Application of life cycle assessment to the LCA case studies single superphosphate production

被引:21
|
作者
Silva, GA [1 ]
Kulay, LA [1 ]
机构
[1] Univ Sao Paulo, Grp Pollut Prevent, BR-05508900 Sao Paulo, Brazil
来源
关键词
life cycle assessment (LCA); life cycle inventory (LCI); single superphosphate manufacture; allocation LCA; fertilizer; phosphate fertilizer; sulfuric acid production; LCA; sulfuric acid; environmental impacts; Brazil; Brazilian industry;
D O I
10.1007/BF02978473
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Goal, Scope and Background. There is a competition between wet and thermal routes for phosphate fertilizers manufacture. In the Brazilian case, the thermal route is represented by thermophosphate. This fertilizer is considered the most adequate one for Brazilian agricultural conditions; its main restriction is the intensive consumption of energy necessary for its production. The wet route uses sulfuric acid to directly produce the single superphosphate (SSP) or the intermediate phosphoric acid, which will be used to result in triple superphosphate (TSP) and ammonium phosphate production. The main restriction of the wet route is the large amount of phosphogypsum generated in phosphoric acid production. Envisaged is an environmental comparison of both routes using LCA methodology. This paper presents the LCA for SSP production. The goal of the study is to establish the Environmental Profile of this fertilizer. Eight impact categories were selected for the study. The system boundaries was defined for a 'cradle to gate' approach, including extraction of natural resources, intermediate products, and production. The SSP System. The SSP system (single superphosphate) comprises the stages of mining and concentration of the phosphate rock, elemental sulfur extraction, production of sulfuric acid, and manufacture of single superphosphate. SSP LCI. The LCI was performed considering the production of 1.0 ton of SSP (single superphosphate) as a Functional Unit. The data collected were developed for different producing companies, all of them located in the same regional area. Allocation criteria of energy and mass were applied to the production of sulfuric acid and manufacture of single superphosphate. The transportation step included either the transport of the mined phosphated rock to the concentration plant or the transport of the phosphate concentrate to the SSP unit. Conclusion, Recommendation and Perspective. The accomplishment of an LCA to SSP production identified the GWP and EP as its meaningful environmental impacts. In reference to global warming, the transportation step was the greatest contributor agent, while the losses of PO4- from the SSP manufacturing were the main cause of ER The most important contribution in terms of water consumption was observed in the concentration step. Finally, the self sufficiency of the sulfuric acid production in energetic terms must be highlighted. The knowledge of the environmental profile of fertilizers is necessary to support LCA studies of agricultural products, a relevant raw material source for many industrial sectors. The method used here may be important for modelling other LCA fertilizer studies. As most of the agricultural raw materials are transferred among different countries, comparisons of the environmental profiles of fertilizers in developed and developing countries are needed.
引用
收藏
页码:209 / 214
页数:6
相关论文
共 50 条
  • [21] Life cycle assessment (LCA) and energy assessment of the production and use of windows in residential buildings
    Zbigniew Kowalczyk
    Sebastian Twardowski
    Mateusz Malinowski
    Maciej Kuboń
    Scientific Reports, 13
  • [22] Life cycle assessment (LCA) and energy assessment of the production and use of windows in residential buildings
    Kowalczyk, Zbigniew
    Twardowski, Sebastian
    Malinowski, Mateusz
    Kubon, Maciej
    SCIENTIFIC REPORTS, 2023, 13 (01)
  • [23] Life Cycle Assessment (LCA) of protected crops: an Italian case study
    Cellura, Maurizio
    Longo, Sonia
    Mistretta, Marina
    JOURNAL OF CLEANER PRODUCTION, 2012, 28 : 56 - 62
  • [24] Application of Life Cycle Assessment (LCA) and extenics theory for building energy conservation assessment
    Zheng, Guozhong
    Jing, Youyin
    Huang, Hongxia
    Zhang, Xutao
    Gao, Yuefen
    ENERGY, 2009, 34 (11) : 1870 - 1879
  • [25] Life cycle assessment (LCA) and exergetic life cycle assessment (ELCA) of the production of biodiesel from used cooking oil (UCO)
    Talens Peiro, L.
    Lombardi, L.
    Villalba Mendez, G.
    Gabarrell i Durany, X.
    ENERGY, 2010, 35 (02) : 889 - 893
  • [26] Life Cycle Assessment (LCA) of Biochar Production from a Circular Economy Perspective
    Carvalho, Joana
    Nascimento, Lucas
    Soares, Margarida
    Valerio, Nadia
    Ribeiro, Andre
    Faria, Luciana
    Silva, Andre
    Pacheco, Nuno
    Araujo, Jorge
    Vilarinho, Candida
    PROCESSES, 2022, 10 (12)
  • [27] Impact of Nanoparticle Additions on Life Cycle Assessment (LCA) of Ceramic Tiles Production
    Saavedra, Euler L.
    Osma, Johann F.
    NANOMATERIALS, 2024, 14 (11)
  • [28] Adaptation of life cycle assessment (LCA) to agricultural production on a regional scale in Japan
    Mishima, S
    Taniguchi, S
    Komada, M
    ECOSYSTEMS AND SUSTAINABLE DEVELOPMENT V, 2005, 81 : 671 - 678
  • [29] Life cycle assessment (LCA) of the industrial production of structural glued laminated bamboo
    Liu, Kewei
    Jayaraman, Durai
    Shi, Yongjiu
    Xiong, Zhenhua
    Yang, Jun
    Symeonidis, Avraam
    Escamilla, Edwin Zea
    Journal of Cleaner Production, 2024, 485
  • [30] EVALUATION OF THE ENVIRONMENTAL IMPACTS OF FRUIT PRODUCTION USING LIFE CYCLE ASSESSMENT (LCA)
    Butcaru, Ana Cornelia
    Catuneanu, Ioana Laura
    Stanica, Florin
    Badulescu, Liliana
    SCIENTIFIC PAPERS-SERIES B-HORTICULTURE, 2021, 65 (02): : 11 - 18