Target the neglected VOCs emission from iron and steel industry in China for air quality improvement

Chenglin Cai , Juexiu Li , Yi He , Jinping Jia

Front. Environ. Sci. Eng. ›› 2023, Vol. 17 ›› Issue (8) : 95

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Front. Environ. Sci. Eng. ›› 2023, Vol. 17 ›› Issue (8) : 95 DOI: 10.1007/s11783-023-1695-z
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Target the neglected VOCs emission from iron and steel industry in China for air quality improvement

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Abstract

● Haze formation in China is highly correlated with iron and steel industry.

● VOCs generated in sinter process were neglected under current emission standard.

● Co-elimination removal of sinter flue gas complex pollutants are timely needed.

Recent years have witnessed significant improvement in China’s air quality. Strict environmental protection measures have led to significant decreases in sulfur dioxide (SO2), nitrogen oxides (NOx), and particulate matter (PM) emissions since 2013. But there is no denying that the air quality in 135 cities is inferior to reaching the Ambient Air Quality Standards (GB 30952012) in 2020. In terms of temporal, geographic, and historical aspects, we have analyzed the potential connections between China’s air quality and the iron and steel industry. The non-target volatile organic compounds (VOCs) emissions from iron and steel industry, especially from the iron ore sinter process, may be an underappreciated index imposing a negative effect on the surrounding areas of China. Therefore, we appeal the authorities to pay more attention on VOCs emission from the iron and steel industry and establish new environmental standards. And different iron steel flue gas pollutants will be eliminated concurrently with the promotion and application of new technology.

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Keywords

Volatile organic compounds / Iron and steel industry / Air quality / Sinter flue gas emission

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Chenglin Cai, Juexiu Li, Yi He, Jinping Jia. Target the neglected VOCs emission from iron and steel industry in China for air quality improvement. Front. Environ. Sci. Eng., 2023, 17(8): 95 DOI:10.1007/s11783-023-1695-z

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References

[1]

Acciai C, Zhang Z, Wang F, Zhong Z, Lonati G. (2017). Characteristics and source analysis of trace elements in PM2.5 in the urban atmosphere of Wuhan in spring. Aerosol and Air Quality Research, 17(9): 2224–2234

[2]

BaiX, LiuW, WuB, LiuS, LiuX, HaoY, LiangW, Lin S, LuoL, ZhaoS, et al. (2022). Emission characteristics and inventory of volatile organic compounds from the Chinese cement industry based on field measurements. EnvironmentalPollution, 316(Pt 1): 120600

[3]

Bai Z, Winiwarter W, Klimont Z, Velthof G, Misselbrook T, Zhao Z, Jin X, Oenema O, Hu C, Ma L. (2019). Further improvement of air quality in China needs clear ammonia mitigation target. Environmental Science & Technology, 53(18): 10542–10544

[4]

Bell M L, Davis D L. (2001). Reassessment of the lethal London fog of 1952: novel indicators of acute and chronic consequences of acute exposure to air pollution. Environmental Health Perspectives, 109(Suppl 3): 389–394

[5]

BrüggemeierF J (1990). The Ruhr Basin 1850–1980: a case of large-scale environmental pollution. The Silent COUNTDOWN. Berlin: Springer-Verlag

[6]

Davidson C I. (1979). Air pollution in Pittsburgh: a historical perspective. Journal of the Air Pollution Control Association, 29(10): 1035–1041

[7]

Ding X, Li Q, Wu D, Huo Y, Liang Y, Wang H, Zhang J, Wang S, Wang T, Ye X, Chen J. (2020). Gaseous and particulate chlorine emissions from typical iron and steel industry in China. Journal of Geophysical Research. Atmospheres, 125(15): e2020JD032729

[8]

Duan W J, Lang J L, Cheng S Y, Jia J, Wang X Q. (2018). Air pollutant emission inventory from iron and steel industry in the Beijing-Tianjin-Hebei region and its impact on PM2.5. Environmental Sciences (Ruse), 39: 1445–1454

[9]

Fu H, Chen J. (2017). Formation, features and controlling strategies of severe haze-fog pollutions in China. Science of the Total Environment, 578: 121–138

[10]

Guo S, Hu M, Zamora M L, Peng J, Shang D, Zheng J, Du Z, Wu Z, Shao M, Zeng L, Molina M J, Zhang R. (2014). Elucidating severe urban haze formation in China. Proceedings of the National Academy of Sciences of the United States of America, 111(49): 17373–17378

[11]

Han T, Yao L, Liu L, Xian A, Chen H, Dong W, Chen J. (2018). Baosteel emission control significantly benefited air quality in Shanghai. Journal of Environmental Sciences (China), 71: 127–135

[12]

Hu F, Guo Y. (2021). Health impacts of air pollution in China. Frontiers of Environmental Science & Engineering, 15(4): 74

[13]

Hua W, Wu B. (2022). Atmospheric circulation anomaly over mid- and high-latitudes and its association with severe persistent haze events in Beijing. Atmospheric Research, 277: 106315

[14]

Huang R J, Zhang Y, Bozzetti C, Ho K F, Cao J J, Han Y, Daellenbach K R, Slowik J G, Platt S M, Canonaco F. . (2014). High secondary aerosol contribution to particulate pollution during haze events in China. Nature, 514(7521): 218–222

[15]

Isard W. (1948). Some locational factors in the iron and steel industry since the early nineteenth century. Journal of Political Economy, 56(3): 203–217

[16]

Jacobs E T, Burgess J L, Abbott M B. (2018). The donora smog revisited: 70 years after the event that inspired the clean air act. American Journal of Public Health, 108(S2): S85–S88

[17]

Koman P D, Mancuso P. (2017). Ozone exposure, cardiopulmonary health, and obesity: a substantive review. Chemical Research in Toxicology, 30(7): 1384–1395

[18]

Le T, Wang Y, Liu L, Yang J, Yung Y L, Li G, Seinfeld J H. (2020). Unexpected air pollution with marked emission reductions during the COVID-19 outbreak in China. Science, 369(6504): 702–706

[19]

Li J, He X, Pei B, Li X, Ying D, Wang Y, Jia J. (2019). The ignored emission of volatile organic compounds from iron ore sinter process. Journal of Environmental Sciences (China), 77: 282–290

[20]

Li S, Liu G, Zheng M, Liu W, Li J, Wang M, Li C, Chen Y. (2017). Unintentional production of persistent chlorinated and brominated organic pollutants during iron ore sintering processes. Journal of Hazardous Materials, 331: 63–70

[21]

Lin B, Wu R. (2020). Designing energy policy based on dynamic change in energy and carbon dioxide emission performance of China’s iron and steel industry. Journal of Cleaner Production, 256: 120412

[22]

Lin Y, Zhao Y, Qiu X, Ma J, Yang Q, Shao M, Zhu T. (2013). Spatial distribution of polychlorinated naphthalenes in the atmosphere across North China based on gridded field observations. Environmental Pollution, 180: 27–33

[23]

LinY C, Hsu S C, ChouC C, ZhangR, WuY, KaoS J, Luo L, HuangC H, LinS H, HuangY T (2016). Wintertime haze deterioration in Beijing by industrial pollution deduced from trace metal fingerprints and enhanced health risk by heavy metals. Environmental Pollution, 208(Pt A): 284–293

[24]

Liu J, Wang S, Yi H, Tang X, Li Z, Yu Q, Zhao S, Gao F, Zhou Y, Wang Y. (2022). Air pollutant emission and reduction potentials from the sintering process of the iron and steel industry in China in 2017. Environmental Pollution, 307: 119512

[25]

Liu Z, Xu C X, Chen J H, Han L, Wang B, Xiong W P, Mei L D. (2020). Emission estimation and component characteristics of volatile organic compounds in typical iron and steel enterprise. China Environmental Science, 40(10): 4292–4303

[26]

Long W, Wang S, Lu C, Xue R, Liang T, Jiang N, Zhang R. (2020). Quantitative assessment of energy conservation potential and environmental benefits of an iron and steel plant in China. Journal of Cleaner Production, 273: 123163

[27]

Luo Y F, Wang Y F, Li J J, Yu Z W, Wei J C, Long H M. (2021). Influence of coking coal ratio on emission characteristics of volatile organic compounds in sintering flue gas. China Evironmental Science, 41: 4077–4084 (in Chinese)

[28]

Ma J, Chu B, Liu J, Liu Y, Zhang H, He H. (2018). NOx promotion of SO2 conversion to sulfate: an important mechanism for the occurrence of heavy haze during winter in Beijing. Environmental Pollution, 233: 662–669

[29]

Peng Y, Yang Q, Wang L, Wang S, Li J, Zhang X, Zhang S, Zhao H, Zhang B, Wang C. . (2021). VOC emissions of coal-fired power plants in China based on life cycle assessment method. Fuel, 292: 120325

[30]

Qian L, Chun T, Long H, Li J, Di Z, Meng Q, Wang P. (2018). Emission reduction research and development of PCDD/Fs in the iron ore sintering. Process Safety and Environmental Protection, 117: 82–91

[31]

Shen X, Zhao Y, Chen Z, Huang D. (2013). Heterogeneous reactions of volatile organic compounds in the atmosphere. Atmospheric Environment, 68: 297–314

[32]

ShiJ, DengH, BaiZ, KongS, WangX, Hao J, HanX, NingP (2015). Emission and profile characteristic of volatile organic compounds emitted from coke production, iron smelt, heating station and power plant in Liaoning Province, China. Science of the Total Environment, 515–516: 101–108

[33]

Sun S, Liu W, Guan W, Zhu S, Jia J, Wu X, Lei R, Jia T, He Y. (2021). Effects of air pollution control devices on volatile organic compounds reduction in coal-fired power plants. Science of the Total Environment, 782: 146828

[34]

Sun Y, Liu L, Fu X, Zhu T, Buekens A, Yang X, Wang Q. (2016). Mechanism of unintentionally produced persistent organic pollutant formation in iron ore sintering. Journal of Hazardous Materials, 306: 41–49

[35]

Sweet C W, Vermette S J, Landsberger S. (1993). Sources of toxic trace elements in urban air in Illinois. Environmental Science & Technology, 27(12): 2502–2510

[36]

Tang L, Xue X, Jia M, Jing H, Wang T, Zhen R, Huang M, Tian J, Guo J, Li L. . (2020b). Iron and steel industry emissions and contribution to the air quality in China. Atmospheric Environment, 237: 117668

[37]

Tang L, Xue X, Bo X, Guo J, Wang P, Zhai W, Cui W, Wang S, Li S, Dong G. (2020a). Contribution of emissions from cement to air quality in China. Environmental Science, 41: 4776–4785

[38]

Tian B, Huang J, Wang B, Deng S, Yu G. (2012). Emission characterization of unintentionally produced persistent organic pollutants from iron ore sintering process in China. Chemosphere, 89(4): 409–415

[39]

TsaiJ H, Lin K H, ChenC Y, LaiN, MaS Y, ChiangH L (2008). Volatile organic compound constituents from an integrated iron and steel facility. Journal of Hazardous Materials, 157(2–3): 569–578

[40]

Wang H, Hao R, Fang L, Nie L, Zhang Z, Hao Z. (2021). Study on emissions of volatile organic compounds from a typical coking chemical plant in China. Science of the Total Environment, 752: 141927

[41]

WangM, Li Q, LiuW (2019). Temporal trends in polychlorinated naphthalene emissions from sintering plants in China between 2005 and 2015. Environmental Pollution, 255(Pt 1): 113096

[42]

Wang P, Zhu S, Vrekoussis M, Brasseur G P, Wang S, Zhang H (2022a). Is atmospheric oxidation capacity better in indicating tropospheric O3 formation? Frontiers of Environmental Science & Engineering, 16(5): 65

[43]

Wang R, Wang X, Cheng S, Wang K, Cheng L, Zhu J, Zheng H, Duan W. (2022b). Emission characteristics and reactivity of volatile organic compounds from typical high-energy-consuming industries in North China. Science of the Total Environment, 809: 151134

[44]

Wang Y, Ding L, Shi Q, Liu S, Qian L, Yu Z, Wang H, Lei J, Gao Z, Long H, Charles Xu C. (2022c). Volatile organic compounds (VOC) emissions control in iron ore sintering process: recent progress and future development. Chemical Engineering Journal, 448: 137601

[45]

WangY, Zhu R, BoX, DanM, ShuM (2022d). Volatile organic compounds constituents of a typical integrated iron and steel plant and influence on O3 pollution. International Journal of Environmental Science and Technology, doi: 10.1007/s13762-022-04135-6

[46]

Wichmann H E, Mueller W, Allhoff P, Beckmann M, Bocter N, Csicsaky M J, Jung M, Molik B, Schoeneberg G. (1989). Health effects during a smog episode in West Germany in 1985. Environmental Health Perspectives, 79: 89–99

[47]

WSA(2010). World Steel in Figures 2010. World Steel Association. Available online at worldsteel.org/wp-content

[48]

WSA(2021). World Steel in Figures 2021. World Steel Association. Available online at worldsteel.org/media-centre

[49]

Wu X, Zhao L, Zhang Y, Zheng C, Gao X, Cen K. (2015). Primary air pollutant emissions and future prediction of iron and steel industry in China. Aerosol and Air Quality Research, 15(4): 1422–1432

[50]

Xu J, Zhu F, Ge X, Li H, Zhao X, Tian W, Zhang X, Bai Y, An F, Wang S. (2022). Research progress on volatile organic compounds emissions from coal-fired power plants. Current Pollution Reports, 8(3): 303–314

[51]

Xu X, Xu X, Chen Q, Che Y. (2018). The impacts on CO2 emission reduction and haze by coal resource tax reform based on dynamic CGE model. Resources Policy, 58: 268–276

[52]

Xu Y, Yu H, Yan Y, Peng L, Li R, Wang C, Li Z. (2021). Emission characteristics of volatile organic compounds from typical coal utilization sources: a case study in Shanxi of northern China. Aerosol and Air Quality Research, 21(9): 210050

[53]

YangH, Tao W, LiuY, QiuM, LiuJ, JiangK, Yi K, XiaoY, TaoS (2019). The contribution of the Beijing-Tianjin-Hebei region’s iron and steel industry to local air pollution in winter. Environmental Pollution, 245: 1095–1106

[54]

Yang W, Ma Q, Liu Y, Ma J, Chu B, Wang L, He H. (2018). Role of NH3 in the heterogeneous formation of secondary inorganic aerosols on mineral oxides. Journal of Physical Chemistry A, 122(30): 6311–6320

[55]

Zhang H, Rao M, Fan Z, Zhang Y, Li G, Jiang T. (2012). Effects of circulated flue gas components on iron ore sintering. ISIJ International, 52(12): 2139–2144

[56]

Zhang R, Wang G, Guo S, Zamora M L, Ying Q, Lin Y, Wang W, Hu M, Wang Y. (2015). Formation of urban fine particulate matter. Chemical Reviews, 115(10): 3803–3855

[57]

Zhang S, Xing J, Sarwar G, Ge Y, He H, Duan F, Zhao Y, He K, Zhu L, Chu B. (2019). Parameterization of heterogeneous reaction of SO2 to sulfate on dust with coexistence of NH3 and NO2 under different humidity conditions. Atmospheric Environment, 208: 133–140

[58]

Zhang X, Gao S, Fu Q, Han D, Chen X, Fu S, Huang X, Cheng J. (2020a). Impact of VOCs emission from iron and steel industry on regional O3 and PM2.5 pollutions. Environmental Science and Pollution Research International, 27(23): 28853–28866

[59]

Zhang X, Wang D, Liu Y, Cui Y, Xue Z, Gao Z, Du J. (2020b). Characteristics and ozone formation potential of volatile organic compounds in emissions from a typical Chinese coking plant. Journal of Environmental Sciences (China), 95: 183–189

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