A Study on Life Cycle Assessment of Energy Consumption and CO2 Emissions in the Manufacturing and Transportation Processes of Nitrogen and Phosphate Fertilizers
In order to apply the LCA method in evaluating environmental measures in agricultural activities, the first task is to draw up scenarios of alternatives for problem solving and subject them to analysis. Secondly, processes and items related to load calculation of life cycle need to be selected and b...
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| Published in | Japanese Journal of Farm Work Research Vol. 36; no. 3; pp. 141 - 151 |
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| Main Authors | , |
| Format | Journal Article |
| Language | English |
| Published |
Japanese Society of Farm Work Research
2001
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| Subjects | |
| Online Access | Get full text |
| ISSN | 0389-1763 1883-2261 1883-2261 |
| DOI | 10.4035/jsfwr.36.141 |
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| Abstract | In order to apply the LCA method in evaluating environmental measures in agricultural activities, the first task is to draw up scenarios of alternatives for problem solving and subject them to analysis. Secondly, processes and items related to load calculation of life cycle need to be selected and basic data prepared. Then environmental loads produced throughout the life cycle for each scenario need to be calculated. In this paper, based on the assumption that the Life Cycle Assessment (LCA) would be used to evaluate measures to reduce environmental loads discharged in the process of agricultural nutrient input, attempts are made to calculate energy consumption and CO2 emissions throughout the life cycle of chemical fertilizer (nitrogen fertilizer, phosphate fertilizer, compound fertilizer and coating fertilizer) productions and transportations, which will provide basic data. The life cycle energy (LC-energy) in the manufacturing of urea, ammonium sulfate, diammonium phosphate (DAP), compound fertilizer and coating fertilizer were found to be 22.3MJ per 1kg of fertilizer (48.6MJ/kg-N), 4.3MJ/kg (20.5MJ/kg-N), 13.2MJ/kg (28.6MJ/kg-P), 2.0MJ/kg and 1.9MJ/kg respectively. Life cycle CO2 (LC-CO2) were 732g-CO2 per 1kg of fertilizer (1.59kg-CO2/kg-N), 262g-CO2/kg (1.25kg-CO2/kg-N), 894g-CO2/kg (1.94kg-CO2/kg-P), 142g-CO2/kg and 137g-CO2/kg respectively. Percentages of CO2 emitted during the transportation stage were approximately 2% for urea and 17% for DAP. In the production of DAP, about 16% of LC-CO2 was generated at the material collection stage. LC-energy figures obtained in this analysis are considered reasonable in comparison with existing figures. |
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| AbstractList | In order to apply the LCA method in evaluating environmental measures in agricultural activities, the first task is to draw up scenarios of alternatives for problem solving and subject them to analysis. Secondly, processes and items related to load calculation of life cycle need to be selected and basic data prepared. Then environmental loads produced throughout the life cycle for each scenario need to be calculated. In this paper, based on the assumption that the Life Cycle Assessment (LCA) would be used to evaluate measures to reduce environmental loads discharged in the process of agricultural nutrient input, attempts are made to calculate energy consumption and CO2 emissions throughout the life cycle of chemical fertilizer (nitrogen fertilizer, phosphate fertilizer, compound fertilizer and coating fertilizer) productions and transportations, which will provide basic data. The life cycle energy (LC-energy) in the manufacturing of urea, ammonium sulfate, diammonium phosphate (DAP), compound fertilizer and coating fertilizer were found to be 22.3MJ per 1kg of fertilizer (48.6MJ/kg-N), 4.3MJ/kg (20.5MJ/kg-N), 13.2MJ/kg (28.6MJ/kg-P), 2.0MJ/kg and 1.9MJ/kg respectively. Life cycle CO2 (LC-CO2) were 732g-CO2 per 1kg of fertilizer (1.59kg-CO2/kg-N), 262g-CO2/kg (1.25kg-CO2/kg-N), 894g-CO2/kg (1.94kg-CO2/kg-P), 142g-CO2/kg and 137g-CO2/kg respectively. Percentages of CO2 emitted during the transportation stage were approximately 2% for urea and 17% for DAP. In the production of DAP, about 16% of LC-CO2 was generated at the material collection stage. LC-energy figures obtained in this analysis are considered reasonable in comparison with existing figures. |
| Author | KOBAYASHI, Hisashi SAGO, Ryuichi |
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| CitedBy_id | crossref_primary_10_1016_j_renene_2014_08_069 crossref_primary_10_3390_en17195011 crossref_primary_10_1007_s10333_013_0375_1 crossref_primary_10_1016_j_seta_2022_101982 crossref_primary_10_3390_en16041747 crossref_primary_10_1016_j_jclepro_2012_03_026 crossref_primary_10_2134_jeq2011_0442 crossref_primary_10_3390_su13010148 crossref_primary_10_2208_jscejg_66_120 |
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| References | 電力中央研究所(1996):産業連関分析による財・サービス生産時のエネルギー消費量とCO2排出量,電力中央研究所報告,Y95013. 環境庁監修,(1996):(環境情報科学センター編ライフサイクルアセスメントの実践),LCAの現状/LCAの考え方,化学工業日報,pp.5-26. Norsk Hydro (1990): (Agriculture and Fertilizer), Norsk Hydro, pp 168-173. Mohinde, S. M. and Travis, P. H. (1987): (Energy in Plant Nutrition and Pest Control' ed. Helsel, Z. R.), Energy requirement, Technology, and Resources in the Fertilizer Sector, Elsevir, pp 25-61. 資源エネルギー庁(1996):(電力需給の概要). 小林久(1998):窒素投入に関するエネルギー消費・CO2排出のライフサイクル分析,農土論集194;51-57. 社団法人プラスチック処理促進協会(2000):樹脂加工におけるインベントリデータ調査報告書,p53. Sherff, J. L.(1976): (Energy, Agriculture and Waste Management, ed. Jewell W. J), pp 433-441. 産業環境管理協会(1998):(LCA実務入門),資料編CD-ROM,丸善. Boswell, F. C., Meisinger, J. J. and Case, N. L. (1985): Fertilizer Technology and Use, ed. Engelstad, O. P. et al., pp 249-251. 藤原彰夫・岸本菊夫(1993):(燐と植物),博友社,pp.17-35. 肥料協会新聞部(1999):(肥料年鑑),肥料協会新聞部,pp44-88. 栗原淳,越野正義(1986):(肥料製造学),養賢堂,pp.10-43. Pimentel, D. et al. (1973): Food Production and the Energy Crisis, Science 182, pp 443-449. 越野正義(1992):農業生産における肥料に関するエネルギー投入についてI-肥料製造に必要なエネルギー投入量-,日土肥誌63(4),pp.479-486. |
| References_xml | – reference: Boswell, F. C., Meisinger, J. J. and Case, N. L. (1985): Fertilizer Technology and Use, ed. Engelstad, O. P. et al., pp 249-251. – reference: Mohinde, S. M. and Travis, P. H. (1987): (Energy in Plant Nutrition and Pest Control' ed. Helsel, Z. R.), Energy requirement, Technology, and Resources in the Fertilizer Sector, Elsevir, pp 25-61. – reference: Norsk Hydro (1990): (Agriculture and Fertilizer), Norsk Hydro, pp 168-173. – reference: 社団法人プラスチック処理促進協会(2000):樹脂加工におけるインベントリデータ調査報告書,p53. – reference: 肥料協会新聞部(1999):(肥料年鑑),肥料協会新聞部,pp44-88. – reference: Pimentel, D. et al. (1973): Food Production and the Energy Crisis, Science 182, pp 443-449. – reference: 産業環境管理協会(1998):(LCA実務入門),資料編CD-ROM,丸善. – reference: 栗原淳,越野正義(1986):(肥料製造学),養賢堂,pp.10-43. – reference: 小林久(1998):窒素投入に関するエネルギー消費・CO2排出のライフサイクル分析,農土論集194;51-57. – reference: 越野正義(1992):農業生産における肥料に関するエネルギー投入についてI-肥料製造に必要なエネルギー投入量-,日土肥誌63(4),pp.479-486. – reference: Sherff, J. L.(1976): (Energy, Agriculture and Waste Management, ed. Jewell W. J), pp 433-441. – reference: 環境庁監修,(1996):(環境情報科学センター編ライフサイクルアセスメントの実践),LCAの現状/LCAの考え方,化学工業日報,pp.5-26. – reference: 藤原彰夫・岸本菊夫(1993):(燐と植物),博友社,pp.17-35. – reference: 資源エネルギー庁(1996):(電力需給の概要). – reference: 電力中央研究所(1996):産業連関分析による財・サービス生産時のエネルギー消費量とCO2排出量,電力中央研究所報告,Y95013. |
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| SubjectTerms | Chemical fertilizer CO2 Emission Coating fertilizer Compound Fertilizer Energy Consumption LCA Nitrogen Nutrient input in agriculture Phosphate Sustainable agriculture |
| Title | A Study on Life Cycle Assessment of Energy Consumption and CO2 Emissions in the Manufacturing and Transportation Processes of Nitrogen and Phosphate Fertilizers |
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