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Sökning: WFRF:(Kushnir Duncan 1979)

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1.
  • Dreos, Ambra, 1987, et al. (författare)
  • Exploring the potential of a hybrid device combining solar water heating and molecular solar thermal energy storage
  • 2017
  • Ingår i: Energy & Environmental Science. - : Royal Society of Chemistry (RSC). - 1754-5692 .- 1754-5706. ; 10:3, s. 728-734
  • Tidskriftsartikel (refereegranskat)abstract
    • A hybrid solar energy system consisting of a molecular solar thermal energy storage system (MOST) combined with a solar water heating system (SWH) is presented. The MOST chemical energy storage system is based on norbornadiene- quadricyclane derivatives allowing for conversion of solar energy into stored chemical energy at up to 103 kJ mol(-1) (396 kJ kg(-1)). It is demonstrated that 1.1% of incoming solar energy can be stored in the chemical system without significantly compromising the efficiency of the solar water heating system, leading to efficiencies of combined solar water heating and solar energy storage of up to 80%. Moreover, prospects for future improvement and possible applications are discussed.
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2.
  • Hellsmark, Hans, 1974, et al. (författare)
  • Teknologiska innovationssystem inom energiområdet: En praktisk vägledning till identifiering av systemsvagheter som motiverar särskilda politiska åtaganden
  • 2014
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • Syftet med denna rapport är att illustrera hur ett praktiskt inriktat ramverk, tekno- logiska innovationssystem (TIS), kan användas av analytiker och beslutsfattare vid departement och myndigheter för att analysera strategiskt viktiga teknikområden ?????????????????????????????????????????????????????????????????????????????I rapporten analyseras fem TIS centrerade kring havsbaserad vindkraft, marin energi, ????????????????????????????????????????????????????????????????????????????????????? systemsvagheter som bromsar områdets vidare utveckling, vilka som kan åtgärdas av systemets aktörer och vilka som motiverar särskilda politiska åtaganden. Rapporten utgör därmed ett underlag för att formulera åtgärder för att åstadkomma ökad innova- tion, teknikspridning och industrialisering inom ovan nämnda teknikområden.Studien har även möjliggjort en jämförande analys av likheter och skillnader ???????????????????????????????????????????????????????????????????????????????? ?????????????????????????????????????????????????????????????????????????????????????? mellan områdena – de är starka respektive svaga av olika orsaker. Detta visar att ???????????????????????????????????????????????????????????????????????Samtidigt har områdena gemensamma drag. Systemets aktörer, där även politiska ???????????????????????????????????????????????????????????????????????????????????? ?????????????????????????????????????????????????????????????????????????????- skapsnätverk. Men de har varit sämre på att skapa tidiga nischmarknader som ger utrymme för fortsatt lärande och kostnadsreduktion. Sådana nischer kan ibland skapas av marknadens aktörer, men ofta krävs politiska styrmedel. De behövs för att investeringar i kunskapsutveckling ska kunna nyttiggöras och för att en bred industriell utveckling inom nya områden skall göras möjlig i Sverige.Vidare presenteras lärdomar kring vad en aktiv teknikpolitik innebär. Två huvud- ??????????????????????????????????????????????????????????????????????????????- hällsbygget och därför bör vara ett politikområde bland många samt att den skarpa ??????????????????????????????????????????????????????????????????????????????- ?????????????????????????????????????????????????????????????????????????????????? ?????????????????????????????????????????????????????????????????????????????????? olika faser av innovationssystemets utveckling.För att lyckas med en aktiv teknikpolitik behövs en hög grad av koordinering ??????????????????????????????????????????????????????????????????????? teknikområden så att ”rätt” typ av åtgärder kan sättas in vid ”rätt” tidpunkt av ”rätt” aktör. TIS-ramverket lyfts här fram som en metod för att skapa ett sådant underlag. Slutligen presenteras en metod för projektbedömningar som syftar till att stötta handläggare i utvärderingar av projekt inom nya teknikområden.Rapporten i sin helhet riktar sig särskilt till beslutsfattare och handläggare vid myndigheter, departement och politiker, men även andra organisationer och indi- vider med intresse av att högt ställda klimatmål ska kunna nås samtidigt som en positiv näringslivsutveckling möjliggörs.
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3.
  • Molander, Sverker, 1957, et al. (författare)
  • Förnybara energikällors inverkan på de svenska miljömålen
  • 2010
  • Rapport (övrigt vetenskapligt/konstnärligt)abstract
    • I denna rapport beskrivs olika förnybara energikällors negativa påverkan på desvenska miljömålen. Resultatet har presenterats i form av ett antal konceptuellabilder som länkar miljöpåverkan i energislagens livscykelsteg till specifika miljömål.De energislag som studerats är vattenkraft, vindkraft, tunnfilmssolceller, kiselbaseradesolceller, solfångare, värmepumpar samt odlade biobränslen (såsometanol och raps metylester), biobränslen från avfall (såsom biogas) och biobränslenfrån skogsråvara (såsom flis och pellets). Miljöpåverkan har inte kvantifierats idenna studie, och ingen jämförelse energislagen emellan har utförts. Vad som dockvisats är att de ovan listade energislagen påverkar många svenska miljömål, ochden påverkan kommer att växa om de aktuella svenska målen för förnybar energiförverkligas. Mer detaljerade studier kring de förnybara energislagens påverkan påmiljömålen krävs således för att undvika negativ miljöpåverkan från förnybar energii framtiden. Denna rapport har utifrån dagens vetenskapsläge kartlagt de viktigasteverkningarna på de svenska miljömålens uppfyllelse från förnyelsebar energiteknik,och utgör således en grund för ett sådant mer omfattande arbete. Avslutningsvisges ett antal rekommendationer inför fortsatta studier på området.
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5.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • Energy and resource use assessment of graphene as a substitute for indium tin oxide in transparent electrodes
  • 2016
  • Ingår i: Journal of Cleaner Production. - : Elsevier BV. - 0959-6526. ; 132, s. 289-297
  • Tidskriftsartikel (refereegranskat)abstract
    • One of the most promising applications of graphene is as material in transparent electrodes in applications such as liquid crystal displays (LCDs) and solar cells. In this study, we assess life cycle resource requirements of producing an electrode area of graphene by chemical vapor deposition (CVD) and compare to the production of indium tin oxide (ITO). The resources considered are energy and scarce metals. The results show that graphene layers can have lower life cycle energy use than ITO layers, with 3–10 times reduction for our best case scenario. Regarding use of scarce metals, the use of indium in ITO production is more problematic than the use of copper in graphene production, although the latter may constitute a resource constraint in the very long run. The substitution of ITO by graphene thus seems favorable from a resource point of view. Higher order effects may outweigh or enhance the energy use benefit. For example, cheaper, graphene-based electrodes may spur increased production of LCDs, leading to increased absolute energy use, or spur the development of new energy technologies, such as solar cells and fuel cells. The latter could potentially lead to larger absolute reductions in resource use if these new technologies will replace fossil-based energy systems.
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6.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • Environmental Assessment of Emerging Technologies: Recommendations for Prospective LCA
  • 2018
  • Ingår i: Journal of Industrial Ecology. - : Wiley. - 1530-9290 .- 1088-1980. ; 22:6, s. 1286-1294
  • Forskningsöversikt (refereegranskat)abstract
    • The challenge of assessing emerging technologies with life cycle assessment (LCA) has been increasingly discussed in the LCA field. In this article, we propose a definition of prospective LCA: An LCA is prospective when the (emerging) technology studied is in an early phase of development (e.g., small-scale production), but the technology is modeled at a future, more-developed phase (e.g., large-scale production). Methodological choices in prospective LCA must be adapted to reflect this goal of assessing environmental impacts of emerging technologies, which deviates from the typical goals of conventional LCA studies. The aim of the article is to provide a number of recommendations for how to conduct such prospective assessments in a relevant manner. The recommendations are based on a detailed review of selected prospective LCA case studies, mainly from the areas of nanomaterials, biomaterials, and energy technologies. We find that it is important to include technology alternatives that are relevant for the future in prospective LCA studies. Predictive scenarios and scenario ranges are two general approaches to prospective inventory modeling of both foreground and background systems. Many different data sources are available for prospective modeling of the foreground system: scientific articles; patents; expert interviews; unpublished experimental data; and process modeling. However, we caution against temporal mismatches between foreground and background systems, and recommend that foreground and background system impacts be reported separately in order to increase the usefulness of the results in other prospective studies.
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7.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • How to make policy-relevant life cycle assessments of future products? Lessons learned from nanomaterials
  • 2013
  • Ingår i: 6th International Conference on Life Cycle Management, Gothenburg, 25-28 August.
  • Konferensbidrag (refereegranskat)abstract
    • Many new nanomaterials are currently being developed, and there is a great demand from policy-makers such as governments and agencies to understand the future environmental impact of nanomaterials. However, assessing the life cycle environmental impacts, e.g. in terms of emissions and energy use, related to these materials and products that contain them constitutes a great challenge, which makes it difficult to meet such needs from policy-makers. The challenge is much due to the many uncertainties that surround new nanomaterials at an early point of technological development, which makes environmental assessment methods such as life cycle assessment difficult to apply. These uncertainties include the future areas of application of the nanomaterial, future designs of products within those areas, and future production processes. When one or more of these uncertainties are present, we say that the life cycle or product chain is embryonic. This embryonic nature of nanomaterial life cycles differentiates them from the life cycles of more established products, such as cups and cucumbers. Assessing the environmental impacts of embryonic nanomaterial life cycles requires the assessor to understand the future, or rather some aspects of a number of possible futures. Hence, we need to make use of methods belonging to the field of future studies, including monitoring of trends in technology development (e.g. via patent analysis) and application areas as well as predicting and exploring by trend analysis, expert judgement, and sometimes even fantasizing. We illustrate the theoretical concept of embryonic life cycles with a number of examples of embryonic nanomaterial life cycles, including carbon nanotubes in composites, titanium dioxide nanoparticles in self-cleaning cement and graphene in electronic devices and composites. We show that a range of future study approaches may enrich, or even be essential to, policy-relevant life cycle assessments. We also show that environmental assessments such as life cycle assessment can be misused or used in questionable ways when applied to embryonic life cycles with the purpose of obtaining policy-relevant results.
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8.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • Is graphene a ”wonder material” also from an environmental life cycle perspective?
  • 2014
  • Ingår i: Abstract of Papers of the American Chemical Society. - 0065-7727. ; 247
  • Konferensbidrag (övrigt vetenskapligt/konstnärligt)abstract
    • The nanomaterial graphene has attracted great interest for its many potential applications, including composites and electronic devises, and has been referred to by some as a "wonder material" from a technical point of view. However, the question remains whether graphene is also a "wonder material" from an environmental life cycle perspective. In order to investigate this, we applied life cycle assessment (LCA) to assess the cradle-to-gate environmental impacts of graphene production. The focus of the assessment was on the foreground system and on more inherent impact categories, namely energy use, water use, human toxicity, and ecotoxicity. Two different production routes were investigated. In the first, called chemical reduction, graphite is first oxidized to graphite oxide, and then reduced by hydrazine to form graphene sheets in solution that could be used in e.g. composites. The second is ultrasonication, where graphite is exposed to ultrasound, and thereby breaks up into graphene sheets in solution, also possible to use in composites. These two routes were compared on a kg of graphene basis. The results indicate that ultrasonication has a considerably lower cradle-to-gate impact than chemical reduction for all included impact categories. For example, the energy use of chemical reduction-made graphene appears to be more than 100 times higher than that of ultrasonication-made graphene. Comparing to the energy use of other nanomaterials, chemical reduction-based graphene appears to have an energy use close to the median. Ultrasonication-made graphene, however, appears to have a lower energy use than any previously assessed nano material. This implicates that the chemical industry should focus their efforts on developing the ultrasonication production route rather than chemical reduction.
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9.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • Is there a "crystal ball"? Assessing environmental life cycle impacts of new nanomaterials
  • 2013
  • Ingår i: 7th International Society for Industrial Ecology Biennial Conference, 25-28 June, Ulsan, South Korea.
  • Konferensbidrag (refereegranskat)abstract
    • Many new nanomaterials are currently being developed, and assessing the life cycle environmental impacts related to these materials and products that contain the materials, e.g. in terms of emissions and energy use, constitutes a great challenge. The challenge is much due to the many uncertainties that surround new nanomaterials at this early point of technological development, which makes the application of environmental assessment methods such as life cycle assessment difficult to apply. These uncertainties include the future areas of application of the nanomaterial, future designs of products within those areas, and the future production processes that will be needed to produce such products. When one or more of these uncertainties are present, we say that the product chain or life cycle is embryonic. This embryonic nature of nanomaterial life cycles differentiates them from more established products, such as cement and cucumbers. We provide a number of examples of a number of embryonic nanomaterial life cycles, including carbon nanotubes in composites, titanium dioxide nanoparticles in self-cleaning cement and graphene in electronic devices and composites, illustrating their embryonic nature. Assessing the environmental impacts of embryonic nanomaterial product chains requires the assessor to use different future studies approaches, i.e. to use a “crystal ball” to understand the future or rather different possible futures. Existing approaches include monitoring, predicting, exploring, and sometimes even fantasizing. We show how some of these approaches have been used in previous life cycle studies on nanomaterials, illustrating that they may all be relevant to include in environmental assessments and life cycle assessments in particular, but also that they can be misused or used in questionable ways. The important thing is to know which approach to apply in a certain situation in order to ensure a relevant assessment, and to avoid uses that leads to more confusion than knowledge.
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10.
  • Arvidsson, Rickard, 1984, et al. (författare)
  • Prospective inventory modelling of emerging chemicals: The case of photonic materials
  • 2019
  • Ingår i: Abstracts book (SETAC Europe Annual Meeting). - 2310-3043 .- 2309-8031. ; 29, s. 96-
  • Konferensbidrag (övrigt vetenskapligt/konstnärligt)abstract
    • Prospective life cycle assessment (LCA), or ex-ante LCA, has been defined as an assessment of a product system modeled at a future time, before its commercialization. Such assessments bring the promise of altering emerging technologies in a more environmentally benefitial direction before they become difficult to change. Since the future cannot be known with certainty, prospective modeling need to rely on scenarios of various kinds. However, how to conduct such prospective scenario modeling in practice still has to be clarified. In this study, we have modeled two emerging chemicals that can be used for a technology called photon upconversion, which converts low-energy light into higher-energy light harvestable by solar photovoltaics, thereby increasing their efficiency. Two chemicals currently considered for this purpose are ruthenium bipyridine chloride (RBC) and diphenylanthracene (DPA). These novel, emerging chemicals have not been studied regarding environmental performance before and are consequently not present in any LCA databases. The aim of this study is to present a generic procedure for prospective inventory modeling of emerging chemicals and apply that to the cases of RBC and DPA by developing unit processes for these two chemicals. An industrial synthesis scenario was adopted as our main scenario, reflecting a possible future time when RBC and DPA are produced at an industrial scale. The modeling was conducted in six steps: (1) Identify likely chemical syntheses. (2) Calculate inputs stoichiometrically based on the chemical synthesis reactions. (3) Modify inputs based on available yields for reactants and solvents (e.g. obtained from patents or estimated). (4) Categorize outputs as by-products or waste depending on their likely subsequent fate. (5)Calculate process emissions. (6) Model energy flows. Unit processes for the two emerging chemicals are thusly developed. The procedure is considered particularly strong for estimating inputs and output materials related to the stoichiometric reaction, but weaker regarding the estimation of emissions and energy requrement. Further research into the modeling of energy flows for high-temperature processes is therefore recommended, as well as estimation procedures for emissions from emerging chemicals production.
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