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Thermodynamic parameters at bio-nano interface and nanomaterial toxicity: A case study on BSA interaction with ZnO, SiO2 and TiO2

Precupas, Aurica; Gheorghe, Daniela; Botea-Petcu, Alina; Leonties, Anca Ruxandra; Sandu, Romica; Popa, Vlad Tudor; Mariussen, Espen; El Yamani, Naouale; Rundén-Pran, Elise; Dumit, Veronica; Xue, Ying; Cimpan, Mihaela Roxana; Dusinska, Maria; Haase, Andrea; Tanasescu, Speranta

2020

Thermal conditions during heat waves of a mid-European metropolis under consideration of climate change, urban development scenarios and resilience measures for the mid-21st century

Trimmel, Heidelinde; Weihs, Philipp; Faroux, Stephanie; Formayer, Herbert; Hamer, Paul David; Hasel, Kristoffer; Laimighofer, Johannes; Leidinger, David; Masson, Valery; Nadeem, Imran; Oswald, Sandro M.; Revesz, Michael; Schoetter, Robert

In this study we produce two urban development scenarios estimating potential urban sprawl and optimized development concerning building construction, and we simulate their influence on air temperature, surface temperatures and human thermal comfort. We select two heat waves representative for present and future conditions of the mid 21st century and simulations are run with the Town Energy Balance Model (TEB) coupled online and offline to the Weather Research and Forecasting Model (WRF). Global and regional climate change under the RCP8.5 scenario causes an increase of daily maximum air temperature in Vienna by 7 K. The daily minimum air temperature will increase by 2–4 K. Changes caused by urban growth or densification mainly affect air temperature and human thermal comfort locally where new urbanisation takes place and does not occur significantly in the central districts. A combination of near zero-energy standards and increasing albedo of building materials on the city scale accomplishes a maximum reduction of urban canyon temperature achieved by changes in urban parameters of 0.9 K for the minima and 0.2 K for the maxima. Local scale changes of different adaptation measures show that insulation of buildings alone increases the maximum wall surface temperatures by more than 10 K or the maximum mean radiant temperature (MRT) in the canyon by 5 K. Therefore, measures to reduce MRT within the urban canyons like tree shade are needed to complement the proposed measures. This study concludes that the rising air temperatures expected by climate change puts an unprecedented heat burden on Viennese inhabitants, which cannot easily be reduced by measures concerning buildings within the city itself. Additionally, measures such as planting trees to provide shade, regional water sensitive planning and global reduction of greenhouse gas emissions in order to reduce temperature extremes are required.

2019

There Are No Environmental Problems in Nikel, Says Putin’s Special Advisor

Berglen, Tore Flatlandsmo (intervjuobjekt); Trellevik, Amund (journalist)

2019

Thematic assessments. ANP, 2004:762

Anttila, P.; Frolova, M.; Heidam, N.Z.; Lövblad, G.; Sjöberg, K.; Pajuste, K.; Schaug, J.; Sopauskiene, D.

2004

The YAK-AEROSIB transcontinental aircraft campaigns: new insights on the transport of CO2 , CO and O3 across Siberia.

Paris, J.-D.; Ciais, P.; Nédélec, P.; Ramonet, M.; Belan,B.D.; Arshinov, M.Y.; Golitsyn, G.S.; Granberg, I.; Stohl, A.; Cayez, G.; Athier, G.; Boumard, F.; Cousin, J.-M.

2008

The who, why and where of Norway's CO2 emissions from tourist travel

Grythe, Henrik; Lopez-Aparicio, Susana

We present emissions from Norway’s tourist travel by the available transport modes, i.e., aviation, maritime (ferries and cruises) and land-based transport (road and railways). Our study includes detailed information on both domestic and international tourist travel within, from and to Norway. We have coupled statistics from several large surveys with detailed emission data to allow us to separate the purpose of the travel (holiday or business).

Total transport emissions for tourists in 2018 were estimated to be 8 530 kt, equivalent to 19% of the reported Norwegian national emissions. Of these emissions, international tourists visiting Norway were responsible for 3 273 kt , whereas travel by Norwegians accounted for 4 875 kt , most of which occur outside Norway’s reporting obligations. Aviation and maritime transport were found to be the largest emission sources, responsible for 71% and 21% of total emissions, respectively. The reduction due to the COVID-19 pandemic was approximately 60% in 2020, and was sustained throughout the year.

Our study shows that officially reported emissions, as limited to the countries territory, are not suitable for accurate evaluation of transport emissions related to tourism. A consumer or tourist-based calculation gives a marked redistribution of emission responsibility. Our results indicate that emissions from Norwegian residents travelling abroad are 1 602 kt higher than those from tourists coming to Norway. This is driven by frequent trips to popular tourist destinations such as Spain, Thailand, Turkey and Greece. Globally consumer based calculations would shift the responsibility of emissions by tourists to the large wealthy nations, with the most international tourists. The understanding of emission distributed by population group or market support in addition the developing of marketing strategies to attract low emission tourist markets and create awareness among the nations with higher shares of international tourist.

Elsevier

2021

The way forward for assessing the human health safety of cosmetics in the EU - Workshop proceedings

Rogiers, Vera; Benfenati, Emilio; Bernauer, Ulrike; Bodin, Laurent; Carmichael, Paul; Chaudhry, Qasim; Coenraads, Pieter Jan; Cronin, Mark T.D.; Dent, Matthew; Dusinska, Maria; Ellison, Corie; Ezendam, Janine; Gaffet, Eric; Galli, Corrado Lodovico; Goebel, Carsten; Granum, Berit; Hollnagel, Heli Miriam; Kern, Petra S.; Kosemund-Meynen, Kirstin; Ouedraogo, Gladys; Panteri, Eirini; Rousselle, Christophe; Stepnik, Maciej; Vanhaecke, Tamara; von Goetz, Natalie; Worth, Andrew

Elsevier

2020

2018

The Volcanic Ash Strategic Initiative Team (VAST) - operational testing activities and exercises.

Wotawa, G.; Arnold, D.; Eckhardt, S.; Kristiansen, N.; Maurer, C.; Prata, F.; Stohl, A.; Zehner, C.

2013

The Volcanic Ash Strategic Initiative Team (VAST) - operational testing activities and exercises. NILU F

Wotawa, G.; Arnold, D.; Eckhardt, S.; Kristiansen, N.; Maurer, C.; Prata, F.; Stohl, A.; Zehner, C.

2013

The value of complementary techniques in suspect and non-target screening – results of the Norman Collaborative Trial of the indoor dust

Rostkowski, Pawel; Haglund, P.; Oswald, P.; Alygizakis, N.; Thomaidis, N.; Aalizadeh, R.; Covaci, A; Moschet, C.; Kaserzon, S.; Yang, C.; Shang, D.; Hindle, R.; Booij, P.; Ionas, A.; Grosse, S.; Arandes, J. B.; Dévier, M. H.; Lestremau, F.; Leonards, P.; Plassmann, M.; Magner, J.; Matsukami, H.; Jobst, K.; Ipolyi, I.; Slobodnik, J.; Reid, Malcolm James

2018

The value of coastal lagoons: Case study of recreation at the Ria de Aveiro, Portugal in comparison to the Coorong, Australia

Clara, Inês; Dyack, Brenda; Rolfe, John; Newton, Alice; Borg, Darien; Povilanskas, Ramunas; Brito, Ana C.

2018

The use of micro-sensors in air quality monitoring. NILU F

Castell, N.; Viana, M.; Minguillón, M.C.; Guerreiro, C.B.; Querol, X.

2014

The use of biomarkers for risk assessment: Reporting from the INTARESE/ENVIRISK Workshop in Prague.

Smolders, R.; Bartonova, A.; Boogaard, P.J.; Dusinska, M.; Koppen, G.; Merlo, F.; Sram, R.J.; Vineis, P.; Schoeters, G.

2010

2017

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