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Occurrence and seasonality of cyclic volatile methyl siloxanes in Arctic air. NILU PP

Krogseth, I.S.; Breivik, K.; Schlabach, M.; Kierkegaard, A.; Mclachlan, M.S.; Hansen, K.M.

2012

Occurrence and seasonality of cyclic volatile methyl siloxanes in Arctic air.

Krogseth, I.S.; Kierkegaard, A.; Mclachlan, M.S.; Breivik, K.; Hansen, K.M.; Schlabach, M.

2013

Occurrence and levels of organochlorine compounds in human breast milk in Bangladesh.

Bergkvist, C.; Aune, M.; Nilsson, I.; Sandanger, T.M.; Hamadani, J.D.; Tofail, F.; Odland, J.-Ø.; Kabir, I.; Vahter, M.

2012

Occurrence and backtracking of microplastic mass loads including tire wear particles in northern Atlantic air

Few studies report the occurrence of microplastics (MP), including tire wear particles (TWP) in the marine atmosphere, and little data is available regarding their size or sources. Here we present active air sampling devices (low- and high-volume samplers) for the evaluation of composition and MP mass loads in the marine atmosphere. Air was sampled during a research cruise along the Norwegian coast up to Bear Island. Samples were analyzed with pyrolysis-gas chromatography-mass spectrometry, generating a mass-based data set for MP in the marine atmosphere. Here we show the ubiquity of MP, even in remote Arctic areas with concentrations up to 37.5 ng m−3. Cluster of polyethylene terephthalate (max. 1.5 ng m−3) were universally present. TWP (max. 35 ng m−3) and cluster of polystyrene, polypropylene, and polyurethane (max. 1.1 ng m−3) were also detected. Atmospheric transport and dispersion models, suggested the introduction of MP into the marine atmosphere equally from sea- and land-based emissions, transforming the ocean from a sink into a source for MP.

2023

Occurence of PCDD/PCDFs and dioxin-like PCBs in sediments from the Neva river and the Eastern Gulf of Finland.

Metelkova, L.; Zhakovskaya, Z.; Kuchareva, G.; Rybalko, A.; Nikiforov, V.

2017

Occupational exposure to mineral fibres. Biomarkers of oxidative damage and antioxidant defence and associations with DNA damage and repair.

Staruchova M.; Collins, A.R.; Volkovova, K.; Mislanova, C.; Kovacikova, Z.; Tulinska J.; Kocan, A., Staruch, L.; Wsolova, L.; Dusinska, M.

2008

OC pesticides in the Norwegian Arctic atmosphere.

Becker, S.; Crispin, H.; Wlodek, T.; Kallenborn, R.

2008

Obsolete pesticides threaten Vikuge Village, Tanzania.

Mihale, M.; Elfvendahl, S.; Kishimba, M.; Kylin, H.

2005

Observing System Simulation Experiments for air quality.

Timmermans, R.; Lahoz, W.A.; Attié, J.-L.; Peuch, V.-H.; Curier, L.; Edwards, D.; Eskes, H.; Builtjes, P.

2015

Observing system simulation experiment.

Masutani, M.; Schlatter, T.W.; Errico, R.M.; Stoffelen, A.; Andersson, E.; Lahoz, W.; Woollen, J.S.; Emmitt, G.D.; Riishøjgaard, L.P.; Lord, S.J.

2010

Observed trends in aerosol optical properties, visualization and comparison to models.

Shultz, M.; Mortier, A.; Andrews, B.; Myhre, C. L.; Collaud-Coen, M.; Griesfeller, J.

2017

Observed recent change in climate and potential for decay of Norwegian wood structures

The wood rot decay of structures and buildings in Norway represents high costs. This paper reports the observed trends for the potential rot decay of Norwegian wood structures in the cities of Oslo and Bergen over the recent 55 years, calculated as the “wood rot climate index” developed by Scheffer, and compares the reports with previous reported values based on climate change modelling. The observed change in the wood rot climate index was close to the modelling result. Bergen is exposed directly to the westerly Atlantic winds and has among the highest rain amounts in Norway, whereas Oslo is shielded by the Scandinavian mountain chain and has much less rain. The change in the wood rot climate index since 1961 was about 20% in both cities, but the trend in the index (climate index change per year) was about 80% stronger in Bergen. The absolute index changes were largest in the summer; then spring (50 to 60% of the summer increase); and small, zero, or even negative (autumn in Oslo) in the remaining seasons. The relative changes were higher in the spring than summer and very high in Bergen in the winter from a low value. The change to positive index values in the spring and winter indicates temperature and humidity conditions favoring the growth of wood rot and, thus, extended the rot duration through the year. The expected increase in the future wood rot decay potential in Norway shows the need for increased focus on adaption measures to reduce the related damages and costs.

2019

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

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