200 results on '"Herzke D"'
Search Results
2. Combining advanced analytical methodologies to uncover suspect PFAS and fluorinated pharmaceutical contributions to extractable organic fluorine in human serum (Tromsø Study)
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Cioni, L., Nikiforov, V., Benskin, J.P., Coêlho, A.C.M.F., Dudášová, Silvia, Lauria, M.Z., Lechtenfeld, Oliver, Plassmann, M.M., Reemtsma, Thorsten, Sandanger, T.M., Herzke, D., Cioni, L., Nikiforov, V., Benskin, J.P., Coêlho, A.C.M.F., Dudášová, Silvia, Lauria, M.Z., Lechtenfeld, Oliver, Plassmann, M.M., Reemtsma, Thorsten, Sandanger, T.M., and Herzke, D.
- Abstract
A growing number of studies have reported that routinely monitored per- and polyfluoroalkyl substances (PFAS) are not sufficient to explain the extractable organic fluorine (EOF) measured in human blood. In this study, we address this gap by screening pooled human serum collected over 3 decades (1986–2015) in Tromsø (Norway) for >5000 PFAS and >300 fluorinated pharmaceuticals. We combined multiple analytical techniques (direct infusion Fourier transform ion cyclotron resonance mass spectrometry, liquid chromatography-Orbitrap-high-resolution mass spectrometry, and total oxidizable precursors assay) in a three-step suspect screening process which aimed at unequivocal suspect identification. This approach uncovered the presence of one PFAS and eight fluorinated pharmaceuticals (including some metabolites) in human serum. While the PFAS suspect only accounted for 2–4% of the EOF, fluorinated pharmaceuticals accounted for 0–63% of the EOF, and their contribution increased in recent years. Although fluorinated pharmaceuticals often contain only 1–3 fluorine atoms, our results indicate that they can contribute significantly to the EOF. Indeed, the contribution from fluorinated pharmaceuticals allowed us to close the organofluorine mass balance in pooled serum from 2015, indicating a good understanding of organofluorine compounds in humans. However, a portion of the EOF in human serum from 1986 and 2007 still remained unexplained.
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- 2024
3. The time for ambitious action is now: Science-based recommendations for plastic chemicals to inform an effective global plastic treaty
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Brander, S.M., Senathirajah, K., Fernandez, M.O., Weis, J.S., Kumar, E., Jahnke, Annika, Hartmann, N.B., Alava, J.J., Farrelly, T., Carney Almroth, B., Groh, K.J., Syberg, K., Buerkert, J.S., Abeynayaka, A., Booth, A.M., Cousin, X., Herzke, D., Monclús, L., Morales-Caselles, C., Bonisoli-Alquati, A., Al-jaibachi, R., Wagner, M., Brander, S.M., Senathirajah, K., Fernandez, M.O., Weis, J.S., Kumar, E., Jahnke, Annika, Hartmann, N.B., Alava, J.J., Farrelly, T., Carney Almroth, B., Groh, K.J., Syberg, K., Buerkert, J.S., Abeynayaka, A., Booth, A.M., Cousin, X., Herzke, D., Monclús, L., Morales-Caselles, C., Bonisoli-Alquati, A., Al-jaibachi, R., and Wagner, M.
- Abstract
The ubiquitous and global ecological footprint arising from the rapidly increasing rates of plastic production, use, and release into the environment is an important modern environmental issue. Of increasing concern are the risks associated with at least 16,000 chemicals present in plastics, some of which are known to be toxic, and which may leach out both during use and once exposed to environmental conditions, leading to environmental and human exposure. In response, the United Nations member states agreed to establish an international legally binding instrument on plastic pollution, the global plastics treaty. The resolution acknowledges that the treaty should prevent plastic pollution and its related impacts, that effective prevention requires consideration of the transboundary nature of plastic production, use and pollution, and that the full life cycle of plastics must be addressed. As a group of scientific experts and members of the Scientists' Coalition for an Effective Plastics Treaty, we concur that there are six essential “pillars” necessary to truly reduce plastic pollution and allow for chemical detoxification across the full life cycle of plastics. These include a plastic chemical reduction and simplification, safe and sustainable design of plastic chemicals, incentives for change, holistic approaches for alternatives, just transition and equitable interventions, and centering human rights. There is a critical need for scientifically informed and globally harmonized information, transparency, and traceability criteria to protect the environment and public health. The right to a clean, healthy, and sustainable environment must be upheld, and thus it is crucial that scientists, industry, and policy makers work in concert to create a future free from hazardous plastic contamination.
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- 2024
4. Persistent organic pollutants and organophosphate esters in feathers and blood plasma of adult kittiwakes (Rissa tridactyla) from Svalbard – associations with body condition and thyroid hormones
- Author
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Svendsen, N.B., Herzke, D., Harju, M., Bech, C., Gabrielsen, G.W., and Jaspers, V.L.B.
- Published
- 2018
- Full Text
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5. Leaching of chemicals and DOC from tire particles under simulated marine conditions
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Foscari, Aurelio Giovanni, Schmidt, N., Seiwert, Bettina, Herzke, D., Sempéré, R., Reemtsma, Thorsten, Foscari, Aurelio Giovanni, Schmidt, N., Seiwert, Bettina, Herzke, D., Sempéré, R., and Reemtsma, Thorsten
- Abstract
Tire wear particles (TWPs) represent one of the major anthropogenic pools of particles ending up in the environment. They contain a large variety of chemicals, a part of which may be released into the environment through leaching, although the influence of sunlight and other environmental factors during this process is still unclear. This laboratory study compares the leaching of organic compounds from TWP in seawater in the dark and under artificial sunlight for (i) cryo-milled tire tread (CMTT), (ii) ‘virgin’ crumb rubber (VCR) and (iii) crumb rubber immersed in the sea for ≥ 12 months prior to the experiments (WCR). Leachates were analyzed for dissolved organic carbon (DOC) and 19 tire-derived chemicals, benzothiazoles and phenylguanidines as well as phenylendiamines by liquid chromatography-high resolution-mass spectrometry. For DOC and most chemicals, the amounts released decreased in the order CMTT > VCR > WCR and increased when leaching occurred under artificial sunlight. Sunlight also led to the formation of 23 transformation processes related to 1,3-diphenylguanidine (DPG). In contrast, 4-hydroxydiphenylamine (4-HDPA) and N-(1,3-dimethylbutyl)-N’-phenyl-p-phenylenediamine quinone (6-PPDQ) were found in lower amounts upon sunlight exposure. The 19 quantified chemicals, however, did only account for 6 – 55% of the DOC in the leachates; most of the DOC, thus, remained unexplained. This study highlights that the amount of chemicals leached from tire particles depends upon their aging history and may be modulated by environmental conditions.
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- 2023
6. CEC04-01 Introduction to environmental pollution.
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Herzke, D.
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POLLUTION - Published
- 2024
- Full Text
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7. List of Contributors
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Abbas, B., primary, Abreu, A., additional, Adams, R., additional, Adolfsson-Erici, M., additional, Afonso, A., additional, Afonso-Olivares, C., additional, Agirbas, E., additional, Aguiló, J.M., additional, Airoldi, L., additional, Aksoy, H., additional, Albentosa, M., additional, Alcaro, L., additional, Aliani, S., additional, Al-Maslamani, I., additional, Alomar, C., additional, Altin, D., additional, Álvarez, E., additional, Amaral-Zettler, L.A., additional, Amato, E., additional, Anderson, A., additional, Andrady, A.L., additional, Andrius, G., additional, Angel, D., additional, Ariese, F., additional, Arp, H.P., additional, Asensio, M., additional, Assidqi, K., additional, Avio, C.G., additional, Aytan, U., additional, Bahri, T., additional, Baini, M., additional, Bakir, A., additional, Ball, H., additional, Baranyi, C., additional, Barboza, L.G.A., additional, Barg, U., additional, Bargelloni, L., additional, Barras, H., additional, Barrera, C., additional, Barria, P., additional, Barrows, A., additional, Barth, A., additional, Batel, A., additional, Baztan, J., additional, Baztan, P., additional, Beiras, R., additional, Benedetti, M., additional, Berber, A.A., additional, Berber, N., additional, Bergmann, M., additional, Berlino, M., additional, Berrow, S., additional, Bessa, F., additional, Besseling, E., additional, Beyer, B., additional, Binaglia, M., additional, Bizjak, T., additional, Bjorndal, K.A., additional, Blust, R., additional, Boertien, M., additional, Bolten, A.B., additional, Booth, A.M., additional, Bounoua, B., additional, Bourseau, P., additional, Brahimi, N., additional, Bramini, M., additional, Brennholt, N., additional, Breuninger, E., additional, Bried, J., additional, Broderick, A., additional, Broglio, E., additional, Browne, M.A., additional, Bruzaud, S., additional, Buceta, J., additional, Buchinger, S., additional, Budimir, S., additional, Budzin-ski, H., additional, Butter, E., additional, Cachot, J., additional, Caetano, M., additional, Callaghan, A., additional, Camedda, A., additional, Capella, S., additional, Cardelli, L., additional, Carpentieri, S., additional, Carrasco, A., additional, Carriço, R., additional, Caruso, A., additional, Cassone, A.-L., additional, Castillo, A., additional, Castro, R.O., additional, Catarino, A.I., additional, Cazenave, P.W., additional, Çelik, İ., additional, Cerralbo, P., additional, César, G., additional, Chouinard, O., additional, Chubarenko, I., additional, Chubarenko, I.P., additional, Cicero, A.M., additional, Clarindo, G., additional, Clarke, B., additional, Clérandeau, C., additional, Clüsener-Godt, M., additional, Codina-García, M., additional, Cole, M., additional, Collard, F., additional, Collignon, A., additional, Collins, T., additional, Compa, M., additional, Conan, P., additional, Constant, M., additional, Cordier, M., additional, Courtene-Jones, W., additional, Cousin, X., additional, Covelo, P., additional, Cózar, A., additional, Crichton, E., additional, Crispi, O., additional, Cronin, M., additional, Croot, P.L., additional, Cruz, M.J., additional, d’Errico, G., additional, Dâmaso, C., additional, Das, K., additional, de Alencastro, L.F., additional, de Araujo, F.V., additional, de Boer, J.F., additional, de Lucia, G.A., additional, Debeljak, P., additional, Dehaut, A., additional, Deudero, S., additional, Devrieses, L., additional, Di Vito, S., additional, Díaz, A., additional, Donohue, J., additional, Doumenq, P., additional, Doyle, T.K., additional, Dris, R., additional, Druon, J.-N., additional, Duarte, C.M., additional, Duflos, G., additional, Dumontier, M., additional, Duncan, E., additional, Dussud, C., additional, Eckerlebe, A., additional, Egelkraut-Holtus, M., additional, Eidsvoll, D.P., additional, Ek, C., additional, Elena, S., additional, Elineau, A., additional, Enevoldsen, H., additional, Eppe, G., additional, Eriksen, M., additional, Ernsteins, R., additional, Espino, M., additional, Estévez-Calvar, N., additional, Ewins, C., additional, Fabre, P., additional, Faimali, M., additional, Fattorini, D., additional, Faure, F., additional, Ferrando, S., additional, Ferreira, J.C., additional, Ferreira-da-Costa, M., additional, Fileman, E., additional, Fischer, M., additional, Fortunato, A.B., additional, Fossi, M.C., additional, Foulon, V., additional, Frank, A., additional, Frenzel, M., additional, Frère, L., additional, Frias, J.P.G.L., additional, Frick, H., additional, Froneman, P.W., additional, Gabet, V.M., additional, Gabrielsen, G.W., additional, Gago, J., additional, Gajst, T., additional, Galgani, F., additional, Gallinari, M., additional, Galloway, T.S., additional, Gamarro, E.G., additional, Gambardella, C., additional, Garaventa, F., additional, Garcia, S., additional, Garrabou, J., additional, Garrido, P., additional, Gary, S.F., additional, Gasperi, J., additional, Gaze, W., additional, Geertz, T., additional, Gelado-Caballero, M.D., additional, George, M., additional, Gercken, J., additional, Gerdts, G., additional, Ghiglione, J.-F., additional, Gies, E., additional, Gilbert, B., additional, Giménez, L., additional, Glassom, D., additional, Glockzin, M., additional, Godley, B., additional, Goede, K., additional, Goksøyr, A., additional, Gómez, M., additional, Gómez-Parra, A., additional, González-Marco, D., additional, González-Solís, J., additional, Gorbi, S., additional, Gorokhova, E., additional, Gorsky, G., additional, Gosch, M., additional, Grose, J., additional, Guebitz, G.M., additional, Guedes-Alonso, R., additional, Guijarro, B., additional, Guilhermino, L., additional, Gundry, T., additional, Gutow, L., additional, Haave, M., additional, Haeckel, M., additional, Haernvall, K., additional, Hajbane, S., additional, Hamann, M., additional, Hämer, J., additional, Hamm, T., additional, Hansen, B.H., additional, Hardesty, B.D., additional, Harth, B., additional, Hartikainen, S., additional, Hassellöv, M., additional, Hatzky, S., additional, Healy, M.G., additional, Hégaret, H., additional, Henry, T.B., additional, Hermabessiere, L., additional, Hernández-Brito, J.J., additional, Hernandez-Gonzalez, A., additional, Hernandez-Milian, G., additional, Hernd, G., additional, Herrera, A., additional, Herring, C., additional, Herzke, D., additional, Heussner, S., additional, Hidalgo-Ruz, V., additional, Himber, C., additional, Holland, M., additional, Hong, N.-H., additional, Horton, A.A., additional, Horvat, P., additional, Huck, T., additional, Huhn, M., additional, Huvet, A., additional, Iglesias, M., additional, Igor, C., additional, Isachenko, I.A., additional, Ivar do Sul, J-A., additional, Jahnke, A., additional, Janis, B., additional, Janis, K., additional, Janis, U., additional, Jemec, A., additional, Jiménez, J.C., additional, Johnsen, H., additional, Jorgensen, B., additional, Jørgensen, J.H., additional, Jörundsdóttir, H., additional, Jung, Y.-J., additional, Kedzierski, M., additional, Keiter, S., additional, Kershaw, P., additional, Kerhervé, P., additional, Kesy, K., additional, Khan, F., additional, Khatmullina, L.I., additional, Kirby, J., additional, Kiriakoulakis, K., additional, Klein, R., additional, Klunderud, T., additional, Knudsen, C.M.H., additional, Knudsen, T.B., additional, Kochleus, C., additional, Koelmans, A.A., additional, Kögel, T., additional, Koistinen, A., additional, Kopke, K., additional, Korez, Š., additional, Kowalski, N., additional, Kreikemeyer, B., additional, Kroon, F., additional, Krumpen, T., additional, Krzan, A., additional, Kržan, A., additional, Labrenz, M., additional, Lacroix, C., additional, Ladirat, L., additional, Laforsch, C., additional, Lagarde, F., additional, Lahive, E., additional, Lambert, C., additional, Lapucci, C., additional, Lattin, G., additional, Law, K.L., additional, Le Roux, F., additional, Le Souef, K., additional, Le Tilly, V., additional, Lebreton, L., additional, Leemans, E., additional, Lehtiniemi, M., additional, Lenz, M., additional, Leskinen, J., additional, Leslie, H., additional, Leslie, H.A., additional, Levasseur, C., additional, Lewis, C., additional, Licandro, P., additional, Lind, K., additional, Lindeque, P., additional, Lindeque, P.K., additional, Lips, I., additional, Liria, A., additional, Liria-Loza, A., additional, Llinás, O., additional, Loiselle, S.A., additional, Long, M., additional, Lorenz, C., additional, Lorenzo, S.M., additional, Loubar, K., additional, Luna-Jorquera, G., additional, Lusher, A.L., additional, Macchia, V., additional, MacGabban, S., additional, Mackay, K., additional, MacLeod, M., additional, Maes, T., additional, Magaletti, E., additional, Maggiore, A., additional, Magnusson, K., additional, Mahon, A.M., additional, Makorič, P., additional, Mallow, O., additional, Marques, J., additional, Marsili, L., additional, Martí, E., additional, Martignac, M., additional, Martin, J., additional, Martínez, I., additional, Martínez, J., additional, Martinez-Gil, M., additional, Martins, H.R., additional, Matiddi, M., additional, Maximenko, N., additional, Mazlum, R., additional, Mcadam, R., additional, Mcknight, L., additional, McNeal, A.W., additional, Measures, J., additional, Mederos, M.S., additional, Mendoza, J., additional, Meyer, M.S., additional, Miguelez, A., additional, Milan, M., additional, Militão, T., additional, Miller, R.Z., additional, Mino-Vercellio-Verollet, M., additional, Mir, G., additional, Miranda-Urbina, D., additional, Misurale, F., additional, Montesdeoca-Esponda, S., additional, Mora, J., additional, Morgana, S., additional, Moriceau, B., additional, Morin, B., additional, Morley, A., additional, Morrison, L., additional, Murphy, F., additional, Naidoo, T., additional, Näkki, P., additional, Napper, I.E., additional, Narayanaswamy, B.E., additional, Nash, R., additional, Negri, A., additional, Nel, H.A., additional, Nerheim, M.S., additional, Nerland, I.L., additional, Neto, J., additional, Neves, V., additional, Nies, H., additional, Noel, M., additional, Nor, N.H.M., additional, Noren, F., additional, O’ Connell, B., additional, O’ Connor, I., additional, Obbard, J.P., additional, Oberbeckmann, S., additional, Obispo, R., additional, Officer, R., additional, Ogonowski, M., additional, Orbea, A., additional, Ortlieb, M., additional, Osborn, A.M., additional, Ostiategui-Francia, P., additional, Packard, T., additional, Pahl, S., additional, Palatinus, A., additional, Palmqvist, A., additional, Pannetier, P., additional, Panti, C., additional, Parmentier, E., additional, Pasanen, P., additional, Patarnello, T., additional, Pattiaratchi, C., additional, Pauletto, M., additional, Paulus, M., additional, Pavlekovsky, K., additional, Pedersen, H.B., additional, Pedrotti, M.-L., additional, Peeken, I., additional, Peeters, D., additional, Peeters, E., additional, Pellegrini, D., additional, Perales, J.A., additional, Perez, E., additional, Perz, V., additional, Petit, S., additional, Pflieger, M., additional, Pham, C.K., additional, Piazza, V., additional, Pinto, M., additional, Planells, O., additional, Plaza, M., additional, Pompini, O., additional, Potthoff, A., additional, Prades, L., additional, Primpke, S., additional, Proietti, M., additional, Proskurowski, G., additional, Puig, C., additional, Pujo-Pay, M., additional, Pullerits, K., additional, Queirós, A.M., additional, Quinn, B., additional, Raimonds, E., additional, Ramis-Pujol, J., additional, Rascher-Friesenhausen, R., additional, Reardon, E., additional, Regoli, F., additional, Reichardt, A.M., additional, Reifferscheid, G., additional, Reilly, K., additional, Reisser, J., additional, Riba, I., additional, Ribitsch, D., additional, Rinnert, E., additional, Rios, N., additional, Rist, S.E., additional, Rivadeneira, M.M., additional, Rivière, G., additional, Robbens, J., additional, Robertson, C.J.R., additional, Rocher, V., additional, Rochman, C.M., additional, Rodrigues, M., additional, Rodriguez, Y., additional, Rodríguez, A., additional, Rodríguez, G., additional, Rodríguez, J.R.B., additional, Rodríguez, S., additional, Rodríguez, Y., additional, Rogan, E., additional, Rojo-Nieto, E., additional, Romeo, T., additional, Ross, P.S., additional, Roveta, A., additional, Rowland, S.J., additional, Ruckstuhl, N.A., additional, Ruiz-Fernández, A-C., additional, Ruiz-Orejón, L.F., additional, Runge, J., additional, Russell, M., additional, Saavedra, C., additional, Saborowski, R., additional, Sahin, B.E., additional, Sailley, S., additional, Sakaguchi-Söder, K., additional, Salaverria, I., additional, Sánchez-Arcilla, A., additional, Sánchez-Nieva, J., additional, Sanderson, W., additional, Santana-Rodríguez, J.J., additional, Santana-Viera, S., additional, Santos, M.B., additional, Santos, M.R., additional, Sanz, M.R., additional, Sardá, R., additional, Savelli, H., additional, Schoeneich-Argent, R., additional, Scholz-Böttcher, B.M., additional, Sciacca, F., additional, Scofield, R.P., additional, Setälä, O., additional, Selenius, M., additional, Sempere, R., additional, Senturk, Y., additional, Shashoua, Y., additional, Sherman, P., additional, Sick, C., additional, Siegel, D., additional, Sierra, J.P., additional, Silva, F., additional, Silvestri, C., additional, Sintija, G., additional, Sire, O., additional, Slat, B., additional, Smit, A., additional, Sobral, P., additional, Sorvari, J., additional, Sosa-Ferrera, Z., additional, Sotillo, M.G., additional, Soudant, P., additional, Speidel, L., additional, Spurgeon, D.J., additional, Steer, M.K., additional, Steindal, C.C., additional, Stifanese, R., additional, Štindlová, A., additional, Stuurman, L., additional, Suaria, G., additional, Suazo, C.G., additional, Sureda, A., additional, Surette, C., additional, Svendsen, C., additional, Syberg, K., additional, Tairova, Z., additional, Talvitie, J., additional, Tassin, B., additional, Tazerout, M., additional, Tekman, M.B., additional, ter Halle, A., additional, Thiel, M., additional, Thomas, K.V., additional, Thompson, R.C., additional, Tinkara, T., additional, Tirelli, V., additional, Tomassetti, P., additional, Toorman, E., additional, Toppe, J., additional, Tornambè, A., additional, Torres, R., additional, Torres-Padrón, M.E., additional, Underwood, A.J., additional, Urbina, M., additional, Usategui-Martín, A., additional, Usta, R., additional, Valdés, L., additional, Valente, A., additional, Valentina, T., additional, van Arkel, K., additional, Van Colen, C., additional, Van Der Hal, N., additional, van Franeker, J.A., additional, Van Herwerden, L., additional, Van Loosdrecht, M., additional, van Oyen, A., additional, Vandeperre, F., additional, Vanderlinden, J-P., additional, Vani, D., additional, Vasconcelos, L., additional, Vega-Moreno, D., additional, Ventero, A., additional, Vethaak, A.D., additional, Vianello, A., additional, Vicioso, M., additional, Vieira, L.R., additional, Viršek, M.K., additional, Vos, M., additional, Wahl, M., additional, Wallace, N., additional, Walton, A., additional, Waniek, J.J., additional, Watts, A., additional, Webster, L., additional, Wesch, C., additional, Whitfield, E., additional, Wichels, A., additional, Wieczorek, A.M., additional, Wilcox, C., additional, Williams, R.J., additional, Wong-Wah-Chung, P., additional, Wright, S., additional, Wyles, K.J., additional, Young, R., additional, Yurtsever, M., additional, Yurtsever, U., additional, Zada, L., additional, Zamani, N.P., additional, and Zampetti, G., additional
- Published
- 2017
- Full Text
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8. Defining the Baselines and Standards for Microplastics Analyses in European Waters (JPI-O BASEMAN)
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Gerdts, G., primary, Thomas, K., additional, Herzke, D., additional, Haeckel, M., additional, Scholz-Böttcher, B., additional, Laforsch, C., additional, Lagarde, F., additional, Mahon, A.M., additional, Pedrotti, M.L., additional, de Lucia, G.A., additional, Sobral, P., additional, Gago, J., additional, Lorenzo, S.M., additional, Noren, F., additional, Hassellöv, M., additional, Kögel, T., additional, Tirelli, V., additional, Caetano, M., additional, Collignon, A., additional, Lips, I., additional, Mallow, O., additional, Seatala, O., additional, Goede, K., additional, and Licandro, P., additional
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- 2017
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9. PLASTOX: Direct and Indirect Ecotoxicological Impacts of Microplastics on Marine Organisms
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Booth, A., primary, Sakaguchi-Söder, K., additional, Sobral, P., additional, Airoldi, L., additional, Sempere, R., additional, Van Franeker, J.A., additional, Magnusson, K., additional, Doyle, T., additional, Salaverria, I., additional, Van Colen, C., additional, Herzke, D., additional, Orbea, A., additional, Gabrielsen, G.W., additional, Nies, H., additional, and Galloway, T., additional
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- 2017
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10. Tracking pan-continental trends in environmental contamination using sentinel raptors—what types of samples should we use?
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Espín, S., García-Fernández, A. J., Herzke, D., Shore, R. F., van Hattum, B., Martínez-López, E., Coeurdassier, M., Eulaers, I., Fritsch, C., Gómez-Ramírez, P., Jaspers, V. L. B., Krone, O., Duke, G., Helander, B., Mateo, R., Movalli, P., Sonne, C., and van den Brink, N. W.
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- 2016
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11. Correspondence regarding the Perspective “Addressing the importance of microplastic particles as vectors for long-range transport of chemical contaminants: perspective in relation to prioritizing research and regulatory actions”
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Glüge, Juliane, Ashta, N.M., Herzke, D., Lebreton, L., Scheringer, M., Glüge, Juliane, Ashta, N.M., Herzke, D., Lebreton, L., and Scheringer, M.
- Abstract
Important clarifications regarding the long-range environmental transport of chemical additives contained in floating plastic debris are presented.
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- 2022
12. Corrigendum to “Per- and polyfluoroalkyl substances in plasma and feathers of nestling birds of prey from Northern Norway” [Environ. Res. 158 (2017) 277–285]
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Gómez-Ramírez, P., Bustnes, J. O., Eulaers, I., Herzke, D., Johnsen, T. V., Lepoint, G., Pérez-García, J. M., García-Fernández, A. J., and Jaspers, V. L.B.
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- 2017
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13. Per- and polyfluoroalkyl substances in plasma and feathers of nestling birds of prey from northern Norway
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Gómez-Ramírez, P., Bustnes, J. O., Eulaers, I., Herzke, D., Johnsen, T. V., Lepoint, G., Pérez-García, J. M., García-Fernández, A. J., and Jaspers, V. L.B.
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- 2017
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14. The NORMAN Association and the European Partnership for Chemicals Risk Assessment (PARC): let’s cooperate!
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Dulio, V. Koschorreck, J. van Bavel, B. van den Brink, P. Hollender, J. Munthe, J. Schlabach, M. Aalizadeh, R. Agerstrand, M. Ahrens, L. Allan, I. Alygizakis, N. Barcelo’, D. Bohlin-Nizzetto, P. Boutroup, S. Brack, W. Bressy, A. Christensen, J.H. Cirka, L. Covaci, A. Derksen, A. Deviller, G. Dingemans, M.M.L. Engwall, M. Fatta-Kassinos, D. Gago-Ferrero, P. Hernández, F. Herzke, D. Hilscherová, K. Hollert, H. Junghans, M. Kasprzyk-Hordern, B. Keiter, S. Kools, S.A.E. Kruve, A. Lambropoulou, D. Lamoree, M. Leonards, P. Lopez, B. López de Alda, M. Lundy, L. Makovinská, J. Marigómez, I. Martin, J.W. McHugh, B. Miège, C. O’Toole, S. Perkola, N. Polesello, S. Posthuma, L. Rodriguez-Mozaz, S. Roessink, I. Rostkowski, P. Ruedel, H. Samanipour, S. Schulze, T. Schymanski, E.L. Sengl, M. Tarábek, P. Ten Hulscher, D. Thomaidis, N. Togola, A. Valsecchi, S. van Leeuwen, S. von der Ohe, P. Vorkamp, K. Vrana, B. Slobodnik, J.
- Abstract
The Partnership for Chemicals Risk Assessment (PARC) is currently under development as a joint research and innovation programme to strengthen the scientific basis for chemical risk assessment in the EU. The plan is to bring chemical risk assessors and managers together with scientists to accelerate method development and the production of necessary data and knowledge, and to facilitate the transition to next-generation evidence-based risk assessment, a non-toxic environment and the European Green Deal. The NORMAN Network is an independent, well-established and competent network of more than 80 organisations in the field of emerging substances and has enormous potential to contribute to the implementation of the PARC partnership. NORMAN stands ready to provide expert advice to PARC, drawing on its long experience in the development, harmonisation and testing of advanced tools in relation to chemicals of emerging concern and in support of a European Early Warning System to unravel the risks of contaminants of emerging concern (CECs) and close the gap between research and innovation and regulatory processes. In this commentary we highlight the tools developed by NORMAN that we consider most relevant to supporting the PARC initiative: (i) joint data space and cutting-edge research tools for risk assessment of contaminants of emerging concern; (ii) collaborative European framework to improve data quality and comparability; (iii) advanced data analysis tools for a European early warning system and (iv) support to national and European chemical risk assessment thanks to harnessing, combining and sharing evidence and expertise on CECs. By combining the extensive knowledge and experience of the NORMAN network with the financial and policy-related strengths of the PARC initiative, a large step towards the goal of a non-toxic environment can be taken. © 2020, The Author(s).
- Published
- 2020
15. The NORMAN Association and the European Partnership for Chemicals Risk Assessment (PARC): let’s cooperate!
- Author
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Dulio, V., Koschorreck, J., van Bavel, B., van den Brink, P., Hollender, J., Munthe, J., Schlabach, M., Aalizadeh, R., Agerstrand, M., Ahrens, L., Allan, I., Alygizakis, N., Barcelo, D., Bohlin‑Nizzetto, P., Boutroup, S., Brack, Werner, Bressy, A., Christensen, J.H., Cirka, L., Covaci, A., Derksen, A., Deviller, G., Dingemans, M.M.L., Engwall, M., Fatta-Kassinos, D., Gago‑Ferrero, P., Hernández, F., Herzke, D., Hilscherová, K., Hollert, H., Junghans, M., Kasprzyk‑Hordern, B., Keiter, S., Kools, S.A.E., Kruve, A., Lambropoulou, D., Lamoree, M., Leonards, P., Lopez, B., López de Alda, M., Lundy, L., Makovinská, J., Marigómez, I., Martin, J.W., McHugh, B., Miège, C., O’Toole, S., Perkola, N., Polesello, S., Posthuma, L., Rodriguez‑Mozaz, S., Roessink, I., Rostkowski, P., Ruedel, H., Samanipour, S., Schulze, Tobias, Schymanski, E.L., Sengl, M., Tarábek, P., Ten Hulscher, D., Thomaidis, N., Togola, A., Valsecchi, S., van Leeuwen, S., von der Ohe, P., Vorkamp, K., Vrana, B., Slobodnik, J., Dulio, V., Koschorreck, J., van Bavel, B., van den Brink, P., Hollender, J., Munthe, J., Schlabach, M., Aalizadeh, R., Agerstrand, M., Ahrens, L., Allan, I., Alygizakis, N., Barcelo, D., Bohlin‑Nizzetto, P., Boutroup, S., Brack, Werner, Bressy, A., Christensen, J.H., Cirka, L., Covaci, A., Derksen, A., Deviller, G., Dingemans, M.M.L., Engwall, M., Fatta-Kassinos, D., Gago‑Ferrero, P., Hernández, F., Herzke, D., Hilscherová, K., Hollert, H., Junghans, M., Kasprzyk‑Hordern, B., Keiter, S., Kools, S.A.E., Kruve, A., Lambropoulou, D., Lamoree, M., Leonards, P., Lopez, B., López de Alda, M., Lundy, L., Makovinská, J., Marigómez, I., Martin, J.W., McHugh, B., Miège, C., O’Toole, S., Perkola, N., Polesello, S., Posthuma, L., Rodriguez‑Mozaz, S., Roessink, I., Rostkowski, P., Ruedel, H., Samanipour, S., Schulze, Tobias, Schymanski, E.L., Sengl, M., Tarábek, P., Ten Hulscher, D., Thomaidis, N., Togola, A., Valsecchi, S., van Leeuwen, S., von der Ohe, P., Vorkamp, K., Vrana, B., and Slobodnik, J.
- Abstract
The Partnership for Chemicals Risk Assessment (PARC) is currently under development as a joint research and innovation programme to strengthen the scientific basis for chemical risk assessment in the EU. The plan is to bring chemical risk assessors and managers together with scientists to accelerate method development and the production of necessary data and knowledge, and to facilitate the transition to next-generation evidence-based risk assessment, a non-toxic environment and the European Green Deal. The NORMAN Network is an independent, well-established and competent network of more than 80 organisations in the field of emerging substances and has enormous potential to contribute to the implementation of the PARC partnership. NORMAN stands ready to provide expert advice to PARC, drawing on its long experience in the development, harmonisation and testing of advanced tools in relation to chemicals of emerging concern and in support of a European Early Warning System to unravel the risks of contaminants of emerging concern (CECs) and close the gap between research and innovation and regulatory processes. In this commentary we highlight the tools developed by NORMAN that we consider most relevant to supporting the PARC initiative: (i) joint data space and cutting-edge research tools for risk assessment of contaminants of emerging concern; (ii) collaborative European framework to improve data quality and comparability; (iii) advanced data analysis tools for a European early warning system and (iv) support to national and European chemical risk assessment thanks to harnessing, combining and sharing evidence and expertise on CECs. By combining the extensive knowledge and experience of the NORMAN network with the financial and policy-related strengths of the PARC initiative, a large step towards the goal of a non-toxic environment can be taken.
- Published
- 2020
16. Large-scale monitoring of the exposure to per- and polyfluoroalkyl substances and mercury in the white-tailed eagle (Haliaeetus albicilla):Clinical-chemical effects and the role of diet
- Author
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Eulaers, Igor, Ambus, P, Sonne, Christian, Bossi, Rossana, Dietz, Rune, Helander, B., Herzke, D., Jaspers, VLB, Johansson, Venla, Johnsen, Trond V, Krogh, Anne Kirstine H, Krone, O., Lepoint, Gilles, Løseth, Mari Engvig, Nygaard, T., Sun, Jiachen, Søndergaard, Jens, and Bustnes, J.O.
- Subjects
humanities - Abstract
Large-scale monitoring of the exposure to per- and polyfluoroalkyl substances and mercury in the white-tailed eagle (Haliaeetus albicilla): clinical-chemical effects and the role of diet I. Eulaers, Aarhus University AU Arctic Research Centre / Department of Bioscience; C. Sonne, Aarhus University AU Arctic Research Centre; P. Ambus, Copenhagen University / Department of Geosciences and Natural Resource management; R. Bossi, Aarhus University / Dept of Environmental Science; R. Dietz, Aarhus University AU Arctic Research Centre / Department of Bioscience, Arctic Research Centre; B. Helander, Swedish Museum of Natural History / Environmental Research & Monitoring; D. Herzke, Norwegian Institute for Air Research / FRAM Centre Tromso; V. Jaspers, Norwegian University of Science & Technology / Biology; V. Johansson, University of Helsinki / Department of Food and Environmental Sciences; T.V. Johnsen, Norwegian Institute for Nature Research NINA; A.K. Krogh, Copenhagen University / Department of Veterinary Clinical and Animal Sciences; O. Krone, Leibniz Institute for Zoo and Wildlife Research; T. Laaksonen, Natural Resources Institute Finland Luke; G. Lepoint, University of Liege; M.E. Løseth, The Norwegian University of Science and Technology / Biology; T. Nygård, Norwegian Institute for Nature Research NINA; C. Stjernegaard, Copenhagen University / Department of Veterinary Clinical and Animal Sciences; J. Sun, University of Antwerp / Department of Biology; J. Søndergaard, Aarhus University AU Arctic Research Centre; J.O. Bustnes, Norwegian Institute for Nature Research NINA; K. Skarphedinsson, Icelandic Institute of Natural History Although bird of prey nestlings are considered valuable sentinels of local environmental contamination, an effort to evaluate their extended suitability for large-scale monitoring was yet to be endeavoured. We have therefore sampled blood and body feathers from white-tailed eagle (Haliaeetus albicilla) nestlings along the Swedish, Finnish, Estonian, German, Danish, Norwegian and Icelandic coasts. This large-scale effort represents the anticipated exposure spectrum and has documented individual traits (age, crop content, foraging habitat and trophic level) that may confound contaminant exposure and effects. Body feathers and blood plasma were analysed for mercury (Hg) and per- and polyfluoroalkyl substances (PFASs), respectively, and a range of blood clinical-chemical parameters (BCCPs) was quantified as well. Finally, stable carbon (foraging habitat) and nitrogen (trophic level) isotopes were analysed in the same body feathers. Our first results confirm elevated exposure to Hg and PFASs in Baltic nestlings and lower exposure in Norway and Iceland. Notable Hg hotspots are located along the Swedish coast and in Finnish Lapland, while only the central Swedish and Finnish Baltic seem to be hotspots for PFASs. We did not observe a significant overall relationship between trophic level and contaminant exposure, which supports the notion of locally elevated environmental background levels. Multiple regression models investigating the simultaneous effects of individual contaminant exposure, age, short-term food ingestion, foraging habitat and trophic level indicate that the latter two stable isotope based dietary descriptors also show relationships with BCCPs indicative for liver, kidney and blood metabolism. Moreover, short-term diet ingestion (recorded crop content) as well as an individual’s age influences these same BCCPs as well as a range of elements. Finally, the models show the potential effect of Hg and PFAS exposure on clinical health as significant relationships where found between the contaminant levels and BCCPs indicative of liver and kidney functioning. We will present a more thorough data analysis of this expanding dataset in order to show the feasibility and importance of large-scale monitoring, which allows evaluating the efficiency of dedicated contaminant Conventions as well as the impact of increasing environmental change.
- Published
- 2019
17. Levels and trends of poly- and perfluoroalkyl substances in the Arctic environment – An update
- Author
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Muir, D. (D.), Bossi, R. (Rossana), Carlsson, P. (Pernilla), Evans, M. (Marlene), De Silva, A. (A.), Halsall, C. (Crispin), Rauert, C. (Cassandra), Herzke, D. (D.), Hung, H. (Hayley), Letcher, R.J. (Robert J.), Rigét, F. (F.), Roos, A. (Anna), Muir, D. (D.), Bossi, R. (Rossana), Carlsson, P. (Pernilla), Evans, M. (Marlene), De Silva, A. (A.), Halsall, C. (Crispin), Rauert, C. (Cassandra), Herzke, D. (D.), Hung, H. (Hayley), Letcher, R.J. (Robert J.), Rigét, F. (F.), and Roos, A. (Anna)
- Abstract
Poly- and perfluoroalkyl substances (PFASs) are important environmental contaminants globally and in the early 2000s they were shown to be ubiquitous contaminants in Arctic wildlife. Previous reviews by Butt et al. and Letcher et al. have covered studies on levels and trends of PFASs in the Arctic that were available to 2009. The purpose of this review is to focus on more recent work, generally published between 2009 and 2018, with emphasis on PFASs of emerging concern such as perfluoroalkyl carboxylates (PFCAs) and short-chain perfluoroalkyl sulfonates (PFSAs) and their precursors. Atmospheric measurements over the period 2006–2014 have shown that fluorotelomer alcohols (FTOHs) as well as perfluorobutanoic acid (PFBA) and perfluoroctanoic acid (PFOA) are the most prominent PFASs in the arctic atmosphere, all with increasing concentrations at Alert although PFOA concentrations declined at the Zeppelin Station (Svalbard). Results from ice cores show generally increasing deposition of PFCAs on the Devon Ice cap in the Canadian arctic while declining fluxes were found in a glacier on Svalbard. An extensive dataset exists for long-term trends of long-chain PFCAs that have been reported in Arctic biota with some datasets including archived samples from the 1970s and 1980s. Trends in PFCAs over time vary among the same species across the North American Arctic, East and West Greenland, and Svalbard. Most long term time series show a decline from higher concentrations in the early 2000s. However there have been recent (post 2010) increasing trends of PFCAs in ringed seals in the Canadian Arctic, East Greenland polar bears and in arctic foxes in Svalbard. Annual biological sampling is helping to determine these relatively short term changes. Rising levels of some PFCAs have been explained by continued emissions of long-chain PFCAs and/or their precursors and inflows to the Arctic Ocean, especially from the North Atlantic. While the effectiveness of biological sampling for te
- Published
- 2019
- Full Text
- View/download PDF
18. Levels and trends of poly- and perfluoroalkyl substances in the Arctic environment – An update
- Author
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Muir, D., Bossi, R., Carlsson, P., Evans, M., De Silva, A., Halsall, C., Rauert, C., Herzke, D., Hung, H., Letcher, R., Rigét, F., Roos, A., Muir, D., Bossi, R., Carlsson, P., Evans, M., De Silva, A., Halsall, C., Rauert, C., Herzke, D., Hung, H., Letcher, R., Rigét, F., and Roos, A.
- Abstract
Poly- and perfluoroalkyl substances (PFASs) are important environmental contaminants globally and in the early 2000s they were shown to be ubiquitous contaminants in Arctic wildlife. Previous reviews by Butt et al. and Letcher et al. have covered studies on levels and trends of PFASs in the Arctic that were available to 2009. The purpose of this review is to focus on more recent work, generally published between 2009 and 2018, with emphasis on PFASs of emerging concern such as perfluoroalkyl carboxylates (PFCAs) and short-chain perfluoroalkyl sulfonates (PFSAs) and their precursors. Atmospheric measurements over the period 2006–2014 have shown that fluorotelomer alcohols (FTOHs) as well as perfluorobutanoic acid (PFBA) and perfluoroctanoic acid (PFOA) are the most prominent PFASs in the arctic atmosphere, all with increasing concentrations at Alert although PFOA concentrations declined at the Zeppelin Station (Svalbard). Results from ice cores show generally increasing deposition of PFCAs on the Devon Ice cap in the Canadian arctic while declining fluxes were found in a glacier on Svalbard. An extensive dataset exists for long-term trends of long-chain PFCAs that have been reported in Arctic biota with some datasets including archived samples from the 1970s and 1980s. Trends in PFCAs over time vary among the same species across the North American Arctic, East and West Greenland, and Svalbard. Most long term time series show a decline from higher concentrations in the early 2000s. However there have been recent (post 2010) increasing trends of PFCAs in ringed seals in the Canadian Arctic, East Greenland polar bears and in arctic foxes in Svalbard. Annual biological sampling is helping to determine these relatively short term changes. Rising levels of some PFCAs have been explained by continued emissions of long-chain PFCAs and/or their precursors and inflows to the Arctic Ocean, especially from the North Atlantic. While the effectiveness of biological sampling for te
- Published
- 2019
19. Zürich statement on future actions on per- and polyfluoroalkyl substances (PFASs)
- Author
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Ritscher, A., Wang, Z., Scheringer, M., Boucher, J.M., Ahrens, L., Berger, Urs, Bintein, S., Bopp, S.K., Borg, D., Buser, A.M., Cousins, I., DeWitt, J., Fletcher, T., Green, C., Herzke, D., Higgins, C., Huang, J., Hung, H., Knepper, T., Lau, C.S., Leinala, E., Lindstrom, A.B., Liu, J., Miller, M., Ohno, K., Perkola, N., Shi, Y., Haug, L.S., Trier, X., Valsecchi, S., van der Jagt, K., Vierke, L., Ritscher, A., Wang, Z., Scheringer, M., Boucher, J.M., Ahrens, L., Berger, Urs, Bintein, S., Bopp, S.K., Borg, D., Buser, A.M., Cousins, I., DeWitt, J., Fletcher, T., Green, C., Herzke, D., Higgins, C., Huang, J., Hung, H., Knepper, T., Lau, C.S., Leinala, E., Lindstrom, A.B., Liu, J., Miller, M., Ohno, K., Perkola, N., Shi, Y., Haug, L.S., Trier, X., Valsecchi, S., van der Jagt, K., and Vierke, L.
- Abstract
Per- and polyfluoroalkyl substances (PFASs) are man-made chemicals that contain at least one perfluoroalkyl moiety, –CnF2n–. To date, over 4,000 unique PFASs have been used in technical applications and consumer products, and some of them have been detected globally in human and wildlife biomonitoring studies. Because of their extraordinary persistence, human and environmental exposure to PFASs will be a long-term source of concern. Some PFASs such as perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) have been investigated extensively and thus regulated, but for many other PFASs, knowledge about their current uses and hazards is still very limited or missing entirely. To address this problem and prepare an action plan for the assessment and management of PFASs in the coming years, a group of more than 50 international scientists and regulators held a two-day workshop in November, 2017. The group identified both the respective needs of and common goals shared by the scientific and the policy communities, made recommendations for cooperative actions, and outlined how the science–policy interface regarding PFASs can be strengthened using new approaches for assessing and managing highly persistent chemicals such as PFASs.
- Published
- 2018
20. Negligible Impact of Ingested Microplastics on Tissue Concentrations of Persistent Organic Pollutants in Northern Fulmars off Coastal Norway
- Author
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Herzke, D., Anker-Nilssen, T., Haughdahl, T., Nøst, T., Götsch, A., Christensen-Dalsgaard, S., Langset, M., Fangel, K., and Koelmans, A.A.
- Subjects
Microplastics ,Aquatic Ecology and Water Quality Management ,Tissue concentrations ,010504 meteorology & atmospheric sciences ,genetic structures ,010501 environmental sciences ,01 natural sciences ,Charadriiformes ,Environmental Chemistry ,Ingestion ,Animals ,Life Science ,14. Life underwater ,Northern fulmar ,0105 earth and related environmental sciences ,Pollutant ,WIMEK ,biology ,Ecology ,Norway ,General Chemistry ,Aquatische Ecologie en Waterkwaliteitsbeheer ,biology.organism_classification ,Gastrointestinal Contents ,Vis ,13. Climate action ,Indicator species ,Environmental chemistry ,Bioaccumulation ,Environmental science ,Plastic pollution ,Plastics ,Water Pollutants, Chemical ,Environmental Monitoring - Abstract
The northern fulmar (Fulmarus glacialis) is defined as an indicator species of plastic pollution by the Oslo-Paris Convention for the North-East Atlantic, but few data exist for fulmars from Norway. Moreover, the relationship between uptake of plastic and pollutants in seabirds is poorly understood. We analyzed samples of fulmars from Norwegian waters and compared the POP concentrations in their liver and muscle tissue with the corresponding concentrations in the loads of ingested plastic in their stomachs, grouped as "no", "medium" (0.01-0.21 g; 1-14 pieces of plastic), or "high" (0.11-0.59 g; 15-106 pieces of plastic). POP concentrations in the plastic did not differ significantly between the high and medium plastic ingestion group for sumPCBs, sumDDTs, and sumPBDEs. By combining correlations among POP concentrations, differences in tissue concentrations of POPs between plastic ingestion subgroups, fugacity calculations, and bioaccumulation modeling, we showed that plastic is more likely to act as a passive sampler than as a vector of POPs, thus reflecting the POP profiles of simultaneously ingested prey.
- Published
- 2016
21. Contaminants in northern fulmars (Fulmarus glacialis) exposed to plastic
- Author
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Ask, A., Anker-Nilssen, T., Herzke, D., Trevail, Alice, van Franeker, J.A., Gabrielsen, G.W., Ask, A., Anker-Nilssen, T., Herzke, D., Trevail, Alice, van Franeker, J.A., and Gabrielsen, G.W.
- Abstract
Northern fulmars are seabirds which feed exclusively at sea, and as such, they are useful indicators of ocean health. Marine plastic pollution is an ever-increasing and global issue that affects the northern fulmar as they are frequently found to have ingested plastic. In this report we investigate whether the amount of ingested plastic affects the concentration of certain plastic-adsorbed toxicants in their tissues. Marine plastic pollution is a field of utmost importance. It is our hope that this continues to be an area which receives increased attention in order to elucidate the potential harmful effects plastics have on the northern fulmar and ocean health, in general.
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- 2016
22. Organochlorine pesticides as markers for source elucidation of water masses in Godthåbsfjord, a Greenland fjord system
- Author
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Carlsson, P, Kallenborn, R, Cornelissen, G, Herzke, D, Bøggild, CE, and Rysgaard, Søren
- Published
- 2011
23. Distribution of POPs and PFCs in tissues of white tailed eagles (**Haliaeetus albicilla**) from Greenland
- Author
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Jaspers Veerle, Soler-Rodriguez, F., Herzke, D., David Boertmann, Christian Sonne, Rune Dietz, Rasmussen, L. M., Adrian Covaci, and Marcel Eens
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Biology - Published
- 2011
24. Bioaccumulation of Brominated Flame Retardants
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Antelo Dominguez, A., Law, R.J., Herzke, D., de Boer, J., Eljarrat, E., Barcelo, D., and Chemistry and Biology
- Published
- 2011
25. Distribution of POPs and PFCs in tissues of white tailed eagles (Haliaeetus albicilla) from Greenland
- Author
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Veerle, Jaspers, Soler-Rodriguez, F., Herzke, D., Boertmann, David, Sonne, Christian, Dietz, Rune, Rasmussen, L.M., Covaci, Adrian, and Eens, Marcel
- Published
- 2011
26. PFCs in feathers of white tailed eagles (Haliaeetus albicilla) from Greenland and Norway ; useful for non-destructive monitoring?
- Author
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Herzke, D., Jaspers Veerle, David Boertmann, Rasmussen, L. M., Christian Sonne, Rune Dietz, Adrian Covaci, Marcel Eens, and Bustnes, J. O.
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Biology - Published
- 2011
27. Polychlorinated biphenyl exposure and corticosterone levels in seven polar seabird species
- Author
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Tartu, S., primary, Angelier, F., additional, Bustnes, J.O., additional, Moe, B., additional, Hanssen, S.A., additional, Herzke, D., additional, Gabrielsen, G.W., additional, Verboven, N., additional, Verreault, J., additional, Labadie, P., additional, Budzinski, H., additional, Wingfield, J.C., additional, and Chastel, O., additional
- Published
- 2015
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28. Retrospective and prospective intake assessment of perfluorinated chemicals within the European Union: the perfood project
- Author
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Brambilla, G., Dellatte, E., di Domenico, A., Heinemeyer, G., D'Hollander, W., Herzke, D., van Leeuwen, S.P.J., de Voogt, W.P., Chemistry and Biology, and Earth Surface Science (IBED, FNWI)
- Abstract
12-17 September 2010
- Published
- 2010
29. Persistent organic pollutants in feathers and blood from nestling raptors of Northern Norway: linkage to stable isotopes and specific ecology
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Jaspers, Veerle, Eulaers, Igor, Covaci, Adrian, Herzke, D., Schnug, L., Johnsen, T., Halley, D.J., Eens, Marcel, and Bustnes, J.O.
- Subjects
animal structures ,food and beverages ,Biology - Abstract
As part of an ongoing project to assess the impact of organic pollutants and biological stressors on the fitness and survival of avian top predators in different northern ecosystems, we collected body feathers and blood samples from nestlings of three different raptor species. Here we investigate the concentrations and profiles of POPs in blood and feathers, the relationships between them and their relation to trophic position (determined by stable isotopes) and ecology. We found that concentrations of most POPs could be quantified in feathers from nestlings, with p,p-DDE and sum PCBs as the most important compounds. Concentrations in feathers were significantly related to concentrations in blood in most cases. Furthermore, concentrations of POPs in feathers could also be related to concentrations of stable isotopes in the feathers, except for the golden eagle (Aquila chrysaetos). Further research is necessary to conclude on the usefulness of nestling raptor feathers for biomonitoring purposes.
- Published
- 2009
30. Nye miljøgifter i luft - 2007. Bromerte flammehemmere og perfluorerte stoffer i luft
- Author
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Schlabach, M., Herzke, D., and Manø, S.
- Subjects
Bakgrunnskonsentrasjoner ,Miljøkjemi ,Luft ,PFAS ,Flammehemmere ,Miljøgifter ,BFH - Abstract
Denne undersøkelsen rapporterer konsentrasjonsnivåer av de nye organiske miljøgiftene bromerte flammehemmere og polyfluorerte alkylstoffer i luft på bakgrunnsmålestasjonene Birkenes og Zeppelinfjell, Ny-Ålesund.
- Published
- 2008
31. Screening of selected metals and new organic contaminants 2007. Phosphorus flame retardents, polyfluorinated organic compounds, nitro-PAHs, silver, platinum and sucralose in air, wastewater treatment falcilities, and freshwater and marine recipients
- Author
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Green, N., Schlabach, M., Bakke, T., Brevik, E., Dye, C., Herzke, D., Huber, S., Plosz, B., Remberger, M., Schøyen, M., Uggerud, H.T., Vogelsang, C., and Green, N. - Project manager
- Subjects
pfc ,Matematikk og naturvitenskap: 400 [VDP] ,nitro-pah ,pfr ,natoional screening ,miljøgifter - marint ,nasjonal screeningundersøkelse - Abstract
Årsliste 2008 This investigation take accound of phosphorus flame retardants (PFRs), polyfluorinated organic compounds (PFCs), nitro-PAHs, silver, platinum, and sucralose in air, samples from wastewater treatment facilities, seawater, marine and freshwater sediment, blue mussel and cod liver taken in 2007 (with the exception of 2 sediment samples from 2003). The survey covers 54 individual compounds and 2 metals from 59 sites, of which 5 are for air sampling, 22 for wastewater treatment facilities, 3 for freshwater sediment and 29 for the marine environment. Samples of air also included dust and road dust. Waste treatment facilities included domestic wastewater treatments plants, a landfill, a car demolishing site and a fire fighting test site. The report should be a guideline in the planning of environmental monitoring where these substances are concerned. Statens Forurensningstilsyn
- Published
- 2008
32. Arctic POPs
- Author
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Herzke, D. and Heimstad, E.S.
- Subjects
Miljøgifter - Published
- 2004
33. Perfluorinated and other persistent halogenated organic compounds in European shag (Phalacrocorax aristotelis) and common eider (Somateria mollissima) from Norway : A suburban to remote pollutant gradient
- Author
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Herzke, D., Nygard, T., Berger, Urs, Huber, S., Rov, N., Herzke, D., Nygard, T., Berger, Urs, Huber, S., and Rov, N.
- Abstract
Samples of two marine bird species, European shag (Phalacrocorax aristotelis) and common eider (Somateria mollissima) sampled at a remote coastal site in Norway were analysed for POPs and PFCs. Additionally samples of common eider were analysed from two other locations in Norway, representing a gradient from "densely populated" to "remote". The variety, concentration and distribution of lipophilic POPs in comparison to PFCs were investigated. PCBs were the dominating group of contaminants in the analysed egg samples. Shag eggs had median sum PCBs levels of 4580 ng/g l.w. in 2004. Six different PBDE congeners could be detected in the shag eggs. BDE 47 and 100 were the main contributors with 24 and 27 ng/g l.w. respectively, sum PBDEs was 90 ng/g l.w. Relatively high concentrations of chlordanes were found witha total sum of 903 ng/g l.w. Of other OCs, toxaphene 26 and 52 together (sum 657 ng/g l.w.) and HCB (165 ng/g l.w.) were contributing majorly to the egg burden. Sum HCHs were low; only 54 ng/g l.w. PFOS was the main PFC in egg, plasma and liver samples. Similar median levels of 29,32 and 27 ng/g w.w. were observed. PFOSA, PFHxS, and PFDcA were observed additionally in all shag samples at minor concentrations with the exception of elevated levels observed in liver for PFOSA and PFDcA with median levels of 7.6 and 7.9 ng/g w.w., respectively. In common eider eggs, the POP concentrations decreased up to 1/8th along the sampled spatial gradient from suburban to remote. of the 9 detected PFCs, PFOS dominated all samples by one order of magnitude, followed by PFOA. Sum PFC concentrations were twice as high at the two fjord sites compared to the remote site. Shorter chained PFCAs like PFOA and PFNA could be detected in the eider eggs whilst being absent in shag eggs.
- Published
- 2009
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34. Historical Trends in Persistent Organic Pollutants and Metals Recorded in Sediment from Lake Ellasjøen, Bjørnøya, Norwegian Arctic
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Evenset, A., Christensen, G.N., Carroll, J., Zaborska, A., Berger, Urs, Herzke, D., Gregor, D., Evenset, A., Christensen, G.N., Carroll, J., Zaborska, A., Berger, Urs, Herzke, D., and Gregor, D.
- Published
- 2007
35. The search for alternative aqueous film forming foams (AFFF) with a low environmental impact: Physiological and transcriptomic effects of two Forafac® fluorosurfactants in turbot
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Hagenaars, A., primary, Meyer, I.J., additional, Herzke, D., additional, Pardo, B.G., additional, Martinez, P., additional, Pabon, M., additional, De Coen, W., additional, and Knapen, D., additional
- Published
- 2011
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36. Perfluorinated and other persistent halogenated organic compounds in European shag (Phalacrocorax aristotelis) and common eider (Somateria mollissima) from Norway: A suburban to remote pollutant gradient
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Herzke, D., primary, Nygård, T., additional, Berger, U., additional, Huber, S., additional, and Røv, N., additional
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- 2009
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37. Historical trends in persistent organic pollutants and metals recorded in sediment from Lake Ellasjøen, Bjørnøya, Norwegian Arctic
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Evenset, A., primary, Christensen, G.N., additional, Carroll, J., additional, Zaborska, A., additional, Berger, U., additional, Herzke, D., additional, and Gregor, D., additional
- Published
- 2007
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38. Brominated flame retardants and other organobromines in Norwegian predatory bird eggs
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Herzke, D., primary, Berger, U., additional, Kallenborn, R., additional, Nygård, T., additional, and Vetter, W., additional
- Published
- 2005
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39. Organochlorines in egg samples from Norwegian birds of prey: Congener-, isomer- and enantiomer specific considerations
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Herzke, D., primary, Kallenborn, R., additional, and Nygård, T., additional
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- 2002
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40. The search for alternative aqueous film forming foams (AFFF) with a low environmental impact: Physiological and transcriptomic effects of two Forafac® fluorosurfactants in turbot
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Hagenaars, A., Meyer, I.J., Herzke, D., Pardo, B.G., Martinez, P., Pabon, M., De Coen, W., and Knapen, D.
- Subjects
- *
ENVIRONMENTAL impact analysis , *TRANSCRIPTION factors , *SURFACE active agents , *PSETTA maxima , *FOAM , *DIGESTIVE organs , *PROTEIN microarrays , *IMMUNOSUPPRESSION , *ENVIRONMENTAL toxicology , *GENE expression - Abstract
Abstract: Fluorosurfactants are the key components in aqueous film forming foams (AFFF). They provide these fire fighting agents with the required low surface tension and they enable film formation on top of lighter fuels to prevent burn back. Development of effective and environmentally acceptable PFOS alternatives is one of the most important priorities in the fire fighting foam industry. DuPont™ offers the fluorosurfactant mixtures Forafac®1157 and Forafac®1157N for the formulation of AFFFs which are alternatives to the persistent and toxic perfluorooctane sulphonate (PFOS). Ecotoxicological testing of these inadequately documented mixtures is necessary to include them in AFFF hazard and risk assessment. Juvenile turbot (Scophthalmus maximus) were exposed for 14 days to 0.1; 0.5 and 1.5mg/L of the fluorosurfactant mixtures used in Forafac®1157 and Forafac®1157N. In an initial transcriptomics experiment, microarray analysis revealed differentially expressed transcripts of genes which were mainly involved in digestion and in the immune system. This discovery-driven screening approach offered the basis for new hypotheses that were tested in two subsequent experiments in which food intake, energy reserves, growth and a set of haematological parameters were examined. Additionally, effects of the two mixtures were compared to those of PFOS. Based on the results of this study, the mode of action of Forafac®1157N was the activation of the acute phase reaction resulting in increased leukocyte concentrations and the inhibition of growth due to the high energetic cost of toxicant exposure. For Forafac®1157, evidences of immunosuppression were found on the transcriptional level and the altered differential leukocyte profiles indicated that stress was induced in these fish. However, food intake, energy reserves and growth were not compromised, even at high exposure concentrations, which was in contrast to the effects seen after PFOS exposure. Taking into account that Forafac®1157 appeared to be less toxic than PFOS, this mixture could be considered as a more environmentally acceptable PFOS alternative for the use in AFFFs. [Copyright &y& Elsevier]
- Published
- 2011
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41. PFAS Exposure is Associated with a Lower Spermatic Quality in an Arctic Seabird.
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Humann-Guilleminot S, Blévin P, Gabrielsen GW, Herzke D, Nikiforov VA, Jouanneau W, Moe B, Parenteau C, Helfenstein F, and Chastel O
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- Animals, Male, Arctic Regions, Birds, Testosterone blood, Charadriiformes, Fluorocarbons, Spermatozoa drug effects
- Abstract
Several studies have reported an increasing occurrence of poly- and perfluorinated alkyl substances (PFASs) in Arctic wildlife tissues, raising concerns due to their resistance to degradation. While some research has explored PFAS's physiological effects on birds, their impact on reproductive functions, particularly sperm quality, remains underexplored. This study aims to assess (1) potential association between PFAS concentrations in blood and sperm quality in black-legged kittiwakes ( Rissa tridactyla ), focusing on the percentage of abnormal spermatozoa, sperm velocity, percentage of sperm motility, and morphology; and (2) examine the association of plasma levels of testosterone, corticosterone, and luteinizing hormone with both PFAS concentrations and sperm quality parameters to assess possible endocrine disrupting pathways. Our findings reveal a positive correlation between the concentration of longer-chain perfluoroalkyl carboxylates (PFCA; C11-C14) in blood and the percentage of abnormal sperm in kittiwakes. Additionally, we observed that two other PFAS (i.e., PFOSlin and PFNA), distinct from those associated with sperm abnormalities, were positively correlated with the stress hormone corticosterone. These findings emphasize the potentially harmful substance-specific effects of long-chain PFCAs on seabirds and the need for further research into the impact of pollutants on sperm quality as a potential additional detrimental effect on birds.
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- 2024
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42. From microplastics to pixels: testing the robustness of two machine learning approaches for automated, Nile red-based marine microplastic identification.
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Meyers N, De Witte B, Schmidt N, Herzke D, Fuda JL, Vanavermaete D, Janssen CR, and Everaert G
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- Plastics, Water Pollutants, Chemical analysis, Microplastics analysis, Machine Learning, Environmental Monitoring methods, Oxazines analysis
- Abstract
Despite the urgent need for accurate and robust observations of microplastics in the marine environment to assess current and future environmental risks, existing procedures remain labour-intensive, especially for smaller-sized microplastics. In addition to this, microplastic analysis faces challenges due to environmental weathering, impacting the reliability of research relying on pristine plastics. This study addresses these knowledge gaps by testing the robustness of two automated analysis techniques which combine machine learning algorithms with fluorescent colouration of Nile red (NR)-stained particles. Heterogeneously shaped uncoloured microplastics of various polymers-polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC)-ranging from 100 to 1000 µm in size and weathered under semi-controlled surface and deep-sea conditions, were stained with NR and imaged using fluorescence stereomicroscopy. This study assessed and compared the accuracy of decision tree (DT) and random forest (RF) models in detecting and identifying these weathered plastics. Additionally, their analysis time and model complexity were evaluated, as well as the lower size limit (2-4 µm) and the interoperability of the approach. Decision tree and RF models were comparably accurate in detecting and identifying pristine plastic polymers (both > 90%). For the detection of weathered microplastics, both yielded sufficiently high accuracies (> 77%), although only RF models were reliable for polymer identification (> 70%), except for PET particles. The RF models showed an accuracy > 90% for particle predictions based on 12-30 pixels, which translated to microplastics sized < 10 µm. Although the RF classifier did not produce consistent results across different labs, the inherent flexibility of the method allows for its swift adaptation and optimisation, ensuring the possibility to fine-tune the method to specific research goals through customised datasets, thereby strengthening its robustness. The developed method is particularly relevant due to its ability to accurately analyse microplastics weathered under various marine conditions, as well as ecotoxicologically relevant microplastic sizes, making it highly applicable to real-world environmental samples., (© 2024. The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature.)
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- 2024
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43. The time for ambitious action is now: Science-based recommendations for plastic chemicals to inform an effective global plastic treaty.
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Brander SM, Senathirajah K, Fernandez MO, Weis JS, Kumar E, Jahnke A, Hartmann NB, Alava JJ, Farrelly T, Almroth BC, Groh KJ, Syberg K, Buerkert JS, Abeynayaka A, Booth AM, Cousin X, Herzke D, Monclús L, Morales-Caselles C, Bonisoli-Alquati A, Al-Jaibachi R, and Wagner M
- Subjects
- United Nations, Environmental Policy, Environmental Pollutants analysis, Humans, International Cooperation, Plastics, Environmental Pollution prevention & control
- Abstract
The ubiquitous and global ecological footprint arising from the rapidly increasing rates of plastic production, use, and release into the environment is an important modern environmental issue. Of increasing concern are the risks associated with at least 16,000 chemicals present in plastics, some of which are known to be toxic, and which may leach out both during use and once exposed to environmental conditions, leading to environmental and human exposure. In response, the United Nations member states agreed to establish an international legally binding instrument on plastic pollution, the global plastics treaty. The resolution acknowledges that the treaty should prevent plastic pollution and its related impacts, that effective prevention requires consideration of the transboundary nature of plastic production, use and pollution, and that the full life cycle of plastics must be addressed. As a group of scientific experts and members of the Scientists' Coalition for an Effective Plastics Treaty, we concur that there are six essential "pillars" necessary to truly reduce plastic pollution and allow for chemical detoxification across the full life cycle of plastics. These include a plastic chemical reduction and simplification, safe and sustainable design of plastic chemicals, incentives for change, holistic approaches for alternatives, just transition and equitable interventions, and centering human rights. There is a critical need for scientifically informed and globally harmonized information, transparency, and traceability criteria to protect the environment and public health. The right to a clean, healthy, and sustainable environment must be upheld, and thus it is crucial that scientists, industry, and policy makers work in concert to create a future free from hazardous plastic contamination., Competing Interests: Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: Susanne M Brander reports financial support was provided by National Science Foundation. Andy Booth reports financial support was provided by The Research Council of Norway. Andy Booth reports financial support was provided by European Commission. Annika Jahnke reports financial support was provided by Heimholtz Association. Dorte Hertz reports financial support was provided by The Research Council of Norway. Amila Abeynayaka reports financial support was provided by European Union Horizon Europe Research and Innovation. Susanne Brander reports a relationship with Southern California Coastal Water Research Project that includes: consulting or advisory. Brander previously consulted for the Environmental Defense fund and is on advisory boards or groups for the Plastic Pollution Coalition, as well as the Department of Toxic Substances Control (California) and the San Francisco Estuary Institute. Martin Wagner is an unremunerated member of the Scientific Advisory Board of the Food Packaging Forum Foundation and received travel support for attending annual board meetings. Marina Fernandez is a member of the Endocrine Society's delegation at the Intergovernmental Negotiating Committee (INC) to develop an international legally binding instrument on plastic pollution. All authors are members of the Scientists Coalition for an Effective Plastics Treaty, and Susanne Brander, Martin Wagner, Marina Fernandez, Trisia Farrelly, Kristian Syberg, Amila Abeynayaka, and Bethanie Carney Alroth are Scientists Coalition Steering Committee Members. If there are other authors, they declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Crown Copyright © 2024. Published by Elsevier B.V. All rights reserved.)
- Published
- 2024
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44. Towards reliable data: Validation of a machine learning-based approach for microplastics analysis in marine organisms using Nile red staining.
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Meyers N, Everaert G, Hostens K, Schmidt N, Herzke D, Fuda JL, Janssen CR, and De Witte B
- Subjects
- Animals, Oxazines, Fishes, Mytilus edulis, Gastrointestinal Tract, Plastics, Machine Learning, Water Pollutants, Chemical analysis, Microplastics analysis, Aquatic Organisms, Environmental Monitoring methods
- Abstract
Microplastic (MP) research faces challenges due to costly, time-consuming, and error-prone analysis techniques. Additionally, the variability in data quality across studies limits their comparability. This study addresses the critical need for reliable and cost-effective MP analysis methods through validation of a semi-automated workflow, where environmentally relevant MP were spiked into and recovered from marine fish gastrointestinal tracts (GITs) and blue mussel tissue, using Nile red staining and machine learning automated analysis of different polymers. Parameters validated include trueness, precision, uncertainty, limit of quantification, specificity, sensitivity, selectivity, and method robustness. For fish GITs a 95 ± 9 % recovery rate was achieved, and 87 ± 11 % for mussels. Polymer identification accuracies were 76 ± 8 % for fish GITs and 80 ± 13 % for mussels. Polyethylene terephthalate fragments showed more variability with lower accuracies. The proposed validation parameters offer a step towards quality management guidelines, as such aiding future researchers and fostering cross-study comparability., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2024. Published by Elsevier Ltd.)
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- 2024
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45. Combining Advanced Analytical Methodologies to Uncover Suspect PFAS and Fluorinated Pharmaceutical Contributions to Extractable Organic Fluorine in Human Serum (Tromsø Study).
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Cioni L, Nikiforov V, Benskin JP, Coêlho ACMF, Dudášová S, Lauria MZ, Lechtenfeld OJ, Plassmann MM, Reemtsma T, Sandanger TM, and Herzke D
- Subjects
- Humans, Fluorocarbons blood, Norway, Halogenation, Pharmaceutical Preparations blood, Chromatography, Liquid, Fluorine
- Abstract
A growing number of studies have reported that routinely monitored per- and polyfluoroalkyl substances (PFAS) are not sufficient to explain the extractable organic fluorine (EOF) measured in human blood. In this study, we address this gap by screening pooled human serum collected over 3 decades (1986-2015) in Tromsø (Norway) for >5000 PFAS and >300 fluorinated pharmaceuticals. We combined multiple analytical techniques (direct infusion Fourier transform ion cyclotron resonance mass spectrometry, liquid chromatography-Orbitrap-high-resolution mass spectrometry, and total oxidizable precursors assay) in a three-step suspect screening process which aimed at unequivocal suspect identification. This approach uncovered the presence of one PFAS and eight fluorinated pharmaceuticals (including some metabolites) in human serum. While the PFAS suspect only accounted for 2-4% of the EOF, fluorinated pharmaceuticals accounted for 0-63% of the EOF, and their contribution increased in recent years. Although fluorinated pharmaceuticals often contain only 1-3 fluorine atoms, our results indicate that they can contribute significantly to the EOF. Indeed, the contribution from fluorinated pharmaceuticals allowed us to close the organofluorine mass balance in pooled serum from 2015, indicating a good understanding of organofluorine compounds in humans. However, a portion of the EOF in human serum from 1986 and 2007 still remained unexplained.
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- 2024
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46. Winter Tracking Data Suggest that Migratory Seabirds Transport Per- and Polyfluoroalkyl Substances to Their Arctic Nesting Site.
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Léandri-Breton DJ, Jouanneau W, Legagneux P, Tarroux A, Moe BR, Angelier F, Blévin P, Bråthen VS, Fauchald P, Gabrielsen GW, Herzke D, Nikiforov VA, Elliott KH, and Chastel O
- Subjects
- Animals, Arctic Regions, Environmental Monitoring, Nesting Behavior, Norway, Birds metabolism, Female, Animal Migration, Seasons, Fluorocarbons blood, Fluorocarbons metabolism, Charadriiformes metabolism
- Abstract
Seabirds are often considered sentinel species of marine ecosystems, and their blood and eggs utilized to monitor local environmental contaminations. Most seabirds breeding in the Arctic are migratory and thus are exposed to geographically distinct sources of contamination throughout the year, including per- and polyfluoroalkyl substances (PFAS). Despite the abundance and high toxicity of PFAS, little is known about whether blood concentrations at breeding sites reliably reflect local contamination or exposure in distant wintering areas. We tested this by combining movement tracking data and PFAS analysis (nine compounds) from the blood of prelaying black-legged kittiwakes ( Rissa tridactyla ) nesting in Arctic Norway (Svalbard). PFAS burden before egg laying varied with the latitude of the wintering area and was negatively associated with time upon return of individuals at the Arctic nesting site. Kittiwakes ( n = 64) wintering farther south carried lighter burdens of shorter-chain perfluoroalkyl carboxylates (PFCAs, C
9 -C12 ) and heavier burdens of longer chain PFCAs (C13 -C14 ) and perfluorooctanesulfonic acid compared to those wintering farther north. Thus, blood concentrations prior to egg laying still reflected the uptake during the previous wintering stage, suggesting that migratory seabirds can act as biovectors of PFAS to Arctic nesting sites.- Published
- 2024
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47. Dechloranes and chlorinated paraffins in sediments and biota of two subarctic lakes.
- Author
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Arriola A, Al Saify I, Warner NA, Herzke D, Harju M, Amundsen PA, Evenset A, Möckel C, and Krogseth IS
- Abstract
Our understanding of the environmental behavior, bioaccumulation and concentrations of chlorinated paraffins (CPs) and Dechloranes (Dec) in the Arctic environment is still limited, particularly in freshwater ecosystems. In this descriptive study, short chain (SCCPs) and medium chain (MCCPs) CPs, Dechlorane Plus (DP) and analogues, and polychlorinated biphenyls (PCBs) were measured in sediments, benthic organisms, three-spined stickleback ( Gasterosteus aculeatus ), Arctic char ( Salvelinus alpinus ) and brown trout ( Salmo trutta ) in two Sub-Arctic lakes in Northern Norway. Takvannet (TA) is a remote lake, with no known local sources for organic contaminants, while Storvannet (ST) is situated in a populated area. SCCPs and MCCPs were detected in all sediment samples from ST with concentration of 42.26-115.29 ng/g dw and 66.18-136.69 ng/g dw for SCCPs and MCCPs, respectively. Only SCCPs were detected in TA sediments (0.4-5.28 ng/g dw). In biota samples, sticklebacks and benthic organisms showed the highest concentrations of CPs, while concentrations were low or below detection limits in both char and trout. The congener group patterns observed in both lakes showed SCCP profiles dominated by higher chlorinated congener groups while the MCCPs showed consistency in their profiles, with C
14 being the most prevalent carbon chain length. Anti- and syn-DP isomers were detected in all sediment, benthic and stickleback samples with higher concentrations in ST than in TA. However, they were only present in a few char and trout samples from ST. Dec 601 and 604 were below detection limits in all samples in both lakes. Dec 603 was detected only in ST sediments, sticklebacks and 2 trout samples, while Dec 602 was the only DP analogue found in all samples from both lakes. While there were clear differences in sediment concentrations of DP and Dec 602 between ST and TA, differences between lakes decreased with increasing δ15 N. This pattern was similar to the PCB behavior, suggesting the lake characteristics in ST are playing an important role in the lack of biomagnification of pollutants in this lake. Our results suggest that ST receives pollutants from local sources in addition to atmospheric transport., Competing Interests: The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest., (Copyright © 2024 Arriola, Al Saify, Warner, Herzke, Harju, Amundsen, Evenset, Möckel and Krogseth.)- Published
- 2024
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48. Life starts with plastic: High occurrence of plastic pieces in fledglings of northern fulmars.
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Collard F, Benjaminsen SC, Herzke D, Husabø E, Sagerup K, Tulatz F, and Gabrielsen GW
- Subjects
- Animals, Svalbard, Water Pollutants, Chemical analysis, Microplastics analysis, Arctic Regions, Plastics analysis, Environmental Monitoring, Birds
- Abstract
Plastic pollution threatens many organisms around the world. In particular, the northern fulmar, Fulmarus glacialis, is known to ingest high quantities of plastics. Since data are sparse in the Eurasian Arctic, we investigated plastic burdens in the stomachs of fulmar fledglings from Kongsfjorden, Svalbard. Fifteen birds were collected and only particles larger than 1 mm were extracted, characterised and analysed with Fourier Transform InfraRed spectroscopy. All birds ingested plastic. In total, 683 plastic particles were found, with an average of 46 ± 40 SD items per bird. The most common shape, colour and polymer were hard fragment, white, and polyethylene, respectively. Microplastics (< 5 mm) were slightly more represented than mesoplastics (> 5 mm). This study confirms high numbers of ingested plastics in fulmar fledglings from Svalbard and suggests that fulmar fledglings may be suitable for temporal monitoring of plastic pollution, avoiding potential biases caused by age composition or breeding state., Competing Interests: Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: France Collard reports financial support was provided by the Fram Centre and the Research Council of Norway. Dorte Herzke reports financial support was provided by the Research Council of Norway., (Copyright © 2024 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2024
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49. Can plastic related chemicals be indicators of plastic ingestion in an Arctic seabird?
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Collard F, Tulatz F, Harju M, Herzke D, Bourgeon S, and Gabrielsen GW
- Subjects
- Humans, Animals, Birds, Gastrointestinal Tract chemistry, Eating, Plastics analysis, Environmental Monitoring, Phthalic Acids
- Abstract
For decades, the northern fulmar (Fulmarus glacialis) has been found to ingest and accumulate high loads of plastic due to its feeding ecology and digestive tract morphology. Plastic ingestion can lead to both physical and toxicological effects as ingested plastics can be a pathway for hazardous chemicals into seabirds' tissues. Many of these contaminants are ubiquitous in the environment and the contribution of plastic ingestion to the uptake of those contaminants in seabirds' tissues is poorly known. In this study we aimed at quantifying several plastic-related chemicals (PRCs) -PBDE209, several dechloranes and several phthalate metabolites- and assessing their relationship with plastic burdens (both mass and number) to further investigate their potential use as proxies for plastic ingestion. Blood samples from fulmar fledglings and liver samples from both fledgling and non-fledgling fulmars were collected for PRC quantification. PBDE209 and dechloranes were quantified in 39 and 33 livers, respectively while phthalates were quantified in plasma. Plastic ingestion in these birds has been investigated previously and showed a higher prevalence in fledglings. PBDE209 was detected in 28.2 % of the liver samples. Dechlorane 602 was detected in all samples while Dechloranes 601 and 604 were not detected in any sample. Dechlorane 603 was detected in 11 individuals (33%). Phthalates were detected in one third of the analysed blood samples. Overall, no significant positive correlation was found between plastic burdens and PRC concentrations. However, a significant positive relationship between PBDE209 and plastic number was found in fledglings, although likely driven by one outlier. Our study shows the complexity of PRC exposure, the timeline of plastic ingestion and subsequent uptake of PRCs into the tissues in birds, the additional exposure of these chemicals via their prey, even in a species ingesting high loads of plastic., Competing Interests: Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: France Collard reports financial support was provided by the Fram Centre and the Research Council of Norway. Dorte Herzke reports financial support was provided by the Research Council of Norway., (Copyright © 2024 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2024
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50. Zürich II Statement on Per- and Polyfluoroalkyl Substances (PFASs): Scientific and Regulatory Needs.
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DeWitt JC, Glüge J, Cousins IT, Goldenman G, Herzke D, Lohmann R, Miller M, Ng CA, Patton S, Trier X, Vierke L, Wang Z, Adu-Kumi S, Balan S, Buser AM, Fletcher T, Haug LS, Heggelund A, Huang J, Kaserzon S, Leonel J, Sheriff I, Shi YL, Valsecchi S, and Scheringer M
- Abstract
Per- and polyfluoroalkyl substances (PFASs) are a class of synthetic organic chemicals of global concern. A group of 36 scientists and regulators from 18 countries held a hybrid workshop in 2022 in Zürich, Switzerland. The workshop, a sequel to a previous Zürich workshop held in 2017, deliberated on progress in the last five years and discussed further needs for cooperative scientific research and regulatory action on PFASs. This review reflects discussion and insights gained during and after this workshop and summarizes key signs of progress in science and policy, ongoing critical issues to be addressed, and possible ways forward. Some key take home messages include: 1) understanding of human health effects continues to develop dramatically, 2) regulatory guidelines continue to drop, 3) better understanding of emissions and contamination levels is needed in more parts of the world, 4) analytical methods, while improving, still only cover around 50 PFASs, and 5) discussions of how to group PFASs for regulation (including subgroupings) have gathered momentum with several jurisdictions proposing restricting a large proportion of PFAS uses. It was concluded that more multi-group exchanges are needed in the future and that there should be a greater diversity of participants at future workshops., Competing Interests: The authors declare the following competing financial interest(s): J. DeWitt serves as a Plaintiff's expert witness in cases involving PFASs., (© 2024 The Authors. Published by American Chemical Society.)
- Published
- 2024
- Full Text
- View/download PDF
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