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Life Cycle - Science topic

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While there is an environmental impact during the manufacturing process, the overall life cycle emissions of electric vehicles (EVs) are lower than those of traditional vehicles. Cleaner energy sources and advances in charging infrastructure further augment the role of EVs in sustainable transportation.
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En general, los vehículos eléctricos tienden a tener un menor impacto ambiental en comparación con los vehículos de combustión interna, especialmente cuando se utilizan con electricidad generada a partir de fuentes renovables. Sin embargo, es importante tener en cuenta todos los aspectos del ciclo de vida de un vehículo eléctrico para obtener una imagen completa de su impacto medioambiental. Además, la transición a los vehículos eléctricos debe ir acompañada de esfuerzos continuos para mejorar las tecnologías y prácticas asociadas a su fabricación y gestión de residuos.
Assessing the environmental impact of electric vehicles (EVs) is a complex issue and depends on several factors, including the source of electricity, the manufacturing of the batteries, and the use of the vehicle. Here are some key aspects to consider:
1. Emissions during manufacturing: The production of electric vehicles, especially the production of batteries, can generate greenhouse gas emissions and other pollutants. However, as technology improves and manufacturing practices become more sustainable, these emissions tend to decrease.
2. Source of electricity: The environmental impact of an electric vehicle depends largely on the source of electricity used to charge it. If the electricity comes from renewable sources such as solar, wind or hydroelectric, electric vehicles can have considerably less environmental impact compared to internal combustion vehicles.
3. Battery life and recycling: Electric vehicle batteries contain materials such as lithium, cobalt and nickel, which can have significant environmental impacts during extraction and processing. However, efforts are underway to improve the efficiency in the use of these materials and to develop more effective methods of battery recycling.
4. Vehicle use: Electric vehicles are more efficient in terms of energy consumption compared to internal combustion vehicles. Its efficiency can contribute to lower greenhouse gas emissions during operation.
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Which dissertations, articles describe the selection of materials, products using quality by design and life cycle assessment? Thank you!
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Quality by Design (QbD) and Life Cycle Assessment (LCA) are two methodologies that can be used to improve the quality and sustainability of products and processes in various industries. Here are some examples of how these methodologies can be applied in practice and some resources that provide more information on the topic:
QbD can be used in the pharmaceutical industry to design and develop drug products that meet predefined quality attributes. The QbD approach involves identifying and controlling critical quality attributes (CQAs) throughout the product lifecycle, from development to manufacturing and distribution. Some resources on this topic include:
"Quality by Design for Biopharmaceuticals: Principles and Case Studies" by Anurag S. Rathore and Rohin Mhatre, which provides an overview of QbD concepts and case studies in the biopharmaceutical industry.
"Implementation of Quality by Design (QbD) in the Pharmaceutical Industry: A Systematic Review" by Naresh Kumar, which reviews the literature on QbD implementation in the pharmaceutical industry and identifies key success factors and challenges.
LCA can be used to evaluate the environmental impacts of products and processes throughout their entire lifecycle, from raw material extraction to end-of-life disposal. LCA can help identify opportunities for improving the environmental performance of products and processes. Some resources on this topic include:
"Introduction to Life Cycle Assessment" by Mary Ann Curran, which provides an overview of LCA concepts and methodology.
"Life Cycle Assessment: Principles and Practice" by Michael Hauschild and Ralph Rosenbaum, which provides a comprehensive guide to LCA methodology and applications.
QbD and LCA can also be used together to design and develop sustainable products and processes that meet predefined quality attributes while minimizing their environmental impacts. Some resources on this topic include:
"A Review of Quality-by-Design and Life Cycle Assessment Concepts in the Pharmaceutical Industry" by Saeed Shojaee and Seyed Mohammad Razavi, which discusses the integration of QbD and LCA in the pharmaceutical industry.
"Quality-by-Design and Life Cycle Assessment for Sustainable Chemical Processes" by Damien Landesmann, which provides a framework for integrating QbD and LCA in the chemical industry.
Overall, the application of QbD and LCA in product and process design can help improve the quality and sustainability of products while minimizing their environmental impacts. There are many resources available on these topics, and the examples provided above are just a few to get started.
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What is the Schistosomal Life cycle and infections with the host of Public Health Entomology?
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The Schistosomal life cycle involves a complex interplay between humans and freshwater snails, and public health. While these snails are not insects, they play a vital role in the transmission of schistosomiasis, and their study is important in understanding and controlling the disease. In this context, public health entomologists may extend their expertise to include snail biology and ecology due to their relevance in the life cycle of the parasites causing schistosomiasis.
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In 'life cycle' under product stages we can give 'waste disposal' process,how does this impact the result?
And under product stage there is also option to make 'waste treatment' stage.So how to analyze this or use it in the impact assessment?
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Waste/disposal scenario" in SimaPro models the final disposal of waste, while "waste treatment" represents pre-disposal treatment processes. Both are essential for assessing the environmental impacts of waste management in a product's life cycle.
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A part of my Research regarding a Middle Eastern country's development, Includes the application of Butler’s Tourism Area Life Cycle Model, My Question is, are the outcomes of the TALC module worth publication aside from the original Idea of my research?
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Hello,
Adding to what Shyju P J have said, it is interesting to discover authors that have used TALC or built upon it like Holladay (2018) did.
TALC have been criticised a lot about how it oversimplified the destination and for considering a destination a product but still I think it gives amazing overview on the stages that a destination can go through.
I am building my thesis on it as well but I am starting from the perspectives that Holladay (2018) have left in his paper.
Citation below :
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Sources or information that can help to operate this software for practical data. For example- LCA of landfill emissions.
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There are several resources available to help you get started with life cycle assessment using SimaPro. Here are a couple of suggestions:
1. Pre-Sustainability offers a variety of SimaPro training courses. These courses can help you learn the basics of LCA and how to use SimaPro to conduct LCA studies.
2. Use the tutorials offered by SimaPro, can be downloaded upon opening the software.
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In your opinion, what is the essence of life in the context of the Universe, i.e. in the context of other life forms potentially occurring on many distant exoplanets relative to the known life occurring on planet Earth?
How do you think very different forms of life might exist on distant exoplanets relative to the life forms we know?
Given what we know and what we don't know about the cosmos, how different do you think life forms might be on distant exoplanets relative to the known life forms found on planet Earth?
Considering how different environmental, climatic, geological conditions, the composition of elements and inorganic and possibly also organic compounds, etc. on distant exoplanets may be under many or even all of the categories known to us, how different life forms may exist on these other planets located many millions of light years from our solar system?
According to some astrophysicists, what we do not know about the cosmos is estimated to be 96 per cent. Included in this is, for example, the essence of dark matter beyond the Universe as we know it and dark matter causing the expansion of the Universe as we know it. Life in its essence is defined in an ambiguous way. Depending on whether the definition refers only to life forms found on planet Earth or to possible other life forms that may exist on distant exoplanets, the definition of life is not necessarily the same.
Depending on what role the billions-of-years-long process of evolution of life forms on planet Earth has played in the development of life forms and the resolution of the question of the randomness of the emergence of life on different exoplanets or the intentionality of the evolutionary process aimed, for example, at the to the creation of more and more complex forms of life, forms of life increasingly adaptable to specific, changing environmental conditions of a specific exoplanet, increasingly better adapted to different environments, and to the possibly intentional or accidental bringing about of intelligent beings, including beings forming organised civilisations, changing the environment of the planet and aiming at space exploration, colonisation of other exoplanets similar to their home planet. These eventualities to be resolved that have not been resolved are many. Consequently, defining the essence of life in the context of possibly other extraterrestrial life forms on many exoplanets is not uniform. In the context of potential completely other, unknown forms of extraterrestrial life that probably occur on many distant exoplanets, life can be defined as a process of spontaneous, self-contained, independent, organised processing of matter based on energy acquired from the environment and forming, through this process, more complex structures of specific chemical compounds, elements of matter available on a specific planet and adapting to the more or less variable environment of the planet, etc. It is likely that many questions will be answered when the first evidence of the existence of other forms of extraterrestrial life occurring on many distant exoplanets emerges. There are already more than 5 500 confirmed existing exoplanets, and there is already fragmentary information about another 9 000, also suggesting their existence. This knowledge has been building up very rapidly over the past decade or so. On some of Jupiter's moons, there are deep water oceans many kilometres deep beneath the icy crust, in which specific but as yet unknown chemical compounds and perhaps certain other forms of life exist. For example, there are planets in our Solar System with largely different environments to planet Earth. For example, the atmosphere of Venus contains mainly sulphuric acid. But does this rule out the existence of some firm, less organised, procariot-type life forms. Not necessarily.
In view of the above, I address the following questions to the esteemed community of scientists and researchers:
Given what we know and what we do not know about the cosmos, how much different environmental, climatic, geological conditions, composition of elements and inorganic and possibly also organic compounds etc. on distant exoplanets can be, how much different life forms can exist on these other planets located many millions of light years from our solar system?
Given what we know and what we don't know about the cosmos, how very different life forms might exist on distant exoplanets to the known life forms found on our planet Earth?
How do you think very different life forms might exist on distant exoplanets to the life forms we know?
What do you think is the essence of life in the context of the Universe, i.e. in the context of other life forms potentially occurring on many distant exoplanets in relation to the known life occurring on planet Earth?
In your opinion, what is the essence of life in the context of the millions of planet Earth-like exoplanets found in the Universe?
What is the essence of life in the context of the Universe?
What do you think about this topic?
What is your opinion on this subject?
Please respond,
I invite you all to discuss,
Counting on your opinions, on getting to know your personal opinion, on an honest approach to the discussion of scientific issues and not the ready-made answers generated in ChatGPT, I deliberately used the phrase "in your opinion" in the question.
The above text is entirely my own work written by me on the basis of my research.
I have not used other sources or automatic text generation systems such as ChatGPT in writing this text.
Copyright by Dariusz Prokopowicz
Thank you very much,
Best regards,
Dariusz Prokopowicz
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I don't know the best answer for it. But good answer is Earth-like exoplanets are our colonial target to sustain by terraforming with the help of asteroid impact to create magnetosphere -air-aqua-atmosphere like our Earth. Simply,Earth is the prototype to examine and validate this feasibility.
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Recommend dissertations that describe material selection techniques using life cycle assessment, target product quality profile, quality by design.
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Developments in Bioengineering and Materials Engineering have in common the processes of physical chemistry. I am developing a method strictly based on these processes and more precisely on the effects of polarization, entropy and internal energy that determine viscosity and redox energetic processes at interfaces. I use it to predict and forecast the lifetime of materials and relate it to their manufacture. I believe that in many areas of biology and medicine, pharmacology and traumatology, radiation treatment and surgical tools, research on the mechanisms that determine the properties of materials will contribute to progress. I propose an online training course giving access to a synthesis book, several unpublished publications and training modules in the form of videos.
If you are concerned, let me know, I will keep you informed of its opening in June 2023 and of the conditions of registration.
Kind regards, good luck.
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What are the effects of the disruption of the carbon cycle on the environment and effect of global warming on the life cycle of organisms?
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Excess carbon in the atmosphere warms the planet and helps plants on land grow more. Excess carbon in the ocean makes the water more acidic, putting marine life in danger. The carbon cycle plays a key role in regulating Earth's global temperature and climate by controlling the amount of carbon dioxide in the atmosphere. The greenhouse effect itself is a naturally occurring phenomenon that makes Earth warm enough for life to exist. The concentration of carbon dioxide in Earth's atmosphere is currently at nearly 412 parts per million (ppm) and rising. This represents a 47 percent increase since the beginning of the Industrial Age, when the concentration was near 280 ppm, and an 11 percent increase since 2000, when it was near 370 ppm. More frequent and intense drought, storms, heat waves, rising sea levels, melting glaciers and warming oceans can directly harm animals, destroy the places they live, and wreak havoc on people's livelihoods and communities. As climate change worsens, dangerous weather events are becoming more frequent or severe. Climate change affects human health and wellbeing through more extreme weather events and wildfires, decreased air quality, and diseases transmitted by insects, food, and water. The changes in the carbon cycle impact each reservoir. Excess carbon in the atmosphere warms the planet and helps plants on land grow more. Excess carbon in the ocean makes the water more acidic, putting marine life in danger. Plants absorb carbon dioxide during photosynthesis and much of this carbon dioxide is then stored in roots, permafrost, grasslands, and forests. Plants and the soil then release carbon dioxide when they decay. Other organisms also release carbon dioxide as they live and die. Without carbon dioxide, Earth's natural greenhouse effect would be too weak to keep the average global surface temperature above freezing. By adding more carbon dioxide to the atmosphere, people are supercharging the natural greenhouse effect, causing global temperature to rise.
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I am going to be writing a dissertation on a cost benefit analysis of using timber as a sustainable building material, and I was wondering if there was any known approaches to conducting cost benefit analysis's on construction materials. and if so what metrics would be best to measure e.g. cost, material characteristic's compared to traditional counter parts, life cycle, environmental impact, social and political impacts?
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Thank you very much for your reply this was very useful information!
Kind Regards
Conner Lamont
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This software is used in the field of life cycle assessment.
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Hi..
What is your question?
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Is there an open-source software or apps supporting Life Cycle Inventory of emissions from agricultural activities?
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I want to study the life cycle of insect, the larva of this insect lives inside the gall which is formed in the stem of host plant. I presume the presence the larva leads to the formation of a gall. Can someone suggest me a standard protocol through which I can study the life cycle of this insect larva.
Thank you in advance
Dr Bisu Singh
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Thank you James and Firas for you suggestions.
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I have worked on soil stabilization using eggshell powder in fine grained soil for subgrade purpose. But the research lacks a life cycle assessment of eggshell powder. Please help me to find out the eggshell life cycle assessment using GaBi software.
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No,Idon't any one work on this subject.
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Dear researchers,
I am currently very interested in performing Life Cycle Assesment analyses, and start learning about this subject. But I need some orientation and to learn the basics first.
Would you recommend me a software to start learning and some guides about this?
Thank you in advance!
Kind regards to you all!
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Dear Forchetti. It is important that you learn, the techniques of data collection and the method in which you will carry out your project. What is your goal of this topic. Best regards
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Hi All,
I'm looking for the possible methods in measuring the response of chytrid fungus cells to environmental stressors in separate generations. As Lee Berger (2005) claimed, chytrid needs 4-5 days at 22 C to complete its life cycle. But it seems that we have cells in various stages and it is difficult to have a uniform population of fungi cells in a particular generations. So, my questions is that how possible it is to conduct a multigenerational study (for instance 4 generations) in the culture (in vitro) to see the potential impacts of stressors through generations? measurements in separate generations are important in my tests.
Hope that does make sense, otherwise, ask me.
Thanks.
Milad
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Could try calcofluor. Acts as a vital stain.if you wash it out after exposing one generation, maybe subsequent generations would not carry the stain.
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In fatigue analysis, satisfying 4 times (scatter factor 4) of the required life cycles has the 99% of the material reliability (probability) as far as I know.
For instance, if the requirement is 100,000 cycles and the analysis shows the life is more than 400,000 cycles, the material is expected to meet the requirement (100,000 cycles) with 99% reliability.
But, in my recent project, it required me to use scatter factor 4 and perform 4 life fatigue test.
In other words, if the requirement is 100,000 cycles as the above, the analysis should meet 400,000 cycles and its fatigue test should also succeed 400,000 cycles.
Here, I have a conflict. The analysis with scatter factor 4 can guarantee 100,000 cycles with 99% reliability. But after that amount of cycles, it cannot anymore. So, if the test fails between 2 and 4 life, there may be a material probability issue.
In order to guarantee the 4 life test, do I have to use scatter factor 16? It sounds too conservative. Its requirement cycles are 100,000 but the fatigue test should perform 4 lives.
What should I do to guarantee the fatigue requirement as performing the fatigue analysis?
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To me, your analysis approach seems somehow too simplified and basically of a deterministic type. If the goal is to compute the failure probability, the information on the PDF must also be provided. Saying that a standard deviation of four gives a certain failure probability in not sufficient, unless the information on cycle PDF is given (or maybe is tacitly understood in your post).
Also the uncertainty of SN parameters estimated on fatigue data (i.e., statistical uncertainty) should be taken into account for a complete reliability analysis, for example by defining a characteristics SN curve for a certain failure probability or defining a confidence interval – maybe this is actually your goal. This task can be accomplished for example by considering a SN curve defined by tolerance interval.
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Dear All,
I would appreciate if you could give an advice what is the best approach how to model phosphorus emissions to water in an Life Cycle Inventory, if only the amount of applied fertilizer is known?
Thank you!
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for calculate phosphorus emissions, you can use SALCA model.
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Will the power/current fluctuation with a high ramp rate but a small amplitude poses a significant impact on battery lifetime?
More specifically, are the answers different under the following three cases:
a) battery power/current changing from one level to another level (both far below the rated one) within a very short time period (e.g. 50ms)?
b) battery power/current frequently fluctuating around a constant level (far below the rated one) without reversing its direction?
c) battery power/current frequently fluctuating around zero, i.e., repeatedly charging/discharging with small cycles?
I got confused, as it seems that previous papers have covered all the three cases in battery lifetime extension schemes, while the battery manufacturers only pay attention to case c). It would be better to share the relevant references.
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Kindly refer this article
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We are in the process of assessing the LIFE CYCLE of Ginger and Pomogranet production. In this regard, we are in search of free and easy-to-use LCA software.
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for me, OpenLCA is easier to learn, agree with Justus Caspers , data availability/compatibility with your model would be the main concern
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Hello, I am currently making a life cycle assessment which includes bio-based activated carbon.
I was wondering if such material could be used in pyrolysis, and what would its advantages be over biochar or even coal.
Regards
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Kindly see also the following useful RG link:
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Hello everyone,
I am trying to model the process stage (Gate to Gate) of FDM on SimaPro. I understand that I need to decide upon my inputs and outputs as well as system boundary before doing that. I am trying to do this properly and was wondering if anyone can advise more on this methodology (i.e., how to decide upon the values for the raw material input and electricity?, etc...).
Any response is very much appreciated. Thank you.
Useful Article: Methodology for systematic analysis and improvement of manufacturing unit process life-cycle inventory (UPLCI) —CO2PE! initiative (cooperative effort on process emissions in manufacturing). Part 1: Methodology description.
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For FDM SimaPro modelling in gate-to-gate first you should have clear system boundaries based on the research scope. I would like to suggest the following research articles for in-depth study:
Hope them helps you
Best regards,
Shuraik
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Is there a life cycle assessment to estimate the emissions of bitcoin life and its impact on climate change?
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Currently I am researching the possibility's of implementing a Feedback loop based on a Lessons Learned database to Close the Loop in a project organization that focusses on Marine Contracting.
I'm looking for articles, best practices, best in class methods for implementing and maintaining these kinds of systems/tools.
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Dear Mr. Wijngaarden!
I found an article you might see as of value for your work:
Hrusto, A., Runeson, P. & Engström, E. Closing the Feedback Loop in DevOps Through Autonomous Monitors in Operations. SN COMPUT. SCI. 2, 447 (2021). https://doi.org/10.1007/s42979-021-00826-y, Open access:
An additional source of information might be the following article:
Oxfam GB (2022). HOW TO OPERATIONALISE ‘CLOSING THE FEEDBACK LOOP’: WHERE IS THE SOLUTION? Free access: https://www.elrha.org/project-blog/operationalise-closing-feedback-loop-isthe-solution/
Yours sincerely, Bulcsu Szekely
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Dear all,
What are the best techquines/procedures to integrate life cycle inventories (LCI) and life cycle impact assessments (LCIA) into energy system optimisation models (ESOM) (energy-focused IAM) to determine the potential impacts of industrial and urban decarbonisation scenarios and policies.
The emission factors used in energy models (e.g. LEAP) are mostly related to direct energy use (e.g. fuel combustion), and industrial process emissions are not always considered, which may lead to underestimated impacts.
Meanwhile, although life cycle assessment (LCA) provides relevant information about the total life cycle impacts of industrial processes, LCA methods not always consider future technology improvements and changes in economic and energy structures as they are usually focused on background data.
I would appreciate if you could send me some suggestions (links, papers, projetcs, comments) about best practices to integrate LCIAs into prospective energy models.
Thank you in advance for your attention!
All the best,
Joan Manuel F. Mendoza
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Recently a tool has been provided - using Python, available on GitHub - to perform prospective LCA by making use of the outputs of integrated assessment models (IAMs, both IMAGE and REMIND) to modify the background life cycle inventory (LCI) database ecoinvent using different socio-economic pathways. Please have a look at https://github.com/polca/premise.
Further, this recently published paper in Renewable and Sustainable Energy Reviews provides a description as well as a couple of case studies of the tool:
Hope this helps,
Tom
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Also, does anyone have a building SimaPro tutorial; PDF or videos?
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Please refer to the database manual attached in the following link:
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Hello,
I'm currently making a life cycle assessment for a liquid hydrogen tank.
One of the materials considered is a carbon fibre reinforced PEEK.
However, there is not a lot of data about the environmental impact of the polymer. Indeed, the only article I have found is the one from Daniel GARRAIN (which served as a reference for the Idemat database).
(PDF) The environmental behaviour of PEEK as an innovative material in a new portable hydrogen fuel cell (researchgate.net)
If any of you have data about it, I would be interested in exchanging with you.
Regards,
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CO2 is used as raw material for chemical syntheses. It paves the opportunity to mitigate the greenhouse gas (GHG) emissions. However, it is not mathematically or logically proved yet that carbon capture benefits the environment in terms of resource efficiency. In my opinion, I believe that the life cycle assesment (LCA) would be the most suitable tool to quantify the resource-based benefits due to carbon based methane (CH4) production and to prove the resource efficacy of carbon capture.
I would like the researchers who read this discussion to provide their own ideas on whether LCA is the most suitable tool to identify the carbon capture resource efficacy or are there any methods better than LCA that can be applied on CO2 based methane production.
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"Life cycle assesment (LCA)" could be jointly addressed with the "circular economy (CE)" and the "ecosystem service valuation (ESV)", as an integrated tool to "quantify the resource-based benefits due to carbon based methane (CH4) production". Besides, this integrated approach can better control the excessive use of material, lowering the energy needs for new products, saving natural sources from overexploitation and environmental degradation, managing labour's capital, and proving the resource efficacy of carbon capture.
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Hello RG members,
Our team is engaged in preparing a comprehensive LCA tool that is freely available for any kind of users to facilitate the global warming potential calculation due to the building structures, pavement structures and hydraulic structures. In reference to this objective, I would like to get opinions from you on what type defects/failures/issues that you encounter with present life cycle assesment softwares such as Oneclick LCA, SimaPro and OpenLCA etc.
Your answers would help our team to develop a well structured LCA tool. Thank you
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The only weakness in my opinion is that all the software are proprietary and two different software cannot communicate with each other without compatibility issues.
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life cycle assessment
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Dear Dr Tobi La, see the following useful link:→LCA software:: openLCA
openLCA is versatile and able to meet needs of different user groups, be it e.g. industry, consultancy, education, and research.
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Dear colleagues,
We ask your kind support to our research on the topic of: Life Cycle Sustainability Impact Categories for Li-Ion Batteries.
This survey is targeted to experts in sustainability assessment, LCA, waste management and similar areas.
Please fill in our survey (expected duration of aprox. 12 minutes) in the link: https://forms.gle/ae3BKh5xYM2ZMywQ8
Your contribution is essential to this study!
Thanks in advance.
A research team from UNESP and CTI, Brazil.
#unesp #batteries #sustainability #lifecycle #ewaste
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Done
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Hello everyone,
I have been asked to develop the state of the art related to the Digital Twin and I have tried to read many of the articles dealing with the topic that are present in the literature, paying special attention to the conceptual ones and reviews. However, the more I read, far from converging towards a unified vision, the more I got the impression that each author develops his own ideas and theories about the Digital Twin, largely depending on the application sector and the objectives to be achieved. So much so, that this concept is turning out to be a nightmare for me, I could not imagine such heterogeneity in terms of perspectives (just my actual perception). Here is a list of some topics that I find difficult to understand:
  • Is it possible to represent an intangible entity with the Digital Twin? Many authors argue so and recognize both tangible and intangible entities for developing Digial Twins. However, even nowadays, many publications continue giving Digital Twin definitions or descriptions where only physical entities are considered. Moreover, when talking about the flow of communications between the real and virtual worlds, the entity of the real world is commonly supposed physical. When tackling other aspects such as the lifecycle, the real entity is normally assumed to be physical and related to a product in the manufacturing domain. There is a trick to this question, because if the Digital Twin is supposed to track the entire lifecycle of the represented real entity and a Digital Twin only comes into existence when the real entity has already been physically built (as-built), what about early lifecycle phases such as design?
  • Generally, from what I have read, aggregation and composition of Digital Twins is allowed. Just as a real-world entity may itself be composed of several elements (each of which may have its own Digital Twin), a Digital Twin may itself be composed of several Digital Twins. Is a 1:1 (bijective) relationship between the real-world entity and its Digital Twin always assumed? In my opinion it should be like this...
  • Does the development of a Digital Twin imply the need for bidirectional communication between the represented entity and the Digital Twin itself? Normally a one-way communication from the real entity to the virtual entity is assumed (in that direction). In my opinion, this link is more than enough to enable the convergence between both worlds and the synchronization of the Digital Twin, since thanks to it the virtual entity will always have the possibility to reflect the real one (in real time or not). However, the existence of a link in the opposite direction (from the virtual entity to the real one) is not always considered. It should be noted that it brings great value, since it enables the Digital Twin to control or act on the represented real entity. This increases its usability and the number of possible applications. However, is it an intrinsic characteristic of the Digital Twin? It should be noted that in some cases it may be difficult to achieve and may lead to different interpretations. Just consider the intangible entities.... It seems complicated to establish an automatic bidirectional flow of communications. To give an example, one can think of production processes. They are real concepts but intangible as such, although it is true that if we think about the characteristic of composition/aggregation of digital twins, a productive process, despite being intangible, can be in turn composed of digital sub-twins of real physical entities such as production cells, in which case the aforementioned bidirectional flow would be feasible... We are almost getting into very abstract and philosophical issues. Another example where I consider bidirectional flow to be complicated is e-health, a field where there is already research on the Digital Twin. For example, it would be feasible to develop a Digital Twin of a diabetic person to monitor his or her blood glucose level. Based on the data collected, the Digital Twin could provide, for example, nutritional recommendations through an application to improve their condition, being the person's own responsibility to read and implement them. Would this be considered bidirectional communication? It affects the represented entity, but indirectly... For now I do not see very viable, at least in this sector, that the Digital Twin gets to control organs through actuators or other devices implanted in the human being's own body where the aforementioned bidirectional communication has a place.
  • Is the concept of lifecycle tracking an essential characteristic of the Digital Twin? In my opinion there are domains where Digital Twins have actually been developed where this view does not fit. Additionally, there are authors that do not consider the need of the Digital Twin to track the whole lifecycle, but the necessary subset of it.
  • Many definitions or descriptions of the Digital Twin pose it as a whole by which it is possible to have a real-time representation of a real-world entity and its traceability throughout its lifecycle. Only the term Digital Twin is used. However, there are other approaches, whereby, based on the stage of the life cycle and the level of realization of the real entity to be represented, other concepts such as the Digital Model or Digital Thread are introduced. To cite a few examples, Grieves proposes the concept of Digital Twin Prototype and Digital Twin Instance (together with Digital Twin Aggregate and also Digital Twin Environment). Another proposal comes from Madni, that proposed Pre-Digital Twin and Digital Twin (together with Adaptative Digital Twin and Intelligent Digital Twin). Hribernik introduces the concept of Product Avatar and Parent Avatar. In a similar approach, Eigner present and distinguish the concept of Digital Model, Digital Thread and Digital Twin. Stark also talks about the Digital Prototype / Digital Master, Digital Shadow and Digital Twin... Among all these, is there one commonly known as the "right" approach? Or all of them are just different visions from different authors?
  • So far and based on what I have read, I have been understanding the Digital Thread as the Digital Model proposed by Eigner or the Digital Master / Prototype proposed by Stark. I get the impression that the same thing happens in other publications, even more so when only the concepts of Digital Twin and Digital Thread are elaborated. In the case of Eigner I think he focuses more on the links itself when referring to the Digital Thread. Is this possible? Do you have the same impression? It may also be that I have misunderstood everything up to now (I hope not to be the case)…
  • In the following I expose a use case related to a van manufacturing company. I am really interested in seeing how would you understand and name each of the aspects I mention below. The paragraphs that present the situation are written in italics, and my thoughts in plain text without any formatting:
  1. The introduction of a new van model usually involves, among other things, arduous exterior, interior and component design tasks. For this purpose, 3D modeling tools are commonly used, whose resulting models prove to be very useful for subsequent prototyping, testing and design refinement steps. All these resulting assets launch the Digital Thread of the new van to be manufactured, framed within the design stage. From this moment, in addition to the vehicle manufacturing company, it is common for all those component or service suppliers to participate, also gaining access to the pertinent models. Would you refer to this as the Digital Model/Master of the generic van model to be produced? As you can see I am saying that at this point the Digital Thread is being launched, thus understanding it a the Digital Thread… I suppose that at this initial design stage, in addition to the different designs and general product specifications that give rise to the generic van and all its possible services (variant free at this point), it is also possible to run different simulations to check the correction of the product and the design decisions made. Since there is not yet a physical van or a physical prototype of the van, these types of product instances should be referred to as Digital Twins? Would it make sense to build a physical prototype at this stage? Does it makes sense? I suppose that it also depends on the domain and use-cases…
  2. With the final general design checked and validated, the production phase of the van begins, where many of the previously created and properly updated models are used to drive different manufacturing processes. It is at this point where, depending on the final customer and unexpected orders, some reengineering on the general models of the new van might be necessary. In fact, it is not the same a common van, a camper van, an armored cash-in-transit van or a van for transporting people with reduced mobility. To make the changes, the general vehicle models are inherited and the appropriate redesigns and validations are carried out, with the active participation of all the involved suppliers. In case such vehicles are to be mass-produced, a digital subthread or the inclusion of vehicle variants on the original digital thread could even be considered. Here different variants of vans are presented that come from the same generic van model… They share common attributes but an initial customization stage starts, although more can be expected in advance… Say, for example, that from the generic van model a passenger and a box/goods vans can be derivated, both of which admit much more customization based on the final customer requirements and orders. How to call to this subgeneral van models? Digital Sub-Model/Master? Digital Sub-Thread? You wouldn't call them Digital Twins yet, would you? Nevertheless, at this phase I see more feasible the fact of building physical prototypes in case they are needed... Again, here different design decisions and simulations could be carried out with the developed models (and in conjunction with the stakeholders) to check the vans to be subsequently produced.
  3. In any of the cases, whenever the changes or information to be introduced on the general models are specific to a particular unit to be produced, the Digital Twin associated to that particular van arises. In its models, in addition to including specific information on its design, the data and peculiarities associated with its production are also recorded. During the operation phase, these Digital Twin models are updated in real time based on the data coming from the physical van, so that they constantly reflect its status. New models for diagnostic and prognostic purposes could also be generated by using such information. I think most of you will more or less agree with this. However, I believe that with this I am violating the multiple definitions of the Digital Twin that indicate that it enables traceability throughout the entire product lifecycle, as it seems to only intervene from the manufacturing phase onwards and not in the design phase. Maybe, once a specific van (particular product without the variance inherent to the general design) is to be produced further final simulations, checks and subtle redesigns could be performed with the derived general models that would still be considered as part of the design. Another question related to the information stored in the Digital Twin that comes to me has to do with the following. The design aspects (or configuration items) that can be shared by more than one van and that are not particular of the specific van to be produced have to be part of the Digital Twin itself, or might be stored in their respective Digital Model/Master or Sub-Model/Master knowing that thanks to the Digital Thread that information would be reachable from Digital Twin (or that the Digital Twin could be expanded or enriched with that information)? Note that here I am adopting the view of Eiger and Stark, as I am considering the existence of a Digital Model / Master and interpreting the Digital Thread as the links itself... Remember that in the first question I was assuming the Diigtal Thread to have the role of the Digital Model / Master...
I am so sorry for the length of all this questions but I have tried to explain them well and in a clear manner. I would be very grateful if you could give me your views on any of these points.
Thank you very much in advance.
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I can add some personal views on a couple of the elements raised, interesting points indeed!
What is the definition of the digital twin... the question is if this is actually the right question to ask. Should the digital twin concept actually be defined (which automatically restricts it) or is it rather a paradigm, a way of thinking, that gets its concrete meaning only from a concrete purpose or for a concrete application? And of course, with a lot of building blocks and aspects appearing in many of those applications and/or purposes. But any new application or purpose may add new dimensions... That may explain why there is such diversity in what people claim to be "the" definition of the digital twin and the zoo of the digital twin derivatives, prefixes and/or suffixes. It makes sense to wonder why people postulate a narrow definition of "the" digital twin, in many cases they see a benefit in restricting the concept in a certain way serving not only their application needs but also their commercial purposes.
Two aspects are very important in this, the digital twin is holistic and dynamic. Holistic in the sense that in principle it should contain all possible information to describe fully the asset behavior and predict the future behavior. Dynamic in the sense that this information will grow, not only in size of data but also in the nature thereof. Typically, this information is enriched within and over the various stages of design, development, manufacturing, commissioning and operation of the asset. Geometry, materials, various behavior specific models etc. But from a conceptual point of view it is never complete. One can add more models or more detailed models or add more sensors or better sensors, and the type and nature of data will be different.
Tangible/intangible... well, there is a difference between an intangible concept (emotion, feeling, social behavior, justice...) and a not-yet-existing physical asset (a physical product one is considering but which does not exist yet) for which only the digital description exists at a certain point in time. The digital twin makes definitely sense for the latter case. For the former case, I believe one may confound 'digital twin' with 'model', but I'm afraid we are not yet much further yet than rather poor models. So in my view, the physical asset does not yet have to exist, but the object of the digital twin should typically be a physical asset. Of course, to be extrapolated... one could consider digital twins e.g. of software, of virtual spaces...
Aggregation of digital twins: yes this is clearly a reality. It all depends on the purpose. We work for example in vehicle noise. But are we concerned with the tyre, the wheel, the suspension, the car body, the car interior trim or the car cavity.... same with autonomous vehicles, the radar sensor, the sensor system, the vehicle dynamics and control, the vehicle in the car flow, the city environment... or in a building context, the BIM model, the performance models the components and systems installed, the operation data. It all depends on the purpose, it depends on the department etc. in what aspect of the digital twin one is interested to do what is needed. The key thing is that one should be able to relate these digital twins and build higher level ones.
Bidirectional data flow or even no data flow... the very existence of the physical asset is not a necessity as discussed above. But data measured on the asset will of course enrich further the digital twin and allow furthermore to calibrate and correct the intrinsically approximative nature of the virtual models. Some users may even consider a purely measurement-based data collection a form of digital twin, which is just another starting point with a specific purpose and span of use.
The comment on the forward connection between digital and physical world is an interesting one. One concept we launched in this context is this of the "Executable Digital Twin" (ref. NAFEMS 2021) where an instantiation of a specific part of the digital twin is used to represent this behavior in the physical context. For example, a real-time or off-line condensed model of the thermal behavior to be used to guide operation decisions or even to build a virtual sensor to measure otherwise inaccessible physical data. Or to use a vehicle dynamics model for model predictive control of the vehicle motion.
The generic/specific digital twin. As with other aspects, a digital twin -even when consisting of design data- can be both. The digital twin can refer to the class of products or the generic product, possibly enriched at some point with information on variances and uncertainties (actually even of fault models and their probability) up to the point where such digital twin can be instantiated for individual systems of a generic group. A recent example I saw was related to wind turbine blades, for which generic (design engineering, first principles based) models linked to geometries, construction processes and materials are developed but can then be calibrated to the individual blades part of a specific wind turbine (ref. project RELIABLADE coordinated by DTU Denmark). Again, what level of detail and instantiation is needed, depends on the purpose. And physical data can be instrumental to enable this instantiation step. Or the instantiation can happen even at the Bill of Materials phase, when the specific instance information is available throughout the subsequent use phases of the digital twin. In safety critical environments such as aerospace systems, this practice of absolute tracking is known.
The data links... indeed the links between the various data constitute the power of the digital twin. Otherwise it is just a model (first principles based or data driven) with a new fancy name. Whether authors focus on these links or on the constituting parts of the digital twin again depends on their interests and purpose.
So in my view the answer goes rather in the direct of the statement: "Or all of them are just different visions from different authors?". So while conceptual research on the nature and aspects of the digital twin is to be applauded, a main challenge is to avoid imposing a too strict definition of "the" digital twin and to be very circumspect when encountering such definition as usually there is a purpose behind it (and not only a purpose for the digital twin but a purpose of the authors).
All above comments have to be interpreted along my own principles of not claiming the single source of truth of the digital twin... but unraveling its mechanisms, expanding the scope, finding new applications and building related tools are great challenges.
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For instance, rebound effect is one type of indirect, ecological and detrimental effect illustrating "how an increase in efficiency can generate a higher than expected use of resources" (Figge & Thorpe, 2019)
We qualify as indirect any effect caused by the action and later in time or farther removed in distance, but still reasonably foreseeable by any means (tools) used by the originator (NEPA, 2017).
  • Do you have knowledge of other similar mecanics? In other words, does the litterature define other mecanics of indirect, ecological and detrimental effects?
For instance, carbon leakage describes "a shift of CO2 emissions from a region with emission constraints to an unregulated area" (Naegele & Zaklan, 2019). On antoher scale, burden shifting occurs when considering only parts of the whole life cycle of a product.
  • What makes carbon leakage or life-cycle burden shifting any different?
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What a great discussion! Thanks, Geoffrey for asking that important question! During our project on collaborative consumption, I think it is not an understatement to say that we struggled a lot regarding semantics! While semantic is, after all, just semantic, I think it is, however, very critical in this case.
If the goal is to make sure we move toward a more sustainable direction (and maybe it means giving up on growth), then we need to assess all potential social and environmental impacts and come up with solutions to avoid them. [Note that I omit the economic pillar of sustainability because, as mentioned above, maybe the solutions should be harmful to our current economic system (however, we have to stay cautious as social and economic wellbeing can be correlated (a slow and thoughtful degrowth could enhance our social wellbeing, not so sure about a sudden collapse of our current economic system)]. Then it's a matter of properly accounting for all potential social and environmental impacts including those from what we can call "unforeseeable effect" for now. That's where semantics matter: we need to know what method can properly account for what type of unforeseeable impacts and that implies naming those impacts. This is also important to avoid double counting some of those impacts.
Now, I think there is a bit of confusion in this discussion regarding what a traditional LCA can do. Yes, it can account for burden-shifting (from one life cycle stage to another, or one type of environmental impact to another), but needs more refinements for other types of unforeseeable effects. If we want to account for burden-shifting from environmental to social impacts (think biofuels), then we will need LCSA. If we want to account for impacts occurring outside the LCA product system (i.e., its life cycle, from cradle to grave) we need consequential LCA or hybrid LCA (i.e., input-output & LCA) to account for impacts from the whole economy that our product systems (as we often compare several systems) cause. And like you said if we need to know what impacts occur because the consumer thinks "I stopped eating meat, I am already making an effort to have a more sustainable life, so it's okay, today I can take my car rather than the bus", then we probably need a psychology model in addition to LCA. (And so on with probably most of the other types of unforeseeable effect we can come up with). So yes, we've come a long way with LCA and system thinking, but practically, we are often still far from accounting for everything in our assessments (because it is so complex!). Even when doing hybrid-LCA, which can account for the entire global economy, we are still missing the informal economy (just a few trillion $...). Behaviors may change suddenly (a great example is what's happening currently with covid) and so one psychological mechanism creating impacts may not be valid anymore (if we take the example above in a covid context, "I stopped eating meat, I am already making an effort to have a more sustainable life, I don't commute anymore because I work at home due to covid, so it's okay, I can treat myself and take the plane for a vacation abroad (if travel's allowed!)"). So again, it is extremely difficult to account for all impacts occurring in different scenarios.
There is also some caution to take when talking about the rebound effect. It's not a synonym to backfire, so it does not necessarily negate all the benefits of efficiency improvements. Sometimes a rebound effect can also be positive for the environment (e.g., if a consumer has more money because of a lower electricity bill due to improved thermal insulation, he may decide to spend that gain in purchasing the same number of products but of higher quality, for instance, organic food instead of conventional food, a more durable car or purchase new products but with negative carbon footprints (e.g., purchase trees for their garden)). While I agree that the problem is complex, I am not sure we can just say "rebound effect will always negate all improvements we are trying to make, no matter what we do".
So proper semantics, and identifying possible "unforeseeable effects" when designing new products/solutions (and maybe we would need a better name and a clear and rigorous definition for unforeseeable effects) is I think critical to i) choose proper methods, ii) account for as much potential social and environmental impacts as possible, and iii) avoid double-counting (as two combined methods could be assessing the same impacts (e.g., in the case of hybrid-LCA where most proposed methods have mechanisms to avoid double-counting)). It is also crucial to have semantics properly characterizing each of those unforeseeable effects (e.g., based on their causal mechanisms), again, in order to avoid double-counting! (A change of behavior described by a psychological model and a re-spending effect described by an economic theory may give different explanations of a causal mechanism but account for the same unforeseen effect (and so applying both models at the same time to evaluate impacts would not make sense)).
As for the original question:
-Warm glow (also called moral cleansing, guilt reduction): feeling good about an action believed to be sustainable although it may not actually be the most sustainable one. (Doorn & Kurz 2021)
-Pro-environmental behavior spillover: Maki et al. 2019 provide an elegant and succinct definition: "When people engage in a first pro-environmental behaviour (PEB1; for example, conserving energy at home), are they more or less likely (positive and negative spillover, respectively) to engage in other pro-environmental behaviours (‘PEB2’; for example, conserving water at home)?" (Maki et al., 2019).
-Boomerang effect (I think I have seen it used as a synonym of the rebound effect, thus the importance of proper semantics!): based on subjective norms - where consumers realize that their peers consume more (or behave worse) and begin increasing consumption (or behave worse) (Wynes et al., 2018).
-Rebound effects are sometimes called ripple effects.
-Not strictly an unforeseeable effect but regroup some of the effects identified in psychological studies: self-licensing = the way people feel psychologically licensed to act. The consequence is: people are more likely to behave in ways they can justify easily. (Parguel et al., 2017). (Again, it can relate to the sort of mental balance we have regarding how sustainable are each of our activities ("I can let myself do this because I have done that")).
Hope that helps rather than further muddy the waters.
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For example, one of the most related papers has been brought at below:
Wu, Jie, and Michael D. Lepech. "Incorporating multi-physics deterioration analysis in building information modeling for life-cycle management of durability performance." Automation in Construction 110 (2020): 103004.
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Please Contact to Defined as unique brands (including subsidiaries with unique product ranges) with products available for download on bimobject.com.
© Copyright 2021 BIMobject AB, all rights reserved. BIMobject® and BIManalytics® are all trademarks of BIMobject AB.
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Dear colleagues,
We ask your kind support to our research on the topic of: Life Cycle Sustainability Impact Categories for Li-Ion Batteries.
This survey is targeted to experts in sustainability assessment, LCA, waste management and similar areas.
Please fill in our survey (expected duration of aprox. 12 minutes) in the link: https://forms.gle/ae3BKh5xYM2ZMywQ8
Your contribution is essential to this study!
Thanks in advance.
A research team from UNESP and CTI, Brazil.
#unesp #batteries #sustainability #lifecycle #ewaste
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Done!
Good luck with your research.
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We are at an era where the technical assessment of processes is digitized. The question that arises is whether in life cycle analysis there are some good practices for digitizing the way in which we assess the environmental indicators through LCA. Excluding the case of buildings, where commercial software already exists (Tally, OneClickLCA) for automatic extraction of life cycle analysis indicators from digital BIM models, are there other cases where the environmental assessment of processes with LCA is done in an automated and digitized way?
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i am working on calculating the carbon footprint of a product, and want to know is there a Life cycle assessment exemple where i can acess detailed information of the Input and Outputs of the inventory ?
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You can try the free case studies of openLCA Nexus, it is free and reasonable.
Please go through this link:
Best wishes,
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Hello everyone !
I'm currently using a Life cycle assessment approach on my case study using OpenLca software,
and I need to know how to establish and model the construction/operation phases of a WWTP( my case is : lagoon wetland wastewater plant), in OpenLCA software ?and then compare both operation phases using an impact method.
Thank you
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Hello,
Yassine Bahi Did you get help with this? I need some guidance as well.
Thanks.
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I am an independent researcher . During the time at University I was able to use Sima-Pro to carry out LCA related assignments. But I would like to know since I do not have the access to Sima-Pro software anymore , any alternative software I could potential use except the OpenLCA software?
Any answers would be highly appreciated.
Thank you
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You could easily use different tools such as open LCA, Umberto LCA and SipaPro for this purpose.
Best
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Hello,
I am wondering about the possibility of exporting data from SimaPro to GaBi and back again. Does the database used in SimaPro have to be the same as what's available in GaBi??
Thanks in advance!
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si creo que es facil en breve le facilitare un folleto para recomendarselo, Saludos
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I have been receiving some feedback from reviewers, specially from those that usually do not work with Life Cycle Assessment (LCA) studies, asking that I should use replicates or statistical analysis other than descriptive statistics in LCA studies. What is the best approach to address their feedback since "replicates" are not listed in any ISO recommendation?
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I had a similar comment from a reviewer and solved it by proposing a sensitivity analysis
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When performing Life Cycle Assessment (LCA) studies, the functional unit provides a reference to which the system's inputs and outputs can be related and a logical basis for comparing the sustainability performance of different products and/or processes. The functional unit is necessary to ensure comparability of LCA results, which is particularly critical when different systems are being assessed, ensuring that such comparisons are made on a common basis. However, the lack of standardization regarding functional units makes LCA studies difficult to compare. Let's say we are performing a systematic review where we need to compare results from different studies (quantitative and/or qualitative data); what would be the best approach to compare results from LCA studies that used different functional units?
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It is indeed worthwhile if you wish to know which are the ideal parameters for LCA and freeze them for constant behaviour. LCA in itself has its objective set right in the beginning and your could try this only when you have no option. Otherwise, it is better to be satisfied with results already achieved, please.
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I want to optimize the usable SOC range of hybrid vehicle in order to improve fuel economy. So. how to choose maximum and minimum SOC values for running an optimization algorithm?
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You need to consider the aging of the batteries because the Depth of Discharge of the battery will be a very important stress factor. This can be tested with the cyclic and calendar aging test. Have a look:
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I would like to include LCA as additional tool for my research and papers. Looking for someone dealing with polymers and composites to cooperate and learn a bit.
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Dear Aleksander,
I am a PhD student who applies the LCA methodology to different biotechnological processes. I have recently written an article, which is being reviewed by the journal, on the production of a PLA biopolymer obtained from the revalorization of an agro-industrial waste stream.
Best regards,
Ana.
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MFCA has been dominantly used for the manufacturing sector. But will it generate useful results when applied to the buildings sectors, considering its entire life-cycle, or is LCA and LCC are better suited. Any suggested papers on the same would also be helpful.
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It could not have been more appropriate in any other sector than the building sector which uses considerable variety of materials right from the beginning until finish. This would add value to the already exercises proposed towards energy and water conservation through LEED and to some extent indigenous applications like Green Rating for Integrated Habitat Assessment - GRIHA, in India.
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I want to study LCA for conventional farming vs organic farming
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second Jesko's idea on OpenLCA, beside with OpenLCA you get free access to the AGRIBALYSE datase (https://nexus.openlca.org/database/Agribalyse) which you could use as foundation of your work
regards
E
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Anyone can suggest to me, software that helps for techno-economic analysis and life cycle assessment for energy generation from wet-organic waste using thermal treatment. Thanks.
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Hello Yonas
I suggest taking a look at the EASETECH which includes several waste treatment modules. Unlike mainstream LCA software, EASETEACH was initially developed to model the LCA of waste treatment additionally it takes care of the mass balance from start to end.
The techno-economic analysis in LCA is more of a conceptual framework, I suggest you take a look at:
Liu, Xinyu, and Bhavik R. Bakshi. 2019. “Ecosystem Services in Life Cycle Assessment While Encouraging Techno‐Ecological Synergies.” Journal of Industrial Ecology 23(2):347–60. doi: 10.1111/jiec.12755.
and
Technische Universität Berlin, Arno Zimmerman, Johannes Wunderlich, Technische Universität Berlin, Georg Buchner, Technische Universität Berlin, Leonard Müller, RWTH Aachen University, Katy Armstrong, The University of Sheffield, Stavros Michailos, The University of Sheffield, Annika Marxen, Institute for Advanced Sustainability Studies e.V. Potsdam, Henriette Naims, Institute for Advanced Sustainability Studies e.V. Potsdam, Fred Mason, CO2 Sciences, Gerald Stokes, CO2 Sciences, Ellen Williams, and CO2 Sciences. 2018. Techno-Economic Assessment & Life-Cycle Assessment Guidelines for CO2 Utilization. Global CO2 Initiative, University of Michigan.
All the best.
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Basically, the aging test methods are carried out by accelerating tests (cycling the exposure of UV light, physical mechanics, like fatigue or crack propagation, water, freeze-thaw, salt spray, etc). I really intrigue is there an official full description or standard method for completely determining the life-cycle of the composite materials for building structure. How correlations test methods' to the time? It would be perfect to give me feedback and ask me closer about my issues by direct message!
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Hello'
Does anyone have any information about reproduction, life cycle, and laboratory culture of Spirobranchus aloni ?
Thanks.
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We have studied only the Mongolian beef and dairy cattle. Our researchers will be studied by in vitro fertilization, next time.
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I know different people will have different answers depending on their backgrounds.
Think in terms of Chemicals for a biorefinery
Initial value
Agriculture
Carbon
Transportation
Integration of the mass culture into the economy
Bioeconomy
life cycle assessments
etc...
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Promising biofuel should have higher calorific value, volatile matter, fixed carbon, and higher carbon and hydrogen content. The moisture content, ash content, oxygen, nitrogen, and sulfur content should be as low as possible.
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Dear all;
I am looking forward to your suggestion regarding the life cycle of a Forward osmosis (FO) membrane.
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See the attached paper
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I'm a university student and I'm writing a paper about Porto. I have to follow some topics like life cycle of Porto; What kind of tourists visit Porto (gender, age, nationality) and their motivation to go there; also any information about thegastronomic tourism in Porto.
Thank you!
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I know that Porto's historic centre was designated a UNESCO World Heritage site in 1996.
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I need to construct nematode infection in roots.
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Hello Vikas,
I usually prepare diagrams and plots using my statistical software (like R) and process the resulting .emf (enhanced metafile) via Inkscape, which is vector based and offers very good tools for graphic manipulation.
For figures and photos I also like using GIMP, which is basically a free Photoshop.
Both softwares are completely free and available for GNU/Linux, OS X, Windows and more operating systems. There are also good tutorials for getting familiar with them.
You can take a look into what is best fitting your requirements. I hope you find what you are looking for :)
Best wishes, Katharina
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What your opinion on the current state of the art in life cycle assessment of chemical substances?
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Besides the green metrics to adress the 12 principles of green chemistry aforesaisd by Torsten, I would also suggest thinking the tool of circular economy (CE) for "life cycle assessment of chemical substances", thus, attributing an economic value through recovering and reusing of (otherwise waste) chemical substances with a positive environmental sign, likewise.
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Which are the documents needed in a construction project which follows the ISO19650? To list a few:
OIR
EIR
AIR
High level Responsbility matrix
Tender invitation
Pre BEP
TIDP
MIDP
Post BEP
Mobilization Plan
Risk register
Please let me know of any other documents
Kind regards
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Interested
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Dear network,
I am looking for the LCA or LCI or at least the energy balances of the non woven fabrics process for my master project, in specific for natural fibers, yet I have found difficulties in finding the proper information. If you have by any chance information or papers containing this kind of info, please let me know,
Thanks in advance
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ps: here you should find more info https://cfda.com
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The eutrophication of groundwater by nitrate leaching is major environmental problem in Germany, especially in areas with intensive agriculture and high N-fertilizer inputs. In addition there are different regional aspects (like soil properties) which make certain areas more vulnerable than others.
I am currently working in a project where we want to improve the sustainability of crop production systems in Germany. Here, we want to assess the impact of crop production on various environmental areas such as GWP, Acidification and Eutrophication, using LCA’s.
We are working with Gabi-Software, which is why we are limited in the choice of LCIA-methods.
I had a closer look on the methods CML 2001, Environmental Footprint 3.0 and ReCiPe 2016 and their underlying models.
I understand the differences between the models. But if we want to assess the impact of Nitrate leaching on groundwater via LCA, it seems only CML is the appropriate method because it considers both - N and P emissions. Also, the characterization factor in Gabi-Software is an average European factor (For ReCiPe it’s a global, for EF it’s European too).
On the other hand, the CML-method is often described as a simple method, since it is a stoichiometric calculation of the contribution of N- and P-emissions to algae growth (Redford-equation). By this, it does not consider any environmental fate.
ReCiPe 2016 or EF 3.0 however differentiate between marine and freshwater eutrophication, in which only N- or P-emissions are considered. So, if I want to assess the impact of N-emissions to groundwater with ReCiPe, I have to use marine eutrophication. But would my results be valid for groundwater at all? The fate factor calculates up to the marine end compartment, and I expect large losses of emissions on the “path” between groundwater and seawater.
I find it extremely difficult to decide, as it is so important to estimate the effects as accurately as possible. Has anyone carried out a similar study on this subject and / or can give me a recommendation?
I would be very grateful!
Best regards and stay safe,
Pia
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Life cycle assessment (LCA) was originally developed as a site-independent tool, where the environments affected by the assessed impacts represent average or generic recipients. For all impact categories where the impact is dependent on the activity location, spatial differentiation can be highly important to achieve representative assessment of the environmental impacts of a system, and failure to take spatial variation into account may give misleading results
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I'd like to calculate the value of trees based on Net Present Value (NPV) in which the value of oxygen supplied by trees in their whole life cycle is also included. Can the learned audience share the easiest method for the same?
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I get highly concerned when economic measurements are applied to ecologic functions.
Start with the discount rate - what is appropriate, and why? The discount rate of fish might be 10% per year, based on the rate of biomass increase. The discount rate for trees might be 1%, as they gain biomass much more slowly than fish. The discount rate for soils would be much, much lower than that. But there are other ecological services than just accumulating biomass - the conversion of CO2 to O2, for example. How would that change the appropriate discount rate?
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To be specific, can you suggest a technological tool (software) that I may use to conduct life cycle analysis of bamboo products?
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The tool I normally use is OpenLCA (https://www.openlca.org/download/) in combination with the ecoinvent database
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Hi all,
I am now working in the evaluation of an innovative renewable energy generation system. For the evaluation of economic aspects I was planning to use the LCOE, levelized cost of energy, and I have some doubts/questions about it.
In particular, I am not sure how I can incorporate in the usual definition, the one that can be found in Wikipedia (https://en.wikipedia.org/wiki/Levelized_cost_of_energy) and normally found in article, terms corresponding to
- Selling excess that cannot used or stored in site. I believe I can add a negative term, Si, to the costs sum, but not sure.
- Residual value at the end of the life cycle. I think I can add a negative term, RV/(1+r)^n, where r is the interest rate and n the useful life time to the numerator. This term arises from the fact that at the end of the life time some materials, in particular, metals, have a value for recycling.
- Disposal cost, I believe I can add a term DC/(1+r)^n, as in certain systems it is necessary to spend some money to be able to properly dispose some of system.
I have some doubts that I am thinking right or not. Thus, can someone give their opinion or reference that help me on issues I am having.
Regards,
António Martins
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Cory, K, and Schwabe, P. Wind Levelized Cost of Energy: A Comparison of Technical and Financing Input Variables. United States: N. p., 2009. Web. doi:10.2172/966296.
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Dear all,
I have been looking for an LCA (Life Cycle Analysis) for the thermoelectric material B2Te3. However, I can't find anything on the internet. Can anyone help me with this? Thank you very much!
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Thanks for the answer! In the first article, there is some info in the reference Ghojel 2005, however, it is said there that: "The databases in the software do not include inventory tables for Bi2Te3 or its constituent elements; therefore, the impact of the TE modules on the environment during material extraction and manufacturing processes was ignored.". So I can't get a lot...
The second one is related to other TE materials. Thanks a lot anyway :).
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Hi all,
I am doing a Life Cycle Study of an Anthraquinone flow battery, and I am having difficulties in finding good references for the production of ferrocyanide. Does anyone have good references for that?
Thanks in advance. Regards,
António Martins
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Madhukar, thanks for your input Do you have also information about process conditions, in particular reaction temperature and reactioj time? It will help a lot.
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Smartbox or energy is an important item of a solar power system. I would be grateful if someone can help me/suggest a literature source to find life cycle inventory of the smart box. Thanks.
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Hello,
I have a set of anatomical variables for around 30 spp (same genus). Along with using these variables in species grouping, I also want to analyze the effect of some other variables (like, habitat type and life cycle pattern) in shaping them i.e. response of the anatomical traits to habitat variation and lifecycle pattern.
I have matrixed all the variables in binary code (0/1) for each species and performed PCA in R, treating all variables as same (same matrix).
So, the main question was that: can we simply depend on the angle range between the "anatomical" vs "ecological" variables in a "variables vs. species PCA biplot" to determine their correlation?
Also, need your suggestions regarding:
1. What kind of analyses can best fit this form of data?
2. Shall I log-transform the data before analyses?
3. Is that a correct form of data-treatment that I have binary-coded the environmental and life cycle variables, or I shall treat them as categorical?
4. Is it necessary to assess the significance of the analysis results statistically (eg., ANOVA...)?
Please note that the ecological variables are of different species, not of different populations of the same species.
I highly appreciate your kind help!
Your's,
Dastan
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Thanks for your answer, Andrew Paul McKenzie Pegman!
OK:)
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Polyurethane insulating foam plays key role in energy-efficient cooling systems such as storage in cold stores, local storage in supermarkets, and domestic refrigerators. In LCA assessment of refrigerators/cold rooms, high priority should be given to impacts from insulation foam.
I would appreciate it very much if anyone shares LCI of end of life recycling/treatment of polyurethane sheet
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You can find some info here and in the attached file:
in: Recycling of Polyurethane Foams: https://doi.org/10.1016/C2016-0-01054-9
I hope they can be useful.
Best regards
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Do the shortening of life cycles of technical products, electronics, household appliances, IT equipment, etc. used by producers is a solution to the potential problem of overproduction?
Please reply
Best wishes
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No, This will create more overproduction.
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I am looking for a method blank which I can use in the heavy metals, terpene, solvents, cannabinoid, pesticide, and microbial analyses I do in my analytical lab on cannabis samples. I have tried Oven drying hemp to remove the residual solvents and terpenes because these are more volatile compounds. It worked for the terpenes, they were all burned off, but it did not work for the residual solvents analysis due to the inherent solvents that plants produce or uptake in their natural life cycle.
For heavy metals the samples failed due to the fact that almost all plants will have some amount of heavy metals in them from the soil they are in. Small amounts of cannabinoids were also found in the hemp so it did not work for potency testing.
Does anyone have any ideas for a suitable plant material that is similar to cannabis that could possibly be used as an "analyte-free" matrix for method blank purposes? I have heard of other labs using vegetable or hemp oils but I feel the matrix is not similar enough to cannabis flower to use in this instance.
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I bet you are not developing all these methods for a university research, but for commercial regulatory testing lab, isn't it?
Let's break down the different tests:
1- Heavy metals: It's hard to find a plant without metals at all. So, use cannabis flower to make two aliquots, one to be extracted directly and the other to be spiked by some metals standard and then extract it. Subtract the unspiked from the spiked to calculate recovery.
2- Terpenes: You are right about what you heard. Use oils such as cooking oils or skin lotions.
3- Solvents: Same as terpenes, just subtract the values measured in the unspiked aliquot from the spiked one to calculate recovery.
4- Cannabinoids: Use a hemp matrix. Hemp doesn't have high THC, maybe no THC at all. Disregard the other cannabinoids, no one cares for them, focus of THC only.
5- Pesticides: Usually the cannabis flower is free of detectable pesticides, so you can use it as blank.
6- Microbial: No idea actually.
You can connect with me to share research ideas and publish papers if interested!
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Methods of LCIAs are a fast developing field of research, not less than LCSA and LCA itself. At the moment i am developing a set of indicators and methods of impact assessment for an LCSA of regional bioeconomy in context of the SDGs. Therefore i would be very interested and grateful for your research, knowledge and/or ideas regarding LCIAs for LCSA.
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Dear Walther Zeug,its an important question pertaining to LCIA
& LCSA.I hope the following article can help you.
1."Sustainability and Life Cycle Assessment in Industrial Biotechnology: A Review of Current Approaches and Future Needs"
2. A critical view on the current application of LCA for new technologies and recommendations for improved practice
Regards,
Md OsimAquatar
CSIR-NEERI,INDIA
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Solar Direct Current (DC) Microgrid for remote areas is relatively an emerging area and there have been installations in different parts of the world. Battery is the obvious storage device for such applications. Any empirical results as to which one among Lead Acid/Li-Ion is effective in a comprehensive perspective say on life-cycle basis? 
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the above discussion is very helpful.
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We are currently working on an LCA paper regarding Non-Recyclable Plastics-to-Energy Processes. We need an LCA expert to prepare an inventory and analyze the data by SimaPro and give us the report. Do you know of any experts or can anyone help, there will be an awarded sum.
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There are many people, also on RG, that works on LCA, you can contact alessandra zamagni from "ecoinnovazione"
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Protein is one of the macro nutrient required by chicken. to satisfy the requirement of the protein source different feed ingredients are used across the globe. I am interested to know how to asses the life cycle of this macro nutrient.
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The condition for the organization to survive and experience a long life cycle is the speed of adaptation to new normal.
S-curve management is attached. Where are you now?