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Found 10000 publications. Showing page 108 of 400:

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Year  
Category

Development, evaluation, and application of a mechanistic bioaccumulation model for organic contaminants in Svalbard polar bears

Krogseth, Ingjerd Sunde; Routti, Heli Anna Irmeli; Eulaers, Igor; Breivik, Knut; Aars, Jon; Eckhardt, Sabine; Frank, Wania

2022

Development, news & issues of ACTRIS data centre for WP3. NILU F

Fiebig, M.; Myhre, C.L.; Fjæraa, A.M.; Hamburger, T.

2014

Development, production and evaluation of aerosol climate data records from European satellite observations (Aerosol_cci).

Popp, T.; de Leeuw, G.; Bingen, C.; Brühl, C.; Capelle, V.; Chedin, A.; Clarisse, L.; Dubovik, O.; Grainger, R.; Griesfeller, J.; Heckel, A.; Kinne, S.; Klüser, L.; Kosmale, M.; Kolmonen, P.; Lelli, L.; Litvinov, P.; Mei, L.; North, P.; Pinnock, S.; Povey, A.; Robert, C.; Schulz, M.; Sogacheva, L.; Stebel, K.; Stein Zweers, D.; Thomas, G.; Tilstra, L.; Vandenbussche, S.; Veefkind, P.; Vountas, M.; Xue, Y.

2016

Developmental toxicity of perfluorooctanesulfonate (PFOS) and its chlorinated polyfluoroalkyl ether sulfonate alternative F-53B in the domestic chicken

Briels, Nathalie; Ciesielski, Tomasz Maciej; Herzke, Dorte; Jaspers, Veerle

The chlorinated polyfluoroalkyl ether sulfonate F-53B is used as a mist suppressant in the Chinese electroplating industry. Because of the regulations on perfluorooctanesulfonate (PFOS), its use is expected to increase. Until now, F-53B toxicity data have been scarce and are, to our knowledge, lacking for birds. This study therefore investigated the effects of PFOS and F-53B, separately and as mixtures, on the development of the chicken (Gallus gallus domesticus). Compounds were injected in ovo, before incubation, at 150 and 1500 ng/g egg. At embryonic day 20, a significantly lower heart rate was observed in all treated groups compared to the control group and hatchlings exposed to the high dose of F-53B had a significantly enlarged liver (8%). Embryonic survival was not affected and no significant effects on hatchling body mass or oxidative stress parameters were found. Our results suggest that these compounds likely have different toxicity thresholds for the investigated endpoints, and/or different modes of action. This study thereby underlines the potential developmental toxicity of PFOS and F-53B at environmentally relevant concentrations. Assessment of PFOS alternatives should therefore continue, preferably prior to their large scale use, as they should be ensured to be less harmful than PFOS itself.

2018

Developments in health risk assessment due to PM2.5 exposure by the European Environment Agency

Soares, Joana; Gsella, Artur; Horálek, Jan; Guerreiro, Cristina; Ortiz, Alberto González

2022

Developments in regional and local air quality monitoring and forecasting - Results of PASODOBLE.

Erbertseder, T.; Balis, D.,Bergemann, C.; Blyth, L.; Carruthers, D.; Choudrie, S.; De Rudder, A.; Di Nicolantonio, W.; Elbern, H.; Eskes, H.; Friese, E.; Ganev, K.; Holzer-Popp, T.; Kukkonen, J.; Lesne, O.; Melas, D.; Meyer-Arnek, J.; Prata, F.; Sicard, P.; Smeets, N.; Sofiev, M.; Stidworthy, A.; Timmermans, R.; Veldeman, N.; Zelle, H.; the PASODOBLE consortium.

2014

Diagnosing the transition layer at extratropical latitudes using MLS O3 and MOPITT CO analyses.

Barré, J.; El Amraoui, L.; Ricaud, P.; Lahoz, W. A.; Attié, J.-L.; Peuch, V.-H.; Josse, B.; Marécal, V.

2013

Dicyclohexylamine: discovery of an environmental contaminant using in-silico screening tools.

Malmvärn, A.; Kierkegaard, A.; Radke, M.; Alsberg, T.; McLachlan MS, Arnot, J.; Breivik, K.; Brown, T.; Wania F.

2011

Dietary exposure estimates of seven selected PFASs to children from four European regions. NILU F

Klenow, S.; Heinemeyer, G.; Dellatte, E.; Herzke, D.

2012

Dietary exposure to legacy and replacement PFASs in the Hubei and Zhejiang province, China.

Zhang, H.; Vestergren, R.; Wang, T.; Herzke, D.; Jiang, G.

2016

Dietary exposure to selected perfluoroalkyl acids (PFAAs) in four European regions.

Klenow, S.; Heinemeyer, G.; Brambilla, G.; Dellatte, E.; Herzke, D.; de Voogt, P.

2013

Differences between Arctic and Atlantic fjord systems on bioaccumulation of persistent organic pollutants in zooplankton from Svalbard.

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

2011

Differences in prenatal exposure to mercury in South African communities residing along the Indian Ocean.

Channa, K.; Odland, J.Ø.; Kootbodien, T.; Theodorou, P.; Naik, I.; Sandanger, T.M.; Röllin, H.B.

2013

Differences in the uptake of biogenic volatile organic compounds (BVOCs) between habitat types and peat layers in boreal peatlands

Korrensalo, Aino; Davie-Martin, Cleo Lisa; Männistö, Elisa; Blande, James D.; Rinnan, Riikka

2024

Differences in Trophic Level, Contaminant Load, and DNA Damage in an Urban and a Remote Herring Gull (Larus argentatus) Breeding Colony in Coastal Norway

Keilen, Ellen Kristine; Borgå, Katrine; Thorstensen, Helene Skjeie; Hylland, Ketil; Helberg, Morten; Warner, Nicholas Alexander; Bæk, Kine; Reiertsen, Tone Kristin; Ruus, Anders

Herring gulls (Larus argentatus) are opportunistic feeders, resulting in contaminant exposure depending on area and habitat. We compared contaminant concentrations and dietary markers between two herring gull breeding colonies with different distances to extensive human activity and presumed contaminant exposure from the local marine diet. Furthermore, we investigated the integrity of DNA in white blood cells and sensitivity to oxidative stress. We analyzed blood from 15 herring gulls from each colony—the urban Oslofjord near the Norwegian capital Oslo in the temperate region and the remote Hornøya island in northern Norway, on the Barents Sea coast. Based on d13C and d34S, the dietary sources of urban gulls differed, with some individuals having a marine and others a more terrestrial dietary signal. All remote gulls had a marine dietary signal and higher relative trophic level than the urban marine feeding gulls. Concentrations (mean ± standard deviation [SD]) of most persistent organic pollutants, such as polychlorinated biphenyl ethers (PCBs) and perfluorooctane sulfonic acid (PFOS), were higher in urban marine (PCB153 17 ± 17 ng/g wet weight, PFOS 25 ± 21 ng/g wet wt) than urban terrestrial feeders (PCB153 3.7 ± 2.4 ng/g wet wt, PFOS 6.7 ± 10 ng/g wet wt). Despite feeding at a higher trophic level (d15N), the remote gulls (PCB153 17 ± 1221 ng/g wet wt, PFOS 19 ± 1421 ng/g wet wt) were similar to the urban marine feeders. Cyclic volatile methyl siloxanes were detected in only a few gulls, except for decamethylcyclopentasiloxane in the urban colony, which was found in 12 of 13 gulls. Only hexachlorobenzene was present in higher concentrations in the remote (2.6 ± 0.42 ng/g wet wt) compared with the urban colony (0.34 ± 0.33 ng/g wet wt). Baseline and induced DNA damage (doublestreak breaks) was higher in urban than in remote gulls for both terrestrial and marine feeders.

2022

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