Publikasjoner

Modelling of aerosols at high latitudes.

Stohl, A.

Modelling of arsenic aerosol in South-West Spain.

Milford, C.; Marrero, C.; Sánchez de la Campa, A.; Fernández-Camacho, R.; Bustos, J.J.; Rodríguez, S.; Castell, N.; De la Rosa, J.; Stein, A.F.

Modelling of CECs

Breivik, Knut; McLachlan, Michael S; Wania, Frank

Modelling of deposited black carbon with the Lagrangian particle dispersion model FLEXPART in backward mode.

Eckhardt, S.; Cassiani, M.; Sollum, E.; Evangeliou, N.; Stohl, A.

Modelling of greenhouse gas at Zeppelin. Powerpoint presentation. NILU F

Holmén, K.; Pedersen, I.-T.; Eneroth, K.

Modelling of methane emissions from offshore oil platforms in the Norwegian sea

Pisso, Ignacio; Foulds, Amy; Allen, Grant

Modelling of Nitrogen Dioxide (NO2) for air quality assessment and planning relevant to the European Air Quality Directive: a FAIRMODE guidance document. NILU F

Denby, B.R.

Modelling of organic aerosols over Europe (2002-2007) using a volatility basis set (VBS) framework: application of different assumptions regarding the formation of secondary organic aerosol.

Bergström, R.; Denier van der Gon, H. A. C.; Prévôt, A. S. H.; Yttri, K. E.; Simpson, D.

Modelling of particulate matter infiltration in the Baroque Library Hall in Prague.

Chatoutsidou, S.E.; Mašková, L.; Lazaridis, M.; Smolík, J.

Modelling of secondary aerosols in urban and rural areas of southwest Spain.

Milford, C.; Castell, N.; Marrero, C.; Sánchez de la Campa, A.; Fernández-Camacho, R.; Rodriguez, S.; De la Rosa, J.; Stein, A.

Modelling of secondary biogenic aerosols. NILU PP

Svendby, T.; Lazaridis, M.

Modelling of the deterioration and conservation costs of polychrome painted wood in two Norwegian medieval stone churches

Grøntoft, Terje

EnvCul (https://envcul.nilu.no/) modelling was performed of condition changes of painted wooden panels and related conservation cost in indoor climate and object response scenarios in two Norwegian Medieval stone churches: Kinn (mean relative humidity = 79%) on the humid west coast, and Ringsaker (mean RH = 49%) in the drier eastern part of the country. It was found that, hypothetical, building measures in Kinn, and conservation heating measures in Ringsaker, to approach an indoor RH of about 65% in the two churches, could probably increase conservation intervals with 20–100%, and correspondingly reduce conservation costs between 10% and 50%. This is in reasonable agreement with an available report of observed conservation requirements in differently heated Norwegian churches. A situation between a linear and accelerating development of the deterioration of the painted wood on approaching a new conservation intervention gave the best correspondence to the observed values. The large modelling uncertainty was mainly due to lacking observations of the deterioration development, but also lacking understanding of the complex mechanisms and phases of the environmental dose-deterioration response of painting conservation treatments.

Elsevier