Publications

Occurrence and risk assessment of organophosphorus and brominated flame retardants in the River Aire (UK).

Cristale, J.; Katsoyiannis, A.; Sweetman, A.J.; Jones, K.C.; Lacorte, S.

Aerosol decadal trends - Part 2: In-situ aerosol particle number concentrations at GAW and ACTRIS stations.

Asmi, A.; Collaud Coen, M.; Ogren, J. A.; Andrews, E.; Sheridan, P.; Jefferson, A.; Weingartner, E.; Baltensperger, U.; Bukowiecki, N.; Lihavainen, H.; Kivekäs, N.; Asmi, E.; Aalto, P. P.; Kulmala, M.; Wiedensohler, A.; Birmili, W.; Hamed, A.; O'Dowd, C.; G Jennings, S.; Weller, R.; Flentje, H.; Fjaeraa, A. M.; Fiebig, M.; Myhre, C. L.; Hallar, A. G.; Swietlicki, E.; Kristensson, A.; Laj, P.

Introduction: Redox interfaces in marine waters. Handbook of Environmental Chemistry, 22

Yakushev, E.V.; Newton, A.

Evaluation of SMOS and ASCAT soil moisture products over Norway using ground-based in situ observations.

Griesfeller, A.; Lahoz, W.A.; Svendby, T.M.; Haugen, L.M.; Wagner, W.; Dorigo, W.; Kerr, Y.; de Jeu, R.A.M.

Heavy metals at Xstrata. Assessment of measured concentration level. NILU OR

Tønnesen, D.

NILU has done an analysis of heavy metal concentrations measured at Xstrata, Kristiansand. Through a simplified dispersion scheme, the measured concentrations have been converted to emissions. These have been compared to the reported emissions from Xstrata. The reported emissions and the measured concentrations are in agreement.

Towards an operational implementation of particle aggregation in ash dispersion models. NILU F

Mastin, L.G.; Van Eaton, A.R.; Durant, A.J.; Schwaiger, H.F.; Denlinger, R.P.

Bye-bye, two degree target? Recent development in observed CO2 and CH4: Do we see signs of reductions? NILU F

Myhre, C.L.

Annual cycle of background aerosol at Troll Station, Antarctica. NILU PP

Fiebig, M.; Hirdman, D.; Lunder, C.R.; Ogren, J.A.; Stohl, A.

Specific absorption coefficient of phytoplankton off the Southwest coast of the Iberian Peninsula: A contribution to algorithm development for ocean colour remote sensing.

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

Evaluation of SMOS and ASCAT soil moisture products over Norway using ground-based in situ observations. NILU PP

Griesfeller, A.; Lahoz, W.A.; Svendby, T.M.; Haugen, L.M.; Wagner, W.; Dorigo, W.; Kerr, Y.; de Jeu, R.A.M.

Introduction: geoscientific knowledgebase of Chernobyl and Fukushima.

Yamauchi, M.; Voitsekhovych, O.; Korobova, E.; Stohl, A.; Wotawa, G.; Kita, K.; Aoyama, M.; Yoshida, N.

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.

VOC measurements 2011. EMEP/CCC

Solberg, S.