Use of Waste Plastics in Coke Oven: A Review
To help in building a recycling-oriented sustainable society, Nippon Steel & Sumitomo Metal Corporation developed a waste plastic-recycling process using coke oven and put it into commercial operation in 2000. Now roughly 200,000 tons per year of waste plastics are processed in coke oven in Japa...
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| Published in | Journal of sustainable metallurgy Vol. 1; no. 1; pp. 85 - 93 |
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| Main Author | |
| Format | Journal Article |
| Language | English |
| Published |
Cham
Springer International Publishing
01.03.2015
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| Abstract | To help in building a recycling-oriented sustainable society, Nippon Steel & Sumitomo Metal Corporation developed a waste plastic-recycling process using coke oven and put it into commercial operation in 2000. Now roughly 200,000 tons per year of waste plastics are processed in coke oven in Japan. In this process, the waste plastics collected from households are agglomerated to the sizes ranging from 20 to 30 mm in diameter and charged into coke ovens with coal at the blending ratio of about 1 mass%. Waste plastics are thermally decomposed into approximately 20 mass% coke, 40 mass% hydrocarbon oil (tar and light oil) and 40 mass% coke oven gas, which are utilized as iron ore-reducing agents in blast furnaces, raw materials for the chemical industry, and a fuel for power plants, respectively. Moreover, 92 mass% of the chlorine in waste plastics is released and absorbed by the ammonia liquor spray for cooling hot coke oven gas and converted to ammonium chloride. The waste plastic-recycling process using coke ovens is superior in that a large amount of waste plastics can be treated, useful materials can be recovered using the existing facilities, coke quality can be kept the same and the chlorine released from waste plastics can be fixed in the existing ammonia liquor spray system. |
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| AbstractList | To help in building a recycling-oriented sustainable society, Nippon Steel & Sumitomo Metal Corporation developed a waste plastic-recycling process using coke oven and put it into commercial operation in 2000. Now roughly 200,000 tons per year of waste plastics are processed in coke oven in Japan. In this process, the waste plastics collected from households are agglomerated to the sizes ranging from 20 to 30 mm in diameter and charged into coke ovens with coal at the blending ratio of about 1 mass%. Waste plastics are thermally decomposed into approximately 20 mass% coke, 40 mass% hydrocarbon oil (tar and light oil) and 40 mass% coke oven gas, which are utilized as iron ore-reducing agents in blast furnaces, raw materials for the chemical industry, and a fuel for power plants, respectively. Moreover, 92 mass% of the chlorine in waste plastics is released and absorbed by the ammonia liquor spray for cooling hot coke oven gas and converted to ammonium chloride. The waste plastic-recycling process using coke ovens is superior in that a large amount of waste plastics can be treated, useful materials can be recovered using the existing facilities, coke quality can be kept the same and the chlorine released from waste plastics can be fixed in the existing ammonia liquor spray system. |
| Author | Nomura, Seiji |
| Author_xml | – sequence: 1 givenname: Seiji surname: Nomura fullname: Nomura, Seiji email: nomura.e9c.seiji@jp.nssmc.com organization: Ironmaking Research Laboratory, Process Research Laboratories, Nippon Steel & Sumitomo Metal Corporation |
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| CitedBy_id | crossref_primary_10_1016_j_psep_2024_01_024 crossref_primary_10_1016_j_fuel_2020_119249 crossref_primary_10_1007_s40831_021_00425_4 crossref_primary_10_1016_j_jaap_2023_106083 crossref_primary_10_3390_polym13152462 crossref_primary_10_1080_19392699_2022_2066088 crossref_primary_10_1002_cssc_202100904 crossref_primary_10_1016_j_fuel_2015_10_053 crossref_primary_10_1515_reveh_2017_0035 crossref_primary_10_3103_S1068364X20120029 crossref_primary_10_1016_j_energy_2022_125920 crossref_primary_10_3985_jjsmcwm_33_11 crossref_primary_10_1039_C6GC00911E crossref_primary_10_2355_tetsutohagane_TETSU_2019_008 crossref_primary_10_1016_j_mset_2019_08_002 crossref_primary_10_2139_ssrn_4073455 crossref_primary_10_3390_ma12040655 crossref_primary_10_1016_j_fuproc_2017_01_016 crossref_primary_10_3390_ma16072782 crossref_primary_10_3390_met11101654 crossref_primary_10_1073_pnas_2001379117 |
| Cites_doi | 10.1016/j.jaap.2004.08.006 10.1051/metal/199693101219 10.1016/S0016-2361(03)00173-X 10.1016/S0165-2370(98)00101-6 10.2355/isijinternational.40.244 10.2355/isijinternational.42.Suppl_S10 10.1016/j.fuel.2009.03.035 10.1016/S0021-9673(01)01501-1 10.1016/j.proeps.2009.09.127 10.1016/j.fuel.2004.03.006 10.1016/j.coal.2010.06.003 10.1179/174328106X113959 10.1016/S0016-2361(83)80019-2 10.1016/S0016-2361(03)00120-0 10.1016/S0021-9673(01)00736-1 10.1016/j.fuproc.2010.10.014 10.1016/0016-2361(88)90157-3 10.1021/ef7004628 10.1016/S0016-2361(99)00117-9 10.1021/ef0501041 10.1016/j.fuel.2011.01.011 10.1016/j.fuel.2005.05.019 10.1016/j.coal.2014.05.004 10.1016/j.fuel.2004.09.017 |
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| Keywords | Waste plastic recycling Carbonization Chlorine Coke Coal |
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