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Cattle egrets as a biosentinels of persistent organic pollutants exposure.

Khan, M.; Mohammad, A.; Ahad, K.; Katsoyiannis, A.; Malik, S.A.; Abdullaha, M.; Rashid, A.; Fasola, M.; Hussain, A.; Bokhari, H.; Eqani, S.A.M.A.S.

2014

Catalysing action towards the sustainability of deltas.

Brondizio, E.S.; Foufoula-Georgiou, E.; Szabo, S.; Vogt, N.; Sebesvari, Z.; Renaud, F.G.; Newton, A.; Anthony, E.; Mansur, A.V.; Matthews, Z.; Hetrick, S.; Costa, S.M.; Tessler, Z.; Tejedor, A.; Longjas, A.; Dearing, J.A.,.

2016

Case study protocol. Air4EU - Air Quality Assessment for Europe: from local to continental scale. Air4EU-D6.1: Protocols for implementation of case studies.

Denby, B. (eds.)

2006

Case study overview.

Denby, B. (eds.)

2007

Case study of the Nidaros Cathedral in Trondheim. NILU OR

Henriksen, J.F.; Dahlin, E.; Navrud, S.

The Nidaros Cathedral has been used as a case study for the "Reach Management System". The two main contributions to the management system has been to obtain direct cost values for maintenance and repair for a historic important building. The second contribution has been on indirect cost, since a willingness to pay study has been performed for the Cathedral. The results from the willingness to pay duly exceeded the average annual budget for the Cathedral with a factor 5.

2001

Case study of the development of polar stratospheric clouds using bistatic imaging.

Enell, C.-F.; Brändström, U.; Gustavsson, B.; Kirkwood, S.; Stebel, K.; Steen, Å.

2003

Case study of "Kristiania Kvadraturen" in Oslo. NILU OR

Henriksen, J.F.; Anda, O.; Ofstad, T.

2001

Case studies on persistence and long-range transport of persistent organic pollutants.

Macdonald, R.W.; Eisenreich, S.J.; Bidleman, T.F.; Dachs, J.; Pacyna, J.M.; Jones, K.C.; Bailey, R.E.; Swackhamer, D.L.; Muir, D.C.G.

2000

Cars Emit More Than Carbon Pollution—They Release Microplastic, Too

Evangeliou, Nikolaos (intervjuobjekt); Funes, Yessenia (journalist)

2020

CARIBIC aircraft measurements of Eyjafjallajökull volcanic clouds in April/May 2010.

Rauthe-Schöch, A.; Weigelt, A.; Hermann, M.; Martinsson, B. G.; Baker, A. K.; Heue, K.-P.; Brenninkmeijer, C.A.M.; Zahn, A.; Scharffe, D.; Eckhardt, S.; Stohl, A.; van Velthoven, P.F.J.

2012

Carbonaceous aerosols in Norwegian urban areas.

Yttri, K.E.; Dye, C.; Braathen, O.-A.; Simpson, D.; Steinnes, E.

2009

Carbon–nitrogen interactions in European forests and semi-natural vegetation – Part 1: Fluxes and budgets of carbon, nitrogen and greenhouse gases from ecosystem monitoring and modelling

Flechard, Chris R.; Ibrom, Andreas; Skiba, Ute; de Vries, Wim; Van Oijen, Marcel; Cameron, David R.; Dise, Nancy B.; Korhonen, Janne; Buchmann, Nina; Legout, Arnaud; Simpson, David; Sanz, Maria J.; Aubinet, Marc; Loustau, Denis; Montagnani, Leonardo; Neirynck, Johan; Janssens, Ivan A.; Pihlatie, Mari; Kiese, Ralf; Siemens, Jan; Francez, Andre-Jean; Augustin, Jurgen; Varlagin, Andrej; Olejnik, Janusz; Juszczak, Radoslaw; Aurela, Mika; Berveiller, Daniel; Chojnicki, Bogdan H.; Dämmgen, Urich; Delpierre, Nicolas; Djuricic, Vesna; Drewer, Julia; Dufrene, Eric; Eugster, Werner; Fauvel, Yannick; Fowler, David; Frumau, Arnoud; Granier, Andre; Gross, Patrick; Hamon, Yannick; Helfter, Carole; Hensen, Arjan; Horvath, Laszlo; Kitzler, Barbara; Kruijt, Bart; Kutsch, Werner; Lobo-do-Vale, Raquel; Lohila, Annalea; Longdoz, Bernard; Marek, Michal V.; Matteucci, Giorgio; Mitosinkova, Marta; Moreaux, Virginie; Neftel, Albrecht; Ourcival, Jean-Marc; Pilegaard, Kim; Pita, Gabriel; Sanz, Francisco; Schjoerring, Jan K.; Sebastià, Maria-Teresa; Tang, Y. Sim; Uggerud, Hilde Thelle; Urbaniak, Marek; van Dijk, Netty; Vesala, Timo; Vidic, Sonja; Vincke, Caroline; Weidinger, Tamas; Sechmeister-Boltenstern, Sophie; Butterbach-Bahl, Klaus; Nemitz, Eiko; Sutton, Mark A.

2020

Carbon and other biogeochemical cycles.

Ciais, P.; Sabine, C.; Bala, G.; Bopp, L.; Brovkin, V.; Canadell, J.; Chhabra, A.; DeFries, R.; Galloway, J.; Heimann, M.; Jones, C.; Le Quéré, C.; Myneni, R. B.; Piao, S.; Thornton, P. [Among contributing authors: Thompson, R. L.].

2013

Carbon and Greenhouse Gas Budgets of Europe: Trends, Interannual and Spatial Variability, and Their Drivers

Lauerwald, Ronny; Bastos, Ana; McGrath, Matthew J.; Petrescu, Ana Maria Roxana; Ritter, François; Andrew, Robbie; Berchet, Antoine; Broquet, Grégoire; Brunner, Dominik; Chevallier, Frédéric; Cescatti, Alessandro; Filipek, Sara; Fortems-Cheiney, Audrey; Forzieri, Giovanni; Friedlingstein, Pierre; Fuchs, Richard; Gerbig, Christoph; Houweling, Sanne; Ke, Piyu; Lerink, Bas J. W.; Li, Wanjing; Li, Wei; Li, Xiaojun; Luijkx, Ingrid; Monteil, Guillaume; Munassar, Saqr; Nabuurs, Gert-Jan; Patra, Prabir K.; Peylin, Philippe; Pongratz, Julia; Regnier, Pierre; Saunois, Marielle; Schelhaas, Mart-Jan; Scholze, Marko; Sitch, Stephen; Thompson, Rona Louise; Tian, Hanqin; Tsuruta, Aki; Wilson, Chris; Wigneron, Jean-Pierre; Yao, Yitong; Zaehle, Sönke; Ciais, Philippe

In the framework of the RECCAP2 initiative, we present the greenhouse gas (GHG) and carbon (C) budget of Europe. For the decade of the 2010s, we present a bottom-up (BU) estimate of GHG net-emissions of 3.9 Pg CO2-eq. yr−1 (using a global warming potential on a 100 years horizon), which are largely dominated by fossil fuel emissions. In this decade, terrestrial ecosystems acted as a net GHG sink of 0.9 Pg CO2-eq. yr−1, dominated by a CO2 sink that was partially counterbalanced by net emissions of CH4 and N2O. For CH4 and N2O, we find good agreement between BU and top-down (TD) estimates from atmospheric inversions. However, our BU land CO2 sink is significantly higher than the TD estimates. We further show that decadal averages of GHG net-emissions have declined by 1.2 Pg CO2-eq. yr−1 since the 1990s, mainly due to a reduction in fossil fuel emissions. In addition, based on both data driven BU and TD estimates, we also find that the land CO2 sink has weakened over the past two decades. A large part of the European CO2 and C sinks is located in Northern Europe. At the same time, we find a decreasing trend in sink strength in Scandinavia, which can be attributed to an increase in forest management intensity. These are partly offset by increasing CO2 sinks in parts of Eastern Europe and Northern Spain, attributed in part to land use change. Extensive regions of high CH4 and N2O emissions are mainly attributed to agricultural activities and are found in Belgium, the Netherlands and the southern UK. We further analyzed interannual variability in the GHG budgets. The drought year of 2003 shows the highest net-emissions of CO2 and of all GHGs combined.

American Geophysical Union (AGU)

2024

Car Tires Contain a Cocktail of Chemicals: Their Characterization, Leaching and Bioavailability

Booth, Andy; Sørensen, Lisbet; Halsband-Lenk, Claudia; Herzke, Dorte

2021

Car Tire Crumb Rubber: Does Leaching Produce a Toxic Chemical Cocktail in Coastal Marine Systems?

Halsband-Lenk, Claudia; Sørensen, Lisbet; Booth, Andy; Herzke, Dorte

Crumb rubber granulate (CRG) produced from end of life tires (ELTs) is commonly applied to synthetic turf pitches (STPs), playgrounds, safety surfaces and walkways. In addition to fillers, stabilizers, cross-linking agents and secondary components (e.g., pigments, oils, resins), ELTs contain a range of other organic compound and heavy metal additives. While previous environmental impact studies on CRG have focused on terrestrial soil and freshwater ecosystems, many sites applying CRG in Norway are coastal. The current study investigated the organic chemical and metal additive content of ‘pristine’ and ‘weathered’ CRG and their seawater leachates, as well as uptake and effects of leachate exposure using marine copepods (Acartia and Calanus sp.). A combination of pyrolysis gas chromatography mass spectrometry (py-GC-MS) and chemical extraction followed by GC-MS analysis revealed similar organic chemical profiles for pristine and weathered CRG, including additives such as benzothiazole, N-1,3-dimethylbutyl-N′-phenyl-p-phenylenediamine and a range of polycyclic aromatic hydrocarbons (PAHs) and phenolic compounds (e.g., bisphenols). ICP-MS analysis revealed g kg–1 quantities of Zn and mg kg–1 quantities of Fe, Mn, Cu, Co, Cr, Pb, and Ni in the CRG. A cocktail of organic additives and metals readily leached from the CRG into seawater, with the most abundant leachate components being benzothiazole and Zn, Fe, Co (metals), as well as detectable levels of PAHs and phenolic compounds. Concentrations of individual components varied with CRG source material and CRG to seawater ratio, but benzothiazole and Zn were typically the organic and metal components present at the highest concentrations in the leachates. While organic chemical concentrations in the leachates stabilized within days, metals continued to leach out over the 30-day period. Marine copepods exposed to high CRG leachate concentrations exhibited high mortalities within 48 h. The smaller lipid-poor Acartia had a higher sensitivity to leachates than the larger lipid-rich Calanus, indicating species-specific differences in vulnerability to leachates. The effect on survival was alleviated at lower leachate concentrations, indicating a dose-response relationship. Benzothiazole and its derivatives appear to be of concern owing to their proven toxicity, while bisphenols are also known to be toxic and were enriched in the leachates relative to the other compounds in the CRG.

Frontiers Media S.A.

2020

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