Abstract:
China, a country with a total industrial energy consumption ranking in the forefront of the world. China's steel industry has a large energy consumption and low energy recycling rate, which is one of the reasons for the limited development of Green & Low-Carbon metallurgy. BOF gas, with an annual output of more than 100 billion standard cubic meters, is one of the main by-product energy resources in the steelmaking process. However, the up to 34.7% abandoned rate of BOF gas has caused a lot of carbon emissions and energy resources waste. The abandoned BOF gas, with a high temperature of 1773~1873K and 20~40%(vol.%) CO and 20~30%(vol.%) CO2, has a huge physical sensible heat and chemical latent heat. It means there is a predictable recyclable value and comprehensive utilization prospects to achieve the ultra-low carbon emissions, reduction of energy consumption, resources recovery and energy conversion in iron and steel making process. The paper has carried out detailed calculation and analysis of the energy value of abandoned BOF gas, and the feasibility analysis and program design of the overall resource recycling and energy utilization in iron and steel making process that include blast furnace (BF) smelting of vanadia-titania magnetite (VTM), Combined blowing in BOF and vanadium-extracting converter, Co-production of steel-chemicals industry.
References:[1] Wenying C, Xiang Y, Ding M. 2014. A bottom-up analysis of China’s iron and steel industrial energy consumption and CO2 emissions. In: Applied Energy. Volume 136. Beijing (China): Tsinghua University. p. 1174-1183. [2] HU L, Hongguang J, Lin G, Na Z. 2014. A polygeneration system for methanol and power production based on coke oven gas and coal gas with CO2 recovery. In: Energy. Volume 74. Beijing (China): Chinese Academy of Sciences. p. 174-180. [3] Kun H, Li W. 2017. A review of energy use and energy-efficient technologies for the iron and steel industry. In: Renewable and Sustainable Energy Reviews. Volume 70. Beijing (China): University of Science and Technology Beijing. p. 1022-1039. [4] Yihui T, Qinghua Z, Yong G. 2013. An analysis of energy-related greenhouse gas emissions in the Chinese iron and steel industry. In: Energy Policy. Volume 56. Dalian (China): Dalian University of Technology. p. 352-361. [5] Qianqian C, Yu G, Zhiyong T, Wei W, Yuhan S. 2018. Assessment of low-carbon iron and steel production with CO2 recycling and utilization technologies: A case study in China. In: Applied Energy. Volume 220. Shanghai (China): Chinese Academy of Sciences. p. 192-207. [6] Qi Z, Yu L, Jin X, Guoyu J. 2018. Carbon element flow analysis and CO2 emission reduction in iron and steel works. In: Journal of Cleaner Production. Volume 172. Shenyang (China): Northeastern University. p. 709-723. [7] Dolf G, Yuichi M. 2002. CO2 in the iron and steel industry: an analysis of Japanese emission reduction potentials. In: Energy Policy. Volume 30. Ibaraki (Japan): National Institute for Environmental Studies. p. 849-863. [8] Xuecheng W, Liang Z, Yongxin Z, Lingjie Z, Chenghang Z, Xiang G, Kefa C. 2016. Cost and potential of energy conservation and collaborative pollutant reduction in the iron and steel industry in China. In: Applied Energy. Volume 184. Hangzhou (China): Zhejiang University. p. 171-183. [9] Yuan L, Lei Z. 2016. Cost of energy saving and CO2 emissions reduction in China’s iron and steel sector. In: Applied Energy. Volume 130. Beijing (China): Chinese Academy of Sciences. p. 603-616. [10] Z.C. G, Z.X. F. 2010. Current situation of energy consumption and measures taken for energy saving in the iron and steel industry in China. In: Energy. Volume 35. Beijing (China): University of Science and Technology Beijing. p. 4356-4360. [11] H. S, Y. M, T. H. 2013. Development of PSA System for the Recovery of Carbon Dioxide and Carbon Monoxide from Blast Furnace Gas in Steel Works. In: Energy Procedia. Volume 35. Hiroshima (Japan): JFE Steel Corp. p. 7152-7159. [12] Chao F, JianBai H, Miao W, Yi S. 2018. Energy efficiency in China's iron and steel industry: Evidence and policy implications. In: Journal of Cleaner Production. Volume 177. Changsha (China): Central South University. p. 837-845. [13] Boqiang L, Ya W, Li Z. 2011. Estimates of the potential for energy conservation in the Chinese steel industry. In: Energy Policy. Volume 39. Fuzhou (China): Minjiang University. p. 3680-3689. [14] Xun W Tianjiao W. 2012. Hydrogen amplification from coke oven gas using a CO2 adsorption enhanced hydrogen amplification reactor. In: Hydrogen energy. Volume 37. Beijing (China): Chinese Academy of Sciences. p. 4974-4986. [15] Bing Y, Xiao L, Yuanbo Q, Lei S. 2015. Low-carbon transition of iron and steel industry in China: Carbon intensity, economic growth and policy intervention. In: Journal of Environmental Science. Volume 28. Beijing (China): Tsinghua University. p. 137-147. [16] Nicolás P, José Antonio M. 2013. Prospective scenarios on energy efficiency and CO2 emissions in the European Iron & Steel industry. In: Energy. Volume 54. Petten (Netherlands): Institute for Energy and Transport. p. 113-128. [17] Fang Z, Keman H. 2017. The role of government in industrial energy conservation in China: Lessons from the iron and steel industry. In: Energy for Sustainable Development. Volume 39. Medford (USA): Tufts University. p. 101-114. [18] Haijuan W, Rong Z, Xueliang W, Zhizheng L. 2017. Utilization of CO2 in metallurgical processes in China. In: Mineral Processing and Extractive Metallurgy. Volume 126. Beijing (China): University of Science and Technology Beijing. p. 47-53. [19] Sari S, Mari T, Pekka A. 2017. Variables affecting energy efficiency and CO2 emissions in the steel industry. In: Energy Policy. Volume 38. Aalto (Finland): Aalto University. p. 2477-2485.
|