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Fant 9850 publikasjoner. Viser side 54 av 394:

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Testing SSbD Tools for Chemical Substitution: A Walk in the PARC

Halling, Maja; Agalliadou, Anna; Battistelli, Chiara L.; Benfenati, Emilio; Milovanovic, Milena; Bossa, Cecilia; Bouman, Evert Alwin; Bourgé, Émilien; Chavan, Swapnil; Hill, Annabel; Iacovidou, Eleni; Iavicol, Ivo; Kanerva, Tomi; Karakitsios, Spyros; Karakoltzidis, Achilleas; Kärnman, Therese; Leso, Veruscka; Linden, Jenny; Lofstedt, M.; Mikolajczyk, Alicja; Nikiforou, F.; Norinder, Ulf; Nowack, Bernd; Resch, Susanne; Sánchez Jiménez, Araceli; Sarigiannis, Denis; Selvestrel, Gianluca; Sharma, Anežka; Siivola, Kirsi; Subramanian, Vrishali; Leggieri, Rosella Telaretti; van Bodegraven, Martin; van Dijk, Joanke; Westra, Jaco; Zheng, Ziye; Zoutendijk, Bas; Rydberg, Tomas

2024

Testing ethical impact assessment for nano risk governance

Malsch, Ineke; Isigonis, Panagiotis; Bouman, Evert Alwin; Afantitis, Antreas; Melagraki, Georgia; Dusinska, Maria

Risk governance of nanomaterials and nanotechnologies has been traditionally mainly limited to risk assessment, risk management and life cycle assessment. Recent approaches have experimented with widening the scope and including economic, social, and ethical aspects. This paper reports on tests and stakeholder feedback on fine-tuning the use of ethical impact assessment guidelines (RiskGONE D3.6) and online tools adapting the CEN Workshop Agreement part 2 CWA 17145-2:2017 (E)) to support risk governance of nanomaterials, in the RiskGONE project. The EIA guidelines and tools are intended to be used as one module in a multicriteria decision support framework for risk governance of nanomaterials, but may also be used for a stand-alone ethical impact assessment.

Nanomaterials are new forms of materials with structures at sizes between 1 and 100 nanometres (a millionth of a millimetre). They can be particles, tubes, platelets or other shaped structures. Nanomaterials can be applied in many different products, ranging from medicine to solar panels. Researchers, governments and stakeholders have been concerned with potential risks for human health and the environment for decades. Also, how nanomaterials behave during the production, use and waste processing of the products they are included in has been investigated in Life Cycle Analysis. However, ethical issues which may be raised by the use of nanomaterials in those products are usually not investigated. In this article, the procedure for an ethical impact assessment described in the CEN Workshop Agreement CWA 17145-@:2017 (E) is adapted to nanomaterials. Users who want to perform this assessment are guided through the procedure by online tools. The guidelines and tools were tested on several case studies and discussed with stakeholders, who commented on the criteria which should be used and on who could use the tools. This results in recommendations for improving the guidelines and online tools.

2024

Testing av utslippsfaktorer for vedfyring i AirQUIS. En sensitivitetsstudie for PM2.5 i Oslo. NILU OR

Sundvor, I.; Randall, S.

Utslipp fra vedfyring gir et av de største bidragene til partikkelutslipp i Norge, men det er en del usikkerhet rundt utslippstallene og hvor mye vedfyring bidrar til de bakkenære konsentrasjonene. Det er gjort spredningsberegninger for Oslo for å vurdere utslipp fra vedfyring og teste ulike parametere som er knyttet opp mot denne kilden. Det er vært testet for 3 ulike vinterperioder for å se på meteorologisk variasjon (Basisberegninger), med nye utslippsfaktorer fra SINTEF (scenario SINTEF), kraftig kutt i utslippene (scenario Forbruk) og med en ny fordeling av utslippet over døgnet (scenario TID).
Modellen overestimerer klart bidraget fra vedfyring i basisberegningene som inkluderer det største utslippet for vedfyring i denne studien. Selv med bruk av nye utslippsfaktorer fra SINTEF som gir mindre utslipp og som gir et noe bedre resultat enn de tidligere faktorene, er det fortsatt klart at utslippene fra vedfyring gir for høye konsentrasjoner, spesielt på kvelden. I kombinasjon med resultatene fra andre scenarioberegninger vurderer vi det til at utslippene ikke er riktige hverken i mengde eller fordeling i tid og rom.

J.W. Cappelens Forlag AS

2013

Testing av renseefekt av fiber-polymerer for PCB-kontaminert vann

Davanger, Kirsten; Enge, Ellen Katrin; Schlabach, Martin

NILU

2020

Test Centre Mongstad. Spredningsberegninger for utslipp til luft fra Test Centre Mongstad (TCM). NILU OR

Berglen, T.F.; Gjerstad, K.I.; Knudsen, S.; Mc Innes, H.; Tønnesen, D.

2008

Terrestrisk naturovervåking. Persistente organiske miljøgifter i rovfuglegg i Norge. NINA oppdragsmelding, 701

Nygård, T.; Skaare, J. U.; Kallenborn, R.; Herzke, D.

2001

Ten-year trends of atmospheric mercury in the high Arctic compared to Canadian sub-Arctic and mid-latitude sites.

Cole, A. S.; Steffen, A.; Pfaffhuber, K. A.; Berg, T.; Pilote, M.; Poissant, L.; Tordon, R.; Hung, H.

2013

Ten years after entry into force of the Stockholm Convention: What do air monitoring data tell about its effectiveness?

Wöhrnschimmel, H.; Scheringer, M.; Bogdal, C.; Hung, H.; Salamova, A.; Venier, M.; Katsoyiannis, A.; Hites, R.A.; Hungerbuhler, K.; Fiedler, H.

2016

Temporal variation in circulating concentrations of organochlorine pollutants in a pelagic seabird breeding in the high Arctic.

Bustnes, J.O.; Bårdsen, B.-J.; Moe, B.; Herzke, D.; Hanssen, S.A.; Sagerup, K.; Bech, C.; Nordstad, T.; Chastel, O.; Tartu, S.; Gabrielsen, G.W.

2017

Temporal variability in surface water pCO2 in Adventfjorden (West Spitsbergen) with emphasis on physical and biogeochemical drivers

Ericson, Ylva; Falck, Eva; Chierici, Melissa; Fransson, Agneta Ingrid; Kristiansen, Svein; Platt, Stephen Matthew; Hermansen, Ove; Myhre, Cathrine Lund

American Geophysical Union (AGU)

2018

Temporal Variability in MERIS water constituents modeled by STL decomposition in SW Iberian Peninsula: Sagres.

Icely, J.; Cordeiro, C.; Cristina, S.; Lavender, S.; Goela, P.; Newton, A.

2016

Temporal trends of PFAS in relation to climate-related variations in feeding habits and food availability in Svalbard, 1997-2021

Gai, Giulia; Fuglei, Eva; Hanssen, Linda; Pedersen, Åshild Ønvik; Madsen, J.; Routti, Heli Anna Irmeli

2022

Temporal trends of persistent organic pollutants (POPs) in arctic air: 20 years of monitoring under the Arctic Monitoring and Assessment Programme (AMAP).

Hung, H.; Katsoyiannis, A.A.; Brorström-Lundén, E.; Olafsdottir, K.; Aas, W.; Breivik, K.; Bohlin-Nizzetto, P.; Sigurdsson, A.; Hakola, H.; Bossi, R.; Skov, H.; Sverko, E.; Barresi, E.; Fellin, P.; Wilson, S.

2016

Temporal trends of persistent organic pollutants (POPs) and other organic contaminants in Arctic air.

Hung, H.; Kallenborn, R.; Breivik, K.; Su, Y.; Ma, J.; Brorström-Lundén, E.; Olafsdottir, K.; Thorlacius, J.M.; Leppänen, S.; Bossi, R.; Skov, H.; Manø, S.; Konoplev, A.; Stern, G.; Sverko, E.; Shoeib, M.; Fellin, P.

2011

Temporal trends of perfluorooctanesulfonate isomer and enantiomer patterns in archived Swedish and American serum samples.

Liu, Y.; Pereira, A.S.; Beesoon, S.; Vestergren, R.; Berger, U.; Olsen, G.W.; Glynn, A.; Martin, J.W.

2015

Temporal Trends of Organochlorine and Perfluorinated Contaminants in a Terrestrial Raptor in Northern Europe Over 34 years (1986–2019)

Bustnes, Jan Ove; Bårdsen, Bård-Jørgen; Herzke, Dorte; Bangjord, Georg; Bourgeon, Sophie; Fritsch, Clémentine; Eulaers, Igor

Fourteen legacy organochlorine (OC) contaminants and 12 perfluoroalkyl substances (PFASs) were measured in eggs of tawny owls (Strix alueco) in central Norway (1986–2019). We expected OCs to have reached stable equilibrium levels due to bans, and that recent phase-out of some PFASs would have slowed the increase of these compounds. ∑OC comprised on average approximately 92% of the measured compounds, whereas ∑PFAS accounted for approximately 8%. However, whereas the ∑OC to ∑PFAS ratio was approximately 60 in the first 5 years of the study, it was only approximately 11 in the last 5 years. Both OC pesticides and polychlorinated biphenyls (PCBs) showed substantial declines over the study period (~85%–98%): hexachlorocyclohexanes and chlordanes seemed to be levelling off, whereas p,p′-dichlorodiphenyldichloroethylene (p,p′-DDE) and hexachlororbenzene (HCB), and most PCB congeners still seemed to decline at a more or less constant rate. While the concentration of perfluorooctane sulfonic acid (PFOS), the dominating PFAS, was reduced by approximately 43%, other perfluorinated sulfonates (PFSAs) showed only minor changes. Moreover, the median concentrations of seven perfluorinated carboxylic acids (PFCAs) increased approximately five-fold over the study period. Perfluorononanoic acid and perfluoroundecanoate acid, however, seemed to be levelling off in recent years. In contrast, perfluorododecanoic acid, perfluorodecanoate acid, perfluorotridecanoic acid, and perfluorotetradecanoic acid seemed to increase more or less linearily. Finally, perfluorooctanoic acid (PFOA) was increasingly likely to be detected over the study period. Hence, most legacy OCs and PFOS have not reached a lower threshold with stable background levels, and voluntary elimination of perfluoroalkyl carboxylates still has not resulted in declining levels in tawny owls in central Norway.

Pergamon Press

2022

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