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Found 9759 publications. Showing page 157 of 391:

Publication  
Year  
Category

Transboundary particulate matter in Europe: Status report 2011. EMEP report, 4/2011

Yttri, K.E.; Aas, W.; Tørseth, K.; Fiebig, M.; Fjæraa, A.M.; Tsyro, S.; Simpson, D.; Bergström, R.; Mareckova, K.; Wankmüller, R.; Klimont, Z.; Borken-Kleefeld, J.; Cavalli, F.; Putaud, J.-P.; Schultz, M.; Querol, X.; Alastuey, A.; Amato, F.; Cusack, M.; Reche, C.; Karanasiou, A.; Viana, M.; Moreno, T.; Pey, J.; Perez, N.; Laj, P.; Wiedersohler, A.

2011

Environmental information systems on the Internet: A need for change. IFIP Advances in Information and Communication Technology, 359

Schade, S.; Fogarty, B.; Kobernus, M.; Schleidt, K.; Gaughan, P.; Mazzetti, P.; Berre, A.J.

2011

Atmospheric Degradation of Amines (ADA). Summary report: Photo-oxidation of methylamine, dimethylamine and trimethylamine. CLIMIT project no. 201604. NILU OR

Nielsen, C.J.; D'Anna, B.; Karl, M.; Aursnes, M.; Boreave, A.; Bossi, R.; Bunkan, A.J.C.; Glasius, M.; Hallquist, M.; Hansen, A.M.K.; Kristensen, K.; Mikoviny, T.; Maguta, M.M.; Müller, M.; Nguyen, Q.; Westerlund, J.; Salo, K.; Skov, H.; Stenstrøm, Y.; Wisthaler, A.

The atmospheric gas phase photo-oxidation of methylamine (CH3NH2), dimethylamine ((CH3)2NH) and trimethylamine ((CH3)3N) has been studied under pseudo natural conditions at the European Photochemical Reactor, EUPHORE, in Valencia, Spain. Major products in the photo-oxidation were imines (methanimine and N-methyl-methanimine) and amides (formamide, N-methyl formamide and N,N-dimethyl formamide). Total aerosol yields obtained in EUPHORE experiments were between 8 and 14%. Mimicking conditions at Mongstad results in a steady-state nitrosamine concentration of less than 0.6 % of photo-oxidized dimethylamine and less than 1.1 % of photo-oxidized trimethylamine. For rural regions it is predicted that the formation yield of the corresponding nitramine in the atmospheric oxidation of CH3NH2, (CH3)2NH and (CH3)3N is less than 0.4 %, 2.5 % and 5 %, respectively. The major uncertainties in the current understanding of the fate of amines emitted to the atmosphere are related to night-time chemistry, to the chemistry of imines, and to chemistry in the aqueous aerosol.

2011

Measurements of air quality and corrosion risk at the Railway Museum in Warsaw. NILU OR

Grøntoft, T.

Measurements of the concentration of SO2, of aerosol concentration in air and of the composition and mass of water soluble cations and anions were performed during four seasons, spring, summer, autumn and winter, at two locations of the Railway Museum in Warsaw: Central Warsaw and Sochazew, which is located 50 km west of Warsaw. The time of wetness was calculated from precipitation data available from the Warsaw Targowek meteorological station. The measurements indicated a low to medium corrosivity for the atmospheres, which is typical for northern European inland environments with low chloride concentrations and relatively low SO2 concentration. The measurements indicated that sulphur dioxide SO2 was the main pollutant which gave increased corrosion at the sites, especially in Sochaczew, and that the presence of chloride, Cl-, and sulphate, SO42-, in the aerosol at significant levels contributed to the corrosion. Higher levels of Cl-, SO42- and H+ were measured in Sochaczew than in central Warsaw. The ISO 9223 corrosion category for SO2 and Cl- was 0 in central Warsaw and 1 in Sochaczew, indicating a significant contribution to the corrosion from anthropogenic sources in Sochaczew. The values for SO2 are slightly higher, but the PM10 values are lower, than tolerable levels for immovable (i.e. outdoor) cultural heritage given in a European wide assessment performed for CAFÉ (EU programme: Clean Air For Europe). The main factor that increases the corrosion to a higher ISO category (2-3) at the locations is the relatively humid climate. A further reduction of air pollutants should further reduce the corrosion, but the largest potential protection effect would be from measures to shelter the objects form rain and reduce the humidity in the air around the objects, e.g. by moving vulnerable smaller objects or particularly valuable objects to the indoor or applying other options for sheltering.

2011

VETAPOS. NILU OR

Kallenborn, R.; Schmidbauer, N.; Reimann, S.

2011

2011

Sub-grid variability and its impact on European wide air quality exposure.

Denby, B.; Cassiani, M.; de Smet, P.; de Leeuw, F.; Horálek, J.

2011

Patterns of CO2 and radiocarbon across high northern latitudes during International Polar Year 2008.

Vay, S.A.; Choi, Y.; Vadrevu, K.P.; Blake, D.R.; Tyler, S.C.; Wisthaler, A.; Hecobian, A.; Kondo, Y.; Diskin, G.S.; Sachse, G.W.; Woo, H.; Weinheimer, A.J.; Burkhart, J.F.; Stohl, A.; Wennberg, P.O.

2011

Observed and modelled record ozone decline over the Arctic during winter/spring 2011.

Balis, D.; Isaksen, I.S.A.; Zerefos, C.; Zyrichidou, I.; Eleftheratos, K.; Tourpali, K.; Bojkov, R.; Rognerud, B.; Stordal, F.; Søvde, O.A.; Orsolini, Y.

2011

Perfluoroalkyl substances in fruits, vegetables and dry food collected in four European countries; Perfood.

D'Hollander, W.; Bervoets, L.; Herzke, D.; Huber, S.; Hasjlova, J.; Brambilla, G.; De Filippis, S.P.; deVogt, P.

2011

Major achievements during the COST Action 729.

Tørseth, K.; Fagerli, H.; Aas, W.; Hole, L.

2011

Top-down assessment of air pollution and GHGs for Dhaka, Bangladesh. Analysis of GAINS derived model data. NILU TR

Randall, S.

The city of Dhaka was chosen for this assessment due to the current ongoing project Bangladesh Air Pollution Management (BAPMAN), which concentrates mostly on the capital city Dhaka. The Greenhouse Gas and Air Pollution Interactions and Synergies model (GAINS) was used to performed this top-down assessment due to the models integrated assessment approach of capturing interactions between air pollution control and economic development, as well as its focus on presenting cost effective pollution control strategies. Results from the GAINS model assessment for Dhaka shows that for 2010 the total PM2.5 emissions were 35000 tons/year, and the total PM10 emissions were 45000 tons/year. The top sectors making up the PM emissions included Industry and Residential sectors, where the specific sub-sectors were brick/cement production and residential cooking respectively; the top activities making up the emissions were 'no fuel use' and 'fuelwood direct'. GAINS estimates that the top 3 technical control measures available for PM can eliminate approximately 1/3 of the PM emissions at a cost of .65 MEuro/year. GAINS results also shows that for Dhaka in 2010 the total SO2 emissions were 34000 tons/year, dominated by the Industrial sector, made up of the sub-sectors of new power plants and industrial combustion; top activities contributing to these emissions are hard coal and natural gas. NOX emissions for Dhaka in 2010 were 30000 tons/year, dominated by the Industrial and Transport sectors, made up of the industrial combustion/power plant and light/heavy duty sub-sectors respectively; top activities contributing to these emissions include natural gas, gasoline, and medium distillates. GHG emissions for Dhaka in 2010 exceeded 23 million tons/year, dominated by the Industrial and Agricultural sectors, comprising of the industrial combustion and new power plant sub-sectors; top activities contributing to these emissions include natural gas and hard coal.

2011

Novel brominated flame retardants: A review of their analysis, environmental fate and behaviour.

Covaci, A.; Harrad, S.; Abdallahd, M. A.-E.; Alia, N.; Lawe, R.J.; Herzke, D.; de Wit, C.A.

2011

PFAS - Comparison of MS/MS and MS-TOF techniques and two extraction methods on lean and fatty fish. NILU PP

Huber, S.; Lacina, O.; Hradkova, P.; Pulkrabova, J.; Herzke, D.; Kallenborn, R.; Hajslova, J.

2011

Minimal analytical characterization of engineered nanomaterials needed for hazard assessment in biological matrices.

Bouwmeester, H.; Lynch, I.; Marvin, H.J.P.; Dawson, K.A.; Berges, M.; Braguer, D.; Byrne, H.J.; Casey, A.; Chambers, G.; Clift, M.J.D.; Elia, G.; Fernandes, T.F.; Fjellsbø, L.B.; Hatto, P.; Juillerat, L.; Klein, C.; Kreyling, W.G.; Nickel, C.; Riediker, M.; Stone, V.

2011

A thermal infrared instrument onboard a geostationary platform for CO and O3 measurements in the lowermost troposphere: Observing System Simulation Experiments (OSSE).

Claeyman, M.; Attié, J.-L.; Peuch, V.-H.; El Amraoui, L.; Lahoz, W. A.; Josse, B.; Joly, M.; Barré, J.; Ricaud, P.; Massart, S.; Piacentini, A.; von Clarmann, T.; Höpfner, M.; Orphal, J.; Flaud, J.-M.; Edwards, D.P.

2011

Factors of change: using trophic magnification factors (TMFs) to assess changes in POP bioaccumulation in Arctic food webs. NILU F

Warner, N.A.; Hallanger, I.G.; Ruus, A.; Evenset, A.; Herzke, D.; Gabrielsen, G.W.; Borgå, K.

2011

Safety of nanoparticles in medicine.

Dusinska, M.; Fjellsbø, L.M.; Magdolenova, Z.; Ravnum, S.; Rinna, A.; Rundén-Pran, E.

2011

Assessment of cytotoxicity and genotoxicity of uncoated and oleic acid coated magnetite nanoparticles.

Magdolenova, Z.; Rinna, A.; Fjellsbø, L.; Drlickova, M.; Bilanicova, D.; Pojana, G.; Marcomini, A.; Dusinska, M.

2011

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