141 results on '"Fick, J."'
Search Results
2. Differential tissue distribution of pharmaceuticals in a wild subtropical marine fish
- Author
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Castillo, N.A., Santos, R.O., James, W.R., Rezek, R., Cerveny, D., Boucek, R.E., Adams, A.J., Fick, J., Brodin, T., and Rehage, J.S.
- Published
- 2024
- Full Text
- View/download PDF
3. Identifying pathways of pharmaceutical exposure in a mesoconsumer marine fish
- Author
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Castillo, N.A., James, W.R., Santos, R.O., Rezek, R., Cerveny, D., Boucek, R.E., Adams, A.J., Trabelsi, S., Distrubell, A., Sandquist, M., Fick, J., Brodin, T., and Rehage, J.S.
- Published
- 2024
- Full Text
- View/download PDF
4. Understanding pharmaceutical exposure and the potential for effects in marine biota: A survey of bonefish (Albula vulpes) across the Caribbean Basin
- Author
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Castillo, N.A., James, W.R., Santos, R.O., Rezek, R., Cerveny, D., Boucek, R.E., Adams, A.J., Goldberg, T., Campbell, L., Perez, A.U., Schmitter-Soto, J.J., Lewis, J.P., Fick, J., Brodin, T., and Rehage, J.S.
- Published
- 2024
- Full Text
- View/download PDF
5. Water temperature affects the biotransformation and accumulation of a psychoactive pharmaceutical and its metabolite in aquatic organisms
- Author
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Cerveny, D., Fick, J., Klaminder, J., McCallum, E.S., Bertram, M.G., Castillo, N.A., and Brodin, T.
- Published
- 2021
- Full Text
- View/download PDF
6. Bioconcentration and behavioral effects of four benzodiazepines and their environmentally relevant mixture in wild fish
- Author
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Cerveny, D., Brodin, T., Cisar, P., McCallum, ES., and Fick, J.
- Published
- 2020
- Full Text
- View/download PDF
7. Fish on steroids: Temperature-dependent effects of 17β-trenbolone on predator escape, boldness, and exploratory behaviors
- Author
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Lagesson, A., Saaristo, M., Brodin, T., Fick, J., Klaminder, J., Martin, J.M., and Wong, B.B.M.
- Published
- 2019
- Full Text
- View/download PDF
8. Understanding pharmaceutical exposure and the potential for effects in marine biota: A survey of bonefish (Albula vulpes) across the Caribbean Basin
- Author
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Castillo, N.A., primary, James, W.R., additional, Santos, R.O., additional, Rezek, R., additional, Cerveny, D., additional, Boucek, R.E., additional, Adams, A.J., additional, Goldberg, T., additional, Campbell, L., additional, Perez, A.U., additional, Schmitter-Soto, J.J., additional, Lewis, J.P., additional, Fick, J., additional, Brodin, T., additional, and Rehage, J.S., additional
- Published
- 2023
- Full Text
- View/download PDF
9. No evidence of increased growth or mortality in fish exposed to oxazepam in semi-natural ecosystems
- Author
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Lagesson, A., Brodin, T., Fahlman, J., Fick, J., Jonsson, M., Persson, J., Byström, P., and Klaminder, J.
- Published
- 2018
- Full Text
- View/download PDF
10. Bioaccumulation of five pharmaceuticals at multiple trophic levels in an aquatic food web - Insights from a field experiment
- Author
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Lagesson, A., Fahlman, J., Brodin, T., Fick, J., Jonsson, M., Byström, P., and Klaminder, J.
- Published
- 2016
- Full Text
- View/download PDF
11. Exposure to an anti-androgenic herbicide negatively impacts reproductive physiology and fertility in Xenopus tropicalis
- Author
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Orton, F., Säfholm, M., Jansson, E., Carlsson, Y., Eriksson, A., Fick, J., Uren Webster, T., McMillan, T., Leishman, M., Verbruggen, B., Economou, T., Tyler, C. R., and Berg, C.
- Published
- 2018
- Full Text
- View/download PDF
12. Optical trapping of photochromic microcrystals by a dual fiber tweezers
- Author
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Uchiyama, K., primary, Fick, J., additional, Huant, S., additional, Uchida, K., additional, Naruse, M., additional, and Hori, H., additional
- Published
- 2022
- Full Text
- View/download PDF
13. Probing Hadronic Interactions with Measurements at Ultra-High Energies with the Pierre Auger Observatory
- Author
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nbsp;, D., Schmidt, A. undefined, Aab, P. undefined, Abreu, M. undefined, Aglietta, J. M. undefined, Albury, I. undefined, Allekotte, A. undefined, Almela, J. undefined, Alvarez-Muñiz, R. undefined, Alves Batista, G. A. undefined, Anastasi, L. undefined, Anchordoqui, B. undefined, Andrada, S. undefined, Andringa, C. undefined, Aramo, P. R. undefined, Araújo Ferreira, H. undefined, Asorey, P. undefined, Assis, G. undefined, Avila, A. M. undefined, Badescu, A. undefined, Bakalova, A. undefined, Balaceanu, F. undefined, Barbato, R. J. undefined, Barreira Luz, K. H. undefined, Becker, J. A. undefined, Bellido, C. undefined, Berat, M. E. undefined, Bertaina, X. undefined, Bertou, P. L. undefined, Bierman, T. undefined, Bister, J. undefined, Biteau, J. undefined, Blazek, C. undefined, Bleve, M. undefined, Boháčová, D. undefined, Boncioli, C. undefined, Bonifazi, L. undefined, Bonneau Arbeletche, N. undefined, Borodai, A. M. undefined, Botti, J. undefined, Brac, T. undefined, Bretz, F. L. undefined, Briechle, P. undefined, Buchholz, A. undefined, Bueno, S. undefined, Buitink, M. undefined, Buscemi, K. S. undefined, Caballero-Mora, L. undefined, Caccianiga, A. undefined, Cancio, F. undefined, Canfora, I. undefined, Caracas, J. M. undefined, Carceller, R. undefined, Caruso, A. undefined, Castellina, F. undefined, Catalani, G. undefined, Cataldi, L. undefined, Cazon, M. undefined, Cerda, J. A. undefined, Chinellato, K. undefined, Choi, J. undefined, Chudoba, L. undefined, Chytka, R. W. undefined, Clay, A. C. undefined, Cobos Cerutti, R. undefined, Colalillo, A. undefined, Coleman, M. R. undefined, Coluccia, R. undefined, Conceição, A. undefined, Condorelli, Consolati, G., undefined, F., Contreras, F. undefined, Convenga, C. E. undefined, Covault, S. undefined, Dasso, K. undefined, Daumiller, B. R. undefined, Dawson, J. A. undefined, Day, R. M. undefined, de Almeida, J. undefined, de Jesús, S. J. undefined, de Jong, G. undefined, De Mauro, J. R. T. undefined, de Mello Neto, I. undefined, De Mitri, J. undefined, de Oliveira, D. undefined, de Oliveira Franco, V. undefined, de Souza, E. undefined, De Vito, J. undefined, Debatin, M. undefined, del Río, O. undefined, Deligny, N. undefined, Dhital, A. undefined, Di Matteo, C. undefined, Dobrigkeit, J. C. undefined, D'Olivo, R. C. undefined, dos Anjos, M. T. undefined, Dova, J. undefined, Ebr, R. undefined, Engel, I. undefined, Epicoco, M. undefined, Erdmann, C. O. undefined, Escoba, A. undefined, Etchegoyen, H. undefined, Falcke, J. undefined, Farmer, G. undefined, Farrar, A. C. undefined, Fauth, N. undefined, Fazzi, F. undefined, Feldbusch, F. undefined, Fenu, B. undefined, Fick, J. M. undefined, Figueira, A. undefined, Filipčič, T. undefined, Fodran, M. M. undefined, Freire, T. undefined, Fujii, A. undefined, Fuster, C. undefined, Galea, C. undefined, Galelli, B. undefined, García, A. L. undefined, Garcia Vegas, H. undefined, Gemmeke, F. undefined, Gesualdi, A. undefined, Gherghel-Lascu, P. L. undefined, Ghia, U. undefined, Giaccari, M. undefined, Giammarchi, M. undefined, Giller, J. undefined, Glombitza, F. undefined, Gobbi, F. undefined, Gollan, G. undefined, Golup, M. undefined, Gómez Berisso, P. F. undefined, Gómez Vitale, J. P. undefined, Gongora, N. undefined, González, I. undefined, Goos, D. undefined, Góra, A. undefined, Gorgi, M. undefined, Gottowik, T. D. undefined, Grubb, F. undefined, Guarino, G. P. undefined, Guedes, E. undefined, Guido, S. undefined, Hahn, R. undefined, Halliday, M. R. undefined, Hampel, P. undefined, Hansen, D. undefined, Harari, V. M. undefined, Harvey, A. undefined, Haungs, T. undefined, Hebbeker, D. undefined, Heck, G. C. undefined, Hill, C. undefined, Hojvat, J. R. undefined, Hörandel, P. undefined, Horvath, M. undefined, Hrabovský, T. undefined, Huege, J. undefined, Hulsman, A. undefined, Insolia, P. G. undefined, Isar, J. A. undefined, Johnsen, J. undefined, Jurysek, A. undefined, Kääpä, K. H. undefined, Kampert, B. undefined, Keilhauer, J. undefined, Kemp, H. O. undefined, Klages, M. undefined, Kleifges, J. undefined, Kleinfeller, M. undefined, Köpke, G. undefined, Kukec Mezek, B. L. undefined, Lago, D. undefined, Lahurd, R. G. undefined, Lang, N. undefined, Langner, M. A. undefined, Leigui de Oliveira, V. undefined, Lenok, A. undefined, Letessier-Selvon, I. undefined, Lhenry-Yvon, D. undefined, Lo Presti, L. undefined, Lopes, R. undefined, López, R. undefined, Lorek, Q. undefined, Luce, A. undefined, Lucero, J. P. undefined, Lundquist, A. undefined, Machado Payeras, G. undefined, Mancarella, D. undefined, Mandat, B. C. undefined, Manning, J. undefined, Manshanden, P. undefined, Mantsc, S. undefined, Marafico, A. G. undefined, Mariazzi, I. C. undefined, Mariş, G. undefined, Marsella, D. undefined, Martello, H. undefined, Martinez, O. undefined, Martínez Bravo, M. undefined, Mastrodicasa, H. J. undefined, Mathes, J. undefined, Matthews, G. undefined, Matthiae, E. undefined, Mayotte, P. O. undefined, Mazu, G. undefined, Medina-Tanco, D. undefined, Melo, A. undefined, Menshikov, K. -D. undefined, Merenda, S. undefined, Michal, M. I. undefined, Micheletti, L. undefined, Miramonti, S. undefined, Mollerach, F. undefined, Montanet, C. undefined, Morello, M. undefined, Mostafá, A. L. undefined, Müller, M. A. undefined, Muller, K. undefined, Mulrey, R. undefined, Mussa, M. undefined, Muzio, W. M. undefined, Namasaka, L. undefined, Nellen, M. undefined, Niculescu-Oglinzanu, M. undefined, Niechciol, D. undefined, Nitz, D. undefined, Nosek, V. undefined, Novotny, L. undefined, Nožka, Nucita, A., undefined, L. A., Núñez, M. undefined, Palatka, J. undefined, Pallotta, P. undefined, Papenbreer, G. undefined, Parente, A. undefined, Parra, M. undefined, Pech, F. undefined, Pedreira, J. undefined, Pękala, R. undefined, Pelayo, J. undefined, Peña-Rodriguez, J. undefined, Perez Armand, M. undefined, Perlin, L. undefined, Perrone, S. undefined, Petrera, T. undefined, Pierog, M. undefined, Pimenta, V. undefined, Pirronello, M. undefined, Platino, B. undefined, Pont, M. undefined, Pothast, P. undefined, Privitera, M. undefined, Prouza, A. undefined, Puyleart, S. undefined, Querchfeld, J. undefined, Rautenberg, D. undefined, Ravignani, M. undefined, Reininghaus, J. undefined, Ridky, F. undefined, Riehn, M. undefined, Risse, P. undefined, Ristori, V. undefined, Rizi, W. undefined, Rodrigues de Carvalho, J. undefined, Rodriguez Rojo, M. J. undefined, Roncoroni, M. undefined, Roth, E. undefined, Roulet, A. C. undefined, Rovero, P. undefined, Ruehl, S. J. undefined, Saffi, A. undefined, Saftoiu, F. undefined, Salamida, H. undefined, Salazar, G. undefined, Salina, J. D. undefined, Sanabria Gomez, F. undefined, Sánchez, E. M. undefined, Santos, E. undefined, Santos, F. undefined, Sarazin, R. undefined, Sarmento, C. undefined, Sarmiento-Cano, R. undefined, Sato, P. undefined, Savina, C. M. undefined, Schäfer, V. undefined, Scherini, H. undefined, Schieler, M. undefined, Schimassek, M. undefined, Schimp, F. undefined, Schlüter, O. undefined, Scholten, P. undefined, Schovánek, F. G. undefined, Schröder, S. undefined, Schröder, J. undefined, Schulte, S. J. undefined, Sciutto, M. undefined, Scornavacche, R. C. undefined, Shellard, G. undefined, Sigl, G. undefined, Silli, O. undefined, Sima, R. undefined, Šmída, P. undefined, Sommers, J. F. undefined, Soriano, J. undefined, Souchard, R. undefined, Squartini, M. undefined, Stadelmaier, D. undefined, Stanca, S. undefined, Stanič, J. undefined, Stasielak, P. undefined, Stassi, A. undefined, Streich, M. undefined, Suárez-Durán, T. undefined, Sudholz, T. undefined, Suomijärvi, A. D. undefined, Supanitsky, J. undefined, Šupík, Z. undefined, Szadkowski, A. undefined, Taboada, A. undefined, Tapia, C. undefined, Timmermans, O. undefined, Tkachenko, P. undefined, Tobiska, C. J. undefined, Todero Peixoto, B. undefined, Tomé, A. undefined, Travaini, P. undefined, Travnicek, C. undefined, Trimarelli, M. undefined, Trini, M. undefined, Tueros, R. undefined, Ulrich, M. undefined, Unger, L. undefined, Vaclavek, M. undefined, Vacula, J. F. undefined, Valdés Galicia, L. undefined, Valore, E. undefined, Varela, V. undefined, Varma K. C., A. undefined, Vásquez-Ramírez, D. undefined, Veberič, C. undefined, Ventura, I. D. undefined, Vergara Quispe, V. undefined, Verzi, J. undefined, Vicha, J. undefined, Vink, S. undefined, Vorobiov, H. undefined, Wahlberg, A. A. undefined, Wat, M. undefined, Weber, A. undefined, Weindl, L. undefined, Wiencke, H. undefined, Wilczyński, T. undefined, Winchen, M. undefined, Wirtz, D. undefined, Wittkowski, B. undefined, Wundheiler, A. undefined, Yushkov, O. undefined, Zapparrata, E. undefined, Zas, D. undefined, Zavrtanik, M. undefined, Zavrtanik, L. undefined, Zehrer, A. undefined, and Zepeda
- Published
- 2020
14. The Radio Detection of Inclined Showers at the Pierre Auger Observatory
- Author
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S. de Jong, A.  , Aab, P. undefined, Abreu, M. undefined, Aglietta, J. M. undefined, Albury, I. undefined, Allekotte, A. undefined, Almela, J. undefined, Alvarez-Muñiz, R. undefined, Alves Batista, G. A. undefined, Anastasi, L. undefined, Anchordoqui, B. undefined, Andrada, S. undefined, Andringa, C. undefined, Aramo, P. R. undefined, Araújo Ferreira, H. undefined, Asorey, P. undefined, Assis, G. undefined, Avila, A. M. undefined, Badescu, A. undefined, Bakalova, A. undefined, Balaceanu, F. undefined, Barbato, R. J. undefined, Barreira Luz, K. H. undefined, Becker, J. A. undefined, Bellido, C. undefined, Berat, M. E. undefined, Bertaina, X. undefined, Bertou, P. L. undefined, Bierman, T. undefined, Bister, J. undefined, Biteau, J. undefined, Blazek, C. undefined, Bleve, M. undefined, Boháčová, D. undefined, Boncioli, C. undefined, Bonifazi, L. undefined, Bonneau Arbeletche, N. undefined, Borodai, A. M. undefined, Botti, J. undefined, Brac, T. undefined, Bretz, F. L. undefined, Briechle, P. undefined, Buchholz, A. undefined, Bueno, S. undefined, Buitink, M. undefined, Buscemi, K. S. undefined, Caballero-Mora, L. undefined, Caccianiga, A. undefined, Cancio, F. undefined, Canfora, I. undefined, Caracas, J. M. undefined, Carceller, R. undefined, Caruso, A. undefined, Castellina, F. undefined, Catalani, G. undefined, Cataldi, L. undefined, Cazon, M. undefined, Cerda, J. A. undefined, Chinellato, K. undefined, Choi, J. undefined, Chudoba, L. undefined, Chytka, R. W. undefined, Clay, A. C. undefined, Cobos Cerutti, R. undefined, Colalillo, A. undefined, Coleman, M. R. undefined, Coluccia, R. undefined, Conceição, A. undefined, Condorelli, Consolati, G., undefined, F., Contreras, F. undefined, Convenga, C. E. undefined, Covault, S. undefined, Dasso, K. undefined, Daumiller, B. R. undefined, Dawson, J. A. undefined, Day, R. M. undefined, de Almeida, J. undefined, de Jesús, G. undefined, De Mauro, J. R. T. undefined, de Mello Neto, I. undefined, De Mitri, J. undefined, de Oliveira, D. undefined, de Oliveira Franco, V. undefined, de Souza, E. undefined, De Vito, J. undefined, Debatin, M. undefined, del Río, O. undefined, Deligny, N. undefined, Dhital, A. undefined, Di Matteo, C. undefined, Dobrigkeit, J. C. undefined, D'Olivo, R. C. undefined, dos Anjos, M. T. undefined, Dova, J. undefined, Ebr, R. undefined, Engel, I. undefined, Epicoco, M. undefined, Erdmann, C. O. undefined, Escoba, A. undefined, Etchegoyen, H. undefined, Falcke, J. undefined, Farmer, G. undefined, Farrar, A. C. undefined, Fauth, N. undefined, Fazzi, F. undefined, Feldbusch, F. undefined, Fenu, B. undefined, Fick, J. M. undefined, Figueira, A. undefined, Filipčič, T. undefined, Fodran, M. M. undefined, Freire, T. undefined, Fujii, A. undefined, Fuster, C. undefined, Galea, C. undefined, Galelli, B. undefined, García, A. L. undefined, Garcia Vegas, H. undefined, Gemmeke, F. undefined, Gesualdi, A. undefined, Gherghel-Lascu, P. L. undefined, Ghia, U. undefined, Giaccari, M. undefined, Giammarchi, M. undefined, Giller, J. undefined, Glombitza, F. undefined, Gobbi, F. undefined, Gollan, G. undefined, Golup, M. undefined, Gómez Berisso, P. F. undefined, Gómez Vitale, J. P. undefined, Gongora, N. undefined, González, I. undefined, Goos, D. undefined, Góra, A. undefined, Gorgi, M. undefined, Gottowik, T. D. undefined, Grubb, F. undefined, Guarino, G. P. undefined, Guedes, E. undefined, Guido, S. undefined, Hahn, R. undefined, Halliday, M. R. undefined, Hampel, P. undefined, Hansen, D. undefined, Harari, V. M. undefined, Harvey, A. undefined, Haungs, T. undefined, Hebbeker, D. undefined, Heck, G. C. undefined, Hill, C. undefined, Hojvat, J. R. undefined, Hörandel, P. undefined, Horvath, M. undefined, Hrabovský, T. undefined, Huege, J. undefined, Hulsman, A. undefined, Insolia, P. G. undefined, Isar, J. A. undefined, Johnsen, J. undefined, Jurysek, A. undefined, Kääpä, K. H. undefined, Kampert, B. undefined, Keilhauer, J. undefined, Kemp, H. O. undefined, Klages, M. undefined, Kleifges, J. undefined, Kleinfeller, M. undefined, Köpke, G. undefined, Kukec Mezek, B. L. undefined, Lago, D. undefined, Lahurd, R. G. undefined, Lang, N. undefined, Langner, M. A. undefined, Leigui de Oliveira, V. undefined, Lenok, A. undefined, Letessier-Selvon, I. undefined, Lhenry-Yvon, D. undefined, Lo Presti, L. undefined, Lopes, R. undefined, López, R. undefined, Lorek, Q. undefined, Luce, A. undefined, Lucero, J. P. undefined, Lundquist, A. undefined, Machado Payeras, G. undefined, Mancarella, D. undefined, Mandat, B. C. undefined, Manning, J. undefined, Manshanden, P. undefined, Mantsc, S. undefined, Marafico, A. G. undefined, Mariazzi, I. C. undefined, Mariş, G. undefined, Marsella, D. undefined, Martello, H. undefined, Martinez, O. undefined, Martínez Bravo, M. undefined, Mastrodicasa, H. J. undefined, Mathes, J. undefined, Matthews, G. undefined, Matthiae, E. undefined, Mayotte, P. O. undefined, Mazu, G. undefined, Medina-Tanco, D. undefined, Melo, A. undefined, Menshikov, K. -D. undefined, Merenda, S. undefined, Michal, M. I. undefined, Micheletti, L. undefined, Miramonti, S. undefined, Mollerach, F. undefined, Montanet, C. undefined, Morello, M. undefined, Mostafá, A. L. undefined, Müller, M. A. undefined, Muller, K. undefined, Mulrey, R. undefined, Mussa, M. undefined, Muzio, W. M. undefined, Namasaka, L. undefined, Nellen, M. undefined, Niculescu-Oglinzanu, M. undefined, Niechciol, D. undefined, Nitz, D. undefined, Nosek, V. undefined, Novotny, L. undefined, Nožka, Nucita, A., undefined, L. A., Núñez, M. undefined, Palatka, J. undefined, Pallotta, P. undefined, Papenbreer, G. undefined, Parente, A. undefined, Parra, M. undefined, Pech, F. undefined, Pedreira, J. undefined, Pękala, R. undefined, Pelayo, J. undefined, Peña-Rodriguez, J. undefined, Perez Armand, M. undefined, Perlin, L. undefined, Perrone, S. undefined, Petrera, T. undefined, Pierog, M. undefined, Pimenta, V. undefined, Pirronello, M. undefined, Platino, B. undefined, Pont, M. undefined, Pothast, P. undefined, Privitera, M. undefined, Prouza, A. undefined, Puyleart, S. undefined, Querchfeld, J. undefined, Rautenberg, D. undefined, Ravignani, M. undefined, Reininghaus, J. undefined, Ridky, F. undefined, Riehn, M. undefined, Risse, P. undefined, Ristori, V. undefined, Rizi, W. undefined, Rodrigues de Carvalho, J. undefined, Rodriguez Rojo, M. J. undefined, Roncoroni, M. undefined, Roth, E. undefined, Roulet, A. C. undefined, Rovero, P. undefined, Ruehl, S. J. undefined, Saffi, A. undefined, Saftoiu, F. undefined, Salamida, H. undefined, Salazar, G. undefined, Salina, J. D. undefined, Sanabria Gomez, F. undefined, Sánchez, E. M. undefined, Santos, E. undefined, Santos, F. undefined, Sarazin, R. undefined, Sarmento, C. undefined, Sarmiento-Cano, R. undefined, Sato, P. undefined, Savina, C. M. undefined, Schäfer, V. undefined, Scherini, H. undefined, Schieler, M. undefined, Schimassek, M. undefined, Schimp, F. undefined, Schlüter, D. undefined, Schmidt, O. undefined, Scholten, P. undefined, Schovánek, F. G. undefined, Schröder, S. undefined, Schröder, J. undefined, Schulte, S. J. undefined, Sciutto, M. undefined, Scornavacche, R. C. undefined, Shellard, G. undefined, Sigl, G. undefined, Silli, O. undefined, Sima, R. undefined, Šmída, P. undefined, Sommers, J. F. undefined, Soriano, J. undefined, Souchard, R. undefined, Squartini, M. undefined, Stadelmaier, D. undefined, Stanca, S. undefined, Stanič, J. undefined, Stasielak, P. undefined, Stassi, A. undefined, Streich, M. undefined, Suárez-Durán, T. undefined, Sudholz, T. undefined, Suomijärvi, A. D. undefined, Supanitsky, J. undefined, Šupík, Z. undefined, Szadkowski, A. undefined, Taboada, A. undefined, Tapia, C. undefined, Timmermans, O. undefined, Tkachenko, P. undefined, Tobiska, C. J. undefined, Todero Peixoto, B. undefined, Tomé, A. undefined, Travaini, P. undefined, Travnicek, C. undefined, Trimarelli, M. undefined, Trini, M. undefined, Tueros, R. undefined, Ulrich, M. undefined, Unger, L. undefined, Vaclavek, M. undefined, Vacula, J. F. undefined, Valdés Galicia, L. undefined, Valore, E. undefined, Varela, V. undefined, Varma K. C., A. undefined, Vásquez-Ramírez, D. undefined, Veberič, C. undefined, Ventura, I. D. undefined, Vergara Quispe, V. undefined, Verzi, J. undefined, Vicha, J. undefined, Vink, S. undefined, Vorobiov, H. undefined, Wahlberg, A. A. undefined, Wat, M. undefined, Weber, A. undefined, Weindl, L. undefined, Wiencke, H. undefined, Wilczyński, T. undefined, Winchen, M. undefined, Wirtz, D. undefined, Wittkowski, B. undefined, Wundheiler, A. undefined, Yushkov, O. undefined, Zapparrata, E. undefined, Zas, D. undefined, Zavrtanik, M. undefined, Zavrtanik, L. undefined, Zehrer, A. undefined, and Zepeda
- Published
- 2020
15. Multi-Messenger Studies with the Pierre Auger Observatory
- Author
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nbsp;, L., Zehrer, A. undefined, Aab, P. undefined, Abreu, M. undefined, Aglietta, J. M. undefined, Albury, I. undefined, Allekotte, A. undefined, Almela, J. undefined, Alvarez-Muniz, R. undefined, Alves Batista, G. A. undefined, Anastasi, L. undefined, Anchordoqui, B. undefined, Andrada, S. undefined, Andringa, C. undefined, Aramo, P. R. undefined, Araújo Ferreira, H. undefined, Asorey, P. undefined, Assis, G. undefined, Avila, A. M. undefined, Badescu, A. undefined, Bakalova, A. undefined, Balaceanu, F. undefined, Barbato, R. J. undefined, Barreira Luz, K. H. undefined, Becker, J. A. undefined, Bellido, C. undefined, Berat, M. E. undefined, Bertaina, X. undefined, Bertou, P. L. undefined, Bierman, T. undefined, Bister, J. undefined, Biteau, J. undefined, Blazek, C. undefined, Bleve, M. undefined, Bohácová, D. undefined, Boncioli, C. undefined, Bonifazi, L. undefined, Bonneau Arbeletche, N. undefined, Borodai, A. M. undefined, Botti, J. undefined, Brac, T. undefined, Bretz, F. L. undefined, Briechle, P. undefined, Buchholz, A. undefined, Bueno, S. undefined, Buitink, M. undefined, Buscemi, K. S. undefined, Caballero-Mora, L. undefined, Caccianiga, A. undefined, Cancio, F. undefined, Canfora, I. undefined, Caracas, J. M. undefined, Carceller, R. undefined, Caruso, A. undefined, Castellina, F. undefined, Catalani, G. undefined, Cataldi, L. undefined, Cazon, M. undefined, Cerda, J. A. undefined, Chinellato, K. undefined, Choi, J. undefined, Chudoba, L. undefined, Chytka, R. W. undefined, Clay, A. C. undefined, Cobos Cerutti, R. undefined, Colalillo, A. undefined, Coleman, M. R. undefined, Coluccia, R. undefined, Conceicao, A. undefined, Condorelli, Consolati, G., undefined, F., Contreras, F. undefined, Convenga, C. E. undefined, Covault, S. undefined, Dasso, K. undefined, Daumiller, B. R. undefined, Dawson, J. A. undefined, Day, R. M. undefined, de Almeida, J. undefined, de Jesús, S. J. undefined, de Jong, G. undefined, De Mauro, J. R. T. undefined, de Mello Neto, I. undefined, De Mitri, J. undefined, de Oliveira, D. undefined, de Oliveira Franco, V. undefined, de Souza, E. undefined, De Vito, J. undefined, Debatin, M. undefined, del Río, O. undefined, Deligny, N. undefined, Dhital, A. undefined, Di Matteo, C. undefined, Dobrigkeit, J. C. undefined, D'Olivo, R. C. undefined, dos Anjos, M. T. undefined, Dova, J. undefined, Ebr, R. undefined, Engel, I. undefined, Epicoco, M. undefined, Erdmann, C. O. undefined, Escoba, A. undefined, Etchegoyen, H. undefined, Falcke, J. undefined, Farmer, G. undefined, Farrar, A. C. undefined, Fauth, N. undefined, Fazzi, F. undefined, Feldbusch, F. undefined, Fenu, B. undefined, Fick, J. M. undefined, Figueira, A. undefined, Filipcic, T. undefined, Fodran, M. M. undefined, Freire, T. undefined, Fujii, A. undefined, Fuster, C. undefined, Galea, C. undefined, Galelli, B. undefined, García, A. L. undefined, Garcia Vegas, H. undefined, Gemmeke, F. undefined, Gesualdi, A. undefined, Gherghel-Lascu, P. L. undefined, Ghia, U. undefined, Giaccari, M. undefined, Giammarchi, M. undefined, Giller, J. undefined, Glombitza, F. undefined, Gobbi, F. undefined, Gollan, G. undefined, Golup, M. undefined, Gómez Berisso, P. F. undefined, Gómez Vitale, J. P. undefined, Gongora, N. undefined, González, I. undefined, Goos, D. undefined, Góra, A. undefined, Gorgi, M. undefined, Gottowik, T. D. undefined, Grubb, F. undefined, Guarino, G. P. undefined, Guedes, E. undefined, Guido, S. undefined, Hahn, R. undefined, Halliday, M. R. undefined, Hampel, P. undefined, Hansen, D. undefined, Harari, V. M. undefined, Harvey, A. undefined, Haungs, T. undefined, Hebbeker, D. undefined, Heck, G. C. undefined, Hill, C. undefined, Hojvat, J. R. undefined, Horandel, P. undefined, Horvath, M. undefined, Hrabovsky, T. undefined, Huege, J. undefined, Hulsman, A. undefined, Insolia, P. G. undefined, Isar, J. A. undefined, Johnsen, J. undefined, Jurysek, A. undefined, Kaapa, K. H. undefined, Kampert, B. undefined, Keilhauer, J. undefined, Kemp, H. O. undefined, Klages, M. undefined, Kleifges, J. undefined, Kleinfeller, M. undefined, Köpke, G. undefined, Kukec Mezek, B. L. undefined, Lago, D. undefined, Lahurd, R. G. undefined, Lang, N. undefined, Langner, M. A. undefined, Leigui de Oliveira, V. undefined, Lenok, A. undefined, Letessier-Selvon, I. undefined, Lhenry-Yvon, D. undefined, Lo Presti, L. undefined, Lopes, R. undefined, López, R. undefined, Lorek, Q. undefined, Luce, A. undefined, Lucero, J. P. undefined, Lundquist, A. undefined, Machado Payeras, G. undefined, Mancarella, D. undefined, Mandat, B. C. undefined, Manning, J. undefined, Manshanden, P. undefined, Mantsc, S. undefined, Marafico, A. G. undefined, Mariazzi, I. C. undefined, Mariş, G. undefined, Marsella, D. undefined, Martello, H. undefined, Martinez, O. undefined, Martínez Bravo, M. undefined, Mastrodicasa, H. J. undefined, Mathes, J. undefined, Matthews, G. undefined, Matthiae, E. undefined, Mayotte, P. O. undefined, Mazu, G. undefined, Medina-Tanco, D. undefined, Melo, A. undefined, Menshikov, K. -D. undefined, Merenda, S. undefined, Michal, M. I. undefined, Micheletti, L. undefined, Miramonti, S. undefined, Mollerach, F. undefined, Montanet, C. undefined, Morello, M. undefined, Mostafá, A. L. undefined, Muller, M. A. undefined, Muller, K. undefined, Mulrey, R. undefined, Mussa, M. undefined, Muzio, W. M. undefined, Namasaka, L. undefined, Nellen, M. undefined, Niculescu-Oglinzanu, M. undefined, Niechciol, D. undefined, Nitz, D. undefined, Nosek, V. undefined, Novotny, L. undefined, Nožka, Nucita, A., undefined, L. A., Nunez, M. undefined, Palatka, J. undefined, Pallotta, P. undefined, Papenbreer, G. undefined, Parente, A. undefined, Parra, M. undefined, Pech, F. undefined, Pedreira, J. undefined, Pękala, R. undefined, Pelayo, J. undefined, Pena-Rodriguez, J. undefined, Perez Armand, M. undefined, Perlin, L. undefined, Perrone, S. undefined, Petrera, T. undefined, Pierog, M. undefined, Pimenta, V. undefined, Pirronello, M. undefined, Platino, B. undefined, Pont, M. undefined, Pothast, P. undefined, Privitera, M. undefined, Prouza, A. undefined, Puyleart, S. undefined, Querchfeld, J. undefined, Rautenberg, D. undefined, Ravignani, M. undefined, Reininghaus, J. undefined, Ridky, F. undefined, Riehn, M. undefined, Risse, P. undefined, Ristori, V. undefined, Rizi, W. undefined, Rodrigues de Carvalho, J. undefined, Rodriguez Rojo, M. J. undefined, Roncoroni, M. undefined, Roth, E. undefined, Roulet, A. C. undefined, Rovero, P. undefined, Ruehl, S. J. undefined, Saffi, A. undefined, Saftoiu, F. undefined, Salamida, H. undefined, Salazar, G. undefined, Salina, J. D. undefined, Sanabria Gomez, F. undefined, Sánchez, E. M. undefined, Santos, E. undefined, Santos, F. undefined, Sarazin, R. undefined, Sarmento, C. undefined, Sarmiento-Cano, R. undefined, Sato, P. undefined, Savina, C. M. undefined, Schafer, V. undefined, Scherini, H. undefined, Schieler, M. undefined, Schimassek, M. undefined, Schimp, F. undefined, Schluter, D. undefined, Schmidt, O. undefined, Scholten, P. undefined, Schovánek, F. G. undefined, Schroder, S. undefined, Schroder, J. undefined, Schulte, S. J. undefined, Sciutto, M. undefined, Scornavacche, R. C. undefined, Shellard, G. undefined, Sigl, G. undefined, Silli, O. undefined, Sima, R. undefined, Smída, P. undefined, Sommers, J. F. undefined, Soriano, J. undefined, Souchard, R. undefined, Squartini, M. undefined, Stadelmaier, D. undefined, Stanca, S. undefined, Stanic, J. undefined, Stasielak, P. undefined, Stassi, A. undefined, Streich, M. undefined, Suárez-Durán, T. undefined, Sudholz, T. undefined, Suomijärvi, A. D. undefined, Supanitsky, J. undefined, Supík, Z. undefined, Szadkowski, A. undefined, Taboada, A. undefined, Tapia, C. undefined, Timmermans, O. undefined, Tkachenko, P. undefined, Tobiska, C. J. undefined, Todero Peixoto, B. undefined, Tomé, A. undefined, Travaini, P. undefined, Travnicek, C. undefined, Trimarelli, M. undefined, Trini, M. undefined, Tueros, R. undefined, Ulrich, M. undefined, Unger, L. undefined, Vaclavek, M. undefined, Vacula, J. F. undefined, Valdés Galicia, L. undefined, Valore, E. undefined, Varela, V. undefined, Varma K. C., A. undefined, Vásquez-Ramírez, D. undefined, Veberic, C. undefined, Ventura, I. D. undefined, Vergara Quispe, V. undefined, Verzi, J. undefined, Vicha, J. undefined, Vink, S. undefined, Vorobiov, H. undefined, Wahlberg, A. A. undefined, Wat, M. undefined, Weber, A. undefined, Weindl, L. undefined, Wiencke, H. undefined, Wilczynski, T. undefined, Winchen, M. undefined, Wirtz, D. undefined, Wittkowski, B. undefined, Wundheiler, A. undefined, Yushkov, O. undefined, Zapparrata, E. undefined, Zas, D. undefined, Zavrtanik, M. undefined, Zavrtanik, A. undefined, and Zepeda
- Published
- 2020
16. Trapping of rare earth-doped nanorods using quasi Bessel beam optical fiber tweezers
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Minz, R. A., primary, Tiwari, U., additional, Kumar, A., additional, Nic Chormaic, S., additional, Lahlil, K., additional, Gacoin, T., additional, Mondal, S. K., additional, and Fick, J., additional
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- 2021
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17. Multi-year inter-laboratory exercises for the analysis of illicit drugs and metabolites in wastewater: Development of a quality control system
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van Nuijs, A.L.N. Lai, F.Y. Been, F. Andres-Costa, M.J. Barron, L. Baz-Lomba, J.A. Berset, J.-D. Benaglia, L. Bijlsma, L. Burgard, D. Castiglioni, S. Christophoridis, C. Covaci, A. de Voogt, P. Emke, E. Fatta-Kassinos, D. Fick, J. Hernandez, F. Gerber, C. González-Mariño, I. Grabic, R. Gunnar, T. Kannan, K. Karolak, S. Kasprzyk-Hordern, B. Kokot, Z. Krizman-Matasic, I. Li, A. Li, X. Löve, A.S.C. Lopez de Alda, M. McCall, A.-K. Meyer, M.R. Oberacher, H. O'Brien, J. Quintana, J.B. Reid, M. Schneider, S. Simoes, S.S. Thomaidis, N.S. Thomas, K. Yargeau, V. Ort, C.
- Abstract
Thirty-seven laboratories from 25 countries present the development of an inter-laboratory testing scheme for the analysis of seven illicit drug residues in standard solutions, tap- and wastewater. Almost 10 000 concentration values were evaluated: triplicates of up to five samples and 26 laboratories per year. The setup was substantially improved with experiences gained across the six repetitions (e.g. matrix type, sample conditions, spiking levels). From this, (pre-)analytical issues (e.g. pH adjustment, filtration) were revealed for specific analytes which resulted in formulation of best-practice protocols for inter-laboratory setup and analytical procedures. The results illustrate the effectiveness of the inter-laboratory setup to assess laboratory performance in the framework of wastewater-based epidemiology. The exercise proved that measurements of laboratories were of high quality (>80% satisfactory results for six out of seven analytes) and that analytical follow-up is important to assist laboratories in improving robustness of wastewater-based epidemiology results. © 2018 Elsevier B.V.
- Published
- 2018
18. Exposure to an anti-androgenic herbicide negatively impacts reproductive physiology and fertility in Xenopustropicalis
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Orton, F., Säfholm, M., Jansson, E., Carlsson, Y., Eriksson, A., Fick, J., Uren Webster, T., McMillan, T., Leishman, M., Verbruggen, B., Economou, T., Tyler, C. R., and Berg, C.
- Subjects
Male ,Ekologi ,Ecology ,Herbicides ,Xenopus ,lcsh:R ,lcsh:Medicine ,Androgen Antagonists ,Xenopus Proteins ,Miljövetenskap ,Article ,Fertility ,Animals ,lcsh:Q ,lcsh:Science ,Infertility, Male ,Environmental Sciences - Abstract
Amphibians are threatened on a global scale and pollutants may be contributing to population declines, but how chemicals impact on their reproduction is poorly understood. We conducted a life cycle analysis to investigate the impacts of early life exposure to two anti-androgens (exposure until completion of metamorphosis;stage 66): flutamide, (50 µg/L)/linuron (9 and 45 µg/L)) on sexual development and breeding competence in Xenopus tropicalis. Our analyses included: mRNA levels of dmrt1, cyp17, amh, cyp19, foxl2 and ar (tadpoles/metamorphs), gonadal histomorphology (metamorphs/adults), mRNA levels of ar/gr (adult male brain/gonad/forelimb), testosterone/corticosterone levels (adult males), secondary sexual characteristics (forelimb width/nuptial pad: adult males) and breeding competence (amplexus/fertility: adult males). Compared to controls, feminised sex ratios and increased number of spermatogonia (adults) were observed after exposure to flutamide and the lower linuron concentration. Exposure to the lower linuron concentration also resulted in demasculinisation of secondary sexual characteristics and reduced male fertility. Flutamide exposure resulted in masculinisation of the nuptial pad and elevated mRNA levels of dmrt1, cyp17, amh and foxl2 in brains (metamorphs). Testosterone levels were higher in all treatment groups, however, overall few effects were observed in response to the higher linuron concentration. Our findings advance understanding of reproductive biology of X. tropicalis and illustrate negative effects of linuron on reproductive processes at a concentration measured in freshwater environments.
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- 2018
19. Pharmaceutical residues are widespread in Baltic Sea coastal and offshore waters – Screening for pharmaceuticals and modelling of environmental concentrations of carbamazepine
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Björlenius, Berndt, Ripszám, M., Haglund, P., Lindberg, R. H., Tysklind, M., Fick, J., Björlenius, Berndt, Ripszám, M., Haglund, P., Lindberg, R. H., Tysklind, M., and Fick, J.
- Abstract
The consumption of pharmaceuticals worldwide coupled with modest removal efficiencies of sewage treatment plants have resulted in the presence of pharmaceuticals in aquatic systems globally. In this study, we investigated the environmental concentrations of a selection of 93 pharmaceuticals in 43 locations in the Baltic Sea and Skagerrak. The Baltic Sea is vulnerable to anthropogenic activities due to a long turnover time and a sensitive ecosystem in the brackish water. Thirty-nine of 93 pharmaceuticals were detected in at least one sample, with concentrations ranging between 0.01 and 80 ng/L. One of the pharmaceuticals investigated, the anti-epileptic drug carbamazepine, was widespread in coastal and offshore seawaters (present in 37 of 43 samples). In order to predict concentrations of pharmaceuticals in the sub-basins of the Baltic Sea, a mass balance-based grey box model was set up and the persistent, widely used carbamazepine was selected as the model substance. The model was based on hydrological and meteorological sub-basin characteristics, removal data from smaller watersheds and wastewater treatment plants, and statistics relating to population, consumption and excretion rate of carbamazepine in humans. The grey box model predicted average environmental concentrations of carbamazepine in sub-basins with no significant difference from the measured concentrations, amounting to 0.57-3.2 ng/L depending on sub-basin location. In the Baltic Sea, the removal rate of carbamazepine in seawater was estimated to be 6.2 10(-9) s(-1) based on a calculated half-life time of 3.5 years at 10 degrees C, which demonstrates the long response time of the environment to measures phasing out persistent or slowly degradable substances such as carbamazepine. Sampling, analysis and grey box modelling were all valuable in describing the presence and removal of carbamazepine in the Baltic Sea., QC 20180516
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- 2018
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20. Effects of ozonated sewage effluent on reproduction and behavioral endpoints in zebrafish (Danio rerio)
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Pohl, J., Björlenius, Berndt, Brodin, T., Carlsson, G., Fick, J., Larsson, D. G. J., Norrgren, L., Örn, S., Pohl, J., Björlenius, Berndt, Brodin, T., Carlsson, G., Fick, J., Larsson, D. G. J., Norrgren, L., and Örn, S.
- Abstract
Pharmaceutical residues and other micro-contaminants may enter aquatic environments through effluent from sewage treatment plants (STPs) and could cause adverse effects in wild fish. One strategy to alleviate this situation is to improve wastewater treatment by ozonation. To test the effectiveness of full-scale wastewater effluent ozonation at a Swedish municipal STP, the added removal efficiency was measured for 105 pharmaceuticals. In addition, gene expression, reproductive and behavioral endpoints were analyzed in zebrafish (Danio rerio) exposed on-site over 21 days to ozonated or non-ozonated effluents as well as to tap water. Ozone treatment (7 g O3/m3) removed pharmaceuticals by an average efficiency of 77% in addition to the conventional treatment, leaving 11 screened pharmaceuticals above detection limits. Differences in biological responses of the exposure treatments were recorded in gene expression, reproduction and behavior. Hepatic vitellogenin gene expression was higher in male zebrafish exposed to the ozonated effluent compared to the non-ozonated effluent and tap water treatments. The reproductive success was higher in fish exposed to ozonated effluent compared to non-ozonated effluent and to tap water. The behavioral measurements showed that fish exposed to the ozonated STP effluent were less active in swimming the first minute after placed in a novel vessel. Ozonation is a capable method for removing pharmaceuticals in effluents. However, its implementation should be thoroughly evaluated for any potential biological impact. Future research is needed for uncovering the factors which produced the in vivo responses in fish., QC 20180529
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- 2018
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21. Size-dependent trapping behavior and optical emission study of NaYF4 nanorods in optical fiber tip tweezers
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Leménager, G., primary, Thiriet, M., additional, Pourcin, F., additional, Lahlil, K., additional, Valdivia-Valero, F., additional, Colas des Francs, G., additional, Gacoin, T., additional, and Fick, J., additional
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- 2018
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22. Investigating potential transferability of place-based research in land system science
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Václavík, Tomas, Langerwisch, F., Cotter, M., Fick, J., Häuser, I., Hotes, S., Kamp, J., Settele, Josef, Spangenberg, Joachim Hans, Seppelt, Ralf, Václavík, Tomas, Langerwisch, F., Cotter, M., Fick, J., Häuser, I., Hotes, S., Kamp, J., Settele, Josef, Spangenberg, Joachim Hans, and Seppelt, Ralf
- Abstract
Much of our knowledge about land use and ecosystem services in interrelated social-ecological systems is derived from place-based research. While local and regional case studies provide valuable insights, it is often unclear how relevant this research is beyond the study areas. Drawing generalized conclusions about practical solutions to land management from local observations and formulating hypotheses applicable to other places in the world requires that we identify patterns of land systems that are similar to those represented by the case study. Here, we utilize the previously developed concept of land system archetypes to investigate potential transferability of research from twelve regional projects implemented in a large joint research framework that focus on issues of sustainable land management across four continents. For each project, we characterize its project archetype, i.e. the unique land system based on a synthesis of more than 30 datasets of land-use intensity, environmental conditions and socioeconomic indicators. We estimate the transferability potential of project research by calculating the statistical similarity of locations across the world to the project archetype, assuming higher transferability potentials in locations with similar land system characteristics. Results show that areas with high transferability potentials are typically clustered around project sites but for some case studies can be found in regions that are geographically distant, especially when values of considered variables are close to the global mean or where the project archetype is driven by large-scale environmental or socioeconomic conditions. Using specific examples from the local case studies, we highlight the merit of our approach and discuss the differences between local realities and information captured in global datasets. The proposed method provides a blueprint for large research programs to assess potential transferability of place-based studies to other geogr
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- 2016
23. Long-Term Persistence of an Anxiolytic Drug (Oxazepam) in a Large Freshwater Lake
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Klaminder, J., primary, Brodin, T., additional, Sundelin, A., additional, Anderson, N. J., additional, Fahlman, J., additional, Jonsson, M., additional, and Fick, J., additional
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- 2015
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24. Drawing the fringe – GIS-supported mapping of the rural-urban fringe in the city of Zagreb
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Valozic, Luka and Heindl, A.-B., Steinführer, A., Fick, J., Breeck, I., Kohring, J., Küpper, P., Neumeier, S.
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rural-urban fringe, Zagreb, GIS, landscape, mapping - Abstract
The aim of this project is to present a framework for the mapping of a rural-urban fringe in a GIS-environment. This research explores the possibilities of urban edge delineation and the separation of the rural land uses, such as farming, forestry, recreation, and conservation, from the urban built-up area. Software tools for proximity and overlay analysis, point aggregation and minimum bounding geometry, point and line density, vegetation indices, and surface analysis, have been employed in order to investigate distinctive areas of administrative unit of the City of Zagreb.
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- 2017
25. Deploying plasma arc reforming to a commercial coal to liquid process : a techno-economic study
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Mapamba, Liberty Sheunesu, Fick, J I J, and 10183906 - Fick, Johan Izak Jacobus (Supervisor)
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Cleaner production ,Carbon reclamation ,Plasma arc reforming ,Coal to liquid ,health care economics and organizations ,Carbon efficiency - Abstract
PhD (Development and Management Engineering), North-West University, Potchefstroom Campus, 2016 The coal to liquids (CTL) process has played an important role in the supply security of liquid fuels and petrochemicals in South Africa and has the potential of doing the same for coal rich countries globally. Considering the abundance of coal reserves relative to other fossil fuels, coal is probably going to be instrumental as a feedstock for the production of oil for longer than crude oil and gas. However, the CTL process has challenges that include high capital cost, low carbon efficiency and high greenhouse gas emissions. Further, as climate change policies become more widely accepted, the cost implications may threaten the viability and competitiveness of the coal to liquid process. These challenges could be mitigated by the application of cleaner production as a process improvement initiative in commercial coal to liquids. Process redesign to use cleaner and more efficient technology is promising for implementation to coal to liquids. One re-design option would be to integrate plasma arc reforming (PAR), which converts greenhouse gases in by-product streams to syngas. Redesigning a coal to liquid process to use PAR instead of auto thermal reforming has the potential to improve carbon efficiency, reducing emissions and possibly capital requirements in the process. Though it has such potential, PAR remains at laboratory scale, which brings to question whether it would be feasible and viable to deploy plasma arc reforming to a commercial coal to liquid process. This thesis explores the feasibility and viability of deploying plasma arc reforming to a coal to liquid process. First, a technology assessment was done to evaluate the most suitable configuration for deployment to coal to liquids and evaluating its scalability, commercial development status and efficacy in improving carbon efficiency. After that, the process effects of deploying plasma arc reforming were quantified. Finally, the impact of deploying plasma arc reforming on economic performance of coal to liquids was evaluated. Technology screening shows that, a plasma reactor using carbon dioxide as a plasma gas has the best balance between performance and compatibility with coal to liquids. The deployment of plasma arc reforming is capable of improving the carbon efficiency of a coal to liquid process by up to 15%. It was also found that it is feasible to scale up plasma reformers to commercial scale using commercially available components. However, complete reformers are not yet ready for commercial applications and require development. Kinetic characterisation is key to the reduction of technology risk. The improvement in carbon efficiency translates to 15% (by mass) reduction of coal, 32% reduction of oxygen and 20% reduction of steam requirements for process needs. This is accompanied by the reduction of required equipment capacities for gasification, air separation and steam generation equipment. Reduction of required steam generation equipment is accompanied by a substantial reduction in dilute greenhouse gas emissions that would be difficult to manage by sequestration or other means and a reduction of water requirements. However, use of plasma arc reforming requires 49% additional electrical energy and leads to externalised emissions if sourced from fossil powered power plants. Hence, procurement of low carbon electricity would be desirable. These process changes have an impact on the economic performance of coal to liquids, with impacts on the capital and operating requirements. In the absence of carbon tax, the deployment of plasma arc reforming reduced the break-even price from a baseline cost of $80.95/bbl. to $77.42/bbl. When considering carbon tax equivalent to the proposed regime for South Africa, at an equivalent of $4.80/ton, the PAR modified plant requires an oil price of $81.57/bbl. versus $88.39 required by a conventional plant. For all configurations evaluated, the project net present value was greater than zero and the internal rate of return exceeded the hurdle rate, which was based on the Sasol hurdle rate for a coal to liquid project. From the findings, it was concluded that it is feasible to deploy plasma arc reforming to a commercial coal to liquid process. The economic measures evaluated in the study support that a plasma arc reforming modified coal to liquids plant would be viable. However, the carbon-pricing regime in act and the cost of low carbon electricity have a significant influence on the crude price that provides sufficient confidence to support investments into such a venture Doctoral
- Published
- 2015
26. Perioperative Estrogen Hormonal Therapy Does Not Increase Venous Thromboembolism Risk in Facial Feminization Surgery.
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Li AY, Park MJ, Fick J, Ousterhout DK, and Deschamps-Braly JC
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- Humans, Female, Retrospective Studies, Male, Adult, Middle Aged, Incidence, Estrogen Replacement Therapy adverse effects, Estrogen Replacement Therapy methods, Transgender Persons, Estrogens adverse effects, Estrogens administration & dosage, Risk Factors, Feminization, Perioperative Care methods, Perioperative Care adverse effects, Face, Sex Reassignment Surgery adverse effects, Venous Thromboembolism etiology, Venous Thromboembolism epidemiology, Venous Thromboembolism prevention & control, Venous Thromboembolism chemically induced, Postoperative Complications epidemiology, Postoperative Complications etiology, Postoperative Complications chemically induced
- Abstract
Background: Conflicting data exist regarding increased perioperative venous thromboembolism (VTE) risk with feminizing hormone therapy. The effect has been poorly studied within the transgender population. Acute perioperative cessation of feminizing hormone therapy often leads to unpleasant side effects and exacerbates gender dysphoria in the perioperative period. The authors sought to identify VTE incidence in patients undergoing facial feminization surgery while continuing hormone replacement therapy throughout the time of surgery., Methods: A 38-year retrospective cohort study within a 2-surgeon practice (D.K.O. and J.C.D.-B.) was designed to evaluate postoperative VTE in patients continuing hormone therapy. The primary outcome variable was postoperative VTE., Results: A total of 1715 patients underwent facial feminization surgery within our search window. A total of 953 patients met final inclusion criteria. One patient (0.10%) was diagnosed with a VTE postoperatively, comparable to reported literature rates for similar cosmetic and orthognathic procedures. The average Caprini score of all patients was 3.1 ± 1.0 and the average case length was 491.9 ± 111.0 minutes. Subgroup analysis of patients before and after internal practice changes identified 714 patients (77.7%) continuing full-dose hormonal therapy perioperatively, 197 (20.7%) undergoing hormonal dose reduction to 25% to 50% perioperatively, and 8 who were either not taking hormonal therapy or stopped in the perioperative period. There was no significant difference in VTE incidence among the 3 subgroups ( P > 0.99)., Conclusions: Perioperative use of feminizing hormonal therapy does not increase risk for perioperative VTE in patients undergoing facial feminization surgery. Therefore, it is reasonable to continue these medications through the time of surgery., Clinical Question/level of Evidence: Therapeutic, III., (Copyright © 2024 The Authors. Published by Wolters Kluwer Health, Inc. on behalf of the American Society of Plastic Surgeons.)
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- 2024
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27. Evaluating Soil-Vegetable Contamination with Heavy Metals in Bogura, Bangladesh: A Risk Assessment Approach.
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Samma S, Khan MSI, Chowdhury MTI, Islam MA, Fick J, and Kaium A
- Abstract
This study quantified hazardous heavy metals (Cu, Cr, and Pb) in soil and vegetables (potato, tomato, pepper, cauliflower, and cabbage) across six upazilas (Kahaloo, Bogura Sadar, Shajahanpur, Shibganj, Nandigram, and Dupchanchia) in Bogura district, Bangladesh, assessing their health and environmental impacts. The detection method was validated for its accuracy and precision with QC samples. Results indicated that Cu levels in all samples were within safe limits set by BFSA and FAO/WHO, whereas Cr and Pb in vegetables exceeded permissible levels, though soil concentrations remained within limits. Pb contamination was particularly severe in vegetables (CF > 6), and all vegetables showed significant contamination degrees (CD), highlighting extensive heavy metal pollution. The Pollution Load Index (PLI) identified Kahaloo and Bogura Sadar as the most polluted, whereas Nandigram and Dupchanchia were the least. Bioaccumulation factors (BF) for all metals were <1, suggesting minimal transfer to edible parts. However, the ecological risk index (ERi) and potential ecological risk index (PERI) suggested low ecological risks, but health risk assessments indicated that vegetable consumption poses significant carcinogenic and non-carcinogenic risks (CHR > 10
-4 , HI > 1) across all upazilas. The findings underscore the urgent need for measures to mitigate heavy metal pollution in these areas to safeguard environmental and public health., Competing Interests: The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article., (© The Author(s) 2024.)- Published
- 2024
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28. Pesticide screening of surface water and soil along the Mekong River in Cambodia.
- Author
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Ngin P, Haglund P, Proum S, and Fick J
- Subjects
- Rivers chemistry, Water analysis, Soil, Dichlorvos analysis, Cambodia, Ecosystem, Environmental Monitoring, Water Pollutants, Chemical analysis, Pesticides analysis, Pesticide Residues analysis, Organothiophosphates
- Abstract
Widespread use of pesticides globally has led to serious concerns about environmental contamination, particularly with regard to aquatic and soil ecosystems. This work involved investigating concentrations of 64 pesticides in surface-water and soil samples collected in four provinces along the Mekong River in Cambodia during the dry and rainy seasons (276 samples in total), and conducting semi-structured interviews with local farmers about pesticide use. Furthermore, an ecological risk assessment of the detected pesticides was performed. In total, 56 pesticides were detected in surface water and 43 in soil, with individual pesticides reaching maximum concentrations of 1300 ng/L in the surface-water samples (tebufenozide) and 1100 ng/g dry weight in the soil samples (bromophos-ethyl). The semi-structured interviews made it quite evident that the instructions that farmers are provided regarding the use of pesticides are rudimentary, and that overuse is common. The perceived effect of pesticides was seen as an end-point, and there was a limited process of optimally matching pesticides to pests and crops. Several pesticides were used regularly on the same crop, and the period between application and harvest varied. Risk analysis showed that bromophos-ethyl, dichlorvos, and iprobenfos presented a very high risk to aquatic organisms in both the dry and rainy seasons, with risk quotient values of 850 for both seasons, and of 67 in the dry season and 78 in the rainy season for bromophos-ethyl, and 49 in the dry season and 16 in the rainy season for dichlorvos. Overall, this work highlights the occurrence of pesticide residues in surface water and soil along the Mekong River in Cambodia, and emphasizes the urgent need for monitoring and improving pesticide practices and regulations in the region., 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
- 2024
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29. Cost-Effective Pharmaceutical Implants in Fish: Validating the Performance of Slow-Release Implants for the Antidepressant Fluoxetine.
- Author
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McCallum ES, Cerveny D, Bose APH, Fick J, and Brodin T
- Subjects
- Animals, Fluoxetine, Coconut Oil, Cost-Benefit Analysis, Antidepressive Agents, Pharmaceutical Preparations, Cyprinidae physiology, Environmental Pollutants, Water Pollutants, Chemical analysis
- Abstract
Internal, slow-release implants can be an effective way to manipulate animal physiology or deliver a chemical exposure over long periods of time without the need for an exogenous exposure route. Slow-release implants involve dissolving a compound in a lipid-based carrier, which is inserted into the body of an organism. However, the release kinetics of the compound from the implant to body tissues also requires careful validation. We tested and validated a slow-release implant methodology for exposing fish to a pharmaceutical pollutant, fluoxetine. We tested two lipid-based carriers (coconut oil or vegetable shortening) in the common roach (Rutilus rutilus). The implants contained either a high (50 μg/g), low (25 μg/g), or control (0 μg/g) concentration of fluoxetine, and we measured tissue uptake in the brain, muscle, and plasma of implanted fish over 25 days. The two carriers released fluoxetine differently over time: coconut oil released fluoxetine in an accelerating manner (tissue uptake displayed a positive quadratic curvature), whereas vegetable shortening released fluoxetine in a decelerating manner (a negative quadratic curvature). For both carrier types, fluoxetine was measured at the highest concentration in the brain, followed by muscle and plasma. By comparing the implant exposures with waterborne exposures in the published literature, we showed that the implants delivered an internal exposure that would be similar if fish were exposed in surface waters containing effluents. Overall, we showed that slow-release internal implants are an effective method for delivering chronic exposures of fluoxetine over at least 1-month time scales. Internal exposures can be an especially powerful experimental tool when coupled with field-based study designs to assess the impacts of pharmaceutical pollutants in complex natural environments. Environ Toxicol Chem 2023;42:1326-1336. © 2023 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC., (© 2023 The Authors. Environmental Toxicology and Chemistry published by Wiley Periodicals LLC on behalf of SETAC.)
- Published
- 2023
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30. Neuroactive pharmaceuticals in estuaries: Occurrence and tissue-specific bioaccumulation in multiple fish species.
- Author
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Duarte IA, Reis-Santos P, Fick J, Cabral HN, Duarte B, and Fonseca VF
- Subjects
- Animals, Estuaries, Ecosystem, Bioaccumulation, Fishes, Water, Pharmaceutical Preparations, Environmental Monitoring, Anti-Anxiety Agents, Water Pollutants, Chemical toxicity, Water Pollutants, Chemical analysis
- Abstract
Contamination of surface waters by pharmaceuticals is an emerging problem globally. This is because the increased access and use of pharmaceuticals by a growing world population lead to environmental contamination, threatening non-target species in their natural environment. Of particular concern are neuroactive pharmaceuticals, which are known to bioaccumulate in fish and impact a variety of individual processes such as fish reproduction or behaviour, which can have ecological impacts and compromise fish populations. In this work, we investigate the occurrence and bioaccumulation of 33 neuroactive pharmaceuticals in brain, muscle and liver tissues of multiple fish species collected in four different estuaries (Douro, Tejo, Sado and Mira). In total, 28 neuroactive pharmaceuticals were detected in water and 13 in fish tissues, with individual pharmaceuticals reaching maximum concentrations of 1590 ng/L and 207 ng/g ww, respectively. The neuroactive pharmaceuticals with the highest levels and highest frequency of detection in the water samples were psychostimulants, antidepressants, opioids and anxiolytics, whereas in fish tissues, antiepileptics, psychostimulants, anxiolytics and antidepressants showed highest concentrations. Bioaccumulation was ubiquitous, occurring in all seven estuarine and marine fish species. Notably, neuroactive compounds were detected in every water and fish brain samples, and in 95% of fish liver and muscle tissues. Despite variations in pharmaceutical occurrence among estuaries, bioaccumulation patterns were consistent among estuarine systems, with generally higher bioaccumulation in fish brain followed by liver and muscle. Moreover, no link between bioaccumulation and compounds' lipophilicity, species habitat use patterns or trophic levels was observed. Overall, this work highlights the occurrence of a highly diverse suite of neuroactive pharmaceuticals and their pervasiveness in waters and fish from estuarine systems with contrasting hydromorphology and urban development and emphasizes the urgent need for toxicity assessment of these compounds in natural ecosystems, linked to internalized body concentration in non-target species., 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 © 2022 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2023
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31. Effects of conventionally treated and ozonated wastewater on the damselfly larva oxylipidome in response to on-site exposure.
- Author
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Späth J, Brodin T, Falås P, Niinipuu M, Lindberg R, Fick J, and Nording M
- Subjects
- Animals, Wastewater chemistry, Oxylipins, Larva, Water, Pharmaceutical Preparations, Waste Disposal, Fluid methods, Water Purification methods, Ozone chemistry, Water Pollutants, Chemical analysis
- Abstract
Pharmaceutical residues discharged through insufficiently treated or untreated wastewater enter aquatic environments, where they may adversely impact organisms such as aquatic invertebrates. Ozonation, an advanced wastewater treatment technique, has been successfully implemented to enhance the removal of a broad range of pharmaceuticals, however diverse byproducts and transformation products that are formed during the ozonation process make it difficult to predict how ozonated wastewater may affect aquatic biota. The aim of this study was to investigate effects on fatty acid metabolites, oxylipins, in a common invertebrate species, damselfly larvae, after on-site exposure to conventional wastewater treatment plant (WWTP) effluent and additionally ozonated effluent at a full-scale WWTP. Subsequent ozonation of the conventionally treated wastewater was assessed in terms of i) removal of pharmaceuticals and ii) potential sub-lethal effects on the oxylipidome. Northern damselfly (Coenagrion hastulatum) larvae were exposed for six days in the treatment plant facility to either conventional WWTP effluent or ozonated effluent and the effects on pharmaceutical levels and oxylipin levels were compared with those from tap water control exposure. Ozonation removed pharmaceuticals at an average removal efficiency of 67% (ozone dose of 0.49 g O
3 /g DOC). Of 38 pharmaceuticals detected in the effluent, 16 were removed to levels below the limit of quantification by ozonation. Levels of two oxylipins, 12(13)-EpODE and 15(16)-EpODE, were reduced in larvae exposed to the conventionally treated wastewater in comparison to the tap water control. 15(16)-EpODE was reduced in the larvae exposed to ozonated effluent in comparison to the tap water control. One oxylipin, 8-HETE, was significantly lower in larvae exposed to conventional WWTP effluent compared to ozonated effluent. In conclusion, the study provides proof-of-principle that damselfly larvae can be used on-site to test the impact of differentially treated wastewater., 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 © 2022 The Authors. Published by Elsevier Ltd.. All rights reserved.)- Published
- 2022
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32. Phosphorus release from hydrothermally carbonized digested sewage sludge using organic acids.
- Author
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Pérez C, Boily JF, Skoglund N, Jansson S, and Fick J
- Subjects
- Carbon chemistry, Organic Chemicals, Oxalates, Phosphorus, Temperature, Metals, Heavy, Sewage
- Abstract
Hydrothermal carbonization (HTC) is a treatment technique with great potential for sanitizing digested sewage sludge (SS) and converting it into valuable products. In particular, phosphorus (P) recovery from hydrothermally carbonized SS has attracted special attention in recent years. This work aims to examine the leaching efficiency of P and the consequent release of metals and heavy metals from SS hydrochars (at 180, 215 and 250 °C) using organic acids (oxalate and citrate) over a range of pH values (0-4) and extraction times (5 min-24 h). Both organic acids triggered P extraction efficiencies exceeding 75 % at the lowest pH, but only oxalate reached a nearly complete P release from hydrochars at pH > 0 and for all carbonization temperatures. Low HTC temperature (180 °C) and short extraction time (5 min) were the optimal conditions treatment for P recovery when reacted in oxalate solutions of maximal pH buffering capacity (pH = 1.4). However, oxalate leaching also transferred metals/heavy metals into the P-leachate, with the exception of Ca being retained in the solid residue from HTC as Ca-oxalate precipitate. Different characterization methods confirmed the presence of this precipitate, and provided information about the surface and morphological changes of the SS hydrochars following acid treatment. The results suggest that HTC not only a promising technique to sanitize and reduce the volume of SS, but also an efficient means for P recovery using oxalic acid, thus contributing to the circular economy of P., (Copyright © 2022 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2022
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33. Environmentally relevant concentration of caffeine-effect on activity and circadian rhythm in wild perch.
- Author
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Cerveny D, Cisar P, Brodin T, McCallum ES, and Fick J
- Subjects
- Animals, Caffeine, Circadian Rhythm, Darkness, Swimming, Perches
- Abstract
We studied the ecological consequences of widespread caffeine contamination by conducting an experiment focused on changes in the behavioral traits of wild perch (Perca fluviatilis) after waterborne exposure to 10 μg L
-1 of caffeine. We monitored fish swimming performance during both light and dark conditions to study the effect of caffeine on fish activity and circadian rhythm, using a novel three-dimensional tracking system that enabled positioning even in complete darkness. All individuals underwent three behavioral trials-before exposure, after 24 h of exposure, and after 5 days of exposure. We did not observe any effect of the given caffeine concentration on fish activity under light or dark conditions. Regardless of caffeine exposure, fish swimming performance was significantly affected by both the light-dark conditions and repeating of behavioral trials. Individuals in both treatments swam significantly more during the light condition and their activity increased with time as follows: before exposure < after 24 h of exposure < after 5 days of exposure. We confirmed that the three-dimensional automated tracking system based on infrared sensors was highly effective for conducting behavioral experiments under completely dark conditions., (© 2022. The Author(s).)- Published
- 2022
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34. Frontiers in quantifying wildlife behavioural responses to chemical pollution.
- Author
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Bertram MG, Martin JM, McCallum ES, Alton LA, Brand JA, Brooks BW, Cerveny D, Fick J, Ford AT, Hellström G, Michelangeli M, Nakagawa S, Polverino G, Saaristo M, Sih A, Tan H, Tyler CR, Wong BBM, and Brodin T
- Subjects
- Animals, Behavior, Animal, Biological Evolution, Environment, Animals, Wild, Ecotoxicology
- Abstract
Animal behaviour is remarkably sensitive to disruption by chemical pollution, with widespread implications for ecological and evolutionary processes in contaminated wildlife populations. However, conventional approaches applied to study the impacts of chemical pollutants on wildlife behaviour seldom address the complexity of natural environments in which contamination occurs. The aim of this review is to guide the rapidly developing field of behavioural ecotoxicology towards increased environmental realism, ecological complexity, and mechanistic understanding. We identify research areas in ecology that to date have been largely overlooked within behavioural ecotoxicology but which promise to yield valuable insights, including within- and among-individual variation, social networks and collective behaviour, and multi-stressor interactions. Further, we feature methodological and technological innovations that enable the collection of data on pollutant-induced behavioural changes at an unprecedented resolution and scale in the laboratory and the field. In an era of rapid environmental change, there is an urgent need to advance our understanding of the real-world impacts of chemical pollution on wildlife behaviour. This review therefore provides a roadmap of the major outstanding questions in behavioural ecotoxicology and highlights the need for increased cross-talk with other disciplines in order to find the answers., (© 2022 The Authors. Biological Reviews published by John Wiley & Sons Ltd on behalf of Cambridge Philosophical Society.)
- Published
- 2022
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35. Wastewater effluent affects behaviour and metabolomic endpoints in damselfly larvae.
- Author
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Späth J, Fick J, McCallum E, Cerveny D, Nording ML, and Brodin T
- Subjects
- Animals, Ecosystem, Invertebrates metabolism, Larva metabolism, Wastewater chemistry, Water Pollutants, Chemical metabolism
- Abstract
Wastewater treatment plant effluents have been identified as a major contributor to increasing anthropogenic pollution in aquatic environments worldwide. Yet, little is known about the potentially adverse effects of wastewater treatment plant effluent on aquatic invertebrates. In this study, we assessed effects of wastewater effluent on the behaviour and metabolic profiles of damselfly larvae (Coenagrion hastulatum), a common aquatic invertebrate species. Four key behavioural traits: activity, boldness, escape response, and foraging (traits all linked tightly to individual fitness) were studied in larvae before and after one week of exposure to a range of effluent dilutions (0, 50, 75, 100%). Effluent exposure reduced activity and foraging, but generated faster escape response. Metabolomic analyses via targeted and non-targeted mass spectrometry methods revealed that exposure caused significant changes to 14 individual compounds (4 amino acids, 3 carnitines, 3 lysolipids, 1 peptide, 2 sugar acids, 1 sugar). Taken together, these compound changes indicate an increase in protein metabolism and oxidative stress. Our findings illustrate that wastewater effluent can affect both behavioural and physiological traits of aquatic invertebrates, and as such might pose an even greater threat to aquatic ecosystems than previously assumed. More long-term studies are now needed evaluate if these changes are linked to adverse effects on fitness. The combination of behavioural and metabolomic assessments provide a promising tool for detecting effects of wastewater effluent, on multiple biological levels of organisation, in aquatic ecosystems., (© 2022. The Author(s).)
- Published
- 2022
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36. Bioconcentration of neuroactive pharmaceuticals in fish: Relation to lipophilicity, experimental design and toxicity in the aquatic environment.
- Author
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Duarte IA, Fick J, Cabral HN, and Fonseca VF
- Subjects
- Animals, Bioaccumulation, Ecosystem, Research Design, Pharmaceutical Preparations, Water Pollutants, Chemical analysis, Water Pollutants, Chemical toxicity
- Abstract
Uptake of contaminants is linked to their toxicity and is usually estimated through their lipophilicity (logK
ow ). Here, we review current literature regarding bioconcentration, i.e. uptake of contaminants from the external environment only, and the effects of exposure to neuroactive pharmaceuticals in fish. We aim to determine if lipophilicity is a suitable predictor of bioconcentration of these compounds in fish, to identify major drivers of bioconcentration and explore the link between bioconcentration potential and toxicity, focusing on survival, growth, condition, behaviour and reproduction endpoints. Additionally, we compare concentrations known to elicit significant effects in fish with current environmental concentrations, identifying exposure risk in ecosystems. The majority of studies have focused on antidepressants, mainly fluoxetine, and encompasses mostly freshwater species. Few studies determined pharmaceuticals bioconcentration, and even a smaller portion combined bioconcentration with other toxicity endpoints. Results show that lipophilicity isn't a good predictor of neuroactive pharmaceuticals' bioconcentration in fish, which in turn is highly influenced by experimental parameters, including abiotic conditions, species and life-stage. The need for increased standardization of experimental settings is key towards improving accuracy of environmental risk assessments and application in future regulatory schemes. Still, increased fish lethality was linked to increased bioconcentration, yet no other correlations were observed when considering effects on growth, condition, behaviour or reproduction, likely as a result of insufficient and variable data. In the context of current environmental concentrations, several neuroactive pharmaceuticals were found to be potentially threatening, while data on occurrence is lacking for some compounds, particularly in brackish/marine systems. Specifically, nine compounds (fluoxetine, citalopram, sertraline, amitriptyline, venlafaxine, clozapine, carbamazepine, metamfetamine and oxazepam) were found at concentrations either above or critically close to minimum response concentrations, thus likely to affect fish in freshwater and brackish or marine environments, which supports further exploration in risk management strategies and monitoring programs in aquatic environments., 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 © 2021 Elsevier B.V. All rights reserved.)- Published
- 2022
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37. Fresnel lens optical fiber tweezers to evaluate the vitality of single algae cells.
- Author
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Asadollahbaik A, Kumar A, Heymann M, Giessen H, and Fick J
- Subjects
- Motion, Optical Fibers, Optical Tweezers
- Abstract
Dunaliella salina algae are trapped and studied using dual-fiber optical tweezers based on nano-imprinted Fresnel lenses. Different forms of cyclic motion of living algae inside the optical trap are observed and analyzed. A characteristic periodic motion in the 0-35 Hz frequency region reflects the algal flagella activity and is used to estimate the algal vitality, by photomovement. The trap stiffness and optical forces are measured for the case of a dead algal cell. It is shown that the dual-fiber optical tweezers can be used to study the vitality (or viability) property of single cells, a property that is essential and can be scaled up to other applications, such as sperm analysis for fertility tests.
- Published
- 2022
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38. Metabolomics reveals changes in metabolite profiles due to growth and metamorphosis during the ontogeny of the northern damselfly.
- Author
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Späth J, Brodin T, McCallum E, Cerveny D, Fick J, and Nording ML
- Subjects
- Animals, Gas Chromatography-Mass Spectrometry, Larva, Metabolomics, Metamorphosis, Biological, Odonata
- Abstract
Many insects have complex life cycles where a drastic ontogenetic change happens between the larval stages and the adult stage, i.e. metamorphosis. Damselflies (order Odonata, suborder Zygoptera) are widely distributed and ecologically important semi-aquatic insects with a complex life cycle. Phenotypic changes over damselfly ontogeny have been documented, however, if and how metabolite profiles are also changing is currently unknown. Here we used a metabolomics methodology to gain insights into the metabolic changes during the life cycle of the Northern damselfly (Coenagrion hastulatum). Hatchlings of wild-caught damselflies were reared in the laboratory and metabolomics analyses using liquid chromatography and gas chromatography coupled to mass spectrometry were carried out at three larval stages and on adult damselflies. Additionally, a subset of larvae was exposed to wastewater effluent to assess how metabolite profiles responded to an environmental stressor. A total of 212 compounds belonging to several classes (e.g. amino acids, fatty acids, sugars) were annotated. Across metamorphosis, we found that damselflies shifted from protein catabolism to lipid catabolism. Wastewater effluent exposure resulted in ontogenetic stage-dependent changes of individual metabolites, but not to a marked extent. Overall, our study is one of the first to describe changes of metabolite profiles during ontogeny of an insect, and it provides a first step towards a greater understanding of the physiological changes occurring during general insect-but especially damselfly-ontogeny., (Copyright © 2021 The Author(s). Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2022
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39. The Challenge of Employee Retention in Medical Practices across the United States: An Exploratory Investigation Into the Relationship between Operational Succession Planning and Employee Turnover.
- Author
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Moore H, Dishman L, and Fick J
- Subjects
- Cross-Sectional Studies, Employment, Humans, Retirement, United States, Leadership, Personnel Turnover
- Abstract
Employee turnover is a growing challenge for health-care providers delivering patient care today. US population demographics are shifting as the population ages, which leaves the field of health care poised to lose key leaders and employees to retirement at a time when patient care has grown more complex. This means health care will lose its core of key employees at a time when skilled leadership and specialized knowledge is most needed and directly impacts health care's ability to deliver quality care. Operational succession planning (OSP) may be one solution to manage this looming challenge in health care, as the process identifies and develops the next generation of leadership. Thus, this exploratory national study used a quantitative and cross-sectional design to examine the relationship between OSP and employee turnover. Demographic and 10-point Likert scale data were collected from n = 66 medical practices, using an online survey instrument. Data were analyzed using various descriptive and inferential statistical methods. Distribution (frequency and chi-square) analyses of the study sample, one-way analysis of variance (ANOVA), and regression analyses were performed across seven demographic characteristics of the medical practices: Specialty, Ownership Structure, Number of full-time equivalent (FTE) Physicians, Number of FTE Clinical Employees, Number of FTE Nonclinical Employees, Number of FTE Employees Left Position, and Region. Study results provided statistically significant evidence to support the relationship between OSP and employee turnover, highlighting that OSP was associated with lower employee turnover. The finding suggests that OSP can serve as an effective mechanism for increasing employee retention., (Copyright © 2022 Jennifer L. Hefner and Ingrid M. Nembhard. Published under exclusive licence by Emerald Publishing Limited.)
- Published
- 2021
- Full Text
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40. The association between effectiveness, burnout, and competency in PA leaders.
- Author
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Hartsell Z, Fick J, Lohenry K, and Crandall S
- Subjects
- Burnout, Psychological, Humans, Surveys and Questionnaires, Burnout, Professional
- Published
- 2021
- Full Text
- View/download PDF
41. Screening of pharmaceuticals in coastal waters of the southern coast of Viti Levu in Fiji, South Pacific.
- Author
-
Dehm J, Singh S, Ferreira M, Piovano S, and Fick J
- Subjects
- Environmental Monitoring, Fiji, Research, Pharmaceutical Preparations, Water Pollutants, Chemical analysis
- Abstract
The global reliance on pharmaceuticals coupled with the lack of effective treatment methods has resulted in pseudo-persistence of pharmaceuticals within the environment. Globally, efforts to quantify and monitor pharmaceuticals within the environment have been well underway, however few studies have been made within small Pacific Islands. This study aims at screening for the occurrence and concentration of pharmaceutical residues within the southern coastal waters of Fiji's main island, Viti Levu. Water samples were collected from a depth of ca. 0.6 m from seven sites and were analyzed for 80 pharmaceuticals via a combination of chromatography and heated electrospray ionization. Seventy-two pharmaceuticals were quantified at least once with average concentrations ranging between 0.04 ng/L (diltiazem) and 19 ng/L (ketoconazole), and with all but two pharmaceuticals (trimethoprim and biperiden) being present in less than 50% of the samples. Findings suggest that even though the release of pharmaceuticals into the marine environment is sporadic and pharmaceuticals are diluted via turbulent mixing, there are measurable concentrations of pharmaceuticals in Fiji and these pollutants are not necessarily restricted to highly populated areas., (Copyright © 2021 Elsevier Ltd. All rights reserved.)
- Published
- 2021
- Full Text
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42. Exposure via biotransformation: Oxazepam reaches predicted pharmacological effect levels in European perch after exposure to temazepam.
- Author
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Cerveny D, Fick J, Klaminder J, Bertram MG, and Brodin T
- Subjects
- Animals, Biotransformation, Hypnotics and Sedatives metabolism, Oxazepam metabolism, Perches metabolism, Temazepam metabolism, Water Pollutants, Chemical metabolism, Hypnotics and Sedatives toxicity, Perches physiology, Temazepam toxicity, Water Pollutants, Chemical toxicity
- Abstract
It is generally expected that biotransformation and excretion of pharmaceuticals occurs similarly in fish and mammals, despite significant physiological differences. Here, we exposed European perch (Perca fluviatilis) to the benzodiazepine drug temazepam at a nominal concentration of 2 µg L
-1 for 10 days. We collected samples of blood plasma, muscle, and brain in a time-dependent manner to assess its bioconcentration, biotransformation, and elimination over another 10 days of depuration in clean water. We observed rapid pharmacokinetics of temazepam during both the exposure and depuration periods. The steady state was reached within 24 h of exposure in most individuals, as was complete elimination of temazepam from tissues during depuration. Further, the biologically active metabolite oxazepam was produced via fish biotransformation, and accumulated significantly throughout the exposure period. In contrast to human patients, where a negligible amount of oxazepam is created by temazepam biotransformation, we observed a continuous increase of oxazepam concentrations in all fish tissues throughout exposure. Indeed, oxazepam accumulated more than its parent compound, did not reach a steady state during the exposure period, and was not completely eliminated even after 10 days of depuration, highlighting the importance of considering environmental hazards posed by pharmaceutical metabolites., (Copyright © 2021 The Authors. Published by Elsevier Inc. All rights reserved.)- Published
- 2021
- Full Text
- View/download PDF
43. Antipredator phenotype in crucian carp altered by a psychoactive drug.
- Author
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Vinterstare J, Brönmark C, Nilsson PA, Langerhans RB, Berglund O, Örjes J, Brodin T, Fick J, and Hulthén K
- Abstract
Predator-inducible defenses constitute a widespread form of adaptive phenotypic plasticity, and such defenses have recently been suggested linked with the neuroendocrine system. The neuroendocrine system is a target of endocrine disruptors, such as psychoactive pharmaceuticals, which are common aquatic contaminants. We hypothesized that exposure to an antidepressant pollutant, fluoxetine, influences the physiological stress response in our model species, crucian carp, affecting its behavioral and morphological responses to predation threat. We examined short- and long-term effects of fluoxetine and predator exposure on behavior and morphology in crucian carp. Seventeen days of exposure to a high dose of fluoxetine (100 µg/L) resulted in a shyer phenotype, regardless of the presence/absence of a pike predator, but this effect disappeared after long-term exposure. Fluoxetine effects on morphological plasticity were context-dependent as a low dose (1 µg/L) only influenced crucian carp body shape in pike presence. A high dose of fluoxetine strongly influenced body shape regardless of predator treatment. Our results highlight that environmental pollution by pharmaceuticals could disrupt physiological regulation of ecologically important inducible defenses., Competing Interests: We declare no conflict of interest., (© 2021 The Authors. Ecology and Evolution published by John Wiley & Sons Ltd.)
- Published
- 2021
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44. Oxylipins at intermediate larval stages of damselfly Coenagrion hastulatum as biochemical biomarkers for anthropogenic pollution.
- Author
-
Späth J, Brodin T, Cerveny D, Lindberg R, Fick J, and Nording ML
- Subjects
- Animals, Biomarkers, Larva, Tandem Mass Spectrometry, Odonata, Oxylipins
- Abstract
Aquatic pollution resulting from anthropogenic activities requires adequate environmental monitoring strategies in sentinel organisms. Thus, biochemical biomarkers have been used as early-warning tools of biological effects in aquatic organisms. However, before using these markers for environmental monitoring, knowledge about their developmental variation is vital. In this study, we assessed baseline levels and developmental variations of a group of potential biomarkers, oxylipins, during the lifespan of the Northern damselfly (Coenagrion hastulatum) using liquid chromatography-tandem mass spectrometry. Effects of wastewater exposure on baseline levels were studied in a subset of damselflies to investigate the responsiveness due to anthropogenic pollution. Thirty-eight oxylipins deriving from four polyunsaturated fatty acids via two enzymatic pathways were detected in damselflies at three larval stages and in the adult form. Overall, oxylipin baseline levels showed developmental variation, which was lowest in the intermediate larval stages. Effects of exposure to wastewater effluent on oxylipin baseline levels were dependent on the life stage and were greatest in the early and intermediate larval stages. The study provides first insights into oxylipin profiles of damselflies at different stages of development and their developmental variation. Based on our results, we propose further strategies for incorporating oxylipins in damselfly larvae as biochemical markers for anthropogenic pollution.
- Published
- 2021
- Full Text
- View/download PDF
45. Evidence for selection of multi-resistant E. coli by hospital effluent.
- Author
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Kraupner N, Hutinel M, Schumacher K, Gray DA, Genheden M, Fick J, Flach CF, and Larsson DGJ
- Subjects
- Anti-Bacterial Agents pharmacology, Hospitals, Sweden, Escherichia coli, Wastewater
- Abstract
There is a risk that residues of antibiotics and other antimicrobials in hospital and municipal wastewaters could select for resistant bacteria. Still, direct experimental evidence for selection is lacking. Here, we investigated if effluent from a large Swedish hospital, as well as influent and effluent from the connected municipal wastewater treatment plant (WWTP) select for antibiotic resistant Escherichia coli in three controlled experimental setups. Exposure of sterile-filtered hospital effluent to a planktonic mix of 149 different E. coli wastewater isolates showed a strong selection of multi-resistant strains. Accordingly, exposure to a complex wastewater community selected for strains resistant to several antibiotic classes. Exposing individual strains with variable resistance patterns revealed a rapid bactericidal effect of hospital effluent on susceptible, but not multi-resistant E. coli. No selection was observed after exposure to WWTP effluent, while exposure to WWTP influent indicated a small selective effect for ceftazidime and cefadroxil resistant strains, and only in the E. coli mix assay. An analysis of commonly used antibiotics and non-antibiotic pharmaceuticals in combination with growth and resistance pattern of individual E. coli isolates suggested a possible contribution of ciprofloxacin and β-lactams to the selection by hospital effluent. However, more research is needed to clarify the contribution from different selective agents. While this study does not indicate selection by the studied WWTP effluent, there is some indications of selective effects by municipal influent on β-lactam-resistant strains. Such effects may be more pronounced in countries with higher antibiotic use than Sweden. Despite the limited antibiotic use in Sweden, the hospital effluent strongly and consistently selected for multi-resistance, indicating widespread risks. Hence, there is an urgent need for further evaluation of risks for resistance selection in hospital sewers, as well as for strategies to remove selective agents and resistant bacteria., (Copyright © 2021 The Author(s). Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2021
- Full Text
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46. Investigating the effects of municipal and hospital wastewaters on horizontal gene transfer.
- Author
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Hutinel M, Fick J, Larsson DGJ, and Flach CF
- Subjects
- Anti-Bacterial Agents, Escherichia coli genetics, Hospitals, Humans, Plasmids, Sweden, Gene Transfer, Horizontal, Wastewater
- Abstract
Horizontal gene transfer (HGT) plays an important role in the dissemination of antibiotic resistance genes. In sewer systems, human-associated and environmental bacteria are mixed together and exposed to many substances known to increase HGT, including various antibacterial compounds. In wastewaters, those substances are most often detected below concentrations known to induce HGT individually. Still, it is possible that such wastewaters induce HGT, for example via mixture effects. Here, a panel of antibiotics, biocides and other pharmaceuticals was measured in filter-sterilized municipal and hospital wastewater samples from Gothenburg, Sweden. The effects on HGT of the chemical mixtures in these samples were investigated by exposing a complex bacterial donor community together with a GFP-tagged E. coli recipient strain. Recipients that captured sulfonamide resistance-conferring mobile genetic elements (MGEs) from the bacterial community were enumerated and characterized by replicon typing, antibiotic susceptibility testing and long read sequencing. While exposure to municipal wastewater did not result in any detectable change in HGT rates, exposure to hospital wastewater was associated with an increase in the proportion of recipients that acquired sulfonamide resistance but also a drastic decrease in the total number of recipients. Although, concentrations were generally higher in hospital than municipal wastewater, none of the measured substances could individually explain the observed effects of hospital wastewater. The great majority of the MGEs captured were IncN plasmids, and resistance to several antibiotics was co-transferred in most cases. Taken together, the data show no evidence that chemicals present in the studied municipal wastewater induce HGT. Still, the increased relative abundance of transconjugants after exposure to hospital wastewater could have implications for the risks of both emergence and transmission of resistant bacteria., 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 © 2021 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2021
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- View/download PDF
47. Do environmental pharmaceuticals affect the composition of bacterial communities in a freshwater stream? A case study of the Knivsta river in the south of Sweden.
- Author
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Hagberg A, Gupta S, Rzhepishevska O, Fick J, Burmølle M, and Ramstedt M
- Subjects
- Ecosystem, Environmental Monitoring, Fresh Water, RNA, Ribosomal, 16S genetics, Sewage, Sweden, Pharmaceutical Preparations, Water Pollutants, Chemical analysis
- Abstract
Pharmaceutical substances present at low concentrations in the environment may cause effects on biological systems such as microbial consortia living on solid riverbed substrates. These consortia are an important part of the river ecosystem as they form part of the food chain. This case study aims to contribute to an increased understanding of how low levels of pharmaceuticals in freshwater streams may influence sessile bacterial consortia. An important point source for pharmaceutical release into the environment is treated household sewage water. In order to investigate what types of effects may occur, we collected water samples as well as riverbed substrates from a small stream in the south of Sweden, Knivstaån, upstream and downstream from a sewage treatment plant (STP). Data from these samples formed the base of this case study where we investigated both the presence of pharmaceuticals in the water and bacterial composition on riverbed substrates. In the water downstream from the STP, 19 different pharmaceuticals were detected at levels below 800 ng/dm
3 . The microbial composition was obtained from sequencing 16S rRNA genes directly from substrates as well as from cultivated isolates. The cultivated strains showed reduced species variability compared with the data obtained directly from the substrates. No systematic differences were observed following the sampling season. However, differences could be seen between samples upstream and downstream from the STP effluent. We further observed large similarities in bacterial composition on natural stones compared to sterile stones introduced into the river approximately two months prior to sampling, giving indications for future sampling methodology of biofilms., 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 © 2020 The Authors. Published by Elsevier B.V. All rights reserved.)- Published
- 2021
- Full Text
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48. Neuroactive drugs and other pharmaceuticals found in blood plasma of wild European fish.
- Author
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Cerveny D, Grabic R, Grabicová K, Randák T, Larsson DGJ, Johnson AC, Jürgens MD, Tysklind M, Lindberg RH, and Fick J
- Subjects
- Animals, Czech Republic, Environmental Monitoring, Germany, Humans, Plasma chemistry, Pharmaceutical Preparations, Water Pollutants, Chemical analysis, Water Pollutants, Chemical toxicity
- Abstract
To gain a better understanding of which pharmaceuticals could pose a risk to fish, 94 pharmaceuticals representing 23 classes were analyzed in blood plasma from wild bream, chub, and roach captured at 18 sites in Germany, the Czech Republic and the UK, respectively. Based on read across from humans, we evaluated the risks of pharmacological effects occurring in the fish for each measured pharmaceutical. Twenty-three compounds were found in fish plasma, with the highest levels measured in chub from the Czech Republic. None of the German bream had detectable levels of pharmaceuticals, whereas roach from the Thames had mostly low concentrations. For two pharmaceuticals, four individual Czech fish had plasma concentrations higher than the concentrations reached in the blood of human patients taking the corresponding medication. For nine additional compounds, determined concentrations exceeded 10% of the corresponding human therapeutic plasma concentration in 12 fish. The majority of the pharmaceuticals where a clear risk for pharmacological effects was identified targets the central nervous system. These include e.g. flupentixol, haloperidol, and risperidone, all of which have the potential to affect fish behavior. In addition to identifying pharmaceuticals of environmental concern, the results emphasize the value of environmental monitoring of internal drug levels in aquatic wildlife, as well as the need for more research to establish concentration-response relationships., (Copyright © 2020 The Author(s). Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2021
- Full Text
- View/download PDF
49. Selective concentrations for trimethoprim resistance in aquatic environments.
- Author
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Kraupner N, Ebmeyer S, Hutinel M, Fick J, Flach CF, and Larsson DGJ
- Subjects
- Anti-Bacterial Agents pharmacology, Drug Resistance, Microbial, Humans, Trimethoprim toxicity, Escherichia coli genetics, Trimethoprim Resistance genetics
- Abstract
Antibiotic resistance presents a serious and still growing threat to human health. Environmental exposure levels required to select for resistance are unknown for most antibiotics. Here, we evaluated different experimental approaches and ways to interpret effect measures, in order to identify what concentration of trimethoprim that are likely to select for resistance in aquatic environments. When grown in complex biofilms, selection for resistant E. coli increased at 100 µg/L, whereas there was only a non-significant trend with regards to changes in taxonomic composition within the tested range (0-100 µg/L). Planktonic co-culturing of 149 different E. coli strains isolated from sewage again confirmed selection at 100 µg/L. Finally, pairwise competition experiments were performed with engineered E. coli strains carrying different trimethoprim resistance genes (dfr) and their sensitive counterparts. While strains with introduced resistance genes grew slower than the sensitive ones at 0 and 10 µg/L, a significant reduction in cost was found already at 10 µg/L. Defining lowest effect concentrations by comparing proportion of resistant strains to sensitive ones at the same time point, rather than to their initial ratios, will reflect the advantage a resistance factor can bring, while ignoring exposure-independent fitness costs. As costs are likely to be highly dependent on the specific environmental and genetic contexts, the former approach might be more suitable as a basis for defining exposure limits with the intention to prevent selection for resistance. Based on the present and other studies, we propose that 1 µg/L would be a reasonably protective exposure limit for trimethoprim in aquatic environments., (Copyright © 2020 The Authors. Published by Elsevier Ltd.. All rights reserved.)
- Published
- 2020
- Full Text
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50. Naproxen affects multiple organs in fish but is still an environmentally better alternative to diclofenac.
- Author
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Näslund J, Asker N, Fick J, Larsson DGJ, and Norrgren L
- Subjects
- Animals, Diclofenac metabolism, Dose-Response Relationship, Drug, Gene Expression drug effects, Humans, Kidney metabolism, Kidney pathology, Liver metabolism, Liver pathology, Male, Models, Theoretical, Naproxen metabolism, Smegmamorpha genetics, Sweden, Water Pollutants, Chemical metabolism, Bioaccumulation, Diclofenac toxicity, Kidney drug effects, Liver drug effects, Naproxen toxicity, Smegmamorpha metabolism, Water Pollutants, Chemical toxicity
- Abstract
The presence of diclofenac in the aquatic environment and the risks for aquatic wildlife, especially fish, have been raised in several studies. One way to manage risks without enforcing improved wastewater treatment would be to substitute diclofenac (when suitable from a clinical perspective) with another non-steroidal anti-inflammatory drug (NSAID) associated with less environmental risk. While there are many ecotoxicity-studies of different NSAIDs, they vary extensively in set-up, species studied, endpoints and reporting format, making direct comparisons difficult. We previously published a comprehensive study on the effects of diclofenac in the three-spined stickleback (Gasterosteus aculeatus). Our present aim was to generate relevant effect data for another NSAID (naproxen) using a very similar setup, which also allowed direct comparisons with diclofenac regarding hazards and risks. Sticklebacks were therefore exposed to naproxen in flow-through systems for 27 days. Triplicate aquaria with 20 fish per aquarium were used for each concentration (0, 18, 70, 299 or 1232 μg/L). We investigated bioconcentration, hepatic gene expression, jaw lesions, kidney and liver histology. On day 21, mortalities in the highest exposure concentration group unexpectedly reached ≥ 25 % in all three replicate aquaria, leading us to terminate and sample that group the same day. On the last day (day 27), the mortality was also significantly increased in the second highest exposure concentration group. Increased renal hematopoietic hyperplasia was observed in fish exposed to 299 and 1232 μg/L. This represents considerably higher concentrations than those expected in surface waters as a result of naproxen use. Such effects were observed already at 4.6 μg/L in the experiment with diclofenac (lowest tested concentration). Similar to the responses to diclofenac, a concentration-dependent increase in both relative hepatic gene expression of c7 (complement component 7) and jaw lesions were observed, again at concentrations considerably higher than expected in surface waters. Naproxen bioconcentrated less than diclofenac, in line with the observed effect data. An analysis of recent sales data and reported concentrations in treated sewage effluent in Sweden suggest that despite higher dosages used for naproxen, a complete substitution would only be expected to double naproxen emissions. In summary, naproxen and diclofenac produce highly similar effects in fish but the environmental hazards and risks are clearly lower for naproxen. Hence, if there are concerns for environmental risks to fish with diclofenac, a substitution would be advisable when naproxen presents an adequate alternative from a clinical point-of-view., (Copyright © 2020 The Author(s). Published by Elsevier B.V. All rights reserved.)
- Published
- 2020
- Full Text
- View/download PDF
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