globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2102
论文题名:
Integrating emissions transfers into policy-making
作者: Marco Springmann
刊名: Nature Climate Change
ISSN: 1758-1437X
EISSN: 1758-7557
出版年: 2014-01-26
卷: Volume:4, 页码:Pages:177;181 (2014)
语种: 英语
英文关键词: Politics ; Energy modelling ; Economics ; Climate-change mitigation
英文摘要:

Net emissions transfers via international trade from developing to developed countries have increased fourfold in the past two decades—from 0.4 GtCO2 in 1990 to 1.6 GtCO2 in 20081. Consumption of goods and services in developed countries is one of the main driving forces of those emissions transfers2, 3. Therefore several proposals have been made to assign the responsibility for those emissions to the beneficiary, that is, to the consumer4, 5, 6. Although consumption-based analyses have become popular7, 8, 9, few proposals have been made for integrating emissions transfers into actual policy making. This study advances and critically evaluates three potential policy options that could be integrated in the climate-policy framework of developed countries. An energy–economic model with global coverage is used for the analysis. I find that connecting emissions transfers to international offset responsibilities is the most promising option from an environmental and economic perspective and may provide another rationale for international climate finance. The two alternative policy options of adjusting domestic emissions targets in developed countries and of implementing carbon-related tariffs and export subsidies are found to be environmentally ineffective in the latter case and economically detrimental, especially for developing countries, in both cases.

Emission transfers provide a lens on the emissions responsibilities that are driven by the import and consumption demands of a country. They denote the balance of emissions embodied in trade, that is, the emissions embodied in exports minus those embodied in imports10. In the current landscape of subglobal climate policies, emissions transfers can undermine the stringency of domestic emissions-reduction targets as countries with emissions-reduction targets can import emissions-intensive products from non-regulating countries11. This so-called ‘weak carbon leakage’1, 2 leads to distributional changes in the burden sharing of emissions responsibilities as the importing country gives the appearance of being less polluting and the exporting country more polluting. In addition, it decreases the emissions coverage and the environmental effectiveness of existing climate policies.

Unresolved questions persist regarding the appropriate policy response in the medium term. An ideal policy response against weak carbon leakage would be to extend the regional coverage of climate policies. Efforts within the United Nations Framework Convention on Climate Change (UNFCCC) are moving into that direction, but the implementation of a new global agreement with broad coverage may not eventuate for decades. A second-best approach for the medium term could therefore be to integrate emissions transfers into existing climate policies. Using emissions transfers as a policy lever could increase the emissions coverage of subglobal climate policies and highlight the consumption-based emissions responsibilities that are currently missed in the territorial emissions accounting system.

Here I analyse three potential policy options that account for emissions transfers and incorporate consumption-based emissions responsibilities into the current climate policy framework of industrialized countries (Table 1). Those policies include adjusting domestic emissions-reduction targets for emissions transfers (DOM scenario), offsetting emissions transfers by financing emissions reductions in the emissions-exporting regions (CDF scenario), and adjusting import and export prices of goods in proportion to their carbon content, that is, extending the domestic carbon price by levying carbon tariffs on imports from non-climate regulating regions and providing export rebates for goods exported to those regions by the regulating regions (BCA scenario). Although some of those policies have been discussed before12, 13, 14, 15, 16, 17, 18, 19, 20, here I present the first consistent analysis of the environmental and economic impacts of those policy options from the perspective of international emissions transfers.

Table 1: Overview of policy scenarios.

This paper uses a multi-region, multi-sector, static computable general equilibrium model of global trade and energy use18. The model provides a comprehensive representation of price-dependent market interactions based on microeconomic theory21, 22, 23. It is based on the optimizing behaviour of economic agents, that is, consumers maximize welfare subject to budget constraints and producers combine intermediate inputs and primary factors at least cost to produce output. Energy resources are included as primary factors whose use is associated with the emission of carbon dioxide (CO2). The production, consumption and trade of goods is described by nested constant-elasticity-of-substitution cost functions which characterize substitution possibilities between inputs.

The model is calibrated to the database version 8 of the Global Trade Analysis Project28. The database includes information on bilateral trade, intermediate demand, direct and indirect taxes on imports and exports, as well as CO2 emissions from the combustion of fossil fuels for the benchmark year of 2007. For the focus of this study, I explicitly resolve four Annex I and seven non-Annex I regions, and differentiate between five energy commodities (coal, natural gas, crude oil, refined oil and electricity), energy-intensive goods, transport services, and a composite of all other goods. Energy-intensive goods include iron and steel; chemicals, including plastics and petrochemical products; non-ferrous metals, including copper and aluminium; and non-metallic minerals, including cement. The Supplementary Information provides further details on the model formulation and calibration.

I implement four policy scenarios into the energy–economic model. The main policy scenarios are a border-carbon-adjustment scenario, a domestic-target-adjustment scenario, and a clean-development finance scenario. The scenarios are implemented on top of a reference scenario, in which Annex I countries reduce their CO2 emissions by 10% below their 2007-levels. This magnitude of emissions reductions is in line with current emissions-reduction pledges submitted to the UNFCCC (ref. 29). The emissions reductions are implemented as an overall cap, which allows emissions trading among Annex I countries.

The border-carbon-adjustment scenario adjusts the pricing of carbon at Annex I countries’ borders. This includes the implementation of carbon tariffs by Annex I countries on energy-intensive imports from non-Annex I countries and export rebates in proportion to the domestic carbon price for energy-intensive goods exported from Annex I countries to non-Annex I countries. The tariff level is determined endogenously in proportion to the carbon content of imports and the price of carbon in Annex I countries. The carbon content of imports consists of all direct and indirect CO2 emissions (excluding process emissions) used for producing the goods in the country of origin plus the transportation services needed for exporting them to Annex I countries. The carbon contents are computed by a recursive diagonalization algorithm described in ref 18. The Supplementary Information considers alternative BCA specifications on the use of carbon-tariff revenues and tax incidence.

The DOM adjusts Annex I countries’ emissions-reduction targets for energy-intensive emissions transfers from non-Annex I countries. The emissions embodied in net imports from a specific non-Annex country are subtracted from the importing Annex I country’s emissions target. This results in more stringent targets for countries with net imports of embodied emissions. The embodied emissions are netted between the trading partners, but not across them, that is, net bilateral imports of embodied emissions from one non-Annex I country are not offset by net bilateral exports of embodied emissions to another non-Annex I country. This corresponds to this study’s focus on the bilateral consumption-based emissions responsibilities of Annex I countries in the climate-policy framework of those countries.

The CDF allows Annex I countries to offset their consumption-based emissions responsibilities vis-à-vis non-Annex I countries by financing clean-development projects in those countries. I use a new, microeconomically consistent modelling framework to represent clean-development investments in non-Annex I countries as a combination of sectoral output subsidies and emissions taxes30. The emissions taxes induce the adoption of more energy-efficient and more expensive production technologies, whereas the output subsidies compensate the representative firm for the increase in production costs. The funds for the clean-development investments cover the subsidy payments net of emissions-tax revenues and are deducted from the financing country’s budget balance. I focus on clean-development investments in the electricity sector, which is in line with the sectoral distribution of projects under the Clean Development Mechanism (CDM) of the Kyoto Protocol15. Also with reference to the CDM, I assume that clean-development investments are subject to transaction costs of 30% (see Supplementary Section 3.3). The magnitude of clean-development investments is iterated within the energy–economic model until the bilateral net emissions embodied in energy-intensive imports to each Annex I countries are offset. The Supplementary Information contain further details on the CDF modelling approach.

  1. Peters, G., Minx, J., Weber, C. L. & Edenhofer, O. Growth in emission transfers via international trade from 1990 to 2008. Proc. Natl Acad. Sci. USA 108, 89038908 (2011).
  2. Hertwich, E. G. & Peters, G. P. Carbon footprint of nations: A global, trade-linked analysis. Environ. Sci. Technol. 43, 64146420 (2009).
  3. Davis, S. J. & Caldeira, K. Consumption-based accounting of CO2 emissions. Proc. Natl Acad. Sci. USA 107, 56875692 (2010).
  4. Rose, A. Reducing conflict in global warming policy: The potential of equity as a unifying principle. Energy Policy 18, 927935 (1990).
  5. Munksgaard, J. & Pedersen, K. A. CO2 accounts for open economies: Producer or consumer responsibility?. Energy Policy 29, 327334 (2001).
  6. Ferng, J-J. Allocating the responsibility of CO2 over-emissions from the perspectives of benefit principle and ecological deficit. Ecol. Econ. 46, 121141 (2003).
  7. Wiedmann, T., Lenzen, M., Turner, K. & Barrett, J. Examining the global environmental impact of regional consumption activities—Part 2: Review of input–output models for the assessment of environmental impacts embodied in trade. Ecol. Econ. 61, 1526 (2007).
  8. Wiedmann, T. A review of recent multi-region input–output models used for consumption-based emission and resource accounting. Ecol. Econ. 69, 211222 (2009).
  9. Jakob, M. & Marschinski, R. Interpreting trade-related CO2 emission transfers. Nature Clim. Change 3, 1923 (2012).
  10. Muradian, R., O’Connor, M. & Martinez-Alier, J. Embodied pollution in trade: Estimating the ‘environmental load displacement’ of industrialised countries. Ecol. Econ. 41, 5167 (2002
URL: http://www.nature.com/nclimate/journal/v4/n3/full/nclimate2102.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/5257
Appears in Collections:气候变化事实与影响
科学计划与规划
气候变化与战略

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Marco Springmann. Integrating emissions transfers into policy-making[J]. Nature Climate Change,2014-01-26,Volume:4:Pages:177;181 (2014).
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