Academic literature on the topic 'Life energy cycle assessment'

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Journal articles on the topic "Life energy cycle assessment"

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

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Kesic, Jelena, and Dejan Skala. "Antifreeze life cycle assessment (LCA)." Chemical Industry 59, no. 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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Baumann, Henrikke, and Tomas Rydberg. "Life cycle assessment." Journal of Cleaner Production 2, no. 1 (January 1994): 13–20. http://dx.doi.org/10.1016/0959-6526(94)90020-5.

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INOUE, Takashi. "Life Cycle Assessment on Biomass Energy Use." Journal of Life Cycle Assessment, Japan 4, no. 2 (2008): 135–40. http://dx.doi.org/10.3370/lca.4.135.

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Uihlein, Andreas. "Life cycle assessment of ocean energy technologies." International Journal of Life Cycle Assessment 21, no. 10 (April 28, 2016): 1425–37. http://dx.doi.org/10.1007/s11367-016-1120-y.

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Asdrubali, F., and G. Grazieschi. "Life cycle assessment of energy efficient buildings." Energy Reports 6 (December 2020): 270–85. http://dx.doi.org/10.1016/j.egyr.2020.11.144.

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Chau, C. K., T. M. Leung, and W. Y. Ng. "Corrigendum to “A review on Life Cycle Assessment, Life Cycle Energy Assessment and Life Cycle Carbon Emissions Assessment on buildings” [Appl. Energy 143 (2015) 395–413]." Applied Energy 158 (November 2015): 656. http://dx.doi.org/10.1016/j.apenergy.2015.08.093.

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Miller, Veronica B., Amy E. Landis, and Laura A. Schaefer. "A benchmark for life cycle air emissions and life cycle impact assessment of hydrokinetic energy extraction using life cycle assessment." Renewable Energy 36, no. 3 (March 2011): 1040–46. http://dx.doi.org/10.1016/j.renene.2010.08.016.

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Kesic, Jelena, and Dejan Skala. "Antifreeze life cycle assessment, II: Mathematical modeling." Chemical Industry and Chemical Engineering Quarterly 11, no. 2 (2005): 85–92. http://dx.doi.org/10.2298/ciceq0502085k.

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A mathematical model based on the mass and energy balances of all the processes included in antifreeze life cycle assessment (LCA) was defined in the first part of this study [1]. The part of energy that can be transformed into some other kind of energy is called exergy in all energy processes. The concept of exergy considers the quality of different types of energy and materials. It is also a connection between energy and mass transformations where the physical meaning of exergy loss is the loss of material and energy that must be used in the process. The results of the LCA calculation are very useful for analyzing the obtained products and used processes and for determining the conditions under which this analysis was conducted. The result of this study indicated that recycling is the most satisfactory solution for the treatment of used antifreeze taking into account two parameters: material and energy consumption. The reuse of antifreeze should not be neglected as a solution of this analysis.
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Menzies, G. F., S. Turan, and P. F. G. Banfill. "Life-cycle assessment and embodied energy: a review." Proceedings of the Institution of Civil Engineers - Construction Materials 160, no. 4 (November 2007): 135–43. http://dx.doi.org/10.1680/coma.2007.160.4.135.

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Dissertations / Theses on the topic "Life energy cycle assessment"

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Hau, Jorge Luis. "Integrating life cycle assessment, energy and emergy analysis." The Ohio State University, 2002. http://rave.ohiolink.edu/etdc/view?acc_num=osu1407139681.

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Gastelum, Zepeda Leonardo. "Life Cycle Assessment of a Wave Energy Converter." Thesis, KTH, Industriell ekologi, 2017. http://urn.kb.se/resolve?urn=urn:nbn:se:kth:diva-206486.

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Renewable energies had accomplish to become part of a new era in the energy development area, making people able to stop relying on fossil fuels. Nevertheless the environmental impacts of these new energy sources also require to be quantified in order to review how many benefits these new technologies have for the environment. In this project the use of a Life Cycle Assessment (LCA) will be implemented in order to quantify the environmental impact of wave energy, an LCA is a technique for assessing various aspects with the development of a product and its potential impact throughout a product’s life (ISO 14040, 1997). Several renewables have been assessed for their environmental impact using this tool (wind power, biofuels, photovoltaic panels, among others). This project will be focused on the study of wave power, specifically devices called point absorbers.At the beginning this thesis offers a description of the Life Cycle Assessment methodology with a brief explanation of each steps and requirements according to the ISO 14000 Standard. Later a description of different wave energy technologies is explained, along with the classification of different devices depending on its location and its form of harvesting energy. After explaining the different types available at the moment, the thesis will focus on the point absorber device and explain an approach that can be taken in order to simplify the complexity of the whole system.Once the device is fully explained the thesis approaches the methodology pursued in order to evaluate the system in terms of environmental impact in the selected category, for this case global warming. After, an evaluation of the different modules from the wave energy converter in terms of its environmental impact and choosing the best conditions in order to reduce it has being done.At the end of the thesis an economical overview of building wave energy converters is considered among its monetized cost to the environment and a comparison of this new technologies among other renewables in the market is done, in order to have an overview of the potential this type of energy can have.The main research question to be answered by this master thesis is how competitive is wave energy among other renewable technologies available at the moment. Since at the moment wave energy is in its early stages a representation of how other renewables had advanced from its early stages until today is presented, and the potential of this type of energy is evaluated in environmental and economic figures showing competitive results that can further be improved.
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Lohse, Tim. "Life cycle assessment of a plus-energy house." Thesis, KTH, Hållbar utveckling, miljövetenskap och teknik, 2020. http://urn.kb.se/resolve?urn=urn:nbn:se:kth:diva-266478.

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Purpose: This study analyses the environmental impacts of a plus-energy house. Such buildings produce more energy in their use-phase than they consume, by generating energy with photovoltaic cells and saving energy via extensive insulation. The entire life cycle of the building is investigated form cradle to grave. The research focuses on the identification of environmental hotspots and the break-even time, after which the avoided burdens from the energy surplus even out the environmental impacts. Method: To answer the research questions, an ISO 14040 compliant environmental impact assessment (LCA) was conducted. It covers the raw material extraction, production and manufacturing of the building, the energy consumption by the inhabitants, the demolition and subsequent waste processing as well as the energy generation from the photovoltaic cells during 50 years lifetime. The life cycle impact assessment method was based on EN 15804 with seven impact categories: global warming potential, depletion potential of the stratospheric ozone, acidification potential of soil and water, eutrophication potential, formation potential of tropospheric ozone, abiotic depletion potential for non-fossil resources, and abiotic depletion potential for fossil resources. Results: The use-phase with energy generation and consumption dominates in all the impact categories except for the stratospheric ozone depletion potential. Photovoltaic cell production has the largest impact in terms of resource and ozone depletion. The building does not set off its impacts with its avoided burdens during its lifetime. The break-even time is calculated for each impact category and starts at 654 years for global warming potential. The geometric standard deviation is calculated for every process, so that a Monte-Carlo simulation can be run. This makes it possible to calculate the standard deviation of the results. Discussion: It is possible to enhance the environmental performance of the building by focusing on the hotspots. A sensitivity analysis shows that enhancing the energy surplus during the use-phase would be the most effective measure. This could be achieved by increasing the photovoltaic cell area or decreasing the energy consumption.
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Fedoruk, M. "Life cycle assessment of energy saving measures in buildings." Thesis, Sumy State University, 2017. http://essuir.sumdu.edu.ua/handle/123456789/64686.

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The energy sector itself poses greаt chаllenges for most countries, especiаlly with the present finаnciаl аnd environmentаl circumstаnces аnd the need to enhаnce economic development while meeting climаte chаnge goаls.
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Petrovic, Bojana. "Life cycle assessment and life cycle cost analysis of a single-family house." Licentiate thesis, Högskolan i Gävle, Energisystem och byggnadsteknik, 2021. http://urn.kb.se/resolve?urn=urn:nbn:se:hig:diva-36901.

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The building industry is responsible for 35% of final energy use and 38% of CO2 emissions at a global level. The European Union aims to reduce CO2 emissions in the building industry by up to 90% by the year 2050. Therefore, it is important to consider the environmental impacts buildings have. The purpose of this thesis was to investigate the environmental impacts and costs of a single-family house in Sweden. In the study, the life cycle assessment (LCA) and the life cycle cost (LCC) methods have been used by following the “cradle to grave” life cycle perspective.  This study shows a significant reduction of global warming potential (GWP), primary energy (PE) use and costs when the lifespan of the house is shifted from 50 to 100 years. The findings illustrate a total decrease in LCA outcome, of GWP to 27% and PE to 18%. Considering the total LCC outcome, when the discount rate increases from 3% to 5% and then 7%, the total costs decrease significantly (60%, 85% to 95%). The embodied carbon, PE use and costs from the production stage/construction stage are significantly reduced, while the maintenance/replacement stage displays the opposite trend. Operational energy use, water consumption and end-of-life, however, remain largely unchanged. Furthermore, the findings emphasize the importance of using wood-based building materials due to its lower carbon-intensive manufacturing process compared to non-wood choices.   The results of the LCA and LCC were systematically studied and are presented visually. Low carbon and cost-effective materials and installations have to be identified in the early stage of a building design so that the appropriate investment choices can be made that will reduce a building’s total environmental and economic impact in the long run. Findings from this thesis provide a greater understanding of the environmental and economic impacts that are relevant for decision-makers when building single-family houses.
Byggbranschen svarar för 35% av den slutliga energianvändningen och 38 % av koldioxidutsläppen på global nivå. Europeiska unionen strävar efter att minska koldioxidutsläppen i byggnadsindustrin med upp till 90% fram till 2050. Därför är det viktigt att beakta byggnaders miljöpåverkan. Syftet med denna avhandling var att undersöka miljöpåverkan och kostnader för ett enfamiljshus i Sverige. I studien har livscykelbedömningen (LCA) och livscykelkostnadsmetoderna (LCC) använts genom att tillämpa livscykelperspektivet ”vagga till grav”. Studien visar en stor minskning av global uppvärmningspotential (GWP), användning av primärenergi (PE) och kostnader vid växling från 50 till 100 års husets livslängd. Resultaten visar en årlig minskning med 27% för utsläpp av växthusgaser och med 18% för användningen av primärenergi. Med tanke på det totala LCC-utfallet, när diskonteringsräntan ökar från 3%, 5% till 7%, minskar de totala kostnaderna avsevärt (60%, 85% till 95%). Det noteras att klimatavtrycket, primärenergianvändningen och kostnaderna från produktionssteget/konstruktionssteget minskar avsevärt, medan underhålls- / utbytessteget visar den motsatta trenden när man byter från 50 till 100 års livslängd. Den operativa energianvändningen, vattenförbrukningen och avfallshanteringen är fortfarande nästan samma när man ändrar livslängden. Vidare betonar resultaten vikten av att använda träbaserade byggmaterial på grund av lägre klimatpåverkan från tillverkningsprocessen jämfört med alternativen. LCA- och LCC-resultaten studerades systematiskt och redovisades visuellt. De koldioxidsnåla och kostnadseffektiva materialen och installationerna måste identifieras i ett tidigt skede av en byggnadskonstruktion genom att välja lämpliga investeringsval som kommer att minska de totala miljö och ekonomiska effekterna på lång sikt. Resultaten från denna avhandling ger ökad förståelse för miljömässiga och ekonomiska konsekvenser som är relevanta för beslutsfattare vid byggnation av ett enfamiljshus.
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Yossef, Delav, and Dino Hot. "Comparative life cycle assessment of organic building materials." Thesis, Högskolan Dalarna, Institutionen för information och teknik, 2021. http://urn.kb.se/resolve?urn=urn:nbn:se:du-37774.

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The ever-increasing awareness of global warming has made the building industry startlooking for alternative building solutions in order to meet the changing demands. Thesechallenges have given rise to organization which aim to go further and construct moresustainable alternatives in the form of Ecovillages. This thesis is conducted in collaborationwith Bysjöstrans Ekoby and aims to investigate what type of organic alternatives exist andhow they perform in building elements.The study was carried out through a comparative LCA where a base case construction forboth roof and wall was established. Followed by comparing different organic materials toeach other and the base case materials in order to determine low-impact materials. The goalwas to replaces as many layers within the structure such as insulation, structure, roofcladding, façade, wind and vapor barrier.This was later followed by combing the materials together in order to identify whichalternative construction options would perform the best in regard to greenhouse gasemissions (CO2 eq kg) and primary energy use (MJ).The results of the study show that the performance or organic materials vary significantly.Whit a lot of materials being better but also worse than traditional materials. It showed thatfor internal wall and roof surface adding clay plater can reduce the GHG emission with 68%, timber frame with 98 %, façade with 43 %, roof cladding with 93 %, vapor barrier with76 % and insulation with 79 %. The best preforming construction option could reduce thebase case emission with 68 %.
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Dahlsten, Hilda. "Life Cycle Assessment of Electricity from Wave Power." Thesis, Institutionen för energi och teknik, SLU, 2009. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-162582.

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The use of ocean wave energy for electricity production has considerable potential, though it has proven to be difficult. A technology utilizing the heaving (up-and-down) motions of the waves was conceived at Uppsala University in the early 2000´s, and is being further developed for commercial use by Seabased Industry AB. The purpose of this master´s degree project was to increase the knowledge of the environmental performance of Seabased´s wave energy conversion concept and identifying possible areas of improvement. This was done by conducting a life cycle assessment (LCA) of a hypothetical prototype wave power plant. All flows of materials, energy, emissions and waste were calculated for all stages of a wave power plant´s life cycle. The potential environmental impact of these flows was then assessed, using the following impact categories: • Emission of greenhouse gases • Emission of ozone depleting gases • Emission of acidifying gases • Emission of gases that contribute to the forming of ground-level ozone • Emission of substances to water contributing to oxygen depletion (eutrophication) • Energy use (renewable and non-renewable) • Water use The methodology used was that prescribed by the ISO standard for Environmental Product Declarations (EPD) and further defined by the International EPD Programme.The potential environmental impact was calculated per kWh of wave power electricity delivered to the grid. The main result of the study is that the potential environmental impact of a wave power plant mainly stems from the manufacturing phase. In particular, the production of steel parts makes a large contribution to the overall results. Future wave power plant designs are expected to be considerably more material efficient, meaning that there are large possibilities to improve the environmental performance of this technology.
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Davidsson, Simon. "Life Cycle Exergy Analysis of Wind Energy Systems : Assessing and improving life cycle analysis methodology." Thesis, Uppsala universitet, Globala energisystem, 2011. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-157185.

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Wind power capacity is currently growing fast around the world. At the same time different forms of life cycle analysis are becoming common for measuring the environmental impact of wind energy systems. This thesis identifies several problems with current methods for assessing the environmental impact of wind energy and suggests improvements that will make these assessments more robust. The use of the exergy concept combined with life cycle analysis has been proposed by several researchers over the years. One method that has been described theoretically is life cycle exergy analysis (LCEA). In this thesis, the method of LCEA is evaluated and further developed from earlier theoretical definitions. Both benefits and drawbacks with using exergy based life cycle analysis are found. For some applications the use of exergy can solve many of the issues with current life cycle analysis methods, while other problems still remain. The method of life cycle exergy analysis is used to evaluate the sustainability of an existing wind turbine. The wind turbine assessed appears to be sustainable in the way that it gives back many times more exergy than it uses during the life cycle.
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Jones, Craig I. "Life cycle energy consumption and environmental burdens associated with energy technologies and buildings." Thesis, University of Bath, 2011. https://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.532723.

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This portfolio of published research contains nine papers and assesses the life cycle environmental burdens of energy technologies and buildings. Several analytical tools were used but these all fall under the umbrella of environmental life cycle assessment (LCA), and include energy analysis, carbon appraisal and the consideration of other environmental issues. The life cycle of all products starts with an assessment of embodied impacts. The current author has completed significant research on the embodied carbon of materials. This includes the creation of a leading embodied carbon database (the ICE database) for materials which has been downloaded by over 10,000 professionals and has made a significant contribution to knowledge. This portfolio of work includes analysis on methods for recycling in embodied impact assessment and LCA. This is an influential topic and therefore appears in two of the publications. The ICE database was applied by the current author to over 40 domestic building case studies and an embodied carbon model for buildings was created from these. The latter was used to provide benchmark values for six types of new houses in the UK.The portfolio of work then progresses to full LCA of energy systems. LCA is used to assess the embodied impacts versus operational impacts of 11 kV electrical cables. In this case embodied impacts were not significant and preference should be given to reducing electrical losses in the cables. The tool of LCA was then applied to a national electricity network. It revealed that Lebanon had a particularly poor centralised electricity network that was both unreliable and unsustainable with high impacts in all environmental categories. The final paper in this portfolio is on Building Integrated PV (BIPV) and brings together all aspects of the current author’s work and knowledge. It considers embodied burdens, electricity generation and BIPV can replace roofing materials.
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Dong, Jun. "MSWs gasification with emphasis on energy, environment and life cycle assessment." Thesis, Ecole nationale des Mines d'Albi-Carmaux, 2016. http://www.theses.fr/2016EMAC0017/document.

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Récemment, la pyro-gazéification de déchets ménagers solides (DMS) a suscité une plus grande attention, en raison de ses bénéfices potentiels en matière d’émissions polluantes et d’efficacité énergique. Afin de développer un système de traitement de ces déchets, durable et intégré, ce manuscrit s’intéresse plus spécifiquement au développement de la technique de pyro-gazéification des DMS, à la fois sur l’aspect technologique (expérimentations) et sur son évaluation globale (modélisation). Pour cette étude, quatre composants principaux représentatifs des DMS (déchet alimentaire, papier, bois et plastique) ont été pyro-gazéifiés dans un lit fluidisé sous atmosphère N2, CO2 ou vapeur d’eau. Les expériences ont été menées avec les composés seuls ou en mélanges afin de comprendre les interactions mises en jeu et leurs impacts sur la qualité du syngas produit. La présence de plastique améliore significativement la quantité et la qualité du syngas (concentration de H2). La qualité du syngas est améliorée plus particulièrement en présence de vapeur d’eau, ou, dans une moindre mesure, en présence de CO2. Les résultats obtenus ont été ensuite intégrés dans un modèle prédictif de pyro-gazéification basé sur un réseau de neurones artificiels (ANN). Ce modèle prédictif s’avère efficace pour prédire les performances de pyro-gazéification des DMS, quelle que soit leur composition (provenance géographique). Pour améliorer la qualité du syngas et abaisser la température du traitement, la gazéification catalytique in-situ, en présence de CaO, a été menée. L’impact du débit de vapeur d’eau, du ratio massique d’oxyde de calcium, ainsi que de la température de réaction a été étudié en regard de la production (quantité et pourcentage molaire dans le gaz) d’hydrogène. La présence de CaO a permis d’abaisser de 100 oC la température de gazéification, à qualité de syngas équivalente. Pour envisager une application industrielle, l’activité du catalyseur a aussi été évaluée du point de vue de sa désactivation et régénération. Ainsi, les températures de carbonatation et de calcination de 650 oC et 800 oC permettent de prévenir la désactivation du catalyseur, tandis que l’hydratation sous vapeur d’eau permet la régénération. Ensuite, une étude a été dédiée à l’évaluation et à l’optimisation de la technologie de pyro-gazéification par la méthode d’analyse de cycle de vie (ACV). Le système de gazéification permet d’améliorer les indicateurs de performances environnementales comparativement à l’incinération conventionnelle. De plus, des systèmes combinant à la fois la transformation des déchets en vecteur énergétique et la mise en œuvre de ce vecteur ont été modélisés. La pyro-gazéification combinée à une turbine à gaz permettrait de maximiser l’efficacité énergétique et de diminuer l’impact environnemental du traitement. Ainsi, les résultats permettent d’optimiser les voies actuelles de valorisation énergétique, et de d’optimiser les techniques de pyro-gazéification
Due to the potential benefits in achieving lower environmental emissions and higher energy efficiency, municipal solid waste (MSW) pyro-gasification has gained increasing attentions in the last years. To develop such an integrated and sustainable MSW treatment system, this dissertation mainly focuses on developing MSW pyro-gasification technique, including both experimental-based technological investigation and assessment modeling. Four of the most typical MSW components (wood, paper, food waste and plastic) are pyro-gasified in a fluidized bed reactor under N2, steam or CO2 atmosphere. Single-component and multi-components mixture have been investigated to characterize interactions regarding the high-quality syngas production. The presence of plastic in MSW positively impacts the volume of gas produced as well as its H2 content. Steam clearly increased the syngas quality rather than the CO2 atmosphere. The data acquired have been further applied to establish an artificial neural network (ANN)-based pyro-gasification prediction model. Although MSW composition varies significantly due to geographic differences, the model is robust enough to predict MSW pyro-gasification performance with different waste sources. To further enhance syngas properties and reduce gasification temperature as optimization of pyro-gasification process, MSW steam catalytic gasification is studied using calcium oxide (CaO) as an in-situ catalyst. The influence of CaO addition, steam flowrate and reaction temperature on H2-rich gas production is also investigated. The catalytic gasification using CaO allows a decrease of more than 100 oC in the reaction operating temperature in order to reach the same syngas properties, as compared with non-catalyst high-temperature gasification. Besides, the catalyst activity (de-activation and re-generation mechanisms) is also evaluated in order to facilitate an industrial application. 650 oC and 800 oC are proven to be the most suitable temperature for carbonation and calcination respectively, while steam hydration is shown to be an effective CaO re-generation method. Afterwards, a systematic and comprehensive life cycle assessment (LCA) study is conducted. Environmental benefits have been achieved by MSW gasification compared with conventional incineration technology. Besides, pyrolysis and gasification processes coupled with various energy utilization cycles are also modeled, with a gasification-gas turbine cycle system exhibits the highest energy conversion efficiency and lowest environmental burden. The results are applied to optimize the current waste-to-energy route, and to develop better pyro-gasification techniques
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Books on the topic "Life energy cycle assessment"

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Demirbas, Ayhan. Waste Energy for Life Cycle Assessment. Cham: Springer International Publishing, 2016. http://dx.doi.org/10.1007/978-3-319-40551-3.

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Sakellariou, Nicholas. Life Cycle Assessment of Energy Systems. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2018. http://dx.doi.org/10.1002/9781119418580.

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Singh, Anoop, Deepak Pant, and Stig Irving Olsen, eds. Life Cycle Assessment of Renewable Energy Sources. London: Springer London, 2013. http://dx.doi.org/10.1007/978-1-4471-5364-1.

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Basosi, Riccardo, Maurizio Cellura, Sonia Longo, and Maria Laura Parisi, eds. Life Cycle Assessment of Energy Systems and Sustainable Energy Technologies. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-319-93740-3.

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Mann, Margaret K. Life cycle assessment of a biomass gasification combined-cycle power system. Golden, CO (1617 Cole Blvd., Golden 880401-3393): National Renewal Energy Laboratory, [1999], 1997.

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Life, Cycle Assessment Symposium (1996 Atlanta GA). TAPPI/AF&PA/NCASI Life Cycle Assessment Symposium: Methods and application for the forest products industry. Atlanta, GA: TAPPI Press, 1996.

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Minnesota Office of Environmental Assistance. Assessment of the effect of MSW management on resource conservation and greenhouse gas emissions. Minnesota?]: R.W. Beck, 1999.

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Association, Canadian Standards. Life cycle assessment. Rexdale, Ont: Canadian Standards Association, 1994.

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Borrion, Aiduan, Mairi J. Black, and Onesmus Mwabonje, eds. Life Cycle Assessment. Cambridge: Royal Society of Chemistry, 2021. http://dx.doi.org/10.1039/9781788016209.

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Hauschild, Michael Z., Ralph K. Rosenbaum, and Stig Irving Olsen, eds. Life Cycle Assessment. Cham: Springer International Publishing, 2018. http://dx.doi.org/10.1007/978-3-319-56475-3.

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Book chapters on the topic "Life energy cycle assessment"

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Laurent, Alexis, Nieves Espinosa, and Michael Z. Hauschild. "LCA of Energy Systems." In Life Cycle Assessment, 633–68. Cham: Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-56475-3_26.

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Dinçer, İbrahim, and Calin Zamfirescu. "Life-Cycle Assessment." In Sustainable Energy Systems and Applications, 663–700. Boston, MA: Springer US, 2011. http://dx.doi.org/10.1007/978-0-387-95861-3_15.

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Dones, Roberto, Xin Zhou, and Chunxiu Tian. "Life Cycle Assessment." In Integrated Assessment of Sustainable Energy Systems in China The China Energy Technology Program, 319–444. Dordrecht: Springer Netherlands, 2003. http://dx.doi.org/10.1007/978-94-010-0153-3_8.

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Falano, Temitope, and Patricia Thornley. "Life Cycle Assessment." In Biomass Energy with Carbon Capture and Storage (BECCS): Unlocking Negative Emissions, 117–27. Chichester, UK: John Wiley & Sons, Ltd, 2018. http://dx.doi.org/10.1002/9781119237716.ch6.

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Huang, Yue, and Tony Parry. "Pavement Life Cycle Assessment." In Climate Change, Energy, Sustainability and Pavements, 1–40. Berlin, Heidelberg: Springer Berlin Heidelberg, 2014. http://dx.doi.org/10.1007/978-3-662-44719-2_1.

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Fthenakis, Vasilis. "Life Cycle Assessment of Photovoltaics." In Photovoltaic Solar Energy, 646–57. Chichester, UK: John Wiley & Sons, Ltd, 2017. http://dx.doi.org/10.1002/9781118927496.ch57.

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Moreau, V. "Chapter 14. Resource Impacts of Fully Renewable Energy Systems: The Case of Metals." In Life Cycle Assessment, 337–57. Cambridge: Royal Society of Chemistry, 2021. http://dx.doi.org/10.1039/9781788016209-00337.

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Saravanan, A., and P. Senthil Kumar. "Social Life Cycle Assessment of Renewable Bio-Energy Products." In Social Life Cycle Assessment, 99–111. Singapore: Springer Singapore, 2018. http://dx.doi.org/10.1007/978-981-13-3233-3_3.

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Randolph, John, and Gilbert M. Masters. "Energy Analysis and Life-Cycle Assessment." In Energy for Sustainability, 133–69. Washington, DC: Island Press/Center for Resource Economics, 2018. http://dx.doi.org/10.5822/978-1-61091-821-3_5.

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Kumari, Neelima, Km Swapnil Singh, and Pratham Arora. "Life Cycle Assessment of Algal Biofuels." In Clean Energy Production Technologies, 67–98. Singapore: Springer Singapore, 2022. http://dx.doi.org/10.1007/978-981-16-4509-9_4.

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Conference papers on the topic "Life energy cycle assessment"

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Kreucher, Walter M., Weijian Han, Dennis Schuetzle, Zhu Qiming, Zhang Alin, Zhao Ruilan, Sun Baiming, and Malcolm A. Weiss. "Economic, Environmental and Energy Life-Cycle Assessment of Coal Conversion to Automotive Fuels in China." In Total Life Cycle Conference & Exposition. 400 Commonwealth Drive, Warrendale, PA, United States: SAE International, 1998. http://dx.doi.org/10.4271/982207.

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Ion, Georgiana, Sorina Costinas, Andrei Stan, and Florin Balasiu. "Assessment of Life Cycle of Autotransformers." In 2022 International Conference on Electrical, Computer and Energy Technologies (ICECET). IEEE, 2022. http://dx.doi.org/10.1109/icecet55527.2022.9872982.

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Khanna, Vikas, Bhavik R. Bakshi, and L. James Lee. "Life Cycle Energy Analysis and Environmental Life Cycle Assessment of Carbon Nanofibers Production." In 2007 IEEE International Symposium on Electronics and the Environment. IEEE, 2007. http://dx.doi.org/10.1109/isee.2007.369380.

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Li, Shuyun. "A case study by life cycle assessment." In MATERIALS SCIENCE, ENERGY TECHNOLOGY, AND POWER ENGINEERING I: 1st International Conference on Materials Science, Energy Technology, Power Engineering (MEP 2017). Author(s), 2017. http://dx.doi.org/10.1063/1.4982494.

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Raynolds, Marlo A., M. David Checkel, and Roydon A. Fraser. "A Case Study for Life Cycle Assessment (LCA) as an Energy Decision Making Tool: The Production of Fuel Ethanol from Various Feedstocks." In Total Life Cycle Conference & Exposition. 400 Commonwealth Drive, Warrendale, PA, United States: SAE International, 1998. http://dx.doi.org/10.4271/982205.

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Annisa, Rina, Linda Faridah, Dwi Muchtar Yuliawan, Ngapuli I. Sinisuka, Indra Surya Dinata, Fauzi Leilan, Tania Revina, D. Iman, and Samuel Darma. "Environmental Impact Assessment of Steam Cycle and Combine Cycle Power Plants Using Life Cycle Assessment Methodology." In 2018 Conference on Power Engineering and Renewable Energy (ICPERE). IEEE, 2018. http://dx.doi.org/10.1109/icpere.2018.8739338.

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Bao, Han P., and Harpreet S. Multani. "Energy-Based Life Cycle Assessment of Industrial Products." In 2007 IEEE International Symposium on Electronics and the Environment. IEEE, 2007. http://dx.doi.org/10.1109/isee.2007.369379.

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Qi, Yu, Yun Zhang, Hui Jiang, and Yufei Zeng. "Life Cycle Assessment Of Urban Food Consumption." In 2016 International Conference on Advances in Energy, Environment and Chemical Science. Paris, France: Atlantis Press, 2016. http://dx.doi.org/10.2991/aeecs-16.2016.10.

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Baharwani, Vishakha, Neetu Meena, Alka Dubey, Deepak Sharma, Urmila Brighu, and Jyotirmay Mathur. "Life cycle inventory and assessment of different solar photovoltaic systems." In 2014 Power and Energy Systems Conference: Towards Sustainable Energy (PESTSE). IEEE, 2014. http://dx.doi.org/10.1109/pestse.2014.6805302.

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Liu, C. H., S. J. Lin, and C. Lewis. "Life cycle impact assessment of the DRAM chip industry in Taiwan." In ENERGY 2007. Southampton, UK: WIT Press, 2007. http://dx.doi.org/10.2495/esus070141.

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Reports on the topic "Life energy cycle assessment"

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Martel, Laura, Paul Smith, Steven Rizea, Joe Van Ryzin, Charles Morgan, Gary Noland, Rick Pavlosky, Michael Thomas, and John Halkyard. Ocean Thermal Energy Conversion Life Cycle Cost Assessment, Final Technical Report, 30 May 2012. Office of Scientific and Technical Information (OSTI), May 2012. http://dx.doi.org/10.2172/1045340.

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Treese II, J. Van, Edward A. Hanlon, Nana Amponsah, Jose Luis Izursa, and John C. Capece. Energy valuation methods for biofuels in South Florida: Introduction to life cycle assessment and emergy approaches. Office of Scientific and Technical Information (OSTI), March 2013. http://dx.doi.org/10.2172/1337169.

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Herceg, Sina, Monique Dick, Estelle Gervais, and Karl-Anders Weiß. Conceptualized Data Structure for Sustainability Assessment of Energy and Material Flows: Example of aPV Life Cycle. University of Limerick, 2021. http://dx.doi.org/10.31880/10344/10208.

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Al-Qadi, Imad, Hasan Ozer, Mouna Krami Senhaji, Qingwen Zhou, Rebekah Yang, Seunggu Kang, Marshall Thompson, et al. A Life-Cycle Methodology for Energy Use by In-Place Pavement Recycling Techniques. Illinois Center for Transportation, October 2020. http://dx.doi.org/10.36501/0197-9191/20-018.

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Worldwide interest in using recycled materials in flexible pavements as an alternative to virgin materials has increased significantly over the past few decades. Therefore, recycling has been utilized in pavement maintenance and rehabilitation activities. Three types of in-place recycling technologies have been introduced since the late 70s: hot in-place recycling, cold in-place recycling, and full-depth reclamation. The main objectives of this project are to develop a framework and a life-cycle assessment (LCA) methodology to evaluate maintenance and rehabilitation treatments, specifically in-place recycling and conventional paving methods, and develop a LCA tool utilizing Visual Basic for Applications (VBA) to help local and state highway agencies evaluate environmental benefits and tradeoffs of in-place recycling techniques as compared to conventional rehabilitation methods at each life-cycle stage from the material extraction to the end of life. The ultimate outcome of this study is the development of a framework and a user-friendly LCA tool that assesses the environmental impact of a wide range of pavement treatments, including in-place recycling, conventional methods, and surface treatments. The developed tool provides pavement industry practitioners, consultants, and agencies the opportunity to complement their projects’ economic and social assessment with the environmental impacts quantification. In addition, the tool presents the main factors that impact produced emissions and energy consumed at every stage of the pavement life cycle due to treatments. The tool provides detailed information such as fuel usage analysis of in-place recycling based on field data.
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Brackley, Allen M., David L. Nicholls, Maureen Puettmann, and Elaine Oneil. Life cycle assessment of wood energy for residential heating—opportunities for wood pellet production in southeast Alaska. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 2017. http://dx.doi.org/10.2737/pnw-gtr-951.

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Tuenge, Jason R., Brad Hollomon, Heather E. Dillon, and Lesley J. Snowden-Swan. Life-Cycle Assessment of Energy and Environmental Impacts of LED Lighting Products, Part 3: LED Environmental Testing. Office of Scientific and Technical Information (OSTI), March 2013. http://dx.doi.org/10.2172/1074312.

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Brackley, Allen M., David L. Nicholls, Maureen Puettmann, and Elaine Oneil. Life cycle assessment of wood energy for residential heating—opportunities for wood pellet production in southeast Alaska. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 2017. http://dx.doi.org/10.2737/pnw-gtr-951.

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Scholand, Michael, and Heather E. Dillon. Life-Cycle Assessment of Energy and Environmental Impacts of LED Lighting Products Part 2: LED Manufacturing and Performance. Office of Scientific and Technical Information (OSTI), May 2012. http://dx.doi.org/10.2172/1044508.

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Sullivan, J. L., E. D. Frank, J. Han, A. Elgowainy, and M. Q. Wang. Geothermal life cycle assessment - part 3. Office of Scientific and Technical Information (OSTI), November 2013. http://dx.doi.org/10.2172/1118131.

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Al-Qadi, Imad, Jaime Hernandez, Angeli Jayme, Mojtaba Ziyadi, Erman Gungor, Seunggu Kang, John Harvey, et al. The Impact of Wide-Base Tires on Pavement—A National Study. Illinois Center for Transportation, October 2021. http://dx.doi.org/10.36501/0197-9191/21-035.

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Researchers have been studying wide-base tires for over two decades, but no evidence has been provided regarding the net benefit of this tire technology. In this study, a comprehensive approach is used to compare new-generation wide-base tires (NG-WBT) with the dual-tire assembly (DTA). Numerical modeling, prediction methods, experimental measurements, and environmental impact assessment were combined to provide recommendations about the use of NG-WBT. A finite element approach, considering variables usually omitted in the conventional analysis of flexible pavement was utilized for modeling. Five hundred seventy-six cases combining layer thickness, material properties, tire load, tire inflation pressure, and pavement type (thick and thin) were analyzed to obtained critical pavement responses. A prediction tool, known as ICT-Wide, was developed based on artificial neural networks to obtain critical pavement responses in cases outside the finite element analysis matrix. The environmental impacts were determined using life cycle assessment. Based on the bottom-up fatigue cracking, permanent deformation, and international roughness index, the life cycle energy consumption, cost, and green-house gas (GHG) emissions were estimated. To make the outcome of this research effort useful for state departments of transportation and practitioners, a modification to AASHTOWare is proposed to account for NG-WBT. The revision is based on two adjustment factors, one accounting for the discrepancy between the AASHTOware approach and the finite element model of this study, and the other addressing the impact of NG-WBT.
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