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Trends of inorganic and organic aerosols and precursor gases in Europe: insights from the EURODELTA multi-model experiment over the 1990–2010 period

Ciarelli, Giancarlo; Theobald, Mark, R.; Vivanco, Marta García; Beekmann, Matthias; Aas, Wenche; Andersson, Camilla; Bergström, Robert; Manders-Groot, Astrid; Couvidat, Florian; Mircea, Mihaela; Tsyro, Svetlana; Fagerli, Hilde; Mar, Kathleen; Raffort, Valentin; Roustan, Yelva; Pay, Maria-Teresa; Schaap, Martijn; Kranenburg, Richard; Adani, Mario; Briganti, Gino; Cappelletti, Andrea; D'Isidoro, Massimo; Cuvelier, Cornelis; Cholakian, Arineh; Bessagnet, Bertrand; Wind, Peter; Colette, Augustin

In the framework of the EURODELTA-Trends (EDT) modeling experiment, several chemical transport models (CTMs) were applied for the 1990–2010 period to investigate air quality changes in Europe as well as the capability of the models to reproduce observed long-term air quality trends. Five CTMs have provided modeled air quality data for 21 continuous years in Europe using emission scenarios prepared by the International Institute for Applied Systems Analysis/Greenhouse Gas – Air Pollution Interactions and Synergies (IIASA/GAINS) and corresponding year-by-year meteorology derived from ERA-Interim global reanalysis. For this study, long-term observations of particle sulfate (SO2−4

), total nitrate (TNO3), total ammonium (TNHx) as well as sulfur dioxide (SO2) and nitrogen dioxide (NO2) for multiple sites in Europe were used to evaluate the model results. The trend analysis was performed for the full 21 years (referred to as PT) but also for two 11-year subperiods: 1990–2000 (referred to as P1) and 2000–2010 (referred to as P2).

The experiment revealed that the models were able to reproduce the faster decline in observed SO2 concentrations during the first decade, i.e., 1990–2000, with a 64 %–76 % mean relative reduction in SO2 concentrations indicated by the EDT experiment (range of all the models) versus an 82 % mean relative reduction in observed concentrations. During the second decade (P2), the models estimated a mean relative reduction in SO2 concentrations of about 34 %–54 %, which was also in line with that observed (47 %). Comparisons of observed and modeled NO2 trends revealed a mean relative decrease of 25 % and between 19 % and 23 % (range of all the models) during the P1 period, and 12 % and between 22 % and 26 % (range of all the models) during the P2 period, respectively.

Comparisons of observed and modeled trends in SO2−4
concentrations during the P1 period indicated that the models were able to reproduce the observed trends at most of the sites, with a 42 %–54 % mean relative reduction indicated by the EDT experiment (range of all models) versus a 57 % mean relative reduction in observed concentrations and with good performance also during the P2 and PT periods, even though all the models overpredicted the number of statistically significant decreasing trends during the P2 period. Moreover, especially during the P1 period, both modeled and observational data indicated smaller reductions in SO2−4

concentrations compared with their gas-phase precursor (i.e., SO2), which could be mainly attributed to increased oxidant levels and pH-dependent cloud chemistry.

An analysis of the trends in TNO3 concentrations indicated a 28 %–39 % and 29 % mean relative reduction in TNO3 concentrations for the full period for model data (range of all the models) and observations, respectively. Further analysis of the trends in modeled HNO3 and particle nitrate (NO−3
) concentrations revealed that the relative reduction in HNO3 was larger than that for NO−3 during the P1 period, which was mainly attributed to an increased availability of “free ammonia”. By contrast, trends in modeled HNO3 and NO−3 concentrations were more comparable during the P2 period. Also, trends of TNHx concentrations were, in general, underpredicted by all models, with worse performance for the P1 period than for P2. Trends in modeled anthropogenic and biogenic secondary organic aerosol (ASOA and BSOA) concentrations together with the trends in available emissions of biogenic volatile organic compounds (BVOCs) were also investigated. A strong decrease in ASOA was indicated by all the models, following the reduction in anthropogenic non-methane VOC (NMVOC) precursors. Biogenic emission data...

2019

Observations of microbarom-generated infrasound in Northern Norway during three different sudden stratospheric warmings

Näsholm, Sven Peter; Assink, Jelle; Blixt, Erik Mårten; Carlo, Marine De; Evers, Läslo G.; Gibbons, Steven John; Kero, Johan; Pichon, Alexis Le; Orsolini, Yvan; Ouden, Oliver F. C. den; Smets, Pieter S

2019

Zeppelinobservatoriet på Svalbard

Tørseth, Kjetil (intervjuobjekt); Andreassen, Rune Nordgård (journalist)

2019

Opinion of the Scientific Committee on Consumer safety (SCCS) – Opinion on the safety of cosmetic ingredient salicylic acid (CAS 69-72-7)

Bernauer, Ulrike; Bodin, Laurent; Chaudhry, Qasim; Coenraads, Pieter; Dusinska, Maria; Ezendam, Janine; Gaffet, E.; Galli, Corrado Lodovico; Granum, Berit; Panteri, E.; Rogiers, V.; Rousselle, C; Stepnik, Maciej; Vanhaecke, T.; Wijnhoven, S.

2019

Lufta er for alle!

Grossberndt, Sonja; Castell, Nuria; Gray, Laura

2019

The relationship between per- and polyfluoroalkyl substances (PFASs), persistent organic pollutants (POPs) and trace elements and thyroid hormone status in glaucous gulls (Larus hyperboreus)

Mortensen, Åse-Karen; Hovden, T. S.; Ciesielski, Tomasz Maciej; Heimstad, Eldbjørg Sofie; Gabrielsen, Geir W.; Jenssen, Bjørn Munro

2019

Innovative environmental monitoring for Norwegian municipalities using low-cost sensor networks. The iFLINK project.

Castell, Nuria; Dauge, Franck Rene; Grossberndt, Sonja; Høiskar, Britt Ann Kåstad; Lahoz, William A.; Lepioufle, Jean-Marie; Logna, Robert; Schneider, Philipp; Vallejo, Islen; Vogt, Matthias; Bartonova, Alena

2019

Europe's urban air quality — re-assessing implementation challenges in cities

Öztürk, Evrim Dogan; Lükewille, Anke; Ortiz, Alberto González; Viana, Mar; Bartonova, Alena; Guerreiro, Cristina D.b.b.; Leeuw, Frank de

This report analyses the implementation of EU air quality legislation at the urban level and identifies some of the reasons behind persistent air quality problems in Europe's cities. It is produced in cooperation with 10 cities involved in a 2013 Air Implementation Pilot project: Antwerp (Belgium), Berlin (Germany), Dublin (Ireland), Madrid (Spain), Malmö (Sweden), Milan (Italy), Paris (France), Plovdiv (Bulgaria), Prague (Czechia) and Vienna (Austria).

European Environment Agency

2019

Year-Round In Situ Measurements of Arctic Low-Level Clouds: Microphysical Properties and Their Relationships With Aerosols

Koike, Makoto; Ukita, Jinro; Ström, Johan; Tunved, Peter; Shiobara, Masataka; Vitale, Vito; Lupi, Angelo; Baumgardner, D.; Ritter, Christoph; Hermansen, Ove; Yamada, K.; Pedersen, Christina Alsvik

Two years of continuous in situ measurements of Arctic low‐level clouds have been made at the Mount Zeppelin Observatory (78°56′N, 11°53′E), in Ny‐Ålesund, Spitsbergen. The monthly median value of the cloud particle number concentration (Nc) showed a clear seasonal variation: Its maximum appeared in May–July (65 ± 8 cm−3), and it remained low between October and March (8 ± 7 cm−3). At temperatures warmer than 0 °C, a clear correlation was found between the hourly Nc values and the number concentrations of aerosols with dry diameters larger than 70 nm (N70), which are proxies for cloud condensation nuclei (CCN). When clouds were detected at temperatures colder than 0 °C, some of the data followed the summertime Nc to N70 relationship, while other data showed systematically lower Nc values. The lidar‐derived depolarization ratios suggested that the former (CCN‐controlled) and latter (CCN‐uncontrolled) data generally corresponded to clouds consisting of supercooled water droplets and those containing ice particles, respectively. The CCN‐controlled data persistently appeared throughout the year at Zeppelin. The aerosol‐cloud interaction index (ACI = dlnNc/(3dlnN70)) for the CCN‐controlled data showed high sensitivities to aerosols both in the summer (clean air) and winter–spring (Arctic haze) seasons (0.22 ± 0.03 and 0.25 ± 0.02, respectively). The air parcel model calculations generally reproduced these values. The threshold diameters of aerosol activation (Dact), which account for the Nc of the CCN‐controlled data, were as low as 30–50 nm when N70 was less than 30 cm−3, suggesting that new particle formation can affect Arctic cloud microphysics.

2019

Low-cost air quality sensors and their use for urban-scale modelling

Schneider, Philipp; Liu, Hai-Ying; Castell, Nuria; Hamer, Paul David; Vogt, Matthias; Dauge, Franck Rene; Bartonova, Alena

2019

Fatty alcohols. Anthropogenic and natural occurence in the environment. 2nd edition.

Mudge, Stephen M.; Belanger, Scott E.; DeLeo, Paul C.

Royal Society of Chemistry (RSC)

2019

Bok

The Atmosphere Above Ny-Ålesund: Climate and Global Warming, Ozone and Surface UV Radiation

Maturilli, Marion; Hanssen-Bauer, Inger; Neuber, Roland; Rex, Markus; Edvardsen, Kåre

2019

Ozonlaget - den internasjonale ozondagen

Hansen, Georg Heinrich (intervjuobjekt)

2019

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