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Found 9854 publications. Showing page 247 of 395:

Publication  
Year  
Category

Aerosol and ozone radiative forcing 1990-2015.

Myhre, C.L.; Myhre, G.; Samset, B.H.; Schulz, M.

2016

POPs in humans.

Hanssen, L.

2016

In vitro and in silico techniques as a tool to assess effects of pollutants on polar bear energy homeostasis.

Routti, H.; Berg, M.; Goksøyr, A.; Harju, M.; Helgason, L.; Fink, T.; Kristiansen, K.; Lille-Langøy, R.; Rusten, M.; Sylte, I.; Øygarden, L.

2016

NO produced by energetic electron precipitation during a geomagnetic storm in April 2010.

Smith-Johnsen, C.; Stordal, F.; Orsolini, Y.J.; Tissøy H.

2016

PFAS in house dust: within and between house variability.

Bohlin-Nizzetto, P.; Hanssen, L.; Herzke, D.; Yeung, L.W.Y.

2016

Assessment of indoor air quality and the risk of damage to cultural heritage objects using MEMORI® dosimetry.

Grøntoft, T.; Thickett, D.; Lankester, P.; Hackney, S.; Townsend, J.H.; Ramsholt, K.; Garrido, M.

2016

Heavy metals and POP measurements, 2014. EMEP/CCC

Aas, W.; Pfaffhuber, K. A.; Bohlin-Nizzetto, P.

2016

Atmospheric deposition of heavy metals in Norway. National moss survey 2015. NILU report

Steinnes, E.; Uggerud, H. T.; Pfaffhuber, K. A.; Berg, T.

Commissioned by the Norwegian Environment Agency, NILU - Norwegian Institute for Air Research in collaboration with Norwegian University of Science and Technology (NTNU), collected moss from 230 sites and determined the content of 53 metals in these. The purpose of the survey is to map atmospheric deposition of heavy metals in Norway. Compared with data from 2005, a decrease is observed in the deposition of vanadium and lead. For chromium, nickel, copper, zinc, arsenic, cadmium and antimony, there is no appreciable change in deposition from 2005 to 2015

2016

Toward improving the representation of the water cycle at High Northern Latitudes.

Lahoz, W.; Svendby, T.; Hamer, P.; Blyverket, J.; Kristiansen, J.; Luijting, H.

2016

Air quality in Europe - 2016 report. EEA report, 28/2016

Guerreiro, C.; Ortiz, A.G.; de Leeuw, F.; Viana, M.; Horálek, J.

2016

Advances in our understanding of nanomaterial carcinogenicity.

Dusinska, M.; Gabelova, A.; El Yamani, N.; Fjellsbø, L. M.; Silva, M.J.; Rundén-Pran, E.

2016

Results from the joint Nordic and the Norwegian non-target screening studies.

Schlabach, M.; Rostkowski, P.; Reid, M.; van Bavel, B.; Thomas, K.; Bæk, K.; Haglund, P.; Venaas, C.

2016

EVDC.

Fjæraa, A.M.; Boyd, I.; Espe, T.

2016

European aerosol phenomenology-5: Climatology of black carbon optical properties at 9 regional background sites across Europe.

Zanatta, M.; Gysel, M.; Bukowiecki, N.; Müller, T.; Weingartner, E.; Areskoug, H.; Fiebig, M.; Yttri, K.E.; Mihalopoulos, N.; Kouvarakis, G.; Beddows, D.; Harrison, R.M.; Cavalli, F.; Putaud, J.P.; Spindler, G.; Wiedensohler, A.; Alastuey, A.; Pandolfi, M.; Sellegri, K.; Swietlicki, E.; Jaffrezo, J.L.; Baltensperger, U.; Laj, P. A.

2016

Monitoring of size-segregated particulate matter fractions with optical instruments in urban areas.

Dunea, D.; Savu, T.; Marsteen, L.

The assessment of harmful PM concentrations i.e. particles with an aerodynamic diameter below 2.5 µm, requires continuous monitoring conducted for 24 hours a day, for 365 days a year. Monitoring campaigns for screening the PM levels in a particular urban area facilitate the conceiving of a continuous monitoring plan by establishing where to deploy optimally the optical instruments for on-line measurement. The paper presents the practical efficiency of the outdoor monitoring of PM size fractions using a new optical equipment i.e. Dusttrak DRX 8533 with environmental enclosure and heating module. The experiments were carried out in Targoviste city, Romania, between 2014 and 2015 within the first two phases of the ROkidAIR project (http://www.rokidair.ro) to perform a screening of the PM concentrations existing in these urban areas and to calibrate the prototype of the PM2.5 microstation developed within the project .The utilization of the DustTrak instrument showed that in heavy traffic conditions without significant industrial emissions, the most frequent PM fraction is the submicrometric one (PM1).The results pointed out the usefulness of monitoring four size segregated mass fractions and their relationship with the potential PM emission sources. Outdoor PM2.5 measurements provide key information for evaluating population exposure, planning of air quality and establishing of reliable measures that allow the lowering of PM emission.

2016

Functionalized porous silica&maghemite core-shell nanoparticles for applications in medicine: design, synthesis, and immunotoxicity.

Zasonska, B.A.; Lískova, A.; Kuricova, M.; Tulinska, J.; Pop-Georgievski, O.; Ciampor, F.; Vavra, I.; Dusinska, M.; Ilavska, S.; Horvathova, M.; Horak, D.

2016

Ground-based assessment of the bias and long-term stability of 14 limb and occultation ozone profile data records.

Hubert, D.; Lambert, J.-C.; Verhoelst, T.; Granville, J.; Keppens, A.; Baray, J.-L.; Bourassa, A. E.; Cortesi, U.; Degenstein, D. A.; Froidevaux, L.; Godin-Beekmann, S.; Hoppel, K. W.; Johnson, B. J.; Kyrölä, E.; Leblanc, T.; Lichtenberg, G.; Marchand, M.; McElroy, C. T.; Murtagh, D.; Nakane, H.; Portafaix, T.; Querel, R.; Russell III, J. M.; Salvador, J.; Smit, H. G. J.; Stebel, K.; Steinbrecht, W.; Strawbridge, K. B.; Stübi, R.; Swart, D. P. J.; Taha, G.; Tarasick, D. W.; Thompson, A. M.; Urban, J.; van Gijsel, J. A. E.; Van Malderen, R.; von der Gathen, P.; Walker, K. A.; Wolfram, E.; Zawodny, J. M.

2016

Modeling the global atmospheric transport and deposition of mercury to the Great Lakes.

Cohen, M. D.; Draxler, R. R.; Artz, R. S.; Blanchard, P.; Gustin, M. S.; Han, Y.-J.; Holsen, T. M.; Jaffe, D. A.; Kelley, P.; Lei, H.; Loughner, C. P.; Luke, W. T.; Lyman, S. N.; Niemi, D.; Pacyna, J. M.; Pilote, M.; Poissant, L.; Ratte, D.; Ren, X.; Steenhuisen, F.; Steffen, A.; Tordon, Wilson, S. J.

2016

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