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The impact of the epoxy thin-film layer for microwave-based gas sensors working at high relative humidity levels

Grochala, Dominik; Paleczek, Anna; Kocoñ, Mateusz; Dudzik, Maciej; Blajszczak, Lukasz; Staszek, Kamil; Wojcikowski, Marek; Cao, Tuan-Vu; Rydosz, Artur

2024

The impact of the Arctic sea ice loss and variation on lower latitudes

Koenigk, Torben; Gao, Yongqi; Gastineau, Guillaume; Keenlyside, Noel; Nakamura, Tetsu; Ogawa, Fumiaki; Orsolini, Yvan; Semenov, Vladimir; Suo, Lingling; Tian, Tian; Yang, Shuting; Wang, Tao

2018

The Impact of Recent European Droughts and Heatwaves on Trace Gas Surface Fluxes: Insights from Land Surface Data Assimilation

Hamer, Paul David; Trimmel, Heidelinde; Calvet, Jean-Christophe; Bonan, Bertrand; Meurey, Catherine; Vallejo, Islen; Eckhardt, Sabine; Santos, Gabriela Sousa; Marécal, Virginie; Tarrasón, Leonor

2023

The impact of organic acids on varnishes in museum environments.

Bonaduce, I.; Colombini, M.P.; Di Girolamo, F.; Orsini, S.; Odlyha, M.; Rutkowska, S.; Scharff, M., Grøntoft, T.

2013

The impact of North American emission on carbon monoxide and ozone concentrations over Europe. NILU PP

Eckhardt, S.; Stohl, A.; Cassiani, M.; Cammas, J.-P.

2011

The impact of North American emission on carbon monoxide and ozone concentrations over Europe. NILU PP

Eckhardt, S.; Stohl, A.; Cassiani, M.; Cammas, J.-P.

2011

The impact of greenhouse gases and halogenated species on future solar UV radiation doses.

Taalas, P.; Kaurola, J.; Kylling, A.; Shindell, D.; Sausen, R.; Dameris, M.; Grewe, V.; Herman, J.

2000

The impact of climate sensitive factors on the exposure to organohalogenated contaminants in an aquatic bird exploiting both marine and freshwater habitats

Bustnes, Jan Ove; Bårdsen, Bård-Jørgen; Herzke, Dorte; Bangjord, Georg; Bollinger, Eric; Bourgeon, Sophie; Schulz, Ralf; Fritsch, Clémentine; Eulaers, Igor

To assess how climate-sensitive factors may affect the exposure to organochlorines (OCs) and perfluoroalkyl substances (PFASs), we monitored concentrations in eggs of the common goldeneye (Bucephala clangula) over two decades (1999–2019) in central Norway. The goldeneye alternates between marine and freshwater habitats and is sensitive to climate variation, especially due to alterations in ice conditions which may affect feeding conditions. We assessed how biological factors such as diet (stable isotopes δ13C and δ15N), the onset of egg laying, and physical characteristics such as winter climate (North Atlantic Oscillation: NAOw) influenced exposure. We predicted compounds to show different temporal trends depending on whether they were still in production (i.e. some PFASs) or have been banned (i.e. legacy OCs and some PFASs). Therefore, we controlled for potential temporal trends in all analyses. There were declining trends for α- and γ-hexachlorocyclohexane (HCH), oxychlordane, cis-chlordane, cis-nonachlor, p,p′-dichlorodiphenyltrichloroethane (p.p′-DDT) and less persistent polychlorinated biphenyl (PCB) congeners (e.g. PCB101). In contrast, the dominant compounds, such as p,p′-dichlorodiphenyldichloroethylene (p,p′-DDE) and persistent PCB congeners, were stable, whereas hexachlorobenzene (HCB) increased over time. Most OCs were positively related to δ15N, suggesting higher exposure in birds feeding at upper trophic levels. Chlordanes and HCB were positively associated with δ13C, indicating traces of marine input for these compounds, whereas the relationships to most PCBs were negative. Among PFASs, perfluorooctanesulfonamide (PFOSA) and perfluorohexane sulfonic acid (PFHxS) declined. Most PFASs were positively associated with δ13C, whereas there were no associations with δ15N. Egg laying date was positively associated to perfluoroheptanesulfonic acid (PFHpS), perfluorooctanesulfonic acid (PFOS) and perfluorooctanoic acid (PFOA), suggesting that some of the PFAS load originated from the wintering locations. Although NAOw had little impact on the exposure to organohalogenated contaminants, factors sensitive to climate change, especially diet, were associated with the exposure to OHCs in goldeneyes.

2022

The impact of climate extremes on the carbon exchange of a Norwegian coastal bog derived from 7 years of observations.

Parmentier, F.-J.; Lund, M.; Hansen, G. H.; Bjerke, J.; Tømmervik, H.; de Wit, H. A.; Weldon, S.; Rasse, D.

2016

The impact of a nickel-copper smelter on concentrations of toxic elements in local wild food from the Norwegian, Finnish, and Russian border regions.

Hansen, M. D.; Nøst, T. H.; Heimstad, E. S.; Evenset, A.; Dudarev, A. A.; Rautio, A.; Myllynen, P.; Dushkina, E. V.; Jagodic, M.; Christensen, G. N.; Anda, E. E.; Brustad, M.; Sandanger, T. M.

2017

The IAGOS-CORE aerosol package: instrument design, operation and performance for continuous measurement aboard in-service aircraft.

Bundke, U.; Berg, M.; Houben, N.; Ibrahim, A.; Fiebig, M.; Tettich, F.; Klaus, C.; Franke, H.; Petzold, A.

2015

The high prevalence of vitamin D insufficiency across Australian populations is only partly explained by season and latitude.

van der Mei, I.A.F.; Ponsonby, A.-L.; Engelsen, O.; Pasco, J.A.; McGrath, J.J.; Eyles, D.W.; Blizzard, L.; Dwyer, T.; Lucas, R.; Jones, G.

2007

The high persistence of PFAS is sufficient for their management as a chemical class

Cousins, Ian T.; Dewitt, Jamie C.; Glüge, Juliane; Goldenman, Gretta; Herzke, Dorte; Lohmann, Rainer; Ng, Carla A.; Scheringer, Martin; Wang, Zhanyun

Per- and polyfluoroalkyl substances (PFAS) are a class of synthetic organic substances with diverse structures, properties, uses, bioaccumulation potentials and toxicities. Despite this high diversity, all PFAS are alike in that they contain perfluoroalkyl moieties that are extremely resistant to environmental and metabolic degradation. The vast majority of PFAS are therefore either non-degradable or transform ultimately into stable terminal transformation products (which are still PFAS). Under the European chemicals regulation this classifies PFAS as very persistent substances (vP). We argue that this high persistence is sufficient concern for their management as a chemical class, and for all “non-essential” uses of PFAS to be phased out. The continual release of highly persistent PFAS will result in increasing concentrations and increasing probabilities of the occurrence of known and unknown effects. Once adverse effects are identified, the exposure and associated effects will not be easily reversible. Reversing PFAS contamination will be technically challenging, energy intensive, and costly for society, as is evident in the efforts to remove PFAS from contaminated land and drinking water sources.

2020

The HERMOSA initiative: Harmonising Environmental Research and Monitoring of Priority Pollutants in the Svalbard Atmosphere

Koziol, Krystyna; Kallenborn, Roland; Nawrot, Adam; NIkulina, Anna; Cappelletti, David; Larose, Catherine; Nikiforov, Vladimir; Zawierucha, Krzysztof; Luks, Bartek; Moroni, Beatrice

2022

The Health and Environment Network and its achievements.

Bartonova, A.; Koppe, J.G.; Fucic, A.; Gutleb, A.; van den Hazel, P.; Keune, H.

2012

The hCOMET project: International database comparison of results with the comet assay in human biomonitoring. Baseline frequency of DNA damage and effect of main confounders

Milić, Mirta; Ceppi, Marcello; Bruzzone, Marco; Azqueta, Amaya; Brunborg, Gunnar; Godschalk, Roger; Koppen, Gudrun; Langie, Sabine; Møller, Peter; Teixeira, João Paulo; Alija, Avdulla; Anderson, Diana; Andrade, Vanessa; Andreoli, Cristina; Asllani, Fisnik; Bangkoglu, Ezgi Eyluel; Barancokova, Magdalena; Basaran, Nursen; Boutet-Robinet, Elisa; Buschini, Annamaria; Cavallo, Delia; Pererira, Cristina Costa; Costa, Carla; Costa, Solange; Silva, Juliana Da; Bo’, Cristian Del; Sreckovic, Vesna Dimitrijevic; Djelic, Ninoslav; Dobrzynska, Malgorzata; Duracková, Zdenka; Dvorakova, Monika; Gajski, Goran; Galati, Serena; Lima, Omar García; Giovannelli, Lisa; Goroshinskaya, Irina A.; Grindel, Annemarie; Gützkow, Kristine Bjerve; Hernández, Alba; Hernandez, Carlos; Holven, Kirsten Bjørklund; Ibero-Baraibar, Idoia; Ottestad, Inger Olaug; Kadioglu, Ela; Kazimirova, Alena; Kuznetsova, Elena; Ladeira, Carina; Laffon, Blanca; Lamonaca, Palma; Lebailly, Pierre; Louro, Henriqueta; Cardoso, Tania Mandina; Marcon, Francesca; Marcos, Ricard; Moretti, Massimo; Moretti, Silvia; Najafzadeh, Mojgan; Nemeth, Zsuzsanna; Neri, Monica; Novotna, Bozena; Orlow, Irene; Paduchova, Zuzana; Pastor, Susana; Perdry, Hervé; Spremo-Potparević, Biljana; Ramadhani, Dwi; Riso, Patrizia; Rohr, Paula; Rojas, Emilio; Rossner, Pavel; Safar, Anna; Sardas, Semra; Silva, Maria João; Sirota, Nikolay; Smolkova, Bozena; Staruchova, Marta; Stetina, Rudolf; Stopper, Helga; Surikova, Ekaterina I.; Ulven, Stine Marie; Ursini, Cinzia Lucia; Valdiglesias, Vanessa; Valverde, Mahara; Vodička, Pavel; Volkovova, Katarina; Wagner, Karl-Heinz; Zivkovic, Lada; Dusinska, Maria; Collins, Andrew Richard; Bonassi, Stefano

The alkaline comet assay, or single cell gel electrophoresis, is one of the most popular methods for assessing DNA damage in human population. One of the open issues concerning this assay is the identification of those factors that can explain the large inter-individual and inter-laboratory variation. International collaborative initiatives such as the hCOMET project - a COST Action launched in 2016 - represent a valuable tool to meet this challenge. The aims of hCOMET were to establish reference values for the level of DNA damage in humans, to investigate the effect of host factors, lifestyle and exposure to genotoxic agents, and to compare different sources of assay variability. A database of 19,320 subjects was generated, pooling data from 105 studies run by 44 laboratories in 26 countries between 1999 and 2019. A mixed random effect log-linear model, in parallel with a classic meta-analysis, was applied to take into account the extensive heterogeneity of data, due to descriptor, specimen and protocol variability. As a result of this analysis interquartile intervals of DNA strand breaks (which includes alkali-labile sites) were reported for tail intensity, tail length, and tail moment (comet assay descriptors). A small variation by age was reported in some datasets, suggesting higher DNA damage in oldest age-classes, while no effect could be shown for sex or smoking habit, although the lack of data on heavy smokers has still to be considered. Finally, highly significant differences in DNA damage were found for most exposures investigated in specific studies. In conclusion, these data, which confirm that DNA damage measured by the comet assay is an excellent biomarker of exposure in several conditions, may contribute to improving the quality of study design and to the standardization of results of the comet assay in human populations.

2021

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