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Fant 9758 publikasjoner. Viser side 200 av 391:

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Enrichment of perfluoroalkyl substances (PFAS) in Arctic sea-ice. NILU F

Bertrand, O.R.A.; Halsall, C.J.; Herzke, D.; Huber, S.; Carlsson, P.; Nordstad, T.; del Vento, S.; Hermanson, M.H.

2013

Levels and source regions of polychlorinated biphenyls (PCBs) measured in background air in Leova, Moldova. NILU PP

Nordum, M.; Breivik, K.; Aas, W.; Eckhardt, S.; Schlabach, M.; Balan, V.

2013

Initial results from high-volume air sampling of industrial organic contaminants at Cape Verde, Africa. NILU PP

Nordum, M.; Breivik, K.; Eckhardt, S.; Schlabach, M.; Bäcklund, A.

2013

Evaluating a forecast system for long-range atmospheric transport episodes of POPs. NILU PP

Halse, A.K.; Eckhardt, S.; Schlabach, M.; Stohl, A.; Breivik, K.

Background air measurements of persistent organic pollutants (POPs) within existing monitoring programs are typically conducted by use of active air samplers (AAS), but the high cost of AAS limits their spatial and temporal coverage. Sampling at many such sites furthermore occurs at fixed intervals (e.g. one day per week) without any a priori consideration of air mass transport (i.e., whether the air is likely to be polluted or not). While the current strategy is appropriate for the purpose of assessing long-term trends (years, decades), the fixed interval non-continuous sampling approach is at risk of missing out key long-range atmospheric transport (LRAT) episodes. The objectives of this study have been to (i) develop a forecast system using the Lagrangian transport model FLEXPART to predict long-range atmospheric transport episodes of POPs using PCB-28 as a model compound, (ii) to evaluate the capability of the forecast system to capture specific LRAT events at a background site in southern Norway (Birkenes) through targeted sampling (i.e. when LRAT events are predicted), (iii) to assess whether predicted LRAT events for PCB-28 coincide with elevated concentrations of additional PCBs and other POPs, and (iv) to identify source regions of POPs during individual episodes. The system has been initially evaluated by comparing targeted samples collected over 12 to 25 hours during individual LRAT episodes, with monitoring samples regularly collected over one day per week throughout 2011. The FLEXPART model was clearly successful in identifying LRAT episodes for both PCB-28 and other PCBs. The model fails to accurately reproduce the magnitude of PCB-28 concentrations during individual episodes, but this can be mainly attributed to uncertainties in the absolute emission rates of PCB-28 used to drive simulations. We conclude that forecasting of pollution episodes has the potential to add value to relevant monitoring efforts which are normally collecting active air samples at fixed intervals in a non-continuous manner. Observations targeted at strong pollution episodes (as in this study) or on transport from specific source regions with highly uncertain emissions (as could be done in a very similar forecasting framework) could significantly enhance our understanding of POP sources.

2013

Prioritization, screening and identification of organosilicon contaminants in the environment. NILU F

Kierkegaard, A.; McLachlan, M.S.; Breivik, K.; Arnot, J.A.; Wania, F.

A mass balance model of chemical fate and bioaccumulation in the environment was used to rank 287 high- and low-production volume organosilicon compounds for their concentration in the environment and in top predators. Key physical chemical properties of each chemical were estimated using quantitative structure-activity relationships (QSARs) and a total emission estimate of each chemical was made using information, which included amounts entering commerce and emission factors. Based on the model predicted concentrations in air, sediment and human tissue, chemicals were selected for screening through environmental sampling and analysis. Known environmental organosilicon contaminants such as the cyclic and linear volatile methyl siloxanes (VMS) were excluded as well as structures subject to rapid hydrolysis, a feature which was not taken into account in the model simulations because of current limitations in predicting hydrolysis half-lives with QSARs. Analytical standards were only commercially available for half of the remaining 30 organosilicon compounds. Ten of these were not stable in solution, which left 5 organosilicon compounds eligible for environmental screening. These were tetrakis(trimethylsilyloxy)silane, phenyl-tris(trimethylsiloxy)silane, trifluoropropyltrimethylcyclotrisiloxane, trifluoropropylmethylcyclotetrasiloxane and tetraphenyltrisiloxane. Four of these chemicals were identified in sewage sludge, in sediment from Stockholm harbor, and in Stockholm ambient air samples. The trifluoropropyl-substituted siloxanes were analysed with UPLC-MS/MS, the others with GC-MS. Trifluoropropyltrimethylcyclotrisiloxane was solely detected as its corresponding linear diol. To date it is unclear whether the diol is present in the environment as such or formed during extraction or cleanup. The concentrations of the chemicals ranged from pg m-3 in air up to ng g-1 d.w. in sewage sludge, which are orders of magnitude below the levels of cyclic VMS (such as D5) in the same matrices.

2013

Fog composition at three sites in Norway. NILU PP

Wang, Y.; Zhang, J.; Marcotte, A.; Herckes, P.; Karl, M.; Dye, C.

2013

High levels of ultraviolet radiation observed by ground-based instruments below the 2011 Arctic ozone hole.

Bernhard, G.; Dahlback, A.; Fioletov, V.; Heikkilä, A.; Johnsen, B.; Koskela, T.; Lakkala, K.; Svendby, T.

2013

Selected NILU projects. NILU F

Sivertsen, B.

2013

Calibration and application of a passive air sampler (XAD-PAS) for volatile methyl siloxanes. NILU PP

Krogseth, I.S.; Zhang, X.; Lei, Y.D.; Wania, F.; Breivik, K.

2013

Global emissions of mercury to the atmosphere.

Wilson, S.; Kondbom, K.; Yaramenka, K.; Steenhuisen, F.; Telmer, K.; Munthe, J. Contributing authors: Devia, L.; Gustafsson, T.; Jozewicz, W.; Kumari, R.; Leaner, J.; Maag, J.; Maioli, O.L.G.; Maxson, P.; Nelson, P.; Pacyna, J.; Pudasainee, D.; Seo, Y.C.; Sloss, L.; Solorzano, G.; Strum, M.; Sundseth, K.; Suzuki, N.

2013

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