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Found 9764 publications. Showing page 194 of 391:

Publication  
Year  
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Transboundary particulate matter in Europe: Status report 2013. EMEP report, 4/2013

Aas, W.; Yttri, K.E.; Stohl, A.; Myhre, C.L.; Karl, M.; Tsyro, S.; Mareckova, K.; Wankmüller, R.; Klimont, Z.; Heyes, C.; Alastuey, A.; Querol, X.; Perez, N.; Moreno, T.; Lucarelli, F.; Areskoug, H.; Balan, V.; Cavalli, F.; Puyaud, J.-P.; Cape,.N.; Catrambone, M.; Ceburnis, D.; Conil, S.; Gevorgyan, L.; Jaffrezo, J.L.; Hueglin, C.; Mihalopoulos, N.; Mitosinkova, M.; Riffault, V.; Sellegri, K.; Spindel, G.; Schuck, T.; Pfeffer, U.; Breuer, L.; Adolfs, D.; Chuntonova, L.; Arabidze, M.; Abdulazizov, E.

2013

Testing of emission factors for woodburning emissions in AirQUIS. A sensitivity study for PM2.5 in Oslo. NILU OR

Sundvor, I.; Randall, S.

Emissions from domestic heating due to woodburning are one of the main emissions sources of PM in Norway. However there are uncertianties in the emission data and especially how much these emissions contribute to the concentrations. Dispersion modeling has been performed for Oslo with different emission scenarios to test some of the parameters related to this emission source. The model results show that the wood burning contribution is overestimated, especially in the evening and conclusions are that the emissions of wood burning are wrong both in quantity as well as spacial distribution in time variation.

J.W. Cappelens Forlag AS

2013

Final report. Experimental Study Investigating Risks of selected Amines (ExSIRA). Task 4: Atmospheric corrosion due to amines. NILU OR

Grøntoft, T.; Ofstad, T.

The effect of selected amines on the corrosion of carbon steel and copper was investigated in the laboratory and in the field. The steel and copper samples were exposed to loads of the amines in the laboratory, representing possible 10 years maximum real exposure due to emission from a CO2 capturing plant, and to higher doses in the laboratory and in the field. No effect on the corrosion rate for steel was detected for the application of a possible 10 years real maximum dose of the amines in the laboratory as compared to blanks. Application of 700 times higher doses of amines in the laboratory was observed to give anodic protection, and thus reduced corrosion, of steel samples, but to dissolve the surface of a copper sample. The anodic protection was due to the formation of an amine surface film that protected the sample form oxidation. The dissolution of copper was probably due to formation of a copper-amine complex at high pH. A slight increase in corrosion was observed for samples that were exposed to the equivalent of possible 65 years maximum real exposure of amines in the field. This may be explained by freezing point depression and increased time of wetness of the sample surfaces due to accumulation of the amine solute on the sample surfaces in the season with frost.

2013

MyAir information services for regional and local air quality monitoring and forecasting. NILU F

Erbertseder, T.; Balis, D.; Berger, U.; Bergemann, C.; Blyth, L.; Carruthers, D.; Choudrie, S.; De Rudder, A.; Di Nicolantonio, W.; Elbern, H.; Eskes, H.; Friese, E.; Ganev, K.; Holzer-Popp, T.; Kukkonen, J.; Lesne, O.; Melas, D.; Meyer-Arnek, J.; Prata, F.; Sicard, P.; Smeets, N.; Sofiev, M.; Stidworthy, A.; Timmermans, R.; Veldeman, N.; Zelle, H.; the PASODOBLE consortium.

2013

Land atmosphere exchange of carbon dioxide in a north Norwegian blanket bog. NILU F

Lund, M.; Bjerke, J.W.; Drake, B.G.; Engelsen, O.; Hansen, G.H.; Parmentier, F.J.W.; Powell, T.; Silvennoinen, H.; Tømmervik, H.; Weldon, S.; Rasse, D.

2013

Using UncertWeb for improved decision making. UncertWeb Consortium Deliverable 3.5.

Heuvelink, G.; Helle, K.; Pebesma, E.; Rasouli, S.; Stasch, C.; Truong, P.; Walker, S.E.

2013

Report on integrating the traffic/individual modelling with the air quality modelling. UncertWeb Consortium Deliverable 8.3.

Gerharz, L.; Helle, K.; Pebesma, E.; Pross, B.; Stasch, C.; Rasouli, S.; Timmermans, H.; Denby, B.; Walker, S.E.

2013

Measurement, effect assessment and mitigation of pollutant impact on movable cultural assets. Innovative research for market transfer. Project final report. MEMORI. Grant agreement no. 265132.

Dahlin, E.; Grøntoft, T.; Wittstadt, K.; Drda-Kühn, K.; Colombini, M.P.; Bonaduce, I.; Vandenabeele, P.; Larsen, R.; Potthast, A.; Marincas, O.; Schieweck, A.; Thicket, D.; Odlyha, M.; Andrade, G.; Hackney, S.; McDonagh, C.; Ackerman, J.J.

2013

Size, charge and stabilizer depended genotoxicity of nanosilver. NILU F

Huk, A.; Izak, E.; Duschl, A.; Dusinska, M.

2013

PBDEs and new brominated flame retardants in Arctic biota. NILU F

Herzke, D.; Sagerup, K.; Harju, M.; Routti, H.; Evenset, A.; Fuglei, E.; Gabrielsen, G.W.

2013

Perfluorinated alkyl substances, chloroparaffins and BFRS in soil, sediments and terrestrial/marine biota in Norway and the Arctic. NILU F

Harju, M.; Herzke, D.; Katsoyiannis, A.; Borgen, A.; Sagerup, K.; Gabrielsen, G.W.

2013

Atmopsheric Speciation of Mercury at Alert and Zeppelin. NILU F

Steffen, A.; Berg, T.; Cole.; A.; Pfaffhuber.; K.A.

2013

Long-term monitoring of atmospheric mercury at the cape point GAW observatory, South Africa. NILU F

Labuschagne, C.; Brunke, E-G.; Weigelt, A.; Ebinghaus, R.; Pfaffhuber, K.A.; Williams, A.; Slemr, F.

2013

Perfluorinated compounds - Are point sources contaminating the environment? Consequences for human exposure in China and Norway. NILU F

Herzke, D.; Vestergren, R.; Cousins, I.T.; Kallenborn, R.; Moe, B.; Wang, T.; Zhang, H.; Jiang, G.

2013

Citi-Sense-MOB: Monitoring air quality on mobile platforms. NILU F

Castell, N.; Berre, A.; Dauge, F.R.; Fredriksen, M.F.; Gandal, R.; Kobernus, M.; Noll, J.

2013

Jakten på nye miljøgifter. NILU F

Krogseth, I.S.

2013

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