Artículos de revistas sobre el tema "Life cycle assessment"

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1

Zagursky, O. M. y E. А. Teslenko. "Length of life cycle assessment of vehicle". Naukovij žurnal «Tehnìka ta energetika» 10, n.º 1 (7 de febrero de 2019): 61–66. http://dx.doi.org/10.31548/machenergy2019.01.061.

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2

Pérez-Hernández, A., H. A. López-Aguilar, E. A. Huerta-Reynoso, J. A. Gómez, J. M. Olivarez-Ramírez y A. Duarte-Moller. "Life cycle assessment of regional brick manufacture". Materiales de Construcción 66, n.º 322 (15 de abril de 2016): e085. http://dx.doi.org/10.3989/mc.2016.02315.

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3

Anex, Robert y Reid Lifset. "Life Cycle Assessment". Journal of Industrial Ecology 18, n.º 3 (mayo de 2014): 321–23. http://dx.doi.org/10.1111/jiec.12157.

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4

White, Allen y Karen Shapiro. "Life Cycle Assessment". Environmental Science & Technology 27, n.º 6 (junio de 1993): 1016–17. http://dx.doi.org/10.1021/es00043a614.

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5

Šenitková, Ingrid y Petra Bednárová. "LIFE CYCLE ASSESSMENT". JP Journal of Heat and Mass Transfer 11, n.º 1 (27 de febrero de 2015): 29–42. http://dx.doi.org/10.17654/jphmtfeb2015_029_042.

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6

Rebitzer, G., T. Ekvall, R. Frischknecht, D. Hunkeler, G. Norris, T. Rydberg, W. P. Schmidt, S. Suh, B. P. Weidema y D. W. Pennington. "Life cycle assessment". Environment International 30, n.º 5 (julio de 2004): 701–20. http://dx.doi.org/10.1016/j.envint.2003.11.005.

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7

Duda, Mark y Jane S. Shaw. "Life cycle assessment". Society 34, n.º 6 (noviembre de 1997): 38–43. http://dx.doi.org/10.1007/s12115-997-1022-5.

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8

Duda, Mark y Jane S. Shaw. "Life cycle assessment". Society 35, n.º 1 (noviembre de 1997): 38–43. http://dx.doi.org/10.1007/s12115-997-1054-x.

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9

Baumann, Henrikke y Tomas Rydberg. "Life cycle assessment". Journal of Cleaner Production 2, n.º 1 (enero de 1994): 13–20. http://dx.doi.org/10.1016/0959-6526(94)90020-5.

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10

Klöpffer, Walter. "Life cycle assessment". Environmental Science and Pollution Research 4, n.º 4 (diciembre de 1997): 223–28. http://dx.doi.org/10.1007/bf02986351.

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11

Kalliala, Eija M. y Pertti Nousiainen. "Life Cycle Assessment". AUTEX Research Journal 1, n.º 1 (1 de noviembre de 1999): 8–20. http://dx.doi.org/10.1515/aut-1999-010102.

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Abstract The aim of this study was to increase the knowledge of environmental impact associated with producing fabrics for hotel textile services. The project was carried out in two parts: studies on hotel textiles and on textile services in three major Scandinavian laundering companies. This paper presents the results of the hotel textile study. The environmental impact was studied by applying the main principles of the life cycle assessment (LCA) methodology. Life-cycle assessments provide useful information on the quantities of energy and resources consumed and emissions associated with production systems. The impact assessment is still under development but some scenarios have been made to describe possible local, regional and global environmental consequences of the system under study. The inventory calculations proved that cotton fibre production consumes about 40% less energy than polyester fibre production. Cotton growing requires, however, huge amounts of water: irrigated amounts vary from 7 to 29 tons per kg of raw cotton fibres. Pesticides and fertilizers used in traditional cotton cultivation have ecotoxic effects in contrast to organic cotton cultivation, where natural alternatives to agrochemicals are used. It could also be concluded that 50/50 CO/PES sheets in hotel use have fewer environmental impacts than 100% CO sheets. This is due to the higher durability as well as lower laundering energy requirements of 50/50 CO/PES sheets.
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12

Liu, Kevin Fong-Rey, Jong-Yih Kuo, Yuan-Hua Chang y Han-Hsi Liang. "Optimization of Life Cycle Assessment-Based Eco-efficiency". International Journal of Environmental Science and Development 7, n.º 3 (2016): 211–15. http://dx.doi.org/10.7763/ijesd.2016.v7.770.

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13

Chau, C. K., T. M. Leung y W. Y. Ng. "A review on Life Cycle Assessment, Life Cycle Energy Assessment and Life Cycle Carbon Emissions Assessment on buildings". Applied Energy 143 (abril de 2015): 395–413. http://dx.doi.org/10.1016/j.apenergy.2015.01.023.

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14

Held, Martin y Walter Klöpffer. "Life Cycle Assessment Without Time? Time Matters in Life Cycle Assessment". GAIA - Ecological Perspectives for Science and Society 9, n.º 2 (1 de junio de 2000): 101–8. http://dx.doi.org/10.14512/gaia.9.2.7.

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15

Ryding, Sven Olof. "ISO 14042 Environmental management • Life cycle assessment • life cycle impact assessment". International Journal of Life Cycle Assessment 4, n.º 6 (noviembre de 1999): 307. http://dx.doi.org/10.1007/bf02978514.

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16

Fullana i Palmer, Pere, Rita Puig, Alba Bala, Grau Baquero, Jordi Riba y Marco Raugei. "From Life Cycle Assessment to Life Cycle Management". Journal of Industrial Ecology 15, n.º 3 (7 de abril de 2011): 458–75. http://dx.doi.org/10.1111/j.1530-9290.2011.00338.x.

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17

Liu, Kevin Fong-Rey, Si-Yu Chiu, Po-Chung Yeh y Jong-Yih Kuo. "Case Study of Using Life Cycle Impact Assessment in Environmental Impact Assessment". International Journal of Environmental Science and Development 6, n.º 11 (2015): 849–56. http://dx.doi.org/10.7763/ijesd.2015.v6.711.

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18

Li, Qingqing, Sean McGinnis, Cutter Sydnor, Anthony Wong y Scott Renneckar. "Nanocellulose Life Cycle Assessment". ACS Sustainable Chemistry & Engineering 1, n.º 8 (31 de mayo de 2013): 919–28. http://dx.doi.org/10.1021/sc4000225.

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19

Kirchain Jr, Randolph E., Jeremy R. Gregory y Elsa A. Olivetti. "Environmental life-cycle assessment". Nature Materials 16, n.º 7 (27 de junio de 2017): 693–97. http://dx.doi.org/10.1038/nmat4923.

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20

Zamagni, Alessandra. "Life cycle sustainability assessment". International Journal of Life Cycle Assessment 17, n.º 4 (22 de febrero de 2012): 373–76. http://dx.doi.org/10.1007/s11367-012-0389-8.

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21

Curran, MAry Ann. "Environmental life-cycle assessment". International Journal of Life Cycle Assessment 1, n.º 3 (septiembre de 1996): 179. http://dx.doi.org/10.1007/bf02978949.

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22

Andrews, Evan, Pascal Lesage, Catherine Benoît, Julie Parent, Gregory Norris y Jean-Pierre Revéret. "Life Cycle Attribute Assessment". Journal of Industrial Ecology 13, n.º 4 (agosto de 2009): 565–78. http://dx.doi.org/10.1111/j.1530-9290.2009.00142.x.

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23

Smith, Joyce K. y J. Jeffrey Peirce. "Life cycle assessment standards". International Journal of Life Cycle Assessment 1, n.º 2 (junio de 1996): 115–18. http://dx.doi.org/10.1007/bf02978658.

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24

Welker, B. "Life cycle assessment V". International Journal of Life Cycle Assessment 1, n.º 4 (diciembre de 1996): 225. http://dx.doi.org/10.1007/bf02978701.

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25

Saur, Konrad. "Life cycle impact assessment". International Journal of Life Cycle Assessment 2, n.º 2 (junio de 1997): 66–70. http://dx.doi.org/10.1007/bf02978760.

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26

Wani, M. F. y A. Anand. "Life-Cycle Assessment Modelling and Life-Cycle Assessment Evaluation of a Triboelement". Proceedings of the Institution of Mechanical Engineers, Part J: Journal of Engineering Tribology 224, n.º 11 (6 de julio de 2010): 1209–20. http://dx.doi.org/10.1243/13506501jet747.

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27

Sivani, G., D. Naveen, B. Revanth Reddy, Ch Deepak y G. Ajay. "Design and Life Cycle Assessment of ApartmentBuilding Using BIM". International Journal of Research Publication and Reviews 4, n.º 3 (10 de marzo de 2023): 1335–42. http://dx.doi.org/10.55248/gengpi.2023.32397.

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28

Klöpffer, Walter, Gerd Rippen y Isa Renner. "Produktlinienanalyse, Ökobilanz, Life Cycle Assessment/Life Cycle Analysis (LCA)". Umweltwissenschaften und Schadstoff-Forschung 3, n.º 3 (mayo de 1991): 189. http://dx.doi.org/10.1007/bf02988765.

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29

Wegener Sleeswijk, Anneke, Reinout Heijungs y Steffen T. rler. "Risk Assessment and Life-cycle Assessment". Greener Management International 2003, n.º 41 (1 de marzo de 2003): 77–87. http://dx.doi.org/10.9774/gleaf.3062.2003.sp.00008.

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30

Arulnathan, Vivek, Mohammad Davoud Heidari, Maurice Doyon, Eric P. H. Li y Nathan Pelletier. "Economic Indicators for Life Cycle Sustainability Assessment: Going beyond Life Cycle Costing". Sustainability 15, n.º 1 (20 de diciembre de 2022): 13. http://dx.doi.org/10.3390/su15010013.

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Life Cycle Costing (LCC) is universally accepted as the method of choice for economic assessment in Life Cycle Sustainability Assessment (LCSA) but the singular focus on costs is ineffective in representing the multiple facets of economic sustainability. This review intends to identify other economic indicators to potentially complement the use of LCC in LCSA. Papers for the review were identified in the Web of Science Core Collection database for the years 2010–2021. The shortlisted indicators were analyzed using 18 criteria. The 21 indicators analyzed performed well with respect to the review criteria for indicator methodology and use but most are unsuitable for direct integration into the LCC/LCSA framework due to the inability to aggregate across life cycles and a lack of correspondingly granular data. The indicators were grouped into six economic impact categories—profitability, productivity, innovation, stability, customers, and autonomy—each of which represents a significant aspect of economic sustainability. On this basis, a conceptual framework is proposed that could maintain the utility of LCC while integrating additional indicators to enable more holistic economic assessments in LCSA. Considering additional economic indicators in LCSA ensures that the positive aspects of LCC are preserved while also improving economic assessment in LCSA.
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31

Irawati, Desrina Yusi y Melati Kurniawati. "Life Cycle Assessment dan Life Cycle Cost untuk Serat Kenaf". Jurnal Rekayasa Sistem Industri 9, n.º 3 (27 de octubre de 2020): 213–24. http://dx.doi.org/10.26593/jrsi.v9i3.4109.213-224.

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Kenaf fiber from the kenaf plant is the excellent raw material for industry because of the various diversified products it produces. To develop sustainable kenaf fiber, information is needed on the strengths and weaknesses of kenaf cultivation systems with respect to productivity and environmental impact. Therefore, a comprehensive environmental and economic impact assessment was conducted from cultivating kenaf to kenaf fiber. The environmental impact assessment uses the Life Cycle Assessment (LCA) method and economic calculations from the life cycle of kenaf to kenaf fiber to collectors use the Life Cycle Cost (LCC) method. The calculation of environmental impacts is in accordance with the stages of ISO 14040, using a single score assessment. The LCA results show that the treatment stage is the highest contributor of the three groups of impact categories. The highest to the lowest in the impact category group that was influenced by the treatment stage were resources with a value of 21.4 mPt, human health with a value of 8.76 mPt, and ecosystem quality with a value of 1.91 mPt. The cost identified through the LCC is Rp. 6,088,468,333, NVP and B/Cnet are positive. The results of the sensitivity analysis if there is a reduction in production> 6%, the business is still profitable and can be run.
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32

Lecouls, Henri. "ISO 14043: Environmental management · life cycle assessment · life cycle interpretation". International Journal of Life Cycle Assessment 4, n.º 5 (septiembre de 1999): 245. http://dx.doi.org/10.1007/bf02979166.

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33

N. Kamble, Nikhil y Gunavant K. Kate. "Cradle-to-Gate Life Cycle Assessment of Compostable Coffee Lids". International Journal of Science and Research (IJSR) 12, n.º 9 (5 de septiembre de 2023): 1601–4. http://dx.doi.org/10.21275/sr23919195433.

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34

Brock, Alice y Ian D. Williams. "Life Cycle Assessment of Beverage Packaging". Detritus, n.º 13 (5 de octubre de 2020): 47–61. http://dx.doi.org/10.31025/2611-4135/2020.14025.

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Global plastic production has been increasing annually since World War II and is currently 380 million tonnes. Global concern about pollution from plastics in the seas and the environmental costs of plastics manufacture is rising. This study aimed to: i) review the costs, benefits, advantages / disadvantages of plastics as packaging materials and ii) use life cycle assessment to determine if there is less environmentally impactful beverage packaging than plastic bottles. As different beverages have different packaging needs, three categories were used: commonly used containers for milk, fruit juice and pressurised ‘fizzy’ drinks. The packaging types included in the assessment were glass bottles, aluminium cans, milk cartons, Tetra Pak, polyethylene terephthalate (PET) bottles and high-density polythene (HDPE) bottles. The ISO 14040:2006 and ISO 14044:2006 standards for life cycle assessment formed the basis of the methodology. The open source software openLCA was used to conduct the assessments. Data was assembled from LCA databases such as the European reference Life Cycle Database of the Joint Research Center (ELCD), existing life cycle assessments, scientific reports and peer reviewed literature. The functional unit was set at a container that held one litre of fluid. The results found that in each category there was a less impactful beverage packaging than plastic bottles. In the Pressurised Beverage Category, 100% recycled aluminium cans would be the least impactful option, in the Fruit Juice Beverage Category Tetra Pak would be the least impactful option and in the Milk Beverage Category milk cartons would be the least impactful option.
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35

Chang, Ya-Ju, The Duy Nguyen, Matthias Finkbeiner y Jörg Krüger. "Adapting Ergonomic Assessments to Social Life Cycle Assessment". Procedia CIRP 40 (2016): 91–96. http://dx.doi.org/10.1016/j.procir.2016.01.064.

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36

Grant, Aneurin, Robert Ries y Charles Kibert. "Life Cycle Assessment and Service Life Prediction". Journal of Industrial Ecology 18, n.º 2 (6 de febrero de 2014): 187–200. http://dx.doi.org/10.1111/jiec.12089.

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37

Yotsuyanagi, Masahiko y Shigehiro Satou. "Life Cycle Assessment for Luminaire". JOURNAL OF THE ILLUMINATING ENGINEERING INSTITUTE OF JAPAN 82, n.º 10 (1998): 828–29. http://dx.doi.org/10.2150/jieij1980.82.10_828.

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38

Shiina, Takeo. "Life Cycle Assessment of Food". Nippon Shokuhin Kagaku Kogaku Kaishi 52, n.º 7 (2005): 324. http://dx.doi.org/10.3136/nskkk.52.324.

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39

Locker, C. Rebecca y Ranjani Theregowda. "Life-cycle assessment of Bioleather1". Cleaner and Circular Bioeconomy 1 (abril de 2022): 100003. http://dx.doi.org/10.1016/j.clcb.2022.100003.

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40

Wu, Ruqun, Dan Yang y Jiquan Chen. "Social Life Cycle Assessment Revisited". Sustainability 6, n.º 7 (2 de julio de 2014): 4200–4226. http://dx.doi.org/10.3390/su6074200.

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41

Rajagopal, Deepak, Caroline Vanderghem y Heather L. MacLean. "Life Cycle Assessment for Economists". Annual Review of Resource Economics 9, n.º 1 (5 de octubre de 2017): 361–81. http://dx.doi.org/10.1146/annurev-resource-100815-095513.

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42

Malmodin, Jens, Dag Lundén, Åsa Moberg, Greger Andersson y Mikael Nilsson. "Life Cycle Assessment of ICT". Journal of Industrial Ecology 18, n.º 6 (16 de mayo de 2014): 829–45. http://dx.doi.org/10.1111/jiec.12145.

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43

Kesic, Jelena y Dejan Skala. "Antifreeze life cycle assessment (LCA)". Chemical Industry 59, n.º 5-6 (2005): 132–40. http://dx.doi.org/10.2298/hemind0506132k.

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Antifreeze based on ethylene glycol is a commonly used commercial product The classification of ethylene glycol as a toxic material increased the disposal costs for used antifreeze and life cycle assessment became a necessity. Life Cycle Assessment (LCA) considers the identification and quantification of raw materials and energy inputs and waste outputs during the whole life cycle of the analyzed product. The objectives of LCA are the evaluation of impacts on the environment and improvements of processes in order to reduce and/or eliminate waste. LCA is conducted through a mathematical model derived from mass and energy balances of all the processes included in the life cycle. In all energy processes the part of energy that can be transformed into some other kind of energy is called exergy. The concept of exergy considers the quality of different types of energy and the quality of different materials. It is also a connection between energy and mass transformations. The whole life cycle can be described by the value of the total loss of exergy. The physical meaning of this value is the loss of material and energy that can be used. The results of LCA are very useful for the analyzed products and processes and for the determined conditions under which the analysis was conducted. The results of this study indicate that recycling is the most satisfactory solution for the treatment of used antifreeze regarding material and energy consumption but the re-use of antifreeze should not be neglected as a solution.
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44

Finkbeiner, Matthias, Erwin M. Schau, Annekatrin Lehmann y Marzia Traverso. "Towards Life Cycle Sustainability Assessment". Sustainability 2, n.º 10 (22 de octubre de 2010): 3309–22. http://dx.doi.org/10.3390/su2103309.

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45

Hertwich, Edgar. "Books: Environmental Life-Cycle Assessment". Journal of Industrial Ecology 1, n.º 4 (octubre de 1997): 128–31. http://dx.doi.org/10.1162/jiec.1997.1.4.128.

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46

Holmberg, John. "Books: Streamlined Life-Cycle Assessment". Journal of Industrial Ecology 3, n.º 1 (diciembre de 1999): 130–33. http://dx.doi.org/10.1162/jiec.1999.3.1.130.

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47

NAKANISHI, Eiji. "Life Cycle Assessment of Plastics". Kobunshi 47, n.º 12 (1998): 890. http://dx.doi.org/10.1295/kobunshi.47.890.

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48

Edwards, D. W. y J. Schelling. "Municipal Waste Life Cycle Assessment". Process Safety and Environmental Protection 77, n.º 5 (septiembre de 1999): 259–74. http://dx.doi.org/10.1205/095758299530143.

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49

Cerdas, Felipe, Sebastian Thiede, Max Juraschek, Artem Turetskyy y Christoph Herrmann. "Shop-floor Life Cycle Assessment". Procedia CIRP 61 (2017): 393–98. http://dx.doi.org/10.1016/j.procir.2016.11.178.

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50

Ciroth, Andreas. "Uncertainties in life cycle assessment". International Journal of Life Cycle Assessment 9, n.º 3 (mayo de 2004): 141–42. http://dx.doi.org/10.1007/bf02994186.

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