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Автор: Grafiati
Опубліковано: 10 грудня 2022
Оновлено: 28 січня 2023

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Статті в журналах з теми "Product life cycle Australia"

1

Moazzem, Shadia, Enda Crossin, Fugen Daver, and Lijing Wang. "Life Cycle Assessment of Apparel Consumption in Australia." Environmental and Climate Technologies 25, no. 1 (January 1, 2021): 71–111. http://dx.doi.org/10.2478/rtuect-2021-0006.

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Abstract This study presents the environmental impact of apparel consumption in Australia using life cycle assessment methodology according to ISO14040/14044:2006. Available published references, the Ecoinvent v3 dataset, the Australian life cycle assessment dataset and apparel country-wise import data with the breakdown of apparel type and fibre type were used in this study. The environmental impact assessment results of the functional unit were scaled up to the total apparel consumption. The impact results were also normalized on a per-capita/year basis. The Total Climate Change Potential (CCP) impact from apparel consumption of 2015 was estimated to be 16 607 028 tonnes CO2eq and 698.07 kg CO2eq/per capita-year. This study also assessed the impact of acidification potential (AP), water depletion (WD), abiotic resource depletion potential (ADP) - fossil fuel and agricultural land occupation (ALO) using the same methodology. The market volume of cotton apparel in Australia is 53.97 %, which accounts for 45 %, 96 %, 40 %, 46 % and 79 % of total CCP, WD, ADP, AP and ALO impact, respectively. Apparel broad categories of cotton shirt, cotton trouser, polyester shirt and polyester trouser have a high volume in the apparel market as well as a high environmental impact contribution. These high-volume apparel products can be included in the prioritization list to reduce environmental impact throughout the apparel supply chain. It was estimated that from 2010 to 2018 the per capita apparel consumption and corresponding impact increased by 24 %.
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2

Mohammadi, James, and Warren South. "Life cycle assessment (LCA) of benchmark concrete products in Australia." International Journal of Life Cycle Assessment 22, no. 10 (January 27, 2017): 1588–608. http://dx.doi.org/10.1007/s11367-017-1266-2.

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3

Holmes, Scott, Gary Kelly, and Ross Cunningham. "The Small Firm Information Cycle: A Reappraisal." International Small Business Journal: Researching Entrepreneurship 9, no. 2 (January 1991): 41–53. http://dx.doi.org/10.1177/026624269100900203.

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DR. SCOTT HOLMES IS PROFESSOR OF Accounting at the University of Arizona, Tucson, United States, and was previously at the University of Queensland, Australia. Cary Kelly is a lecturer in the department adn Ross Cunningham a senior lecturer in the Departmet of Statistic at the Australian National University. Prior research has identified various stages in the lfie of a small enterprise. These states are commonly combined to produce a business life cycle. This paper proposed that small enterprise consists of a serios f interrelated cycles and as such, the presentation of an overall life cycle provides and over-simplified view of the firm. the concept of the information sub-cycle is introduced, which in itself can take many forms. Logistics regression modelling techniques incorporating those variables which appera to be significant in infulecing the level of accounting information prepared or acquired are applied to the development of an information cycle. The result obtained indicate that the acquistion and /or preparation of a relatively detailed level of accounting information is dependent on firm age, size, industry membership and level of owner-manger education. the pattern which emerges from these results supports the revision of traditional life cycle concepts. in particular, the need to segment the firm into severl sun-cycle is recommended.
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4

Sehlin MacNeil, Kristina, Sheelagh Daniels-Mayes, Skye Akbar, Jillian Marsh, Jenny Wik-Karlsson, and Åsa Össbo. "Social Life Cycle Assessment Used in Indigenous Contexts: A Critical Analysis." Sustainability 13, no. 9 (May 5, 2021): 5158. http://dx.doi.org/10.3390/su13095158.

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This paper evaluates the method Social Life Cycle Assessment (S-LCA) from the perspectives of Indigenous methodologies and Indigenous standpoint, in order to identify some strengths and limitations of using S-LCA in Indigenous contexts. Life Cycle Assessment (LCA) is used to measure environmental impacts connected with all stages of the life cycle of a commercial product, process, or service. S-LCA is a methodology designed to include the social aspects of sustainability in the LCA methodology. S-LCA emphasizes stakeholder involvement and the United Nations Environment Programme (UNEP) S-LCA guidelines (2020) lists Indigenous communities as possible stakeholders. With a focus on Indigenous communities in the Arctic region we also include comparative aspects from Australia to generate new conceptualizations and understandings. The paper concludes that S-LCA has the potential to facilitate opposing worldviews and with some further developments can be a valuable methodology for Indigenous contexts.
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5

Rasmussen, Freja Nygaard, Camilla Ernst Andersen, Alexandra Wittchen, Rasmus Nøddegaard Hansen, and Harpa Birgisdóttir. "Environmental Product Declarations of Structural Wood: A Review of Impacts and Potential Pitfalls for Practice." Buildings 11, no. 8 (August 18, 2021): 362. http://dx.doi.org/10.3390/buildings11080362.

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The use of wood and timber products in the construction of buildings is repeatedly pointed towards as a mean for lowering the environmental footprint. With several countries preparing regulation for life cycle assessment of buildings, practitioners from industry will presumably look to the pool of data on wood products found in environmental product declarations (EPDs). However, the EPDs may vary broadly in terms of reporting and results. This study provides a comprehensive review of 81 third-party verified EN 15804 EPDs of cross laminated timber (CLT), glulam, laminated veneer lumber (LVL) and timber. The 81 EPDs represent 86 different products and 152 different product scenarios. The EPDs mainly represent European production, but also North America and Australia/New Zealand productions are represented. Reported global warming potential (GWP) from the EPDs vary within each of the investigated product categories, due to density of the products and the end-of-life scenarios applied. Median results per kg of product, excluding the biogenic CO2, are found at 0.26, 0.24, and 0.17 kg CO2e for CLT, glulam, and timber, respectively. Results further showed that the correlation between GWP and other impact categories is limited. Analysis of the inherent data uncertainty showed to add up to ±41% to reported impacts when assessed with an uncertainty method from the literature. However, in some of the average EPDs, even larger uncertainties of up to 90% for GWP are reported. Life cycle assessment practitioners can use the median values from this study as generic data in their assessments of buildings. To make the EPDs easier to use for practitioners, a more detailed coordination between EPD programs and their product category rules is recommended, as well as digitalization of EPD data.
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6

Cribb, TH. "Life-Cycle and Biology of Prototransversotrema-Steeri Angel, 1969 (Digenea, Transversotrematidae)." Australian Journal of Zoology 36, no. 2 (1988): 111. http://dx.doi.org/10.1071/zo9880111.

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A population of Prototransversotrema steeri Angel, 1969 is recorded from the introduced fish Gambusia affinis and the native species Pseudomugil signifer and Mugil cephalus in fresh water in Queensland, Australia. Adults of P. steeri are considerably smaller than adults previously described from marine fish. This appears to be a host-related phenomenon, possibly reflecting the size of the subscale niche offered by the host. The intermediate host is Posticobia brazieri, a hydrobiid snail. It is suggested that different hydrobiid snails may act as intermediate hosts in other parts of Australia. The miracidium develops into a mother sporocyst which produces a single mother redia. Mother rediae produce daughter rediae which may produce further daughter rediae or cercariae. Cercariae emerge from the redia while still embryonic and develop independently in the tissues of the snail. Upon emergence the cercariae attach directly to the definitive host and commence egg-production within 6 days. Gambusia affinis, Xiphophorus rnaculatus, X. helleri, Craterocephalus marjoriae and Mugil cephalus were all infected experimentally. I discuss various theories concerning the phylogenetic position of the Transverso- trematidae within the Digenea and conclude that the family occupies an isolated position not closely allied with any other group.
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7

Rouwette, Rob. "Life-cycle assessment: use and application in the Australian energy context." APPEA Journal 52, no. 2 (2012): 661. http://dx.doi.org/10.1071/aj11075.

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Australia is experiencing a time of major change in its energy sector. First, there is record investment in developing new fossil fuel resources—such as coal, LNG and coal seam methane gas—for export. Second, there is an ever-increasing attention to renewable energy generation for the domestic market. The looming introduction of a price on carbon (greenhouse gas emissions) in 2012 has fuelled the debate about how clean various energy sources are, and how any/all emissions associated with their development and the generation of energy should be treated. As a market reponse, a significant increase in using life-cycle assessment (LCA) results to communicate environmental performance, particularly about greenhouse gas emissions, have been witnessed. When undertaken appropriately, a full life-cycle approach is the only acceptable methodology to compare disparate technologies or products; however, given the often technical nature of LCA studies, the results are not always conveyed accurately in the non-technical mainstream media. This extended abstract discusses case studies related to the energy sector using LCA results—their benefits and shortcomings—in Australian media; suggestions for better communication and decision making in the coming period are also discussed.
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8

Hoque, Zahirul, and Wendy James. "Linking Balanced Scorecard Measures to Size and Market Factors: Impact on Organizational Performance." Journal of Management Accounting Research 12, no. 1 (January 1, 2000): 1–17. http://dx.doi.org/10.2308/jmar.2000.12.1.1.

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This paper examines the relationship between organization size, product life-cycle stage, market position, balanced scorecard (BSC) usage and organizational performance. Using financial and nonfinancial measures, the BSC appraises four dimensions of performance: customers, financial (or shareholders), learning and growth, and internal aspects. Based on a survey of 66 Australian manufacturing companies, the paper suggests that larger firms make more use of a BSC. In addition, firms that have a higher proportion of new products have a greater tendency to make use of measures related to new products. A firm's market position has not been found to be associated significantly with greater BSC usage. The paper also suggests that greater BSC usage is associated with improved performance, but this relationship does not depend significantly on organization size, product life cycle, or market position.
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9

Higham, Rebecca K., and John J. Todd. "Life-cycle assessment and its relevance to Australian forestry and wood product industries." Australian Forestry 61, no. 2 (January 1998): 65–69. http://dx.doi.org/10.1080/00049158.1998.10674721.

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10

Bunn, SE. "Life histories of some Benthic invetebrates form streams of the Northern Jarrah Forest, Western Australia." Marine and Freshwater Research 39, no. 6 (1988): 785. http://dx.doi.org/10.1071/mf9880785.

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Life history patterns of thirteen species of invertebrates from streams of the northern jarrah forest were examined over a 1-year period. Five species had univoltine cycles with a single cohort and demonstrated a high degree of synchrony of larval development and a restricted period of adult emergence. Two species of Leptophlebiidae also had univoltine cycles but showed the more typical pattern of Australian mayflies, with extended recruitment, multiple overlapping cohorts and a long period of adult emergence. Uroctena sp., a small gammarid, had a generation time of 1 year but showed considerable spatial variation in the degree of synchrony of development. This appeared to be a result of differences in the constancy of stream discharge and was not attributable to differences in the temperature regime of the streams. At least three species demonstrated cohort splitting which resulted in an apparently bivoltine cycle. A life-history pattern of alternating long and short development times is described which, on average, would produce two generations every 3 years. This is considered to be a highly adaptive strategy for Australian stream insects with slow life cycles and can explain the extended periods of recruitment and adult emergence so often observed. Streams of the northern jarrah forest are depauperate compared with other Australian streams, despite predictable temperature and discharge regimes. The insular nature of the south-west Bassian region and its long period of isolation may be the principle cause of this reduced diversity. The invertebrate community of these streams is simple in structure and has a high degree of seasonality that is atypical of the temperate streams of Australia and New Zealand.
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Більше джерел

Дисертації з теми "Product life cycle Australia"

1

Wright, Lucy. "Product life cycle management." Thesis, University of Surrey, 1999. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.301674.

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2

Usanmaz, Gokhan. "End-of-life cycle product management." Thesis, Massachusetts Institute of Technology, 2000. http://hdl.handle.net/1721.1/8736.

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Thesis (M.Eng.)--Massachusetts Institute of Technology, Engineering Systems Division, 2000.
Includes bibliographical references (leaves 75-77).
Market leadership requires effective management of product life cycle, starting from the launch of a new product until its retirement. In this particular project, an exploratory study of business practices in the management of products in the decline phase and the eventual decision of product abandonment is conducted through surveys and interviews of senior executives from Fortune 500 companies, focusing mainly on food, networking equipment, medical devices, consumer electronics and retail industries. Actual names of the companies are not revealed for confidentiality reasons. Also, the implementations, assumptions and level of acceptance of decision support system (DSS) modules on product lifecycle management are analyzed. Finally, companies' business processes are compared and enhancements to current DSS systems are proposed.
by Gokhan Usanmaz.
M.Eng.
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3

Karlsson, Charlie. "Innovation adoption and the product life cycle." Doctoral thesis, Umeå universitet, Institutionen för nationalekonomi, 1988. http://urn.kb.se/resolve?urn=urn:nbn:se:umu:diva-100373.

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4

Sousa, Inês (Maria Inês Silva Sousa) 1972. "Integrated product design and life-cycle assessment." Thesis, Massachusetts Institute of Technology, 1998. http://hdl.handle.net/1721.1/46141.

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5

Kudrna, Jiri, and g. kudrna@unsw edu au. "Retirement Income Policy in Australia: Life-Cycle Analyses." University of Sydney, 2009. http://hdl.handle.net/2123/4119.

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Doctor of Philosophy(PhD)
Retirement income policy in Australia has undergone significant changes over the last two decades, including the introduction of the Superannuation Guarantee [SG] with mandatory contributions in 1992 and the 2007 superannuation changes with the benefit tax abolition. Numerical implications of adopted pension reforms and reform proposals such as further increases in the SG contribution rate, changes to superannuation taxation and to means-testing of the age pension have been examined mainly by micro-simulation models. These models, often criticized for their lack of theoretical content, provide an incomplete picture of pension policy effects because of no or limited behavioural responses to underlying policy changes. In this thesis, models based on the life-cycle theory of saving pioneered by Modigliani and Brumberg (1954) are applied to simulate behavioural, welfare and macroeconomics effects of proposed changes to Australia’s pension policy. In particular, this thesis develops the following computable models: a life-cycle, single household model, a partial equilibrium, household model and a general equilibrium model with overlapping generations [OLG]. The single household model describes lifetime behaviour of the utility-maximising single household with uncertain lifespan. The model features perfect capital markets, endogenous labour supply and retirement decisions, and it incorporates main aspects of Australia’s pension and income tax policy settings. The simulated policy changes are (i) increase in the SG contribution rate, (ii) superannuation tax changes and (iii) abolition of the age pension means test. The results indicate higher retirement consumption and welfare gains from all the analysed pension policy changes. Partial equilibrium and general equilibrium models introduced in this thesis are built on lifetime behaviour of the single household. Both models distinguish many generations of households by age and, therefore, are capable of studying behavioural and welfare effects of policy changes for different generations. The partial equilibrium model examines behaviour of the household sector in the environment of the fixed factor prices. It is shown, for instance, that welfare gains from the investigated pension policy changes are not uniformly distributed across generations. The general equilibrium OLG model extends the partial equilibrium analyses by incorporating production, government and foreign sectors in addition to household and pension sectors. The model is a small open economy version of Auerbach and Kotlikoff’s (1987) OLG model. The simulation results are significantly different from those in the partial equilibrium framework, driven mainly by the changes in aggregate labour supply. For instance, the higher SG rate policy increases aggregate assets and saving. However, the saving increases are exported abroad rather than invested in the domestic capital stock. Hence, the implications of this policy change for the capital stock and output are minimal. Younger cohorts and future born generations experience consumption and welfare gains but older cohorts are negatively affected by a higher consumption tax rate resulting from this hypothetical policy change.
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Rodseth, Clare Josephine. "End-of-life in South African product life cycle assessment." Master's thesis, University of Cape Town, 2018. http://hdl.handle.net/11427/29363.

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Анотація:
Life cycle assessment (LCA) is a tool specifically developed for quantifying and assessing the environmental burden of a product across its entire life cycle, thus providing powerful support for sustainable product design. There exists a geographical imbalance in the adoption and distribution of LCA studies, with a notably poor penetration into developing countries, resulting from a lack of technical expertise, reliable data, and an inability to engage with the key issues of developing countries. These challenges are particularly prevalent in waste management. The limitations in current LCA capacity for representing product end-of-life, coupled to the disparity in waste management practices between developed and developing countries means that LCA is currently unable to accurately model product end-of-life in South Africa. This means that, for imported products designed on the basis of LCA, the upstream impacts may be accurate, while the end-of-life is not. Therefore, to improve the use of LCA as a tool to support sustainable product design, there is a need to develop life cycle datasets and methods that accurately reflect the realities of waste management in developing countries. The objectives of this dissertation are to (i) identify the current shortcomings of existing LCA datasets in representing the end-of-life stage of general waste in a South African context, and (ii) propose modifications to existing datasets to better reflect the realities of waste management in a South African context and extract lessons from this for use elsewhere. To meet these objectives, research was undertaken in three main stages, with the outcome of each stage used to inform the development of each subsequent stage. The first stage aimed to establish the status quo with regards to general waste management in South Africa. This investigation was informed through a desktop review of government and other publicly available reports, supplemented by field work and stakeholder engagements. These results formed the basis for the second stage: a review of LCA capacity for representing product end-of-life in the South African context. The review of datasets was limited to those contained within SimaPro v8.3 and was undertaken with the aim of understanding the extent to which current datasets are capable of representing South African waste management practices. Finally, three cases of existing LCA datasets were explored. This included testing modifications that could be made in an attempt to improve their applicability to the South African reality. In South Africa, a major limitation in developing a quantified mapping of waste flows lies in the paucity of reliable waste data and the exclusion of the contribution of the informal sector in existing waste data repositories. It was estimated that South Africa generates approximately 12.7 million tonnes of domestic waste per annum, of which an estimated 29% is not collected or treated via formal management options. For both formal and informal general waste, disposal to land (landfill and dumping) represents the most utilised waste management option. Landfill conditions in South Africa range from well-managed sanitary landfills to open dumps. Considering only licensed landfill facilities, it is estimated that large and medium landfill sites accept the majority of South Africa’s general waste (54% and 31% respectively), while the balance is managed in small (12%) and communal (3%) sites. Considering the quantity of informal domestic waste enables a crude estimation of household waste distribution between different landfill classes. In this instance, while the majority of waste (40%) is still managed in large formal landfill sites, an appreciable quantity (26%) is managed in private dumps. Within SimaPro v8.3 landfill disposal is best represented by the sanitary landfill datasets contained within the ecoinvent v3.3 database. SimaPro preserves the modular construction of the ecoinvent dataset, meaning that various generic modifications to these datasets can be made, such as the elimination or addition of burdens, redefinition of the value of a burden, or substitution of a linked dataset. Practically, such modifications are limited to process-specific burdens. However, wastespecific burdens are of greater significance in the life cycle impact assessment (LCIA) result of a landfill process. Waste-specific emissions are generated using the underlying ecoinvent landfill emission model. The current model structure allows for the parametrisation of waste composition in addition to landfill gas (LFG) capture and utilisation efficiencies. However, besides the incorporation of a methane correction factor to account for the effect that various site conditions have on the waste degradation environment, the extent to which the existing model can be adapted to represent alternative landfill conditions is limited. This is particularly true in the case of leachate generation and release. Although adaptation that incorporates the effect of climatic conditions on waste degradability and emission release is possible, this requires a high level of country-specific data and modelling expertise. Thus, the practicality of such a modification within the skills set of most LCA practitioners is questionable. Further limitations in the existing modelling framework include its inability to quantify the potential impacts of practices characteristic of unmanaged sites such as open-burning, waste scavenging, and the presence of vermin and other animal vectors for disease. Analysis of the LCIA results for different landfill scenarios showed that regardless of either the deposited material or the specific landfill conditions modelled, the time frame considered had the most pronounced effect on the normalised potential impacts. Regardless of landfill conditions, when long-term leachate emissions are considered, freshwater and marine ecotoxicity impacts dominate the overall potential impacts of the site. This result implies that if landfill disposal is modelled over the long-term, the potential impacts of the process has less to do with site-specific conditions than it does to do with the intrinsic properties of the material itself. Given the ensuing extent of degradation that occurs over the time frame considered, the practise of very long-term modelling can equalise landfills that differ strongly in the short-term. In terms of product design on the basis of LCA, the choice of material can be more strongly influenced by the time frame considered than the specific landfill scenario. From a short-term perspective, for fast degrading materials the impacts incurred from leachate emissions and their subsequent treatment are of lesser importance than those arising from LFG. From a long-term perspective by contrast, leachate emissions have a significant effect on the LCIA result. Investigation into the effect of reduced precipitation on the LCIA result showed that the exclusion of leachate emissions lowers the potential impacts of a number of impact categories, with the most substantial quantified reduction observed in the freshwater and marine ecotoxicity impact categories. This result implies that for dry climates, the long-term impacts of landfilling could be significantly lower than when compared to landfill under temperate conditions, with the potential impacts of the waste remaining locked-up in the landfill. Given quantified findings on South Africa’s dependence on both formal and informal disposal, and the variation in landfill conditions across the country, it can be concluded that LCA results for the impacts of products originating from global supply chains, but consumed and disposed of in South Africa, will be inaccurate for the end-of-life stage if modifications to end-of-life modelling are not made. The findings from this dissertation provide the basis for i) a crude estimate of ‘market shares’ of different disposal practises and ii) guidelines for parameterisation of material specific emission factors, in particular for shorter term emissions, focused on LFG and leachate emissions.
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7

Kalyan, Seshu Uma Sankar D. "Including life cycle considerations in computer aided design." Thesis, Georgia Institute of Technology, 1998. http://hdl.handle.net/1853/16877.

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8

Ny, Henrik. "Strategic Life-Cycle Modeling for Sustainable Product Development." Licentiate thesis, Karlskrona : Blekinge Institute of Technology, 2006. http://urn.kb.se/resolve?urn=urn:nbn:se:bth-00352.

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Анотація:
Decision makers are challenged by complex sustainability problems within the socio-ecological system. In response, a vast range of sustainability-related methods/tools have been developed, each focusing on certain aspects of this challenge. Without a unifying theory it is, however, unclear how these methods/tools can support strategic progress towards sustainability and how they relate to each other. This need for clarity and structure urged some sustainability pioneers to start develop an overarching framework for strategic sustainable development (SSD), often called “The Natural Step (TNS) framework”, from the NGO that has facilitated its development and application, or the “backcasting from sustainability principles (BSP) framework” from its main operational philosophy. The aim of this thesis is to study if, and in that case how, this framework can aid coordination and further development of various sustainability-related methods/tools, specifically to increase their capacity to support sustainable product development (SPD). Life-cycle assessment (LCA), “templates” for SPD and systems modeling and simulation (SMS) are the methods/tools in focus. A new strategic life-cycle management approach is presented, in which the main sustainability aspects, LCA “impacts”, are identified through socioecological sustainability principles. This creates new opportunities to avoid the reductionism that often follows from traditional system boundaries or from a focus on specific impacts. Ideas of how this approach can inform the studied tools are given. This may eventually lead to a whole integrated toolbox for SPD (a “Design Space”). As part of such a Design Space, a new “template” approach for SPD is developed. A case study of a sustainability assessment of TVs at the Matsushita Electric Group indicates that this approach can create a quick overview of critical sustainability aspects in the early part of the product development process and facilitate communication of this overview between top management, product developers, and other stakeholders. A potential integration between BSP and SMS is also discussed. It is suggested that this should start with BSP to create lists of critical presentday flows and practices, ideas of long term solutions and visions, and a first rough idea about prioritized early investments. After that, SMS should be applied to study the interrelationships between the listed items, in order to create more robust and refined analyses of the problems at hand, possible solutions and investment paths, while constantly coupling back to the sustainability principles and guidelines of the BSP framework. v Decision makers seem to need more of an overview and of simplicity around sustainability issues. A general conclusion is, however, that it is important that this is achieved without a loss of relevant aspects and their interrelations. Over-simplifications might lead to sub-optimized designs and investments paths. Combining the BSP framework with more detailed methods/tools seems to be a promising approach to finding the right balance and to get synergies between various methods/tools.
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9

Besbes, Khaoula. "Supply chain design with product life cycle considerations." Thesis, Artois, 2013. http://www.theses.fr/2013ARTO0209/document.

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Анотація:
Notre travail de recherche traite la problématique de la conception d’une chaîne logistique multi-niveaux tout en tenant compte du cycle de vie du produit. Par cycle de vie du produit, nous voulons dire la succession des quatre phases de commercialisation que traverse un produit à travers le temps, à savoir : l’introduction, la croissance, la maturité et le déclin. L’objectif est de mette en place un modèle mathématique qui soit fondé sur une analyse approfondie des différents acteurs de la chaîne, selon la phase du cycle de vie du produit.Trois principaux modèles ont été développés dans cette thèse. Chacun fait l’objet d’un chapitre à part entière.Le premier modèle développé vise à concevoir une chaîne logistique de coût minimum, tout en prenant en considération l’efficacité des différents acteurs potentiels calculée selon plusieurs critères (coût, qualité, innovation, qualité du service, délais de livraisons, …), ainsi que sa variation au cours du cycle de vie du produit. Un deuxième modèle a été mis en place pour la conception d’une chaîne logistique durable, tout en prenant en considération le cycle de vie du produit. Dans ce modèle, trois objectifs différents ont été pris en compte à la fois, à savoir, un objectif économique, un objectif environnemental et un objectif social. Dans les deux premiers modèles, nous avons supposé que le produit aura un cycle de vie classique. Cependant, dans la réalité, ceci n’est pas toujours le cas. En effet, quelques produits connaissent des cycles de vie très atypiques et donc très éloignés de la courbe d’un cycle de vie théorique. Pour ce faire, un troisième modèle stochastique a été proposé pour la conception d’une chaîne logistique robuste, tenant compte des différents scénarios du cycle de vie du produit
Our research addresses the problem of designing a multi-level supply chain, while taking into consideration the product life cycle. By product life cycle, we mean the succession of the four marketing stages that a product goes through since its introduction to the market and until it will be removed from. All products have a life cycle which can be classified into four discrete stages: introduction, growth, maturity and decline.Depending on the product life cycle phases, and based on a thorough analysis of the different supply chain potential actors, this study aims to establish mathematical models to design an efficient supply chain network. Three main models have been developed in this thesis. The first proposed model aims to design a product-driven supply chain with a minimal total cost, taking into consideration the evaluation of the different potential actors effectiveness, according to several criteria (cost, quality, innovation, quality service, timely delivery, ...).A second model was developed to design of a sustainable supply chain network, taking into account the product life cycle. In this model, three different objectives at the time were considered, namely, an economic objective, an environmental objective and a social objective.In the two previous models, we have assumed that the product has a classical life cycle. However, in the reality this is not always the case. Indeed, some products have very atypical life cycles, whose curves are very different from the classical one. To tackle this problem, in the third part of this thesis, we propose a stochastic model to design a robust supply chain network, taking into account the different product life cycle scenarios
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Chen-hong, Christina Yun-ju. "Cycle time modeling /." Digital version accessible at:, 1999. http://wwwlib.umi.com/cr/utexas/main.

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Книги з теми "Product life cycle Australia"

1

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

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J, Shaw John, ed. Product life cycles and product management. New York: Quorum Books, 1989.

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Giordano, Max. Product life-cycle management: Geometric variations. Hoboken, NJ: ISTE Ltd/John Wiley and Sons Inc., 2010.

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Soenen, René, and Gustav J. Olling, eds. Feature Based Product Life-Cycle Modelling. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-0-387-35637-2.

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Jovanovic, Boyan. The product cycle and inequality. Cambridge, MA: National Bureau of Economic Research, 2004.

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6

Environmental life cycle analysis. Boca Raton: Lewis Publishers, 1997.

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Streamlined life-cycle assessment. Upper Saddle River, NJ: Prentice Hall, 1998.

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8

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

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Life cycle reliability engineering. Hoboken, NJ: John Wiley & Sons, Inc., 2007.

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McCurry, Larry. Managing inventory through the product life cycle. [s.l: The Author], 1993.

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Частини книг з теми "Product life cycle Australia"

1

Bartlett, Dean, and John Twineham. "Product Life Cycle." In Encyclopedia of Corporate Social Responsibility, 1914–20. Berlin, Heidelberg: Springer Berlin Heidelberg, 2013. http://dx.doi.org/10.1007/978-3-642-28036-8_56.

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Cordell, Andrea, and Ian Thompson. "Product Life Cycle." In The Procurement Models Handbook, 19–21. Third edition. | Abingdon, Oxon ; New York, NY : Routledge, 2019. | Earlier editions published as: Purchasing models handbook: a guide to the most popular business models used in purchasing / Andrea Reynolds and Ian Thompson.: Routledge, 2019. http://dx.doi.org/10.4324/9781351239509-6.

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Klepper, Steven. "Product Life Cycle." In The New Palgrave Dictionary of Economics, 10812–15. London: Palgrave Macmillan UK, 2018. http://dx.doi.org/10.1057/978-1-349-95189-5_2851.

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Klepper, Steven. "Product Life Cycle." In The New Palgrave Dictionary of Economics, 1–4. London: Palgrave Macmillan UK, 2008. http://dx.doi.org/10.1057/978-1-349-95121-5_2851-1.

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Hampshire, Natasha, Glaudia Califano, and David Spinks. "Product Life Cycle." In Mastering Collaboration in a Product Team, 16–17. Berkeley, CA: Apress, 2022. http://dx.doi.org/10.1007/978-1-4842-8254-0_8.

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Su, Daizhong, and Zhongming Ren. "Gearbox Life Cycle Assessment." In Sustainable Product Development, 193–219. Cham: Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-39149-2_10.

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Wu, You, and Daizhong Su. "Social Life Cycle Assessment." In Sustainable Product Development, 127–52. Cham: Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-39149-2_7.

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Wu, You, and Daizhong Su. "Life Cycle Inventory Management." In Sustainable Product Development, 153–66. Cham: Springer International Publishing, 2020. http://dx.doi.org/10.1007/978-3-030-39149-2_8.

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Kahn, Kenneth B., and Mayoor Mohan. "Life Cycle Management." In Innovation and New Product Planning, 177–85. New York, NY: Routledge, 2021.: Routledge, 2020. http://dx.doi.org/10.4324/9781003025313-14.

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Herrmann, Christoph. "Product Life Cycle Management." In CIRP Encyclopedia of Production Engineering, 1–4. Berlin, Heidelberg: Springer Berlin Heidelberg, 2018. http://dx.doi.org/10.1007/978-3-642-35950-7_6610-3.

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Тези доповідей конференцій з теми "Product life cycle Australia"

1

Sakai, N., G. Tanaka, and Y. Shimomura. "Product life cycle design based on product life control." In 2003 IEEE 58th Vehicular Technology Conference. VTC 2003-Fall (IEEE Cat. No.03CH37484). IEEE, 2003. http://dx.doi.org/10.1109/vetecf.2003.240266.

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Sakai, Tanaka, and Shimomura. "Product life cycle design based on product life control." In 2003. 3rd International Symposium on Environmentally Conscious Design and Inverse Manufacturing - EcoDesign'03. IEEE, 2003. http://dx.doi.org/10.1109/ecodim.2003.1322645.

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Brandherm, Boris, and Alexander Kroner. "Digital Product Memories and Product Life Cycle." In 2011 7th International Conference on Intelligent Environments (IE). IEEE, 2011. http://dx.doi.org/10.1109/ie.2011.76.

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Han, Ni. "Analysis of Music Life Cycle Based on Product Life Cycle Theory." In 2021 International Conference on Public Art and Human Development ( ICPAHD 2021). Paris, France: Atlantis Press, 2022. http://dx.doi.org/10.2991/assehr.k.220110.033.

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Friedrich, Jürgen, and Horst Krasowski. "Ecology-Based Product Data Model." In Total Life Cycle Conference & Exposition. 400 Commonwealth Drive, Warrendale, PA, United States: SAE International, 1998. http://dx.doi.org/10.4271/982227.

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Joshi, Alhad, Binu Panicker, and Shashidhar Lakshminarayana. "Product Performance Validation Life Cycle Management." In ASME 2009 International Design Engineering Technical Conferences and Computers and Information in Engineering Conference. ASMEDC, 2009. http://dx.doi.org/10.1115/detc2009-86088.

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Анотація:
This paper will discuss critical issues and needs in the product performance validation domain. There is a primary need to manage a vast variety of CAE and Test data files that are used and generated throughout the product performance life cycle. The paper will discuss the different elements of managing such data including basic data structures, process and work flow requirements, product validation plans, and security and access privilege considerations. The goal of executing CAE Analysis or performing physical tests is to gather all product performance information. Evaluating all performance measurements specified for the product makes it possible to ensure that the product will behave as specified throughout its service life. The key here is that decision makers need access to all possible performance metrics for a product, an assembly or a component. There is a primary need to manage a vast variety of CAE and Test data files that are used and generated through the product performance life cycle. The paper addresses the different elements of managing such data including basic data structures, process and work flow requirements, product validation plans, security access privilege considerations and data standardization. This paper will also outline how the product validation management system architecture can support all the needs of this domain. The principal elements of the system include the supporting data structures that are mapped to a database management system and access methods using a service-oriented architecture (SOA).
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Ondemir, Onder, and Surendra M. Gupta. "End-of-Life Decisions Using Product Life Cycle Information." In ASME 2008 International Mechanical Engineering Congress and Exposition. ASMEDC, 2008. http://dx.doi.org/10.1115/imece2008-67039.

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The concept of disassembly-to-order (DTO) has recently become popular. The goal of DTO is to determine the optimum number of end-of-life (EOL) products to be disassembled in order to fulfill the demand for components and materials such that some desired criteria of the system are satisfied. However, the outcome of this problem is fraught with errors. This is due to the unpredictable circumstances of the EOL products which stem from many sources such as the operating environment, different usage patterns and customers upgrades. If one could get advanced information about the status of the products, it could prove to be quite invaluable in making EOL management decisions. Advanced product information consists of two types of data, viz., static and dynamic. The static data consists of the product name, the brand name, the model type, etc. The dynamic data consists of cumulative data covering the circumstances to which the product was subjected to during its useful life. Capturing these data has become an important goal of many manufacturers. Numerous technological advances and the availability of various monitoring devices, embedded in products, offer us with many product monitoring and data collection alternatives. In this paper, an integer program is developed to model and solve the DTO problem that utilizes the captured data from EOL products. A numerical example is considered to illustrate the use of this methodology.
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Suhas, V. N. J., and R. C. Yadav. "Product Life Cycle System Approach In CIM." In International Body Engineering Conference & Exhibition and Automotive & Transportation Technology Congress. 400 Commonwealth Drive, Warrendale, PA, United States: SAE International, 2002. http://dx.doi.org/10.4271/2002-01-2120.

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Nasr, Nabil, and Edward A. Varel. "Total Product Life-Cycle Analysis and Costing." In 1997 Total Life Cycle Conference and Exposition. 400 Commonwealth Drive, Warrendale, PA, United States: SAE International, 1997. http://dx.doi.org/10.4271/971157.

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Ovsyannikov, Mikhail. "Formal ontology of the product life cycle." In Systems Analysis in Economics - 2020. Moscow, "Science" Publishing House, 2021. http://dx.doi.org/10.33278/sae-2020.book1.452-455.

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Звіти організацій з теми "Product life cycle Australia"

1

Walaszek, Jeffrey J., William D. Goran, Cary D. Butler, Kay C. McGuire, Terri L. Prickett, Kathleen D. White, and William J. Wolfe. Product Life Cycle Planning. Fort Belvoir, VA: Defense Technical Information Center, June 2003. http://dx.doi.org/10.21236/ada419127.

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Rusch, Magdalena, Josef Peter Schöggl, Lukas Stumpf, and Rupert J. Baumgartner. Interplay of Digital Technologies and Sustainable Product Development –What Can Product Life Cycle Data Tell Us? University of Limerick, 2021. http://dx.doi.org/10.31880/10344/10239.

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Subrahmanian, Eswaran, and Yoram Reich. Advancing problem definition and concept generation for improved product life cycle management. Gaithersburg, MD: National Institute of Standards and Technology, 2007. http://dx.doi.org/10.6028/nist.ir.7430.

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Lee, Dong-Yeon, Amgad A. Elgowainy, and Qiang Dai. Life Cycle Greenhouse Gas Emissions of By-product Hydrogen from Chlor-Alkali Plants. Office of Scientific and Technical Information (OSTI), December 2017. http://dx.doi.org/10.2172/1418333.

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Edison, Tom, and Andre Murphy. Performance-Based Life Cycle Product Support: A New Look at Enablers and Barriers. Fort Belvoir, VA: Defense Technical Information Center, April 2011. http://dx.doi.org/10.21236/ada543740.

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Lu, Bin, Bo Li, Xiaolong Song, and Jianxin Yang. Multi Life Cycle Assessment: A Potential Assessment Method for Product Lifespan and Environmental Performance. University of Limerick, 2021. http://dx.doi.org/10.31880/10344/10225.

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Greenstein, Shane, and James Wade. Dynamic Modeling of the Product Life Cycle in the Commercial Mainframe Computer Market, 1968-1982. Cambridge, MA: National Bureau of Economic Research, August 1997. http://dx.doi.org/10.3386/w6124.

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Jordan, Gretchen, Jonathan Mote, Rosalie Ruegg, Thomas Choi, and Angela Becker-Dippmann. A Framework for Evaluating R&D Impacts and Supply Chain Dynamics Early in a Product Life Cycle. Looking inside the black box of innovation. Office of Scientific and Technical Information (OSTI), June 2014. http://dx.doi.org/10.2172/1336535.

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Resch, Alois. 2020 Subsidies for PVT collectors in selected countries. IEA SHC Task 60, July 2020. http://dx.doi.org/10.18777/ieashc-task60-2020-0005.

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Анотація:
Report D6: PVT collectors can be still considered as young technology, but with significant growing tendency in terms of market development and number of manufacturers on a worldwide point of view. Nevertheless, PVT is definitely in an early stage of its product life cycle, where economic competitiveness among other renewable technologies providing heat and electricity is challenging.
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Führ, Martin, Julian Schenten, and Silke Kleihauer. Integrating "Green Chemistry" into the Regulatory Framework of European Chemicals Policy. Sonderforschungsgruppe Institutionenanalyse, July 2019. http://dx.doi.org/10.46850/sofia.9783941627727.

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Анотація:
20 years ago a concept of “Green Chemistry” was formulated by Paul Anastas and John Warner, aiming at an ambitious agenda to “green” chemical products and processes. Today the concept, laid down in a set of 12 principles, has found support in various arenas. This diffusion was supported by enhancements of the legislative framework; not only in the European Union. Nevertheless industry actors – whilst generally supporting the idea – still see “cost and perception remain barriers to green chemistry uptake”. Thus, the questions arise how additional incentives as well as measures to address the barriers and impediments can be provided. An analysis addressing these questions has to take into account the institutional context for the relevant actors involved in the issue. And it has to reflect the problem perception of the different stakeholders. The supply chain into which the chemicals are distributed are of pivotal importance since they create the demand pull for chemicals designed in accordance with the “Green Chemistry Principles”. Consequently, the scope of this study includes all stages in a chemical’s life-cycle, including the process of designing and producing the final products to which chemical substances contribute. For each stage the most relevant legislative acts, together establishing the regulatory framework of the “chemicals policy” in the EU are analysed. In a nutshell the main elements of the study can be summarized as follows: Green Chemistry (GC) is the utilisation of a set of principles that reduces or eliminates the use or generation of hazardous substances in the design, manufacture and application of chemical products. Besides, reaction efficiency, including energy efficiency, and the use of renewable resources are other motives of Green Chemistry. Putting the GC concept in a broader market context, however, it can only prevail if in the perception of the relevant actors it is linked to tangible business cases. Therefore, the study analyses the product context in which chemistry is to be applied, as well as the substance’s entire life-cycle – in other words, the six stages in product innovation processes): 1. Substance design, 2. Production process, 3. Interaction in the supply chain, 4. Product design, 5. Use phase and 6. After use phase of the product (towards a “circular economy”). The report presents an overview to what extent the existing framework, i.e. legislation and the wider institutional context along the six stages, is setting incentives for actors to adequately address problematic substances and their potential impacts, including the learning processes intended to invoke creativity of various actors to solve challenges posed by these substances. In this respect, measured against the GC and Learning Process assessment criteria, the study identified shortcomings (“delta”) at each stage of product innovation. Some criteria are covered by the regulatory framework and to a relevant extent implemented by the actors. With respect to those criteria, there is thus no priority need for further action. Other criteria are only to a certain degree covered by the regulatory framework, due to various and often interlinked reasons. For those criteria, entry points for options to strengthen or further nuance coverage of the respective principle already exist. Most relevant are the deltas with regard to those instruments that influence the design phase; both for the chemical substance as such and for the end-product containing the substance. Due to the multi-tier supply chains, provisions fostering information, communication and cooperation of the various actors are crucial to underpin the learning processes towards the GCP. The policy options aim to tackle these shortcomings in the context of the respective stage in order to support those actors who are willing to change their attitude and their business decisions towards GC. The findings are in general coherence with the strategies to foster GC identified by the Green Chemistry & Commerce Council.
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