerging economies such as China and India6. As the proposal is likely to form the foundation of the future HFC agreement, we analyse its implication for China's HFC emissions.

Considering data constraints, NAP suggests to use HCFC activities to calculate HFC production and consumption baselines for those parties that are regarded as developing countries in the Montreal Protocol (referred to as Article 5 parties). In the base years (2008–2010), China's average annual HCFC production was 681 MMT CO2e and consumption was 443 MMT CO2e. HCFC-22 accounts for about 80% in both production and consumption. The 2013 NAP suggests that the HFC baseline is 90% of the average HCFC production and consumption in the base years. Therefore, China's HFC production baseline is 613 MMT CO2e and the consumption baseline is 398 MMT CO2e. China's HFC cap under NAP is illustrated in Fig. 2.

Figure 2: China's HFC reduction steps under the 2013 North American HFC amendment proposal.
China's HFC reduction steps under the 2013 North American HFC amendment proposal.

The calculation is based on Supplementary Tables 3,4,5. The proposed baseline and reduction steps were determined on the basis of global warming potential instead of ozone-depleting potential. The percentage of reduction is applicable to the Article 5 countries.

HFC-23 is one of the most potent greenhouse gases with a 100 yr GWP of 14,800. It is of very limited direct use and its emissions mainly come from HCFC-22 production lines. As the world's largest producer of HCFC-22, China generated about 182 MMT CO2e HFC-23 as a by-product in 20107. Destruction of HFC-23 has been subsidized by the Kyoto Protocol's Clean Development Mechanism (CDM). China has dominated the CDM activities with 11 registered HFC-23 projects, eliminating 66 MMT CO2e per year.

HFC-23 has been a controversial issue since the start of the CDM8. One argument is that HFC-23 incineration projects are being overcompensated. This is a natural outcome of a competitive carbon market: every unit of emissions reduction has the same price regardless of its source of abatement. Although HFC-23 incineration is much cheaper than switching to renewable energy, their carbon credits are equally valuable.

The deeper concern is that the lucrative business opportunities could create a perverse incentive for chemical companies to expand HFC-23 production and increase overall emissions. This is a common problem for a baseline-and-credit programme like the CDM that does not have emissions caps in developing countries9.

HFC-23 mitigation is unlikely to continue under the CDM regime. Under NAP, the HFC-23 by-product emissions controls that are not registered as CDM projects will be eligible for funding under the Montreal Protocol's Multilateral Fund. The rate of subsidy has not been determined. If HFC-23 abatement is only compensated by its cost, this would imply a huge discount compared with the price of carbon credit.

The recent diplomatic breakthroughs on HFCs have important implications for climate talks. On the one hand, given the sluggish progress of international climate negotiations, a global phase-down of HFCs reduces climate risks, buying time for the formation of a comprehensive climate treaty on CO2 emissions10. On the other hand, top emitters have achieved some success in exploring alternative platforms for climate change diplomacy outside the United Nations Framework Convention on Climate Change11. The more focused dialogues, such as the US–China bilateral talk and the G20 forum, have the potential to complement the unwieldy United Nations-led process.

However, China's participation in a new HFC agreement still faces many obstacles. For the fluorine chemical industry, although NAP allows China to increase production up to 2018, the HFC production lines have to retire gradually after 2025. As they lack indigenous technologies, domestic chemical companies are reluctant to make early moves. For the air conditioning and refrigeration industry, low-GWP alternatives are generally more expensive, which raises concern that the manufacturing sector may become less competitive. For the HFC-23 by-product emissions controls, the rate of subsidy of the Multilateral Fund is likely to be much lower than that of the CDM carbon market. The HCFC-22 production facilities have less incentive to capture and destroy HFC-23 under the Montreal Protocol.

We address the above concerns with the following points. First, the Multilateral Fund can assist in financing the conversion of the existing manufacturing processes, technology transfer and capacity building. Second, most HFC production capacity is flexible enough to produce non-HFC chemicals, which lowers the cost of switching. Third, whether or not China joins in an HFC agreement, developed countries' embargo of HFCs will eventually eliminate the international demand for China's HFC exports. Fourth, the sooner the domestic firms start to develop low-GWP substitutes, the better the chance they will avoid being locked into a high-GWP HFC production and consumption economy. Last, but not least, the remarkably generous subsidy for HFC-23 incineration by carbon emissions reduction credits is not sustainable, which has already been addressed by the CDM executive board.

Reducing HFC emissions is a cost-effective option for China to contribute to the global climate target that limits temperature increase to 2 °C above pre-industrial levels. A study shows that China is unlikely to achieve the Copenhagen commitment to slash its carbon intensity by 40–45% by 2020 relative to the 2005 level without further mitigation effort4. A phase-down of HFCs is an economically viable way of compliance as it affects a small number of sectors with moderate costs. In addition, switching to some cooling and insulation technologies without refrigerants ('not-in-kind' alternatives) can reduce not only HFCs, but also CO2 emissions from energy consumption.

Eliminating HFCs is also associated with political benefits. As the world's top greenhouse gas emitter, China has been under mounting pressure in international climate negotiations. Although China has taken domestic actions to slow down emissions growth, it is questioned frequently for its incongruous international commitment. An active participation in the phase-down of HFCs will alleviate China's diplomatic pressure on climate change. Furthermore, while China and the United States are competing on many fronts, HFC phase-down can be a promising area of collaboration for both countries to build mutual political trust and improve diplomatic relations.

  1. Velders, G. J. M. et al. Science 335, 922923 (2012).
  2. United Nations Environment Programme HFCs: A Critical Link in Protecting Climate and the Ozone Layer (UNEP, 2011); http://www.unep.org/dewa/Portals/67/pdf/HFC_report.pdf
  3. Velders, G. J. M., Fahey, D. W., Daniel, J. S., McFarland, M. & Andersen, S. O. Proc. Natl Acad. Sci. USA 106, 1094910954 (2009).
  4. Yang, Y., Zhang, J. & Wang, C. Is China on Track to Comply with its 2020 Copenhagen Carbon Intensity Commitment? (UC San Diego, 2014); www.escholarship.org/uc/item/1r5251g8
  5. United Nations Environment Programme Proposed Amendment to the Montreal Protocol Submitted by Canada, Mexico and the United States of America UNEP/OzL.Pro.WG.1/33/3 (UNEP, 2013); http://go.nature.com/C6nghj
  6. Institute for Governance and Sustainable Development Support for Montreal Protocol Amendment Grows with Commitments by Leaders at the Highest Levels of Government (IGSD, 2013); http://www.igsd.org/news/documents/OzoNewsarticle.pdf
  7. Lin, H., Cui, Y-L. & Yang, L-R. Adv. Clim. Change Res. 4, 260266 (2013).
  8. Wara, M. Nature 445, 595596 (2007).
  9. Zhang, J. & Wang, C. J. Environ. Econ. Manag. 62, 140154 (2011).
  10. Xu, Y., Zaelke, D., Velders, G. J. M. & Ramanathan, V. Atmos. Chem. Phys. 13, 60836089 (2013).
  11. Bi, J. et al. Glob. Environ. Change 24, 24 (2014).

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This study is supported by the National Natural Science Foundation of China (NO.71273153). We thank J. Lin for excellent research assistance.

Affiliations

  1. Junjie Zhang is at the School of International Relations and Pacific Studies, University of California, San Diego, 9500 Gilman Drive #0519, La Jolla, California 92093-0519, USA

  2. Can Wang is at the School of Environment and Center for Earth System Science, Tsinghua University, Beijing 100084, China

PDF files

  1. Supplementary Information (125 KB)

    Main HFCs produced in China

URL: http://www.nature.com/nclimate/journal/v4/n11/full/nclimate2377.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/4943
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气候变化与战略

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Junjie Zhang. China's hydrofluorocarbon challenge[J]. Nature Climate Change,2014-10-29,Volume:4:Pages:943;945 (2014).
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