Life cycle inventory processes of the integrated steel plant (ISP) in Krakow, Poland-continuous casting of steel (CCS): a case study

Purpose The purpose of this study is to perform the life cycle inventory (LCI) to continuous casting of steel (CCS) process in integrated steel plant (ISP) in Krakow, Poland. The present LCI is representative for year 2015 by application of PN-EN ISO 14040 ( 2009 ). The system boundary was labeled a...

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Veröffentlicht in:The international journal of life cycle assessment 2018-06, Vol.23 (6), p.1274-1285
Hauptverfasser: Bieda, Boguslaw, Skalna, Iwona, Gaweł, Bartłomiej, Grzesik, Katarzyna, Henclik, Anna, Sala, Dariusz
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container_end_page 1285
container_issue 6
container_start_page 1274
container_title The international journal of life cycle assessment
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creator Bieda, Boguslaw
Skalna, Iwona
Gaweł, Bartłomiej
Grzesik, Katarzyna
Henclik, Anna
Sala, Dariusz
description Purpose The purpose of this study is to perform the life cycle inventory (LCI) to continuous casting of steel (CCS) process in integrated steel plant (ISP) in Krakow, Poland. The present LCI is representative for year 2015 by application of PN-EN ISO 14040 ( 2009 ). The system boundary was labeled as gate to gate. The background input and output data from the CCS has been inventoried as follows: consumption of energy and fuels, materials inputs, and waste. Methods In this paper, LCI CCS process on integrated permit (secondary data), literature information, and expert consultations was developed. The functional unit (FU) is represented by 1 t of steel slabs produced by CCS. Operating parameters as well as air emissions associated with the CCS process were presented. The production data (slabs) was given. The emissions of dust, Fe, PM10 and PM2.5, and waste (iron dust, iron particles, the others) are outcomes of the CCS processes. Results and discussion Annually production of steel slabs in CCS plant amounted to 200,000 t. Coke oven gas, natural gas, steam, air, oxygen, casting powders for crystallizer and for intermediate tundish, refractory material, oil, lubricant, argon, and industrial water amounts were in the order of 2,750,000 Nm 3 /year, 770,000 Nm 3 /year, 2000 t/year, 90,000,000 Nm 3 /year, 970 t/year, 1300 t/year, 810 t/year, 30 t/year, 45 t/year, 330 t/year, and 13,175,300 m 3 /year, respectively. The average heat and electric energy consumptions were about 0.023 to 0.068 GJ/t and 12.0 to 17.2 kWh/t, respectively. Emissions in air of dust, Fe, PM10, and PM2.5 were in the order of 1.3, 0.1, 0.5, and 0.44 kg/h, respectively. The amounts of iron dust and the other waste were 200 t/year and 240 t, respectively. No information is available on CO 2 emission. Conclusions The LCI study resulted in the development of a database with an inventory of secondary data regarding CCS process referring to the year 2015 . The scope of this study considered input items needed in CCS production (entry gate) to the final delivery of steel slabs (exit gate). The raw materials, supplies, and equipment to the CCS plant and infrastructure are not taken into consideration in the analysis. The FU is 1 t of steel slabs. Recommendations and outlook The LCI offers environmental information consisting of the list of environmental loads. The impact assessment phase aims to present more understandable results from the inventory analysis, and life cycle impact assessment will be
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The present LCI is representative for year 2015 by application of PN-EN ISO 14040 ( 2009 ). The system boundary was labeled as gate to gate. The background input and output data from the CCS has been inventoried as follows: consumption of energy and fuels, materials inputs, and waste. Methods In this paper, LCI CCS process on integrated permit (secondary data), literature information, and expert consultations was developed. The functional unit (FU) is represented by 1 t of steel slabs produced by CCS. Operating parameters as well as air emissions associated with the CCS process were presented. The production data (slabs) was given. The emissions of dust, Fe, PM10 and PM2.5, and waste (iron dust, iron particles, the others) are outcomes of the CCS processes. Results and discussion Annually production of steel slabs in CCS plant amounted to 200,000 t. Coke oven gas, natural gas, steam, air, oxygen, casting powders for crystallizer and for intermediate tundish, refractory material, oil, lubricant, argon, and industrial water amounts were in the order of 2,750,000 Nm 3 /year, 770,000 Nm 3 /year, 2000 t/year, 90,000,000 Nm 3 /year, 970 t/year, 1300 t/year, 810 t/year, 30 t/year, 45 t/year, 330 t/year, and 13,175,300 m 3 /year, respectively. The average heat and electric energy consumptions were about 0.023 to 0.068 GJ/t and 12.0 to 17.2 kWh/t, respectively. Emissions in air of dust, Fe, PM10, and PM2.5 were in the order of 1.3, 0.1, 0.5, and 0.44 kg/h, respectively. The amounts of iron dust and the other waste were 200 t/year and 240 t, respectively. No information is available on CO 2 emission. Conclusions The LCI study resulted in the development of a database with an inventory of secondary data regarding CCS process referring to the year 2015 . The scope of this study considered input items needed in CCS production (entry gate) to the final delivery of steel slabs (exit gate). The raw materials, supplies, and equipment to the CCS plant and infrastructure are not taken into consideration in the analysis. The FU is 1 t of steel slabs. Recommendations and outlook The LCI offers environmental information consisting of the list of environmental loads. The impact assessment phase aims to present more understandable results from the inventory analysis, and life cycle impact assessment will be the direction for future research.</description><identifier>ISSN: 0948-3349</identifier><identifier>EISSN: 1614-7502</identifier><identifier>DOI: 10.1007/s11367-017-1365-0</identifier><language>eng</language><publisher>Berlin/Heidelberg: Springer Berlin Heidelberg</publisher><subject>Carbon dioxide ; Carbon dioxide emissions ; Coke oven gas ; Coke ovens ; Continuous casting ; Data processing ; Dust ; Earth and Environmental Science ; Emission analysis ; Energy consumption ; Environment ; Environmental Chemistry ; Environmental Economics ; Environmental Engineering/Biotechnology ; Environmental impact ; Environmental information ; Industrial water ; Integrated iron and steel plants ; Iron ; Iron and steel making ; ISO standards ; Lci Methodology and Databases ; Life cycle analysis ; Life cycle assessment ; Life cycle engineering ; Life cycles ; Lubricants ; Natural gas ; Particulate matter ; Raw materials ; Slabs ; Steel ; Steel industry</subject><ispartof>The international journal of life cycle assessment, 2018-06, Vol.23 (6), p.1274-1285</ispartof><rights>Springer-Verlag GmbH Germany 2017</rights><rights>The International Journal of Life Cycle Assessment is a copyright of Springer, (2017). All Rights Reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c374t-2fe1dd21d81e085de6b75a5d88fe82536168b9a4131a21c384ecabcd5f55fca3</citedby><cites>FETCH-LOGICAL-c374t-2fe1dd21d81e085de6b75a5d88fe82536168b9a4131a21c384ecabcd5f55fca3</cites><orcidid>0000-0003-0416-1859</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s11367-017-1365-0$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s11367-017-1365-0$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,780,784,27923,27924,41487,42556,51318</link.rule.ids></links><search><creatorcontrib>Bieda, Boguslaw</creatorcontrib><creatorcontrib>Skalna, Iwona</creatorcontrib><creatorcontrib>Gaweł, Bartłomiej</creatorcontrib><creatorcontrib>Grzesik, Katarzyna</creatorcontrib><creatorcontrib>Henclik, Anna</creatorcontrib><creatorcontrib>Sala, Dariusz</creatorcontrib><title>Life cycle inventory processes of the integrated steel plant (ISP) in Krakow, Poland-continuous casting of steel (CCS): a case study</title><title>The international journal of life cycle assessment</title><addtitle>Int J Life Cycle Assess</addtitle><description>Purpose The purpose of this study is to perform the life cycle inventory (LCI) to continuous casting of steel (CCS) process in integrated steel plant (ISP) in Krakow, Poland. The present LCI is representative for year 2015 by application of PN-EN ISO 14040 ( 2009 ). The system boundary was labeled as gate to gate. The background input and output data from the CCS has been inventoried as follows: consumption of energy and fuels, materials inputs, and waste. Methods In this paper, LCI CCS process on integrated permit (secondary data), literature information, and expert consultations was developed. The functional unit (FU) is represented by 1 t of steel slabs produced by CCS. Operating parameters as well as air emissions associated with the CCS process were presented. The production data (slabs) was given. The emissions of dust, Fe, PM10 and PM2.5, and waste (iron dust, iron particles, the others) are outcomes of the CCS processes. Results and discussion Annually production of steel slabs in CCS plant amounted to 200,000 t. Coke oven gas, natural gas, steam, air, oxygen, casting powders for crystallizer and for intermediate tundish, refractory material, oil, lubricant, argon, and industrial water amounts were in the order of 2,750,000 Nm 3 /year, 770,000 Nm 3 /year, 2000 t/year, 90,000,000 Nm 3 /year, 970 t/year, 1300 t/year, 810 t/year, 30 t/year, 45 t/year, 330 t/year, and 13,175,300 m 3 /year, respectively. The average heat and electric energy consumptions were about 0.023 to 0.068 GJ/t and 12.0 to 17.2 kWh/t, respectively. Emissions in air of dust, Fe, PM10, and PM2.5 were in the order of 1.3, 0.1, 0.5, and 0.44 kg/h, respectively. The amounts of iron dust and the other waste were 200 t/year and 240 t, respectively. No information is available on CO 2 emission. Conclusions The LCI study resulted in the development of a database with an inventory of secondary data regarding CCS process referring to the year 2015 . The scope of this study considered input items needed in CCS production (entry gate) to the final delivery of steel slabs (exit gate). The raw materials, supplies, and equipment to the CCS plant and infrastructure are not taken into consideration in the analysis. The FU is 1 t of steel slabs. Recommendations and outlook The LCI offers environmental information consisting of the list of environmental loads. 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Skalna, Iwona ; Gaweł, Bartłomiej ; Grzesik, Katarzyna ; Henclik, Anna ; Sala, Dariusz</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c374t-2fe1dd21d81e085de6b75a5d88fe82536168b9a4131a21c384ecabcd5f55fca3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Carbon dioxide</topic><topic>Carbon dioxide emissions</topic><topic>Coke oven gas</topic><topic>Coke ovens</topic><topic>Continuous casting</topic><topic>Data processing</topic><topic>Dust</topic><topic>Earth and Environmental Science</topic><topic>Emission analysis</topic><topic>Energy consumption</topic><topic>Environment</topic><topic>Environmental Chemistry</topic><topic>Environmental Economics</topic><topic>Environmental Engineering/Biotechnology</topic><topic>Environmental impact</topic><topic>Environmental information</topic><topic>Industrial water</topic><topic>Integrated iron and steel plants</topic><topic>Iron</topic><topic>Iron and steel making</topic><topic>ISO standards</topic><topic>Lci Methodology and Databases</topic><topic>Life cycle analysis</topic><topic>Life cycle assessment</topic><topic>Life cycle engineering</topic><topic>Life cycles</topic><topic>Lubricants</topic><topic>Natural gas</topic><topic>Particulate matter</topic><topic>Raw materials</topic><topic>Slabs</topic><topic>Steel</topic><topic>Steel industry</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Bieda, Boguslaw</creatorcontrib><creatorcontrib>Skalna, Iwona</creatorcontrib><creatorcontrib>Gaweł, Bartłomiej</creatorcontrib><creatorcontrib>Grzesik, Katarzyna</creatorcontrib><creatorcontrib>Henclik, Anna</creatorcontrib><creatorcontrib>Sala, Dariusz</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Environment Abstracts</collection><collection>Mechanical &amp; 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The present LCI is representative for year 2015 by application of PN-EN ISO 14040 ( 2009 ). The system boundary was labeled as gate to gate. The background input and output data from the CCS has been inventoried as follows: consumption of energy and fuels, materials inputs, and waste. Methods In this paper, LCI CCS process on integrated permit (secondary data), literature information, and expert consultations was developed. The functional unit (FU) is represented by 1 t of steel slabs produced by CCS. Operating parameters as well as air emissions associated with the CCS process were presented. The production data (slabs) was given. The emissions of dust, Fe, PM10 and PM2.5, and waste (iron dust, iron particles, the others) are outcomes of the CCS processes. Results and discussion Annually production of steel slabs in CCS plant amounted to 200,000 t. Coke oven gas, natural gas, steam, air, oxygen, casting powders for crystallizer and for intermediate tundish, refractory material, oil, lubricant, argon, and industrial water amounts were in the order of 2,750,000 Nm 3 /year, 770,000 Nm 3 /year, 2000 t/year, 90,000,000 Nm 3 /year, 970 t/year, 1300 t/year, 810 t/year, 30 t/year, 45 t/year, 330 t/year, and 13,175,300 m 3 /year, respectively. The average heat and electric energy consumptions were about 0.023 to 0.068 GJ/t and 12.0 to 17.2 kWh/t, respectively. Emissions in air of dust, Fe, PM10, and PM2.5 were in the order of 1.3, 0.1, 0.5, and 0.44 kg/h, respectively. The amounts of iron dust and the other waste were 200 t/year and 240 t, respectively. No information is available on CO 2 emission. Conclusions The LCI study resulted in the development of a database with an inventory of secondary data regarding CCS process referring to the year 2015 . The scope of this study considered input items needed in CCS production (entry gate) to the final delivery of steel slabs (exit gate). The raw materials, supplies, and equipment to the CCS plant and infrastructure are not taken into consideration in the analysis. The FU is 1 t of steel slabs. Recommendations and outlook The LCI offers environmental information consisting of the list of environmental loads. The impact assessment phase aims to present more understandable results from the inventory analysis, and life cycle impact assessment will be the direction for future research.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><doi>10.1007/s11367-017-1365-0</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0003-0416-1859</orcidid></addata></record>
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subjects Carbon dioxide
Carbon dioxide emissions
Coke oven gas
Coke ovens
Continuous casting
Data processing
Dust
Earth and Environmental Science
Emission analysis
Energy consumption
Environment
Environmental Chemistry
Environmental Economics
Environmental Engineering/Biotechnology
Environmental impact
Environmental information
Industrial water
Integrated iron and steel plants
Iron
Iron and steel making
ISO standards
Lci Methodology and Databases
Life cycle analysis
Life cycle assessment
Life cycle engineering
Life cycles
Lubricants
Natural gas
Particulate matter
Raw materials
Slabs
Steel
Steel industry
title Life cycle inventory processes of the integrated steel plant (ISP) in Krakow, Poland-continuous casting of steel (CCS): a case study
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