Publications

The Fukushima inverse problem.

Martinez-Camara, M.; Dokmanic, I.; Ranieri, J.; Scheibler, R.; Vetterli, M.; Stohl, A.

Lagrangian modeling of the atmosphere. Geophysical Monograph Series, 200

Lin, J.; Brunner, D.; Gerbig, C.; Stohl, A.; Luhar, A.; Webley, P. (eds.)

Calibration of a passive air sampler for volatile methyl siloxanes. NILU F

Krogseth, I.S.; Zhang, X.; Lei, Y.D.; Wania, F.; Breivik, K.

Presentation of WP4: Management, Organization and outreach. NILU F

Myhre, C.L.

Applications of inverse modelling for understanding of emissions and analysis of observations. NILU F

Thompson, R.; Stohl, A.; Pisso, I.; Myhre, C.L. et al.

The importance of biomass burning as a source of BC in the European Arctic - Based on measurements at the Zeppelin Observatory, Svalbard. NILU F

Myhre, C.L.; Yttri, K.E.; Eckhardt, S.; Stohl, A.; Fiebig, M.; Dye, C.; Ström, J.; Klimont, Z.

ACTRIS - Aerosols, Clouds and Trace gases Research InfraStructure and access to ACTRIS Data: http://actris.nilu.no/ NILU F

Myhre, C.L.; Pappalardo, G.; Laj, P.

CITI-SENSE: Can sensor technologies contribute to raising awareness of environmental health? NILU F

Bartonova, A.

Using ground station data for improving accuracy in (global) modeling. NILU F

Fiebig, M.

NILU 2013. Et historisk tilbakeblikk. Min arbeidsplass gjennom 43 år. NILU F

Sivertsen, B.

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.

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.

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.