160 results on '"Laforsch C"'
Search Results
2. Filter feeders are key to small microplastic residence times in stratified lakes: A virtual experiment
- Author
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Gilfedder, B.S., Elagami, H., Boos, J.P., Brehm, J., Schott, M., Witt, L., Laforsch, C., and Frei, S.
- Published
- 2023
- Full Text
- View/download PDF
3. Textile microfibers in wild Antarctic whelk Neobuccinum eatoni (Smith, 1875) from Terra Nova Bay (Ross Sea, Antarctica)
- Author
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Bergami, E., Ferrari, E., Löder, M.G.J., Birarda, G., Laforsch, C., Vaccari, L., and Corsi, I.
- Published
- 2023
- Full Text
- View/download PDF
4. Supposedly identical microplastic particles substantially differ in their material properties influencing particle-cell interactions and cellular responses
- Author
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Ramsperger, A.F.R.M., Jasinski, J., Völkl, M., Witzmann, T., Meinhart, M., Jérôme, V., Kretschmer, W.P., Freitag, R., Senker, J., Fery, A., Kress, H., Scheibel, T., and Laforsch, C.
- Published
- 2022
- Full Text
- View/download PDF
5. Occurence of microplastics in the hyporheic zone of rivers
- Author
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Frei, S., Piehl, S., Gilfedder, B. S., Löder, M. G. J., Krutzke, J., Wilhelm, L., and Laforsch, C.
- Published
- 2019
- Full Text
- View/download PDF
6. Plastic waste interferes with chemical communication in aquatic ecosystems
- Author
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Trotter, B., Ramsperger, A. F. R. M., Raab, P., Haberstroh, J., and Laforsch, C.
- Published
- 2019
- Full Text
- View/download PDF
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)
- Author
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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
- Published
- 2017
- Full Text
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9. Hazards assessment of micro- and nanoplastics and associated additives/contaminants to human health
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Katsumiti, Alberto, Rodríguez-Llopis, Isabel, Boland, S, Devineau, S, Miremont, D, Ramsperger, A.F.R.M, Löder, MGJ, Laforsch, C, Drobne, D, Michelini, S, Repar, N, Hoekstra, L, Duivenvoorde, L, van der Zande, M, Tamargo, A, Di Maira, G, Tedesco, E, Benetti, F, Antonello, G, Fenoglio, I, Riganti, C, Bergamaschi, E, Jacobsen, N.R, Kazour, M, Peijnenburg, W, Kühnel, D, Haugen, Ø. P, Wallin, H, Narui, S, and Afanou, A.J.K
- Subjects
hazard assessment ,microplastics ,exposure ,toxicity ,human health ,nanoplastics ,plastic particles - Abstract
Summary of objectives, test materials, target systems,strategies, and expected outcomes of Work Package 3 of the PlasticsFatE Project PlasticsFatE has received funding from the European Union’s Horizon 2020 Research and Innovation programme, under the Grant Agreement number 965367
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- 2022
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10. Nano- and microplastics: a comprehensive review on their exposure routes, translocation, and fate in humans
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Ramsperger, A.F.R.M., Bergamaschi, E., Panizzolo, M., Fenoglio, I., Barbero, F., Peters, R., Undas, A., Purker, S., Giese, B., Lalyer, C.R., Tamargo, A., Moreno-Arribas, M.V., Grossart, H.-P., Kühnel, Dana, Dietrich, J., Paulsen, F., Afanou, A.K., Zienolddiny-Narui, S., Eriksen Hammer, S., Kringlen Ervik, T., Graff, P., Brinchmann, B.C., Nordby, K.-C., Wallin, H., Nassi, M., Benetti, F., Zanella, M., Brehm, J., Kress, H., Löder, M.G.J., Laforsch, C., Ramsperger, A.F.R.M., Bergamaschi, E., Panizzolo, M., Fenoglio, I., Barbero, F., Peters, R., Undas, A., Purker, S., Giese, B., Lalyer, C.R., Tamargo, A., Moreno-Arribas, M.V., Grossart, H.-P., Kühnel, Dana, Dietrich, J., Paulsen, F., Afanou, A.K., Zienolddiny-Narui, S., Eriksen Hammer, S., Kringlen Ervik, T., Graff, P., Brinchmann, B.C., Nordby, K.-C., Wallin, H., Nassi, M., Benetti, F., Zanella, M., Brehm, J., Kress, H., Löder, M.G.J., and Laforsch, C.
- Abstract
Contamination of the environment with nano-and microplastic particles (NMPs) and its putative adverse effects on organisms, ecosystems, and human health is gaining increasing scientific and public attention. Various studies show that NMPs occur abundantly within the environment, leading to a high likelihood of human exposure to NMPs. Here, different exposure scenarios can occur. The most notable exposure routes of NMPs into the human body are via the airways and gastrointestinal tract (GIT) through inhalation or ingestion, but also via the skin due to the use of personal care products (PCPs) containing NMPs. Once NMPs have entered the human body, it is possible that they are translocated from the exposed organ to other body compartments. In our review article, we combine the current knowledge on the (1) exposure routes of NMPs to humans with the basic understanding of the potential (2) translocation mechanisms into human tissues and, consequently, their (3) fate within the human body. Regarding the (1) exposure routes, we reviewed the current knowledge on the occurrence of NMPs in food, beverages, personal care products and the air (focusing on indoors and workplaces) and found that the studies suggest an abundant presence of MPs within the exposure scenarios. The overall abundance of MPs in exposure matrices relevant to humans highlights the importance of understanding whether NMPs have the potential for tissue translocation. Therefore, we describe the current knowledge on the potential (2) translocation pathways of NMPs from the skin, GIT and respiratory systems to other body compartments. Here, particular attention was paid to how likely NMPs can translocate from the primary exposed organs to secondary organs due to naturally occurring defence mechanisms against tissue translocation. Based on the current understanding, we conclude that a dermal translocation of NMPs is rather unlikely. In contrast, small MPs and NPs can generally translocate from the GIT and resp
- Published
- 2022
11. Coral surface area quantification–evaluation of established techniques by comparison with computer tomography
- Author
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Naumann, M. S., Niggl, W., Laforsch, C., Glaser, C., and Wild, C.
- Published
- 2009
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12. A precise and non-destructive method to calculate the surface area in living scleractinian corals using X-ray computed tomography and 3D modeling
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Laforsch, C., Christoph, E., Glaser, C., Naumann, M., Wild, C., and Niggl, W.
- Published
- 2008
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13. Cyclomorphosis and Phenotypic Changes
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Laforsch, C., primary and Tollrian, R., additional
- Published
- 2009
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14. B10.2 A Novel Approach to Identify Wood Species Optically Using Fluorescence Lifetime Imaging Microscopy
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Leiter, N., primary, Wohlschläger, M., additional, Auer, V., additional, Versen, M., additional, and Laforsch, C., additional
- Published
- 2021
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15. Animal Prey Defenses
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Jeschke, J.M., primary, Laforsch, C., additional, and Tollrian, R., additional
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- 2008
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16. Environmental exposure enhances the internalization of microplastic particles into cells
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Ramsperger, A. F. R. M., primary, Narayana, V. K. B., additional, Gross, W., additional, Mohanraj, J., additional, Thelakkat, M., additional, Greiner, A., additional, Schmalz, H., additional, Kress, H., additional, and Laforsch, C., additional
- Published
- 2020
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17. Mikroplastik-Analytik: Probenahme, Probenaufbereitung und Detektionsverfahren. Statuspapier im Rahmen des Forschungsschwerpunktes 'Plastik in der Umwelt - Quellen, Senken, Lösungsansätze'
- Author
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Braun, U., Stein, U., Schritt, H., Altmann, K., Bannick, C., Becker, R., Ritter, H., Bochow, M., Dierkes, G., Enders, K., Eslahian, K., Fischer, D., Földi, C., Fuchs, M., Gerdts, G., Hagendorf, C., Heller, C., Ivleva, N., Jekel, M., Kerpen, J., Klaeger, F., Knoop, O., Labrenz, M., Laforsch, C., Obermaier, N., Primke, S., Reiber, J., Richter, S., Ricking, M., Scholz-Böttcher, B., Stock, F., Wagner, S., Wendt-Potthoff, K., and Zumbülte, N.
- Abstract
Das Statuspapier fasst die Inhalte der Verbundprojekt-übergreifenden Diskussionen und Abstimmungen innerhalb des Querschnittsthemas (QST) „Analytik und Referenzmaterialien“ des Forschungsschwerpunkts zusammen. Die vorliegende Fassung wurde aus dem Diskussionspapier (Link Dokument Stand Oktober 2018) entwickelt. Dieser kontinuierliche Entwicklungs- oder Erarbeitungsprozess wurde durch eine Reihe von Veranstaltungen organisatorisch untermauert: • 1. Workshop (21. März 2018, Karlsruhe) • 2. Workshop (4. Juli 2018, Augsburg) • Statuskonferenz (9.-10. April 2019, Berlin) • 3. Workshop (27. November 2019, Berlin). Folgende Verbundprojekte haben sich aktiv bei den Veranstaltungen eingebracht: EmiStop, ENSURE, MicBin, MicroCatch_Balt, MikroPlaTaS, PLASTRAT, PLAWES, RAU, REPLAWA, RUSEKU, SubµTrack und TextileMission, sowie Vorläuferprojekte (MiWa, BASEMAN). Die einzelnen Textbeiträge im vorliegenden Statuspapier wurden durch ein Kommentierungsverfahren innerhalb des QST „Analytik und Referenzmaterialien“ abgestimmt. Motivation dieses Statuspapiers ist es, die im Forschungsschwerpunkt „Plastik in der Umwelt“ verwendeten physikochemischen Untersuchungsverfahren zur Analytik von Mikroplastik (MP) zusammenzuführen. Dadurch sollen möglichst validierte Methoden und vergleichbare Ergebnisse in den verschiedenen Projekten für die jeweils spezifische Fragestellung erreicht werden – insbesondere für zukünftige Projekte. Am Ende soll ein möglichst einheitlicher Methodenpool für die relevanten Fragestellungen in Wissenschaft, Wirtschaft und Verwaltung zur Verfügung stehen. Die vorliegenden Verfahrensempfehlungen beruhen auf dem aktuellen Wissensstand zur Analytik von MP und richtet sich an Akteure in der Wissenschaft als auch Anwender in der Praxis. BMBF Forschungsschwerpunkt „Plastik in der Umwelt“ November 2020 Statuspapier Mikroplastikanalytik 7 Es werden keine Verfahrensempfehlungen zu Untersuchungen von Wirkungen von MP auf Umweltmedien, Pflanzen oder Tiere gegeben (Siehe QST „Ökotoxikologie“). Es stellt nicht einzelne Ergebnisse oder Daten dar, die im Rahmen des Forschungsschwerpunktes entstanden sind.
- Published
- 2020
18. Mikroplastik-Analytik : Probenahme, Probenaufbereitung und Detektionsverfahren. BMBF Forschungsschwerpunkt „Plastik in der Umwelt“. Statuspapier Mikroplastikanalytik. Statuspapier im Rahmen des Forschungsschwerpunktes Plastik in der Umwelt Quellen, Senken, Lösungsansätze
- Author
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Braun, U., Altmann, K., Bannick, C.G., Becker, R., Bitter, H., Bochow, M., Dierkes, G., Enders, K., Eslahian, K.A., Fischer, D., Földi, C., Fuchs, M., Gerdts, G., Hagendorf, C., Heller, C., Ivleva, N.P., Jekel, M., Kerpen, J., Klaeger, F., Knoop, O., Labrenz, M., Laforsch, C., Obermaier, N., Primpke, S., Reiber, J., Richter, S., Ricking, M., Scholz-Böttcher, B., Stock, F., Wagner, Stephan, Wendt-Potthoff, Katrin, Zumbülte, N., Braun, U., Altmann, K., Bannick, C.G., Becker, R., Bitter, H., Bochow, M., Dierkes, G., Enders, K., Eslahian, K.A., Fischer, D., Földi, C., Fuchs, M., Gerdts, G., Hagendorf, C., Heller, C., Ivleva, N.P., Jekel, M., Kerpen, J., Klaeger, F., Knoop, O., Labrenz, M., Laforsch, C., Obermaier, N., Primpke, S., Reiber, J., Richter, S., Ricking, M., Scholz-Böttcher, B., Stock, F., Wagner, Stephan, Wendt-Potthoff, Katrin, and Zumbülte, N.
- Abstract
Das Statuspapier fasst die Inhalte der Verbundprojekt-übergreifenden Diskussionen und Abstimmungen innerhalb des Querschnittsthemas (QST) „Analytik und Referenzmaterialien“ des Forschungsschwerpunkts zusammen. Die vorliegenden Verfahrensempfehlungen beruhen auf dem aktuellen Wissensstand zur Analytik von MP und richtet sich an Akteur*innen in der Wissenschaft als auch Anwender*innen in der Praxis. Die vorliegende Fassung wurde aus dem Diskussionspapier (Link Dokument Stand Oktober 2018) entwickelt. Dieser kontinuierliche Entwicklungs- oder Erarbeitungsprozess wurde durch eine Reihe von Veranstaltungen organisatorisch untermauert: 1. Workshop (21. März 2018, Karlsruhe)2. Workshop (4. Juli 2018, Augsburg)Statuskonferenz (9.-10. April 2019, Berlin)3. Workshop (27. November 2019, Berlin)Folgende Verbundprojekte haben sich aktiv bei den Veranstaltungen eingebracht: EmiStop, ENSURE, MicBin, MicroCatch_Balt, MikroPlaTaS, PLASTRAT, PLAWES, RAU, REPLAWA, RUSEKU, SubµTrack und TextileMission, sowie Vorläuferprojekte (MiWa, BASEMAN). Die einzelnen Textbeiträge im vorliegenden Statuspapier wurden durch ein Kommentierungsverfahren innerhalb des QST „Analytik und Referenzmaterialien“ abgestimmt. Motivation dieses Statuspapiers ist es, die im Forschungsschwerpunkt „Plastik in der Umwelt“ verwendeten physikochemischen Untersuchungsverfahren zur Analytik von Mikroplastik (MP) zusammenzuführen. Dadurch sollen möglichst validierte Methoden und vergleichbare Ergebnisse in den verschiedenen Projekten für die jeweils spezifische Fragestellung erreicht werden – insbesondere für zukünftige Projekte. Am Ende soll ein möglichst einheitlicher Methodenpool für die relevanten Fragestellungen in Wissenschaft, Wirtschaft und Verwaltung zur Verfügung stehen.
- Published
- 2020
19. Coastal accumulation mapping of microplastic particles emitted from the Po River, Italy: Integrating remote sensing, in situ sample collections and ocean current modelling
- Author
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Atwood, E., Falcieri, F., Piehl, S., Bochow, M., Matthies, M., Franke, J., Carniel, S., Scavo, M., Laforsch, C., and Siegert, F.
- Abstract
Plastic pollution in inland waters and the open ocean is a long recognized problem for marine wildlife, coral reefs,the fishing industry and shipping transport safety. Microplastics, defined as particles < 5 mm, form a considerableportion of this pollution and have increasingly received public attention following recent discoveries that not onlycan these particles be ingested by planktonic animals, but also outnumber natural food items in some ocean ar-eas. Microplastic research has mainly concentrated on open seas, while riverine plumes and coastal areas remainlargely unexplored despite their hypothesized importance as microplastic sources. This work models coastal accu-mulation along the Adriatic coastline of microplastic particles (1-5 mm) emitted by the Po River, northern Italy,over 1.5 years. We hypothesize that river-induced microplastic accumulation on adjacent coasts can be predictedusing (1) hydrodynamic-based and (2) remote sensing-based modelling. Model accumulation maps were validatedagainst sampling at nine beaches (analyzed particle size range: 1-5 mm), with sediment microplastic concentra-tions up to 78 particles/kg (dry weight). Hydrodynamic modelling revealed that discharged particle amount is onlysemi-coupled to beaching rates, which are strongly river mouth dependent and occur primarily within the first tendays after discharge. Particles which did not beach within this period, representing more than 80% of all modelledparticles, were transported offshore and remained offshore. Remote sensing modelling was found to better captureriver mouth relative strength, and accumulation patterns were found largely consistent with hydrodynamic mod-elling. Comparison with remote sensing based accumulation maps and validation against in situ beach samplingare discussed. Suggestions are presented for future development of an operational monitoring system to assessmicroplastic pollution being emitted by a major river and its distribution along adjacent coastlines as well as intothe open ocean.
- Published
- 2019
20. Defining the Baselines and Standards for Microplastics Analyses in European Waters (JPI-O BASEMAN)
- Author
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Gerdts, G., Thomas, K., Herzke, D., Haeckel, M., Scholz-Böttcher, B., Laforsch, C., Lagarde, F., Mahon, A.M., Pedrotti, M.L., de Lucia, G.A., Sobral, P., Gago, J., Lorenzo, S.M., Noren, F., Hassellöv, M., Kögel, T., Tirelli, V., Caetano, M., Collignon, A., Lips, I., Mallow, O., Seatala, O., Goede, K., and Licandro, P.
- Published
- 2017
- Full Text
- View/download PDF
21. Coastal accumulation mapping of microplastic particles emitted from the Po River, Italy: Comparing remote sensing, in situ sample collections and ocean current modelling
- Author
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Atwood, E., Falcieri, F., Piehl, S., Bochow, M., Matthies, M., Franke, J., Carniel, S., Scalvo, M., Laforsch, C., and Siegert, F.
- Abstract
Plastic pollution in inland waters and the open ocean is a long recognized problem for marine wildlife, coral reefs,the fishing industry and shipping transport safety. Microplastics, defined as particles < 5 mm, form a considerableportion of this pollution and have increasingly received public attention following recent discoveries that not onlycan these particles be ingested by planktonic animals, but also outnumber natural food items in some ocean ar-eas. Microplastic research has mainly concentrated on open seas, while riverine plumes and coastal areas remainlargely unexplored despite their hypothesized importance as microplastic sources. This work models coastal accu-mulation along the Adriatic coastline of microplastic particles (1-5 mm) emitted by the Po River, northern Italy,over 1.5 years. We hypothesize that river-induced microplastic accumulation on adjacent coasts can be predictedusing (1) hydrodynamic-based and (2) remote sensing-based modelling. Model accumulation maps were validatedagainst sampling at nine beaches (analyzed particle size range: 1-5 mm), with sediment microplastic concentra-tions up to 78 particles/kg (dry weight). Hydrodynamic modelling revealed that discharged particle amount is onlysemi-coupled to beaching rates, which are strongly river mouth dependent and occur primarily within the first tendays after discharge. Particles which did not beach within this period, representing more than 80% of all modelledparticles, were transported offshore and remained offshore. Remote sensing modelling was found to better captureriver mouth relative strength, and accumulation patterns were found largely consistent with hydrodynamic mod-elling. Comparison with remote sensing based accumulation maps and validation against in situ beach samplingare discussed. Suggestions are presented for future development of an operational monitoring system to assessmicroplastic pollution being emitted by a major river and its distribution along adjacent coastlines as well as intothe open ocean.
- Published
- 2018
22. The use of spiked samples for the validation of microplastic recovery and analysis methods: density separation, enzymatic purification and FTIR analysis
- Author
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Dris, R., Bochow, M., Löder, M., Kögel, T., Scholz-Böttcher, B., Gerdts, G., and Laforsch, C.
- Published
- 2018
23. The ecoresponsive genome of Daphnia pulex
- Author
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Colbourne, J. K., Pfrender, M. E., Gilbert, D., Thomas, W. K., Tucker, A., Oakley, T. H., Tokishita, S., Aerts, A., Arnold, G. J., Basu, M. K., Bauer, D. J., C當eres, C. E., Carmel, L., Casola, C., Choi, J. H., Detter, J. C., Dong, Q., Dusheyko, S., Eads, B. D., Frlich, T., Geiler-Samerotte, K. A., Gerlach, D., Hatcher, P., Jogdeo, S., Krijgsveld, J., Kriventseva, E. V., K�ltz, D., Laforsch, C., Lindquist, E., Lopez, J., Manak, J. R., Muller, J., Pangilinan, J., Patwardhan, R. P., Pitluck, S., Pritham, E. J., Rechtsteiner, A., Rho, M., Rogozin, I. B., Sakarya, O., Salamov, A., Schaack, S., Shapiro, H., Shiga, Y., Skalitzky, C., Smith, Z., Souvorov, A., Sung, W., Tang, Z., Tsuchiya, D., Tu, H., Vos, H., Wang, M., Wolf, Y. I., Yamagata, H., Yamada, Takuji, Ye, Y., Shaw, J. R., Andrews, J., Crease, T. J., Tang, H., Lucas, S. M., Robertson, H. M., Bork, P., Koonin, E. V., Zdobnov, E. M., Grigoriev, I. V., Lynch, M., Boore, J. L., Gerlach, Daniel, Kriventseva, Evgenia, and Zdobnov, Evgeny
- Subjects
0106 biological sciences ,Molecular Sequence Data ,Gene Conversion ,Gene Expression ,Biology ,Environment ,010603 evolutionary biology ,01 natural sciences ,Genome ,Daphnia pulex ,Evolution, Molecular ,03 medical and health sciences ,Genes, Duplicate ,Gene Duplication ,Gene duplication ,Gene family ,Animals ,ddc:576.5 ,Gene conversion ,Amino Acid Sequence ,Gene ,Ecosystem ,Phylogeny ,030304 developmental biology ,Regulation of gene expression ,Genetics ,0303 health sciences ,Multidisciplinary ,Base Sequence ,Daphnia/genetics/physiology ,Metabolic Networks and Pathways/genetics ,Gene Expression Profiling ,fungi ,Chromosome Mapping ,Molecular Sequence Annotation ,Sequence Analysis, DNA ,biology.organism_classification ,Adaptation, Physiological ,Gene expression profiling ,Daphnia ,Gene Expression Regulation ,Genes ,Multigene Family ,Metabolic Networks and Pathways - Abstract
We describe the draft genome of the microcrustacean Daphnia pulex, which is only 200 megabases and contains at least 30,907 genes. The high gene count is a consequence of an elevated rate of gene duplication resulting in tandem gene clusters. More than a third of Daphnia's genes have no detectable homologs in any other available proteome, and the most amplified gene families are specific to the Daphnia lineage. The coexpansion of gene families interacting within metabolic pathways suggests that the maintenance of duplicated genes is not random, and the analysis of gene expression under different environmental conditions reveals that numerous paralogs acquire divergent expression patterns soon after duplication. Daphnia-specific genes, including many additional loci within sequenced regions that are otherwise devoid of annotations, are the most responsive genes to ecological challenges.
- Published
- 2011
- Full Text
- View/download PDF
24. Enzymatic Purification of Microplastics in Environmental Samples
- Author
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Löder, M. G. J., Imhof, H. K., Ladehoff, M., Löschel, L. A., Lorenz, C., Mintenig, S., Piehl, S., Primpke, S., Schrank, I., Laforsch, C., Gerdts, G., Löder, M. G. J., Imhof, H. K., Ladehoff, M., Löschel, L. A., Lorenz, C., Mintenig, S., Piehl, S., Primpke, S., Schrank, I., Laforsch, C., and Gerdts, G.
- Abstract
Micro-Fourier transform infrared (micro-FTIR) spectroscopy and Raman spectroscopy enable the reliable identification and quantification of microplastics (MPs) in the lower micron range. Since concentrations of MPs in the environment are usually low, the large sample volumes required for these techniques lead to an excess of coenriched organic or inorganic materials. While inorganic materials can be separated from MPs using density separation, the organic fraction impedes the ability to conduct reliable analyses. Hence, the purification of MPs from organic materials is crucial prior to conducting an identification via spectroscopic techniques. Strong acidic or alkaline treatments bear the danger of degrading sensitive synthetic polymers. We suggest an alternative method, which uses a series of technical grade enzymes for purifying MPs in environmental samples. A basic enzymatic purification protocol (BEPP) proved to be efficient while reducing 98.3 ± 0.1 % of the sample matrix in surface water samples. After showing a high recovery rate ( 84.5 ± 3.3% ), the BEPP was successfully applied to environmental samples from the North Sea where numbers of MPs range from 0.05 to 4.42 items m -3_ Experiences with different environmental sample matrices were considered in an improved and universally applicable version of the BEPP, which is suitable for focal plane array detector (FPA)-based micro-FTIR analyses of water, wastewater, sediment, biota, and food samples.
- Published
- 2017
- Full Text
- View/download PDF
25. Satelliten-gestützte Methoden zur Erfassung von Quellen und Verbreitungsmuster von Mikroplastik in aquatischen Ökosystemen
- Author
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Piehl, S., Bochow, M., Atwood, L., Imhof, H., Schrank, I., Franke, J., Englhart, S., Siegert, F., and Laforsch, C.
- Published
- 2015
26. Strukturelle Veränderungen und Belastungen von Gewässern. V-6.1 Mikroplastik in Binnengewässern
- Author
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Hupfer, M., Calmano, W., Fischer, H., Klapper, H., Wendt-Potthoff, Katrin, Imhof, H.K., Wagner, M., Primpke, S., Fischer, D., Scholz-Böttcher, B., Laforsch, C., Hupfer, M., Calmano, W., Fischer, H., Klapper, H., Wendt-Potthoff, Katrin, Imhof, H.K., Wagner, M., Primpke, S., Fischer, D., Scholz-Böttcher, B., and Laforsch, C.
- Published
- 2015
27. List of Contributors
- Author
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Abbas, B., Abreu, A., Adams, R., Adolfsson-Erici, M., Afonso, A., Afonso-Olivares, C., Agirbas, E., Aguiló, J.M., Airoldi, L., Aksoy, H., Albentosa, M., Alcaro, L., Aliani, S., Al-Maslamani, I., Alomar, C., Altin, D., Álvarez, E., Amaral-Zettler, L.A., Amato, E., Anderson, A., Andrady, A.L., Andrius, G., Angel, D., Ariese, F., Arp, H.P., Asensio, M., Assidqi, K., Avio, C.G., Aytan, U., Bahri, T., Baini, M., Bakir, A., Ball, H., Baranyi, C., Barboza, L.G.A., Barg, U., Bargelloni, L., Barras, H., Barrera, C., Barria, P., Barrows, A., Barth, A., Batel, A., Baztan, J., Baztan, P., Beiras, R., Benedetti, M., Berber, A.A., Berber, N., Bergmann, M., Berlino, M., Berrow, S., Bessa, F., Besseling, E., Beyer, B., Binaglia, M., Bizjak, T., Bjorndal, K.A., Blust, R., Boertien, M., Bolten, A.B., Booth, A.M., Bounoua, B., Bourseau, P., Brahimi, N., Bramini, M., Brennholt, N., Breuninger, E., Bried, J., Broderick, A., Broglio, E., Browne, M.A., Bruzaud, S., Buceta, J., Buchinger, S., Budimir, S., Budzin-ski, H., Butter, E., Cachot, J., Caetano, M., Callaghan, A., Camedda, A., Capella, S., Cardelli, L., Carpentieri, S., Carrasco, A., Carriço, R., Caruso, A., Cassone, A.-L., Castillo, A., Castro, R.O., Catarino, A.I., Cazenave, P.W., Çelik, İ., Cerralbo, P., César, G., Chouinard, O., Chubarenko, I., Chubarenko, I.P., Cicero, A.M., Clarindo, G., Clarke, B., Clérandeau, C., Clüsener-Godt, M., Codina-García, M., Cole, M., Collard, F., Collignon, A., Collins, T., Compa, M., Conan, P., Constant, M., Cordier, M., Courtene-Jones, W., Cousin, X., Covelo, P., Cózar, A., Crichton, E., Crispi, O., Cronin, M., Croot, P.L., Cruz, M.J., d’Errico, G., Dâmaso, C., Das, K., de Alencastro, L.F., de Araujo, F.V., de Boer, J.F., de Lucia, G.A., Debeljak, P., Dehaut, A., Deudero, S., Devrieses, L., Di Vito, S., Díaz, A., Donohue, J., Doumenq, P., Doyle, T.K., Dris, R., Druon, J.-N., Duarte, C.M., Duflos, G., Dumontier, M., Duncan, E., Dussud, C., Eckerlebe, A., Egelkraut-Holtus, M., Eidsvoll, D.P., Ek, C., Elena, S., Elineau, A., Enevoldsen, H., Eppe, G., Eriksen, M., Ernsteins, R., Espino, M., Estévez-Calvar, N., Ewins, C., Fabre, P., Faimali, M., Fattorini, D., Faure, F., Ferrando, S., Ferreira, J.C., Ferreira-da-Costa, M., Fileman, E., Fischer, M., Fortunato, A.B., Fossi, M.C., Foulon, V., Frank, A., Frenzel, M., Frère, L., Frias, J.P.G.L., Frick, H., Froneman, P.W., Gabet, V.M., Gabrielsen, G.W., Gago, J., Gajst, T., Galgani, F., Gallinari, M., Galloway, T.S., Gamarro, E.G., Gambardella, C., Garaventa, F., Garcia, S., Garrabou, J., Garrido, P., Gary, S.F., Gasperi, J., Gaze, W., Geertz, T., Gelado-Caballero, M.D., George, M., Gercken, J., Gerdts, G., Ghiglione, J.-F., Gies, E., Gilbert, B., Giménez, L., Glassom, D., Glockzin, M., Godley, B., Goede, K., Goksøyr, A., Gómez, M., Gómez-Parra, A., González-Marco, D., González-Solís, J., Gorbi, S., Gorokhova, E., Gorsky, G., Gosch, M., Grose, J., Guebitz, G.M., Guedes-Alonso, R., Guijarro, B., Guilhermino, L., Gundry, T., Gutow, L., Haave, M., Haeckel, M., Haernvall, K., Hajbane, S., Hamann, M., Hämer, J., Hamm, T., Hansen, B.H., Hardesty, B.D., Harth, B., Hartikainen, S., Hassellöv, M., Hatzky, S., Healy, M.G., Hégaret, H., Henry, T.B., Hermabessiere, L., Hernández-Brito, J.J., Hernandez-Gonzalez, A., Hernandez-Milian, G., Hernd, G., Herrera, A., Herring, C., Herzke, D., Heussner, S., Hidalgo-Ruz, V., Himber, C., Holland, M., Hong, N.-H., Horton, A.A., Horvat, P., Huck, T., Huhn, M., Huvet, A., Iglesias, M., Igor, C., Isachenko, I.A., Ivar do Sul, J-A., Jahnke, A., Janis, B., Janis, K., Janis, U., Jemec, A., Jiménez, J.C., Johnsen, H., Jorgensen, B., Jørgensen, J.H., Jörundsdóttir, H., Jung, Y.-J., Kedzierski, M., Keiter, S., Kershaw, P., Kerhervé, P., Kesy, K., Khan, F., Khatmullina, L.I., Kirby, J., Kiriakoulakis, K., Klein, R., Klunderud, T., Knudsen, C.M.H., Knudsen, T.B., Kochleus, C., Koelmans, A.A., Kögel, T., Koistinen, A., Kopke, K., Korez, Š., Kowalski, N., Kreikemeyer, B., Kroon, F., Krumpen, T., Krzan, A., Kržan, A., Labrenz, M., Lacroix, C., Ladirat, L., Laforsch, C., Lagarde, F., Lahive, E., Lambert, C., Lapucci, C., Lattin, G., Law, K.L., Le Roux, F., Le Souef, K., Le Tilly, V., Lebreton, L., Leemans, E., Lehtiniemi, M., Lenz, M., Leskinen, J., Leslie, H., Leslie, H.A., Levasseur, C., Lewis, C., Licandro, P., Lind, K., Lindeque, P., Lindeque, P.K., Lips, I., Liria, A., Liria-Loza, A., Llinás, O., Loiselle, S.A., Long, M., Lorenz, C., Lorenzo, S.M., Loubar, K., Luna-Jorquera, G., Lusher, A.L., Macchia, V., MacGabban, S., Mackay, K., MacLeod, M., Maes, T., Magaletti, E., Maggiore, A., Magnusson, K., Mahon, A.M., Makorič, P., Mallow, O., Marques, J., Marsili, L., Martí, E., Martignac, M., Martin, J., Martínez, I., Martínez, J., Martinez-Gil, M., Martins, H.R., Matiddi, M., Maximenko, N., Mazlum, R., Mcadam, R., Mcknight, L., McNeal, A.W., Measures, J., Mederos, M.S., Mendoza, J., Meyer, M.S., Miguelez, A., Milan, M., Militão, T., Miller, R.Z., Mino-Vercellio-Verollet, M., Mir, G., Miranda-Urbina, D., Misurale, F., Montesdeoca-Esponda, S., Mora, J., Morgana, S., Moriceau, B., Morin, B., Morley, A., Morrison, L., Murphy, F., Naidoo, T., Näkki, P., Napper, I.E., Narayanaswamy, B.E., Nash, R., Negri, A., Nel, H.A., Nerheim, M.S., Nerland, I.L., Neto, J., Neves, V., Nies, H., Noel, M., Nor, N.H.M., Noren, F., O’ Connell, B., O’ Connor, I., Obbard, J.P., Oberbeckmann, S., Obispo, R., Officer, R., Ogonowski, M., Orbea, A., Ortlieb, M., Osborn, A.M., Ostiategui-Francia, P., Packard, T., Pahl, S., Palatinus, A., Palmqvist, A., Pannetier, P., Panti, C., Parmentier, E., Pasanen, P., Patarnello, T., Pattiaratchi, C., Pauletto, M., Paulus, M., Pavlekovsky, K., Pedersen, H.B., Pedrotti, M.-L., Peeken, I., Peeters, D., Peeters, E., Pellegrini, D., Perales, J.A., Perez, E., Perz, V., Petit, S., Pflieger, M., Pham, C.K., Piazza, V., Pinto, M., Planells, O., Plaza, M., Pompini, O., Potthoff, A., Prades, L., Primpke, S., Proietti, M., Proskurowski, G., Puig, C., Pujo-Pay, M., Pullerits, K., Queirós, A.M., Quinn, B., Raimonds, E., Ramis-Pujol, J., Rascher-Friesenhausen, R., Reardon, E., Regoli, F., Reichardt, A.M., Reifferscheid, G., Reilly, K., Reisser, J., Riba, I., Ribitsch, D., Rinnert, E., Rios, N., Rist, S.E., Rivadeneira, M.M., Rivière, G., Robbens, J., Robertson, C.J.R., Rocher, V., Rochman, C.M., Rodrigues, M., Rodriguez, Y., Rodríguez, A., Rodríguez, G., Rodríguez, J.R.B., Rodríguez, S., Rodríguez, Y., Rogan, E., Rojo-Nieto, E., Romeo, T., Ross, P.S., Roveta, A., Rowland, S.J., Ruckstuhl, N.A., Ruiz-Fernández, A-C., Ruiz-Orejón, L.F., Runge, J., Russell, M., Saavedra, C., Saborowski, R., Sahin, B.E., Sailley, S., Sakaguchi-Söder, K., Salaverria, I., Sánchez-Arcilla, A., Sánchez-Nieva, J., Sanderson, W., Santana-Rodríguez, J.J., Santana-Viera, S., Santos, M.B., Santos, M.R., Sanz, M.R., Sardá, R., Savelli, H., Schoeneich-Argent, R., Scholz-Böttcher, B.M., Sciacca, F., Scofield, R.P., Setälä, O., Selenius, M., Sempere, R., Senturk, Y., Shashoua, Y., Sherman, P., Sick, C., Siegel, D., Sierra, J.P., Silva, F., Silvestri, C., Sintija, G., Sire, O., Slat, B., Smit, A., Sobral, P., Sorvari, J., Sosa-Ferrera, Z., Sotillo, M.G., Soudant, P., Speidel, L., Spurgeon, D.J., Steer, M.K., Steindal, C.C., Stifanese, R., Štindlová, A., Stuurman, L., Suaria, G., Suazo, C.G., Sureda, A., Surette, C., Svendsen, C., Syberg, K., Tairova, Z., Talvitie, J., Tassin, B., Tazerout, M., Tekman, M.B., ter Halle, A., Thiel, M., Thomas, K.V., Thompson, R.C., Tinkara, T., Tirelli, V., Tomassetti, P., Toorman, E., Toppe, J., Tornambè, A., Torres, R., Torres-Padrón, M.E., Underwood, A.J., Urbina, M., Usategui-Martín, A., Usta, R., Valdés, L., Valente, A., Valentina, T., van Arkel, K., Van Colen, C., Van Der Hal, N., van Franeker, J.A., Van Herwerden, L., Van Loosdrecht, M., van Oyen, A., Vandeperre, F., Vanderlinden, J-P., Vani, D., Vasconcelos, L., Vega-Moreno, D., Ventero, A., Vethaak, A.D., Vianello, A., Vicioso, M., Vieira, L.R., Viršek, M.K., Vos, M., Wahl, M., Wallace, N., Walton, A., Waniek, J.J., Watts, A., Webster, L., Wesch, C., Whitfield, E., Wichels, A., Wieczorek, A.M., Wilcox, C., Williams, R.J., Wong-Wah-Chung, P., Wright, S., Wyles, K.J., Young, R., Yurtsever, M., Yurtsever, U., Zada, L., Zamani, N.P., and Zampetti, G.
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- 2017
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28. Interclonal variation, effectiveness and long-term implications of Triops-induced morphological defences in Daphnia magna Strauss
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Rabus, M., primary, Waterkeyn, A., additional, van Pottelbergh, N., additional, Brendonck, L., additional, and Laforsch, C., additional
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- 2011
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29. Extreme helmet formation in Daphnia cucullata induced by small-scale turbulence
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Laforsch, C., primary
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- 2004
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30. Fighting parasites and predators: How to deal with multiple threats?
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Hesse Olivia, Engelbrecht Wolfgang, Laforsch Christian, and Wolinska Justyna
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Daphnia ,Host-parasite ,Inducible defences ,Metschnikowia sp. ,Multiple stressors ,Phenotypic plasticity ,Predator–prey ,Ecology ,QH540-549.5 - Abstract
Abstract Background Although inducible defences have been studied extensively, only little is known about how the presence of parasites might interfere with these anti-predator adaptations. Both parasites and predators are important factors shaping community structure and species composition of ecosystems. Here, we simultaneously exposed Daphnia magna to predator cues (released by the tadpole shrimp, Triops, or by a fish) and spores of the yeast parasite Metschnikowia sp. to determine how life history and morphological inducible defences against these two contrasting types of predators are affected by infection. Results The parasite suppressed some Triops-induced defences: Daphnia lost the ability to produce a greater number of larger offspring, a life-history adaptation to Triops predation. In contrast, the parasite did not suppress inducible defences against fish: induction (resulting in smaller body length of the mothers as well as of their offspring) and infection acted additively on the measured traits. Thus, fish-induced defences may be less costly than inducible defences against small invertebrate predators like Triops; the latter defences could no longer be expressed when the host had already invested in fighting off the parasite. Conclusions In summary, our study suggests that as specific inducible defences differ in their costs, some might be suppressed if a target prey is additionally infected. Therefore, adding parasite pressure to predator–prey systems can help to elucidate the costs of inducible defences.
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- 2012
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31. Resolving the infection process reveals striking differences in the contribution of environment, genetics and phylogeny to host-parasite interactions
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Laforsch Christian, Ben-Ami Frida, Luijckx Pepijn, Duneau David, and Ebert Dieter
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Biology (General) ,QH301-705.5 - Abstract
Abstract Background Infection processes consist of a sequence of steps, each critical for the interaction between host and parasite. Studies of host-parasite interactions rarely take into account the fact that different steps might be influenced by different factors and might, therefore, make different contributions to shaping coevolution. We designed a new method using the Daphnia magna - Pasteuria ramosa system, one of the rare examples where coevolution has been documented, in order to resolve the steps of the infection and analyse the factors that influence each of them. Results Using the transparent Daphnia hosts and fluorescently-labelled spores of the bacterium P. ramosa, we identified a sequence of infection steps: encounter between parasite and host; activation of parasite dormant spores; attachment of spores to the host; and parasite proliferation inside the host. The chances of encounter had been shown to depend on host genotype and environment. We tested the role of genetic and environmental factors in the newly described activation and attachment steps. Hosts of different genotypes, gender and species were all able to activate endospores of all parasite clones tested in different environments; suggesting that the activation cue is phylogenetically conserved. We next established that parasite attachment occurs onto the host oesophagus independently of host species, gender and environmental conditions. In contrast to spore activation, attachment depended strongly on the combination of host and parasite genotypes. Conclusions Our results show that different steps are influenced by different factors. Host-type-independent spore activation suggests that this step can be ruled out as a major factor in Daphnia-Pasteuria coevolution. On the other hand, we show that the attachment step is crucial for the pronounced genetic specificities of this system. We suggest that this one step can explain host population structure and could be a key force behind coevolutionary cycles. We discuss how different steps can explain different aspects of the coevolutionary dynamics of the system: the properties of the attachment step, explaining the rapid evolution of infectivity and the properties of later parasite proliferation explaining the evolution of virulence. Our study underlines the importance of resolving the infection process in order to better understand host-parasite interactions.
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- 2011
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32. LC-MS/MS-based proteome profiling in Daphnia pulex and Daphnia longicephala: the Daphnia pulex genome database as a key for high throughput proteomics in Daphnia
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Mayr Tobias, Fritsch Rainer, Arnold Georg J, Fröhlich Thomas, and Laforsch Christian
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Biotechnology ,TP248.13-248.65 ,Genetics ,QH426-470 - Abstract
Abstract Background Daphniids, commonly known as waterfleas, serve as important model systems for ecology, evolution and the environmental sciences. The sequencing and annotation of the Daphnia pulex genome both open future avenues of research on this model organism. As proteomics is not only essential to our understanding of cell function, and is also a powerful validation tool for predicted genes in genome annotation projects, a first proteomic dataset is presented in this article. Results A comprehensive set of 701,274 peptide tandem-mass-spectra, derived from Daphnia pulex, was generated, which lead to the identification of 531 proteins. To measure the impact of the Daphnia pulex filtered models database for mass spectrometry based Daphnia protein identification, this result was compared with results obtained with the Swiss-Prot and the Drosophila melanogaster database. To further validate the utility of the Daphnia pulex database for research on other Daphnia species, additional 407,778 peptide tandem-mass-spectra, obtained from Daphnia longicephala, were generated and evaluated, leading to the identification of 317 proteins. Conclusion Peptides identified in our approach provide the first experimental evidence for the translation of a broad variety of predicted coding regions within the Daphnia genome. Furthermore it could be demonstrated that identification of Daphnia longicephala proteins using the Daphnia pulex protein database is feasible but shows a slightly reduced identification rate. Data provided in this article clearly demonstrates that the Daphnia genome database is the key for mass spectrometry based high throughput proteomics in Daphnia.
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- 2009
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33. Cellular internalization pathways of environmentally exposed microplastic particles: Phagocytosis or macropinocytosis?
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Ramsperger AFRM, Wieland S, Wilde MV, Fröhlich T, Kress H, and Laforsch C
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Microplastic particles (MP) ubiquitously occur in all environmental compartments where they interact with biomolecules, forming an eco-corona on their surfaces. The eco-corona affects the surface properties of MP and consequently how they interact with cells. Proteins, an integral component within the eco-corona, may serve as a ligand driving the interaction of MP with membrane receptors. To date, it is not known, whether eco-coronae originating from different environmental media differ in their proteinaceous compositions and whether these particles interact differently with cells. We show that the protein composition of the eco-coronae formed in freshwater (FW) and salt water (SW) are distinct from each other. We did not observe different adhesion strengths between MP coated with different eco-coronae and cells. However, the internalization efficiency and the underlying internalization mechanisms significantly differed between FW- and SW eco-coronae. By inhibiting actin-driven and receptor-mediated internalization processes using Cytochalasin-D, Amiloride, and Amantadine, we show that FW microplastic particles predominantly become internalized via phagocytosis, while macropinocytosis is more important for SW microplastic particles. Overall, our findings show that the origin of eco-coronae coatings are important factors for the cellular internalization of microplastic particles. This highlights the relevance of eco-coronae for adverse effects of environmentally relevant microplastic particles on cells and organisms., 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 © 2025 The Authors. Published by Elsevier B.V. All rights reserved.)
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- 2025
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34. What Goes Around Should Not Move Around: Immobilizing Microplastics as a New Approach for Analytical Ring Trials.
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Lenz R, Enders K, Vizsolyi EC, Schumacher M, Lötsch J, Löder MGJ, Eder G, Voronko Y, Andrade-Garda JM, Muniategui-Lorenzo S, Laforsch C, Fischer D, and Labrenz M
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- Environmental Monitoring methods, Filtration, Particulate Matter, Particle Size, Microplastics
- Abstract
Microplastics have gained importance as pervasive environmental particulate pollutants. Their analysis demands precise quantification methods, with interlaboratory comparisons (ILCs) being crucial for performance assessment. Typically, ILCs follow a parallel design: participants each analyze their own sample specimen, often with significant variability due to challenges in producing identical subsamples of the particulate analyte, inseparably masking the relevant uncertainty sources the ILC intends to measure. We provide a filtration-immobilization approach for particles ≤100 μm, creating permanently immobilized microplastics samples. This enables serial ILC designs where participants sequentially measure the same sample. Demonstrating the concept using 5 polymers immobilized on 10 μm pore-sized silicon filters, we expose the specific measurement uncertainty being 77% lower than the total combined uncertainty observed in a parallel ILC (relative standard deviations: 5 and 23%, respectively). Particle immobilization opens further applications in sample archiving and creation of durable reference samples also for other fields of particulate matter research beyond microplastics.
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- 2024
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35. A review on nanomaterial-based SERS substrates for sustainable agriculture.
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Mahanty S, Majumder S, Paul R, Boroujerdi R, Valsami-Jones E, and Laforsch C
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- Spectrum Analysis, Raman methods, Agriculture methods, Nanostructures, Crops, Agricultural
- Abstract
The agricultural sector plays a pivotal role in driving the economy of many developing countries. Any dent in this economical structure may have a severe impact on a country's population. With rising climate change and increasing pollution, the agricultural sector is experiencing significant damage. Over time this cumulative damage will affect the integrity of food crops and create food security issues around the world. Therefore, an early warning system is needed to detect possible stress on food crops. Here we present a review of the recent developments in nanomaterial-based Surface Enhanced Raman Spectroscopy (SERS) substrates which could be utilized to monitor agricultural crop responses to natural and anthropogenic stress. Initially, our review delves into diverse and cost-effective strategies for fabricating SERS substrates, emphasizing their intelligent utilization across various agricultural scenarios. In the second phase of our review, we spotlight the specific application of SERS in addressing critical food security issues. By detecting nutrients, hormones, and effector molecules in plants, SERS provides valuable insights into plant health. Furthermore, our exploration extends to the detection of contaminants, chemicals, and foodborne pathogens within plants, showcasing the versatility of SERS in ensuring food safety. The cumulative knowledge derived from these discussions illustrates the transformative potential of SERS in bolstering the agricultural economy. By enhancing precision in nutrient management, monitoring plant health, and enabling rapid detection of harmful substances, SERS emerges as a pivotal tool in promoting sustainable and secure agricultural practices. Its integration into agricultural processes not only augments productivity but also establishes a robust defence against potential threats to crop yield and food quality. As SERS continues to evolve, its role in shaping the future of agriculture becomes increasingly pronounced, promising a paradigm shift in how we approach and address challenges in food production and safety., Competing Interests: Declaration of competing interest The authors have no relevant financial or non-financial interests to disclose., (Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.)
- Published
- 2024
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36. Production and characterisation of environmentally relevant microplastic test materials derived from agricultural plastics.
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Hurley R, Binda G, Briassoulis D, Carroccio SC, Cerruti P, Convertino F, Dvořáková D, Kernchen S, Laforsch C, Löder MGL, Pulkrabova J, Schettini E, Spanu D, Tsagkaris AS, Vox G, and Nizzetto L
- Abstract
Soil environments across the globe, particularly in agricultural settings, have now been shown to be contaminated with microplastics. Agricultural plastics - such as mulching films - are used in close or direct contact with soils and there is growing evidence demonstrating that they represent a potential source of microplastics. There is a demand to undertake fate and effects studies to understand the behaviour and potential long-term ecological risks of this contamination. Yet, there is a lack of test materials available for this purpose. This study describes the manufacture and characterisation of five large (1-40 kg) batches of microplastic test materials derived from agricultural mulching films. Batches were produced from either polyethylene-based conventional mulching films or starch-polybutadiene adipate terephthalate blend mulching films that are certified biodegradable in soil. Challenges encountered and overcome during the micronisation process provide valuable insights into the future of microplastic test material generation from these material types. This includes difficulties in micronising virgin polyethylene film materials. All five batches were subjected to a thorough physical and chemical characterisation - both of the original virgin films and the subsequent microplastic particles generated - including a screening for the presence of chemical additives. This is a critical step to provide essential information for interpreting particle fate or effects in scientific testing. Trade-offs between obtaining preferred particle typologies and time and cost constraints are elucidated. Several recommendations emerging from the experiences gained in this study are put forward to advance the research field towards greater harmonisation and utilisation of environmentally relevant test materials., Competing Interests: Declaration of competing interest The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: Rachel Hurley reports financial support was provided by European Commission. Rachel Hurley reports financial support was provided by Research Council of Norway. Christian Laforsch reports financial support was provided by German Research Foundation. 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., (Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.)
- Published
- 2024
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37. Retention of microplastics by biofilms and their ingestion by protists in rivers.
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Hamann L, Werner J, Haase FJ, Thiel M, Scherwaß A, Laforsch C, Löder MGJ, Blanke A, and Arndt H
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- Germany, Ciliophora physiology, Water Pollutants, Chemical metabolism, Water Pollutants, Chemical analysis, Rivers microbiology, Rivers chemistry, Rivers parasitology, Microplastics analysis, Biofilms growth & development
- Abstract
Microplastics (MPs) are released into the environment through human activities and are transported by rivers from land to sea. Biofilms, which are ubiquitous in aquatic ecosystems such as rivers, may play an essential role in the fate of MPs and their ingestion by biofilm protists. To assess this, biofilms were naturally grown on clay tiles in the River Rhine, Germany, and analysed in a combined field and laboratory study. Compared to the ambient river water, biofilms grown for 6, 12, and 18 months in the River Rhine contained up to 10 times more MPs. Between 70% and 78% of all MPs were smaller than 50 μm. In laboratory experiments, clay tiles covered with 1-month-old naturally grown biofilm retained 6-12 times more MPs than clay tiles without biofilm coverage. Furthermore, the ingestion of MPs of 6 and 10 μm by the ciliate Stentor coeruleus was confirmed, and a positive correlation between ingestion rates and ambient MP concentrations was found. The results are relevant for particle transport models in riverine systems, risk assessment of MPs regarding their distribution and fate in the aquatic environment, and the effects of MPs on micro- and macroorganisms., (© 2024 The Author(s). Environmental Microbiology Reports published by John Wiley & Sons Ltd.)
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- 2024
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38. The cuticle proteome of a planktonic crustacean.
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Otte KA, Fredericksen M, Fields P, Fröhlich T, Laforsch C, and Ebert D
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- Animals, Proteomics methods, Chitin metabolism, Chitin analysis, Proteome metabolism, Proteome analysis, Proteome genetics, Daphnia metabolism, Daphnia genetics, Arthropod Proteins metabolism, Arthropod Proteins genetics, Arthropod Proteins analysis
- Abstract
The cuticles of arthropods provide an interface between the organism and its environment. Thus, the cuticle's structure influences how the organism responds to and interacts with its surroundings. Here, we used label-free quantification proteomics to provide a proteome of the moulted cuticle of the aquatic crustacean Daphnia magna, which has long been a prominent subject of studies on ecology, evolution, and developmental biology. We detected a total of 278 high-confidence proteins. Using protein sequence domain and functional enrichment analyses, we identified chitin-binding structural proteins and chitin-modifying enzymes as the most abundant protein groups in the cuticle proteome. Structural cuticular protein families showed a similar distribution to those found in other arthropods and indicated proteins responsible for the soft and flexible structure of the Daphnia cuticle. Finally, cuticle protein genes were also clustered as tandem gene arrays in the D. magna genome. The cuticle proteome presented here will be a valuable resource to the Daphnia research community, informing genome annotations and investigations on diverse topics such as the genetic basis of interactions with predators and parasites., (© 2024 The Authors. PROTEOMICS published by Wiley‐VCH GmbH.)
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- 2024
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39. Unraveling root and rhizosphere traits in temperate maize landraces and modern cultivars: Implications for soil resource acquisition and drought adaptation.
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Wild AJ, Steiner FA, Kiene M, Tyborski N, Tung SY, Koehler T, Carminati A, Eder B, Groth J, Vahl WK, Wolfrum S, Lueders T, Laforsch C, Mueller CW, Vidal A, and Pausch J
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- Phenotype, Nitrogen metabolism, Zea mays physiology, Zea mays microbiology, Plant Roots microbiology, Plant Roots physiology, Rhizosphere, Droughts, Soil chemistry, Adaptation, Physiological, Mycorrhizae physiology
- Abstract
A holistic understanding of plant strategies to acquire soil resources is pivotal in achieving sustainable food security. However, we lack knowledge about variety-specific root and rhizosphere traits for resource acquisition, their plasticity and adaptation to drought. We conducted a greenhouse experiment to phenotype root and rhizosphere traits (mean root diameter [Root D], specific root length [SRL], root tissue density, root nitrogen content, specific rhizosheath mass [SRM], arbuscular mycorrhizal fungi [AMF] colonization) of 16 landraces and 22 modern cultivars of temperate maize (Zea mays L.). Our results demonstrate that landraces and modern cultivars diverge in their root and rhizosphere traits. Although landraces follow a 'do-it-yourself' strategy with high SRLs, modern cultivars exhibit an 'outsourcing' strategy with increased mean Root Ds and a tendency towards increased root colonization by AMF. We further identified that SRM indicates an 'outsourcing' strategy. Additionally, landraces were more drought-responsive compared to modern cultivars based on multitrait response indices. We suggest that breeding leads to distinct resource acquisition strategies between temperate maize varieties. Future breeding efforts should increasingly target root and rhizosphere economics, with SRM serving as a valuable proxy for identifying varieties employing an outsourcing resource acquisition strategy., (© 2024 The Authors. Plant, Cell & Environment published by John Wiley & Sons Ltd.)
- Published
- 2024
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40. Size dependent uptake and trophic transfer of polystyrene microplastics in unicellular freshwater eukaryotes.
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Mondellini S, Schwarzer M, Völkl M, Jasinski J, Jérôme V, Scheibel T, Laforsch C, and Freitag R
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- Environmental Monitoring, Tetrahymena pyriformis metabolism, Amoeba metabolism, Paramecium caudatum metabolism, Particle Size, Microplastics, Water Pollutants, Chemical metabolism, Food Chain, Polystyrenes, Fresh Water
- Abstract
Microplastics (MP) have become a well-known and widely investigated environmental pollutant. Despite the huge amount of new studies investigating the potential threat posed by MP, the possible uptake and trophic transfer in lower trophic levels of freshwater ecosystems remains understudied. This study aims to investigate the internalization and potential trophic transfer of fluorescent polystyrene (PS) beads (0.5 μm, 3.6 × 10
8 particles/mL; 6 μm, 2.1 × 105 particles/mL) and fragments (<30 μm, 5 × 103 particles/mL) in three unicellular eukaryotes. This study focuses on the size-dependent uptake of MP by two freshwater Ciliophora, Tetrahymena pyriformis, Paramecium caudatum and one Amoebozoa, Amoeba proteus, serving also as predator for experiments on potential trophic transfer. Size-dependent uptake of MP in all three unicellular eukaryotes was shown. P. caudatum is able to take up MP fragments up to 27.7 μm, while T. pyriformis ingests particles up to 10 μm. In A. proteus, small MP (PS0.5μm and PS6μm ) were taken up via pinocytosis and were detected in the cytoplasm for up to 14 days after exposure. Large PS-MP (PS<30μm ) were detected in A. proteus only after predation on MP-fed Ciliophora. These results indicate that A. proteus ingests larger MP via predation on Ciliophora (PS<30μm ), which would not be taken up otherwise. This study shows trophic transfer of MP at the base of the aquatic food web and serves as basis to study the impact of MP in freshwater ecosystems., Competing Interests: Declaration of competing interest The authors declare no competing interest., (Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.)- Published
- 2024
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41. Effect of micro- and nanoplastic particles on human macrophages.
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Adler MY, Issoual I, Rückert M, Deloch L, Meier C, Tschernig T, Alexiou C, Pfister F, Ramsperger AF, Laforsch C, Gaipl US, Jüngert K, and Paulsen F
- Subjects
- Humans, THP-1 Cells, Leukocytes, Mononuclear drug effects, Nanoparticles toxicity, Nanoparticles chemistry, Cell Survival drug effects, Microscopy, Electron, Transmission, Particle Size, Macrophages drug effects, Macrophages metabolism, Reactive Oxygen Species metabolism, Polystyrenes chemistry, Polystyrenes toxicity, Microplastics toxicity
- Abstract
Micro- and nanoplastics (MNPs) are ubiquitous in the environment, resulting in the uptake of MNPs by a variety of organisms, including humans, leading to particle-cell interaction. Human macrophages derived from THP-1 cell lines take up Polystyrene (PS), a widespread plastic. The question therefore arises whether primary human macrophages also take up PS micro- and nanobeads (MNBs) and how they react to this stimulation. Major aim of this study is to visualize this uptake and to validate the isolation of macrophages from peripheral blood mononuclear cells (PBMCs) to assess the impact of MNPs on human macrophages. Uptake of macrophages from THP-1 cell lines and PBMCs was examined by transmission electron microscopy (TEM), scanning electron microscopy and live cell imaging. In addition, the reaction of the macrophages was analyzed in terms of metabolic activity, cytotoxicity, production of reactive oxygen species (ROS) and macrophage polarization. This study is the first to visualize PS MNBs in primary human cells using TEM and live cell imaging. Metabolic activity was size- and concentration-dependent, necrosis and ROS were increased. The methods demonstrated in this study outline an approach to assess the influence of MNP exposure on human macrophages and help investigating the consequences of worldwide plastic pollution., 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. Competing interests The authors declare no competing interests regarding the publication of this article., (Copyright © 2024 The Authors. Published by Elsevier B.V. All rights reserved.)
- Published
- 2024
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42. Identification of different plastic types and natural materials from terrestrial environments using fluorescence lifetime imaging microscopy.
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Wohlschläger M, Versen M, Löder MGJ, and Laforsch C
- Abstract
Environmental pollution by plastics is a global issue of increasing concern. However, microplastic analysis in complex environmental matrices, such as soil samples, remains an analytical challenge. Destructive mass-based methods for microplastic analysis do not determine plastics' shape and size, which are essential parameters for reliable ecological risk assessment. By contrast, nondestructive particle-based methods produce such data but require elaborate, time-consuming sample preparation. Thus, time-efficient and reliable methods for microplastic analysis are needed. The present study explored the potential of frequency-domain fluorescence lifetime imaging microscopy (FD-FLIM) for rapidly and reliably identifying as well as differentiating plastics and natural materials from terrestrial environments. We investigated the fluorescence spectra of ten natural materials from terrestrial environments, tire wear particles, and eleven different transparent plastic granulates <5 mm to determine the optimal excitation wavelength for identification and differentiation via FD-FLIM under laboratory conditions. Our comparison of different excitation wavelengths showed that 445 nm excitation exhibited the highest fluorescence intensities. 445 nm excitation was also superior for identifying plastic types and distinguishing them from natural materials from terrestrial environments with a high probability using FD-FLIM. We could demonstrate that FD-FLIM analysis has the potential to contribute to a streamlined and time-efficient direct analysis of microplastic contamination. However, further investigations on size-, shape-, color-, and material-type detection limitations are necessary to evaluate if the direct identification of terrestrial environmental samples of relatively low complexity, such as a surface inspection soil, is possible., (© 2024. The Author(s).)
- Published
- 2024
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43. Multi-method analysis of microplastic distribution by flood frequency and local topography in Rhine floodplains.
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Rolf M, Laermanns H, Horn J, Kienzler L, Pohl C, Dierkes G, Kernchen S, Laforsch C, Löder MGJ, and Bogner C
- Abstract
Rivers are important transport pathways for microplastics into the ocean, but they can also be potential sinks due to microplastic deposition in the sediments of the river bed and adjacent floodplains. In particular, floods can (re)mobilise microplastics from sediments and floodplains, (re)deposit and relocate them depending on the floodplain topography. The knowledge about fluvial microplastic input to floodplains, their spatial distribution and their fate in floodplain soils is limited. To investigate this topic, we sampled soil at a depth of 5-20 cm along three transects in three different Rhine floodplains. We analysed the soil samples in tandem with pyrolysis GC/MS and ATR- & μ-FPA-FTIR for their microplastic abundance and mass concentrations. To study the influence of flood frequency on the microplastic abundance in the three floodplains, we fitted a hydrodynamic flood model (MIKE 21, DHI, Hørsholm, Denmark) and related the results to the respective spatial microplastic distribution. We found similar microplastic distribution patterns in each floodplain. The highest microplastic abundance (8516-70,124 microplastics kg
-1 ) and mass concentration (46.2-141.6 mg kg-1 ) were consistently found in the farthest transects from the Rhine in a topographical depression. This microplastic distribution pattern is detectable with both, pyrolysis GC/MS and FTIR. The strongest correlation between the results of both methods was found for small, abundant microplastic particles. Our results suggest that the spatial distribution of microplastics in floodplains is related to the combination of flood frequency and local topography, that ought to be explicitly considered in future studies conducted in floodplains. Finally, our results indicate that pyrolysis GC/MS and FTIR data are comparable under certain conditions, which may help in the decision for the analytical method and sampling design in future studies., 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 The Authors. Published by Elsevier B.V. All rights reserved.)- Published
- 2024
- Full Text
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44. Sexual dimorphism in the proventriculus of the buff-tailed bumblebee Bombus terrestris (L. 1758) (Hymenoptera: Apidae).
- Author
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Hüftlein F, Ritschar S, and Laforsch C
- Subjects
- Bees, Male, Female, Animals, Proventriculus, Sex Characteristics, Semen, Reproduction, Hymenoptera
- Abstract
Research on eusocial bee species like Bombus terrestris is primarily focused on the worker caste, which is why their morphology and anatomy are already well described. This includes the alimentary tract, which is adapted for feeding on nectar and pollen. Located at the transition between crop and ventriculus is a highly specialised compartment, the proventriculus. In female workers of B. terrestris, the proventriculus is surrounded by muscles and consists of four anterior lips. A detailed description, however, is only provided for B. terrestis worker bees while studies on the proventriculus of the male reproductive caste are absent. Here, we provide a detailed analysis of the differences between the proventriculus of the B. terrestris males and females through morphometrics, histology and scanning electron microscopy imaging, and unravel a distinct sexual dimorphism. The male proventriculus is wider resulting in a greater volume than the female proventriculus. Histological analysis revealed 4 distinctive chambers of the male proventriculus, which are completely covered with hairs on the inside. In contrast, those chambers in the proventriculus of female B. terrestris, are only rudimentarily present forming only small pouches with hairs in the junctions between the proventricular folds inside the proventriculus. The morphological differences in the proventriculus may be based on different modi vivendi, as males do not return to the colony and fly longer distances. This and the synthesis of sperm and mating plug might require higher energy reserves, leading to the necessity of higher food storage capacities., (© 2023 The Authors. Journal of Morphology published by Wiley Periodicals LLC.)
- Published
- 2024
- Full Text
- View/download PDF
45. Nominally identical microplastic models differ greatly in their particle-cell interactions.
- Author
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Wieland S, Ramsperger AFRM, Gross W, Lehmann M, Witzmann T, Caspari A, Obst M, Gekle S, Auernhammer GK, Fery A, Laforsch C, and Kress H
- Subjects
- Plastics, Polystyrenes toxicity, Microspheres, Cell Communication, Environmental Monitoring, Microplastics toxicity, Water Pollutants, Chemical analysis
- Abstract
Due to the abundance of microplastics in the environment, research about its possible adverse effects is increasing exponentially. Most studies investigating the effect of microplastics on cells still rely on commercially available polystyrene microspheres. However, the choice of these model microplastic particles can affect the outcome of the studies, as even nominally identical model microplastics may interact differently with cells due to different surface properties such as the surface charge. Here, we show that nominally identical polystyrene microspheres from eight different manufacturers significantly differ in their ζ-potential, which is the electrical potential of a particle in a medium at its slipping plane. The ζ-potential of the polystyrene particles is additionally altered after environmental exposure. We developed a microfluidic microscopy platform to demonstrate that the ζ-potential determines particle-cell adhesion strength. Furthermore, we find that due to this effect, the ζ-potential also strongly determines the internalization of the microplastic particles into cells. Therefore, the ζ-potential can act as a proxy of microplastic-cell interactions and may govern adverse effects reported in various organisms exposed to microplastics., (© 2024. The Author(s).)
- Published
- 2024
- Full Text
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46. Detection and specific chemical identification of submillimeter plastic fragments in complex matrices such as compost.
- Author
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Steiner T, Leitner LC, Zhang Y, Möller JN, Löder MGJ, Greiner A, Laforsch C, and Freitag R
- Subjects
- Microplastics, Polymers, Polypropylenes, Plastics analysis, Composting
- Abstract
Research on the plastic contamination of organic fertilizer (compost) has largely concentrated on particles and fragments > 1 mm. Small, submillimeter microplastic particles may be more hazardous to the environment. However, research on their presence in composts has been impeded by the difficulty to univocally identify small plastic particles in such complex matrices. Here a method is proposed for the analysis of particles between 0.01 and 1.0 mm according to number, size, and polymer type in compost. As a first demonstration of its potential, the method is used to determine large and small microplastic in composts from eight municipal compost producing plants: three simple biowaste composters, four plants processing greenery and cuttings and one two-stage biowaste digester-composter. While polyethylene, PE, tends to dominate among fragments > 1 mm, the microplastic fraction contained more polypropylene, PP. Whereas the contamination with PE/PP microplastic was similar over the investigated composts, only composts prepared from biowaste contained microplastic with a signature of biodegradable plastic, namely poly(butylene adipate co-terephthalate), PBAT. Moreover, in these composts PBAT microplastic tended to form the largest fraction. When the bulk of residual PBAT in the composts was analyzed by chloroform extraction, an inverse correlation between the number of particles > 0.01 mm and the total extracted amount was seen, arguing for breakdown into smaller particles, but not necessarily a mass reduction. PBAT oligomers and monomers as possible substrates for subsequent biodegradation were not found. Remaining microplastic will enter the environment with the composts, where its subsequent degradability depends on the local conditions and is to date largely uninvestigated., (© 2024. The Author(s).)
- Published
- 2024
- Full Text
- View/download PDF
47. A promising method for fast identification of microplastic particles in environmental samples: A pilot study using fluorescence lifetime imaging microscopy.
- Author
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Wohlschläger M, Versen M, Löder MGJ, and Laforsch C
- Abstract
Microplastic pollution of the environment has been extensively studied, with recent studies focusing on the prevalence of microplastics in the environment and their effects on various organisms. Identification methods that simplify the extraction and analysis process to the point where the extraction can be omitted are being investigated, thus enabling the direct identification of microplastic particles. Currently, microplastic samples from environmental matrices can only be identified using time-consuming extraction, sample processing, and analytical methods. Various spectroscopic methods are currently employed, such as micro Fourier-transform infrared, attenuated total reflectance, and micro Raman spectroscopy. However, microplastics in environmental matrices cannot be directly identified using these spectroscopic methods. Investigations using frequency-domain fluorescence lifetime imaging microscopy (FD-FLIM) to identify and differentiate plastics from environmental materials have yielded promising results for directly identifying microplastics in an environmental matrix. Herein, two artificially prepared environmental matrices that included natural soil, grass, wood, and high-density polyethylene were investigated using FD-FLIM. Our first results showed that we successfully identified one plastic type in the two artificially prepared matrices using FD-FLIM. However, further research must be conducted to improve the FD-FLIM method and explore its limitations for directly identifying microplastics in environmental samples., Competing Interests: 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., (© 2024 The Authors.)
- Published
- 2024
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48. Corrigendum to "flooding frequency and floodplain topography determine abundance of microplastics in an alluvial Rhine soil" [Sci. Total Environ. 836 (2022) article number 155141].
- Author
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Rolf M, Laermanns H, Kienzler L, Pohl C, Möller JN, Laforsch C, Löder MGJ, and Bogner C
- Abstract
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.
- Published
- 2023
- Full Text
- View/download PDF
49. The fate of microplastics from municipal wastewater in a surface flow treatment wetland.
- Author
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Büngener L, Postila H, Löder MGJ, Laforsch C, Ronkanen AK, and Heiderscheidt E
- Abstract
Microplastics (MPs) are an anthropogenic pollutant of emerging concern prominent in both raw and treated municipal wastewater as well as urban and agricultural run-off. There is a critical need for the mitigation of both point- and diffuse sources, with treatment wetlands a possible sustainable nature-based solution. In this study, the possible retention of MPs in treatment wetlands of the widely used surface flow (SF) type was investigated. In- and outflow water, as well as atmospheric deposition, at a full-scale reed-based SF wetland (operating as a polishing phase of municipal wastewater treatment) was analyzed for MPs in a size range of 25-1000 μm. FPA-based μFT-IR spectroscopic imaging was used in combination with automated data analysis software, allowing for an unbiased assessment of MP numbers, polymer types and size distribution. Inflow water samples (secondary treated wastewater) contained 104 MPs m
-3 and 56 MPs m-3 in sampling campaigns 1 and 2, respectively. Passage through the SF wetland increased the MP concentration in the water by 92 % during a rain intense period (campaign 1) and by 43 % during a low precipitation period (campaign 2). The MP particle numbers, size and polymer type distribution varied between the two sampling campaigns, making conclusions around the fate of specific types of MPs in SF wetlands difficult. Atmospheric deposition was measured to be 590 MPs m-2 week-1 during the rain-intense period. Our findings point towards atmospheric deposited MPs as an important factor in the fate of MPs in SF wetlands, causing an increase of MP concentrations, and potentially explaining the variations observed in MP concentrations in wetland effluent and removal efficiency. Furthermore, atmospheric deposition might also be a reason for the considerable inter-study variation regarding MPs removal efficiency in SF wetlands found in the available literature., 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 © 2023 The Authors. Published by Elsevier B.V. All rights reserved.)- Published
- 2023
- Full Text
- View/download PDF
50. Seasonal variations of microplastic pollution in the German River Weser.
- Author
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Moses SR, Löder MGJ, Herrmann F, and Laforsch C
- Abstract
Rivers play a major role in the distribution of microplastics (MPs) in the environment, however, research on temporal variations in these highly dynamic systems is still in its infancy. To date, most studies dealing with the seasonality of MP contamination in rivers focus on bi-yearly analysis, while temporal fluctuations over the course of the year are rarely studied. To shed more light on seasonal variability of MP abundance and potential driving factors, we have thus sampled the water surface of one location in the Weser River in Germany monthly over one entire year. In our study, we targeted MP in the size range 10-5000 μm, using two different state-of-the-art sampling methods (manta net for large MP (l-MP; 500-5000 μm) and a filtration system for small MP (s-MP; 10-500 μm)) and analysis techniques (ATR-FTIR and FPA-μFTIR) for chemical identification. Our findings show a strong size-dependent positive correlation of the MP concentration with discharge rates (specifically direct runoff) and suspended particulate matter (SPM) for s-MPs, specifically in the size range 10-149 μm. L-MPs, however, show a different environmental behaviour and do not follow these patterns. With our study, we were able to deliver a much higher temporal resolution, covering a broader size range of MPs compared to most studies. Our findings point towards an interplay of two possible mechanisms: a) the riverbeds play an important role in large-scale MP and SPM release via resuspension during high discharge events, and b) precipitation-driven soil erosion and runoff from urban surfaces (e.g. rain sewers) introduce MP and SPM. Hence, our study serves as a basis for more detailed investigations of MP transport in and between ecosystems., 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 © 2023 Elsevier B.V. All rights reserved.)
- Published
- 2023
- Full Text
- View/download PDF
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