globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2515
论文题名:
Carbon emissions due to deforestation for the production of charcoal used in Brazil’s steel industry
作者: Laura J. Sonter
刊名: Nature Climate Change
ISSN: 1758-1025X
EISSN: 1758-7145
出版年: 2015-02-09
卷: Volume:5, 页码:Pages:359;363 (2015)
语种: 英语
英文关键词: Climate-change mitigation
英文摘要:

Steel produced using coal generates 7% of global anthropogenic CO2 emissions annually1. Opportunities exist to substitute this coal with carbon-neutral charcoal sourced from plantation forests to mitigate project-scale emissions2 and obtain certified emission reduction credits under the Kyoto Protocols Clean Development Mechanism3. This mitigation strategy has been implemented in Brazil4, 5 and is one mechanism among many used globally to reduce anthropogenic CO2 emissions6; however, its potential adverse impacts have been overlooked to date. Here, we report that total CO2 emitted from Brazilian steel production doubled (91 to 182 MtCO2) and specific emissions increased (3.3 to 5.2 MtCO2 per Mt steel) between 2000 and 2007, even though the proportion of coal used declined. Infrastructure upgrades and a national plantation shortage increased industry reliance on charcoal sourced from native forests, which emits up to nine times more CO2 per tonne of steel than coal. Preventing use of native forest charcoal could have avoided 79% of the CO2 emitted from steel production between 2000 and 2007; however, doing so by increasing plantation charcoal supply is limited by socio-economic costs and risks further indirect deforestation pressures and emissions. Effective climate change mitigation in Brazils steel industry must therefore minimize all direct and indirect carbon emissions generated from steel manufacture.

Growing global demand for steel, along with requirements to mitigate anthropogenic climate change, have increased the importance of reducing CO2 emissions from steel production7, 8. One mitigation strategy is to substitute the coal used as a reducing agent in steel production with biomass charcoal9. When this charcoal is produced from plantation forests grown on non-forested land (herein, plantation charcoal), it can be considered net carbon neutral under the UNFCCC Kyoto Protocols Clean Development Mechanism (CDM) because carbon flux to the atmosphere during charcoal production and use is offset by carbon sequestration from plantation tree growth10. Substituting coal with plantation charcoal therefore mitigates CO2 emissions from steel production at the project scale2 and, when registered, can be used to offset emissions in Annex B countries, provided that plantation charcoal production is additional and does not generate indirect emissions from deforestation elsewhere11, 12.

More than half of Brazils steel is produced using charcoal13. Historically, this charcoal was mainly sourced from native forests (herein, native charcoal)13, 14, generating carbon emissions to the atmosphere from wood harvest, carbonization and charcoal use15, 16. However, the CDM provides policy and financial incentives in the form of Certified Emission Reduction (CER) credits to substitute the coal used in steel production with carbon-neutral plantation charcoal3, 10. In 2000, the first CDM project of this type established tree plantations for charcoal production on cleared and degraded land5; later projects used this plantation charcoal in place of coal to produce steel and mitigate CO2 emissions4. Despite approval of these projects as CER credits for utilization by Annex B countries, extensive charcoal production has also occurred outside the CDM framework to impact on Brazils aggregate emissions as a non-Annex B country. The size of this impact is unknown.

In this study, we analysed annual steel production trajectories in Brazil between the years 2000 and 2007. We determined the quantity of each carbon source used in steel production (that is, coal, native charcoal and plantation charcoal; Supplementary Table 1) and quantified associated CO2 emissions (Supplementary Table 3). We assumed all plantation charcoal qualified as carbon neutral under the CDM, whether or not it was produced by CDM-funded projects (<8% of plantation charcoal used in steel production4). In doing so, we assumed all plantations were planted on already cleared land (see Methods) and did not cause carbon leakage. We analysed results at the national and state level to investigate the spatial impacts of charcoal production and use in Brazil. Specifically, the state-level analysis focused on Minas Gerais, Brazils most productive and industrialized steel and plantation charcoal producer14, 17 (Supplementary Fig. 1).

We found that annual steel production in Brazil increased between 2000 and 2007 (from 28 Mt to 35 Mt; Supplementary Table 1)17 and relative coal use declined (from 50 to 46%; Fig. 1); yet annual CO2 emissions from steel production doubled (from 91 ± 10 MtCO2 to 182 ± 21 MtCO2; Fig. 2 and Supplementary Table 3). Emissions increased owing to growing industry use of native charcoal outside of CDM-funded projects (Fig. 1 and Supplementary Table 1).

Figure 1: Carbon sources used in Brazilian steel production between 2000 and 2007.
Carbon sources used in Brazilian steel production between 2000 and 2007.

Column series: Percentage of steel produced with coal, native charcoal and plantation charcoal.

Steel and carbon sources.

We compiled best available data on annual steel production and carbon sources (coal, native charcoal and plantation charcoal) used in steel production in Brazil and Minas Gerais between the years 2000 and 2007. Supplementary Table 1 contains the raw data analysed in this study and Supplementary Table 2 describes data sources, their collection methods and assumptions. The 2000–2007 time frame was chosen for data availability and relevance to the start of CDM projects and the climate change mitigation strategy of substituting coal with plantation charcoal in steel production. We also obtained steel production projections between 2015 and 2030 (Supplementary Table 2) to investigate future possible trajectories.

CO2 emissions.

We quantified annual CO2 emissions from each carbon source used in steel production using equations (1)–(7). We assumed steel production followed the blast furnace–basic oxygen furnace (BF–BOF) route, which is common in Brazil4, 30. We quantified emissions using the approved CDM assessment methodology10, which assesses both process emissions (emissions from coal and charcoal use in steel production) and upstream emissions (domestic emissions from coal and charcoal production and transportation). We assumed no wood residues or chemical volatiles were recovered during charcoal use in steel production, given these practices are not common in Brazil4. All equation variables are described in Supplementary Table 5, and equation parameters are shown in Supplementary Tables 6 and 7. Some parameters were set stochastically, using a distribution of literature-based means and standard deviations (Supplementary Table 6). For each equation below, 10,000 realizations were performed to quantify the mean and 95th percentile confidence interval to bound uncertainty in our results.

We quantified CO2 emissions from steel produced with coal with equation (1).

where CO2C is the CO2 emitted from steel produced with coal; C is the coal used in steel production; EFC is the CO2 emission factor of metallurgical coal; SC is the steel produced with coal; CS is the carbon factor of steel; 44/12 is the conversion factor of carbon to CO2; EFR is the CO2 emission factor of transporting coal by rail in Brazil; D is the distance travelled by rail from port to steel production regions in Brazil; T is the number of trips required per tonne of coal. All coal used in steel production was imported into Brazil17 and we assumed this was transported from major ports to steel production regions by rail4 (see Supplementary Fig. 1).

We quantified CO2 emissions from steel produced with native charcoal with equation (2).

where CO2NC is the CO2 emitted from steel produced with native charcoal; NC is the native charcoal used in steel production; W is the dry wood required per tonne of charcoal; YN is the wood yield per hectare of native forest, assuming all wood was harvested from a savanna forest (Supplementary Discussion 3); CAGWB is the carbon lost from live aboveground woody biomass when savanna is cleared for native charcoal production (Supplementary Table 4); SNC is the steel produced with native charcoal. Dead and belowground carbon losses were not included in our analysis. CO2 emissions from transporting charcoal were ignored, as transportation distance was unknown; however, these emissions were considered small relative to those emitted during charcoal production and use (Supplementary Discussion 9).

We quantified CO2 emissions from steel produced with plantation charcoal with equation (3).

where CO2PC is the CO2 emitted from steel produced with plantation charcoal; PC is the plantation charcoal used in steel production, which is sourced from both CDM-funded and non-CDM-funded plantation charcoal production projects; EFPC is the CO2 emission factor of plantation charcoal production, considering emissions from diesel used for tree establishment, management and harvest. As required by the CDM, all plantations were established on land cleared for at least ten years10; therefore, net carbon flux from aboveground woody biomass between plantation establishment and harvest was zero. We also assumed all non-CDM-funded projects established plantations on already cleared land. This was reasonable, given prior evidence that forests are not deforested for plantation establishment in Brazilian steel production regions21.

Additional coal/plantation charcoal.

We quantified the coal and plantation charcoal required to eliminate native charcoal used in steel production, using equations (4) and (5) respectively. We also quantified the areas required to produce the plantation charcoal used in steel production, and the additional plantation charcoal required to eliminate native charcoal used in steel production, with equations (6) and (7) respectively.

where CNC=0 is the coal required to eliminate native charcoal used in steel production; SPC is the steel produced with plantation charcoal; PCNC=0 is the plantation charcoal required to eliminate native charcoal used in steel production; A is the area required to produce plantation charcoal used in steel production; YP is the annual plantation wood yield; ANC=0 is the plantation area required to eliminate native charcoal used in steel production.

  1. Kim, Y. & Worrell, E. International comparison of CO2 emission trends in the iron and steel industry. Energy Policy 30, 827838 (2002).
  2. Fearnside, P. M. Global warming response options in Brazils forest sector: Comparison of project-level costs and benefits. Biomass Bioenergy 8, 309322 (1995).
  3. UNFCCC Kyoto Protocol to the UN Framework Convention on Climate Change (United Nations, 1997).
  4. CDM—Executive Board Project 7577: Use of Charcoal from Renewable Biomass Plantations as Reducing Agent in Pig Iron Mill in Brazil (UNFCCC, 2012).
  5. CDM—Executive Board Project 2569: Reforestation as Renewable Source of Wood Supplies for Industrial Use in Brazil (UNFCCC, 2009).
  6. IPCC in Climate Change 2014: Mitigation of Climate Change (eds Edenhofer, O. et al.) (Cambridge Univ. Press, 2014).
  7. Carpenter, A. CO2 Abatement in the Iron and Steel Industry (International Energy Agency, 2012).
  8. Gutowski, T. G., Allwood, J. M., Herrmann, C. & Sahni, S. A global assessment of manufacturing: Economic development, energy use, carbon emissions, and the potential for energy efficiency and materials recycling. Annu. Rev. Environ. Resour. 38, 81106 (2013).
  9. Steels Contribution to a Low Carbon Future (World Steel Association, 2013)
  10. CDM—Executive Board Approved Baseline and Monitoring Methodology AM0082: Use of Charcoal from Planted Renewable Biomass in the Iron Ore Reduction Process (UNFCCC, 2009).
  11. Searchinger, T. et al. Use of US croplands for biofuels increases greenhouse gases through emissions from land-use change. Science 319, 12381240 (2008).
  12. Lapola, D. M. et al. Indirect land-use changes can overcome carbon savings from biofuels in Brazil. Proc. Natl Acad. Sci. USA 107, 33883393 (2010).
  13. Anuário estatístico 2008 (Associação Mineira da Silvicultura, 2009)
URL: http://www.nature.com/nclimate/journal/v5/n4/full/nclimate2515.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/4853
Appears in Collections:气候变化事实与影响
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Laura J. Sonter. Carbon emissions due to deforestation for the production of charcoal used in Brazil’s steel industry[J]. Nature Climate Change,2015-02-09,Volume:5:Pages:359;363 (2015).
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