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9. Towards a Comprehensive Evaluation of the Environmental and Health Impacts of Shipping Emissions

Author

Kukkonen, J., Fridell, E., Jalkanen, J.-P., Moldanova, J., Ntziachristos, L., Grigoriadis, A., Barmpas, F., Tsegas, G., Maragkidou, A., Sofiev, Mikhail, Grönholm, T., Majamäki, E., Borken-Kleefeld, J., Sokhi, R. S., Tiwari, P. R., Ozdemir, U. A., Zervakis, V., Krasakopoulou, E., Hassellöv, I.-M., Ytreberg, E., Williams, I., Hudson, M., Zapata-Restrepo, L., Hole, L. R., Aghito, M., Breivik, O., Petrovic, M., Rodriguez-Mozaz, S., Ktoris, A., Neophytou, M., Monteiro, A., Russo, M. A., Oikonomou, F., Arampatzi, P., Gondikas, A., Marcomini, A., Giubilato, E., Calgaro, L., Jaakkola, J. J. K., Kiihamäki, S.-P., Aittamaa, R., Broström, G., Hassellöv, M., Tamminen, J., Nicolas, F., Kaitaranta, J., Granberg, M., Magnusson, K., Mensink, Clemens, editor, and Jorba, Oriol, editor

Published
2022
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11. Towards a Comprehensive Evaluation of the Environmental and Health Impacts of Shipping Emissions

Author

Kukkonen, J., primary, Fridell, E., additional, Jalkanen, J.-P., additional, Moldanova, J., additional, Ntziachristos, L., additional, Grigoriadis, A., additional, Barmpas, F., additional, Tsegas, G., additional, Maragkidou, A., additional, Sofiev, Mikhail, additional, Grönholm, T., additional, Majamäki, E., additional, Borken-Kleefeld, J., additional, Sokhi, R. S., additional, Tiwari, P. R., additional, Ozdemir, U. A., additional, Zervakis, V., additional, Krasakopoulou, E., additional, Hassellöv, I.-M., additional, Ytreberg, E., additional, Williams, I., additional, Hudson, M., additional, Zapata-Restrepo, L., additional, Hole, L. R., additional, Aghito, M., additional, Breivik, O., additional, Petrovic, M., additional, Rodriguez-Mozaz, S., additional, Ktoris, A., additional, Neophytou, M., additional, Monteiro, A., additional, Russo, M. A., additional, Oikonomou, F., additional, Arampatzi, P., additional, Gondikas, A., additional, Marcomini, A., additional, Giubilato, E., additional, Calgaro, L., additional, Jaakkola, J. J. K., additional, Kiihamäki, S.-P., additional, Aittamaa, R., additional, Broström, G., additional, Hassellöv, M., additional, Tamminen, J., additional, Nicolas, F., additional, Kaitaranta, J., additional, Granberg, M., additional, and Magnusson, K., additional

Published
2022
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15. What is in the fish? Collaborative trial in suspect and non-target screening of organic micropollutants using LC- and GC-HRMS

Author

Dürig, W., Lindblad, S., Golovko, O., Gkotsis, G., Aalizadeh, R., Nika, M.-C., Thomaidis, N., Alygizakis, N.A., Plassmann, M., Haglund, P., Fu, Qiuguo, Hollender, J., Chaker, J., David, A., Kunkel, U., Macherius, A., Belova, L., Poma, G., Preud'Homme, H., Munschy, C., Aminot, ., Jaeger, C., Lisec, J., Hansen, M., Vorkamp, K., Zhu, L., Cappelli, F., Roscioli, C., Valsecchi, S., Bagnati, R., González, B., Prieto, A., Zuloaga, O., Gil-Solsona, R., Gago-Ferrero, P., Rodriguez-Mozaz, S., Budzinski, H., Devier, M.-H., Dierkes, G., Boulard, L., Jacobs, G., Voorspoels, S., Rüdel, H., Ahrens, L., Dürig, W., Lindblad, S., Golovko, O., Gkotsis, G., Aalizadeh, R., Nika, M.-C., Thomaidis, N., Alygizakis, N.A., Plassmann, M., Haglund, P., Fu, Qiuguo, Hollender, J., Chaker, J., David, A., Kunkel, U., Macherius, A., Belova, L., Poma, G., Preud'Homme, H., Munschy, C., Aminot, ., Jaeger, C., Lisec, J., Hansen, M., Vorkamp, K., Zhu, L., Cappelli, F., Roscioli, C., Valsecchi, S., Bagnati, R., González, B., Prieto, A., Zuloaga, O., Gil-Solsona, R., Gago-Ferrero, P., Rodriguez-Mozaz, S., Budzinski, H., Devier, M.-H., Dierkes, G., Boulard, L., Jacobs, G., Voorspoels, S., Rüdel, H., and Ahrens, L.

Abstract

A collaborative trial involving 16 participants from nine European countries was conducted within the NORMAN network in efforts to harmonise suspect and non-target screening of environmental contaminants in whole fish samples of bream (Abramis brama). Participants were provided with freeze-dried, homogenised fish samples from a contaminated and a reference site, extracts (spiked and non-spiked) and reference sample preparation protocols for liquid chromatography (LC) and gas chromatography (GC) coupled to high resolution mass spectrometry (HRMS). Participants extracted fish samples using their in-house sample preparation method and/or the protocol provided. Participants correctly identified 9-69% of spiked compounds using LC-HRMS and 20-60% of spiked compounds using GC-HRMS. From the contaminated site, suspect screening with participants’ own suspect lists led to putative identification of on average ∼145 and ∼20 unique features per participant using LC-HRMS and GC-HRMS, respectively, while non-target screening identified on average ∼42 and ∼56 unique features per participant using LC-HRMS and GC-HRMS, respectively. Within the same sub-group of sample preparation method, only a few features were identified by at least two participants in suspect screening (16 features using LC-HRMS, 0 features using GC-HRMS) and non-target screening (0 features using LC-HRMS, 2 features using GC-HRMS). The compounds identified had log octanol/water partition coefficient (KOW) values ranging from -9.9 to 16 and mass-to-charge ratio (m/z) of 68 to 761 (LC-HRMS and GC-HRMS). A significant linear trend was found between log KOW and m/z for the GC-HRMS data. Overall, these findings indicate that differences in screening results are mainly due to the data analysis workflows used by different participants. Further work is needed to harmonise the results obtained when applying suspect and non-target screening approaches to environmental biota samples.

Published
2023

16. Towards a Comprehensive Evaluation of the Environmental and Health Impacts of Shipping Emissions

Author

Mensink, C., Jorba, O., Kukkonen, J., Fridell, E., Jalkanen, J.-P., Moldanova, J., Ntziachristos, L., Grigoriadis, A., Barmpas, F., Tsegas, G., Maragkidou, A., Sofiev, M., Grönholm, T., Majamäki, E., Borken-Kleefeld, J., Sokhi, R. S., Tiwari, P. R., Ozdemir, U. A., Zervakis, V., Krasakopoulou, E., Hassellöv, I.-M., Ytreberg, E., Williams, I., Hudson, M., Zapata-Restrepo, L., Hole, L. R., Aghito, M., Breivik, O., Petrovic, M., Rodriguez-Mozaz, S., Ktoris, A., Neophytou, M., Monteiro, A., Russo, M. A., Oikonomou, F., Arampatzi, P., Gondikas, A., Marcomini, A., Giubilato, E., Calgaro, L., Jaakkola, J. J. K., Kiihamäki, S.-P., Aittamaa, R., Broström, G., Hassellöv, M., Tamminen, J., Nicolas, F., Kaitaranta, J., Granberg, M., Magnusson, K., Mensink, C., Jorba, O., Kukkonen, J., Fridell, E., Jalkanen, J.-P., Moldanova, J., Ntziachristos, L., Grigoriadis, A., Barmpas, F., Tsegas, G., Maragkidou, A., Sofiev, M., Grönholm, T., Majamäki, E., Borken-Kleefeld, J., Sokhi, R. S., Tiwari, P. R., Ozdemir, U. A., Zervakis, V., Krasakopoulou, E., Hassellöv, I.-M., Ytreberg, E., Williams, I., Hudson, M., Zapata-Restrepo, L., Hole, L. R., Aghito, M., Breivik, O., Petrovic, M., Rodriguez-Mozaz, S., Ktoris, A., Neophytou, M., Monteiro, A., Russo, M. A., Oikonomou, F., Arampatzi, P., Gondikas, A., Marcomini, A., Giubilato, E., Calgaro, L., Jaakkola, J. J. K., Kiihamäki, S.-P., Aittamaa, R., Broström, G., Hassellöv, M., Tamminen, J., Nicolas, F., Kaitaranta, J., Granberg, M., and Magnusson, K.

Abstract

We present a new concept for marine research, applied in the EU-funded project EMERGE, “Evaluation, control and Mitigation of the EnviRonmental impacts of shippinG Emissions” (2020–2024; https://emerge-h2020.eu/). For the first time, both the various marine and atmospheric impacts of the shipping sector have been and will be comprehensively analyzed, using a concerted modelling and measurements framework. The experimental part of the project focuses on five European geographical case studies in different ecologically vulnerable regions, and a mobile onboard case study. The EMERGE consortium has also developed a harmonised and integrated modelling framework to assess the combined impacts of shipping emissions, both (i) on the marine ecosystems and (ii) the atmospheric environment. The first results include substantial refinements of a range of models to be applied, especially those for the STEAM and OpenDrift models. In particular, the STEAM (Ship Traffic Emission Assessment Model) model has been extended to allow for the effects of atmospheric and oceanographic factors on the fuel consumption and emissions of the ships. The OpenDrift model has been improved to take into account the partitioning, degradation, and volatilization of pollutants in water. The predicted emission and discharge values have been used as input for both regional scale atmospheric dispersion models, such as WRF-CMAQ (Weather Research and Forecasting—Community Multiscale Air Quality Model) and SILAM (System for Integrated modeLling of Atmospheric composition), and water quality and circulation models, such as OpenDrift (Open source model for the drifting of substances in the ocean) and Delft3D (oceanographic model). The case study regions are Eastern Mediterranean, Northern Adriatic Sea, the Lagoon of Aveiro, the Solent Strait and the Öresund Strait. We have also conducted a substantial part of the experimental campaigns scheduled in the project. The final assessment will include the benefits an

Published
2023
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28. The NORMAN Association and the European Partnership for Chemicals Risk Assessment (PARC): let’s cooperate!

Author

Dulio, V. Koschorreck, J. van Bavel, B. van den Brink, P. Hollender, J. Munthe, J. Schlabach, M. Aalizadeh, R. Agerstrand, M. Ahrens, L. Allan, I. Alygizakis, N. Barcelo’, D. Bohlin-Nizzetto, P. Boutroup, S. Brack, W. Bressy, A. Christensen, J.H. Cirka, L. Covaci, A. Derksen, A. Deviller, G. Dingemans, M.M.L. Engwall, M. Fatta-Kassinos, D. Gago-Ferrero, P. Hernández, F. Herzke, D. Hilscherová, K. Hollert, H. Junghans, M. Kasprzyk-Hordern, B. Keiter, S. Kools, S.A.E. Kruve, A. Lambropoulou, D. Lamoree, M. Leonards, P. Lopez, B. López de Alda, M. Lundy, L. Makovinská, J. Marigómez, I. Martin, J.W. McHugh, B. Miège, C. O’Toole, S. Perkola, N. Polesello, S. Posthuma, L. Rodriguez-Mozaz, S. Roessink, I. Rostkowski, P. Ruedel, H. Samanipour, S. Schulze, T. Schymanski, E.L. Sengl, M. Tarábek, P. Ten Hulscher, D. Thomaidis, N. Togola, A. Valsecchi, S. van Leeuwen, S. von der Ohe, P. Vorkamp, K. Vrana, B. Slobodnik, J.

Abstract

The Partnership for Chemicals Risk Assessment (PARC) is currently under development as a joint research and innovation programme to strengthen the scientific basis for chemical risk assessment in the EU. The plan is to bring chemical risk assessors and managers together with scientists to accelerate method development and the production of necessary data and knowledge, and to facilitate the transition to next-generation evidence-based risk assessment, a non-toxic environment and the European Green Deal. The NORMAN Network is an independent, well-established and competent network of more than 80 organisations in the field of emerging substances and has enormous potential to contribute to the implementation of the PARC partnership. NORMAN stands ready to provide expert advice to PARC, drawing on its long experience in the development, harmonisation and testing of advanced tools in relation to chemicals of emerging concern and in support of a European Early Warning System to unravel the risks of contaminants of emerging concern (CECs) and close the gap between research and innovation and regulatory processes. In this commentary we highlight the tools developed by NORMAN that we consider most relevant to supporting the PARC initiative: (i) joint data space and cutting-edge research tools for risk assessment of contaminants of emerging concern; (ii) collaborative European framework to improve data quality and comparability; (iii) advanced data analysis tools for a European early warning system and (iv) support to national and European chemical risk assessment thanks to harnessing, combining and sharing evidence and expertise on CECs. By combining the extensive knowledge and experience of the NORMAN network with the financial and policy-related strengths of the PARC initiative, a large step towards the goal of a non-toxic environment can be taken. © 2020, The Author(s).

Published
2020

29. The NORMAN Association and the European Partnership for Chemicals Risk Assessment (PARC): let’s cooperate!

Author

Dulio, V., Koschorreck, J., van Bavel, B., van den Brink, P., Hollender, J., Munthe, J., Schlabach, M., Aalizadeh, R., Agerstrand, M., Ahrens, L., Allan, I., Alygizakis, N., Barcelo, D., Bohlin‑Nizzetto, P., Boutroup, S., Brack, Werner, Bressy, A., Christensen, J.H., Cirka, L., Covaci, A., Derksen, A., Deviller, G., Dingemans, M.M.L., Engwall, M., Fatta-Kassinos, D., Gago‑Ferrero, P., Hernández, F., Herzke, D., Hilscherová, K., Hollert, H., Junghans, M., Kasprzyk‑Hordern, B., Keiter, S., Kools, S.A.E., Kruve, A., Lambropoulou, D., Lamoree, M., Leonards, P., Lopez, B., López de Alda, M., Lundy, L., Makovinská, J., Marigómez, I., Martin, J.W., McHugh, B., Miège, C., O’Toole, S., Perkola, N., Polesello, S., Posthuma, L., Rodriguez‑Mozaz, S., Roessink, I., Rostkowski, P., Ruedel, H., Samanipour, S., Schulze, Tobias, Schymanski, E.L., Sengl, M., Tarábek, P., Ten Hulscher, D., Thomaidis, N., Togola, A., Valsecchi, S., van Leeuwen, S., von der Ohe, P., Vorkamp, K., Vrana, B., Slobodnik, J., Dulio, V., Koschorreck, J., van Bavel, B., van den Brink, P., Hollender, J., Munthe, J., Schlabach, M., Aalizadeh, R., Agerstrand, M., Ahrens, L., Allan, I., Alygizakis, N., Barcelo, D., Bohlin‑Nizzetto, P., Boutroup, S., Brack, Werner, Bressy, A., Christensen, J.H., Cirka, L., Covaci, A., Derksen, A., Deviller, G., Dingemans, M.M.L., Engwall, M., Fatta-Kassinos, D., Gago‑Ferrero, P., Hernández, F., Herzke, D., Hilscherová, K., Hollert, H., Junghans, M., Kasprzyk‑Hordern, B., Keiter, S., Kools, S.A.E., Kruve, A., Lambropoulou, D., Lamoree, M., Leonards, P., Lopez, B., López de Alda, M., Lundy, L., Makovinská, J., Marigómez, I., Martin, J.W., McHugh, B., Miège, C., O’Toole, S., Perkola, N., Polesello, S., Posthuma, L., Rodriguez‑Mozaz, S., Roessink, I., Rostkowski, P., Ruedel, H., Samanipour, S., Schulze, Tobias, Schymanski, E.L., Sengl, M., Tarábek, P., Ten Hulscher, D., Thomaidis, N., Togola, A., Valsecchi, S., van Leeuwen, S., von der Ohe, P., Vorkamp, K., Vrana, B., and Slobodnik, J.

Abstract

The Partnership for Chemicals Risk Assessment (PARC) is currently under development as a joint research and innovation programme to strengthen the scientific basis for chemical risk assessment in the EU. The plan is to bring chemical risk assessors and managers together with scientists to accelerate method development and the production of necessary data and knowledge, and to facilitate the transition to next-generation evidence-based risk assessment, a non-toxic environment and the European Green Deal. The NORMAN Network is an independent, well-established and competent network of more than 80 organisations in the field of emerging substances and has enormous potential to contribute to the implementation of the PARC partnership. NORMAN stands ready to provide expert advice to PARC, drawing on its long experience in the development, harmonisation and testing of advanced tools in relation to chemicals of emerging concern and in support of a European Early Warning System to unravel the risks of contaminants of emerging concern (CECs) and close the gap between research and innovation and regulatory processes. In this commentary we highlight the tools developed by NORMAN that we consider most relevant to supporting the PARC initiative: (i) joint data space and cutting-edge research tools for risk assessment of contaminants of emerging concern; (ii) collaborative European framework to improve data quality and comparability; (iii) advanced data analysis tools for a European early warning system and (iv) support to national and European chemical risk assessment thanks to harnessing, combining and sharing evidence and expertise on CECs. By combining the extensive knowledge and experience of the NORMAN network with the financial and policy-related strengths of the PARC initiative, a large step towards the goal of a non-toxic environment can be taken.

Published
2020

32. Antibiotic resistance in European wastewater treatment plants mirrors the pattern of clinical antibiotic resistance prevalence

Author

Ministerio de Economía y Competitividad (España), Martínez, José Luis [0000-0001-8813-7607], Pärnänen, K. M. M., Narciso-Da-Rocha, C., Kneis, D., Berendonk, Thomas Ulrich, Cacace, D., Do, T. T., Elpers, C., Fatta-Kassinos, Despo, Henriques, I., Jaeger, T., Karkman, A., Martínez, J. L., Michael, S.G., Michael-Kordatou, I., O'Sullivan, K., Rodriguez-Mozaz, S., Schwartz, T., Sheng, H., Sørum, H., Stedtfeld, R.D., Tiedje, J.M., Giustina, S.V.D., Walsh, F., Vaz-Moreira, I., Virta, M., Manaia, Célia M., Ministerio de Economía y Competitividad (España), Martínez, José Luis [0000-0001-8813-7607], Pärnänen, K. M. M., Narciso-Da-Rocha, C., Kneis, D., Berendonk, Thomas Ulrich, Cacace, D., Do, T. T., Elpers, C., Fatta-Kassinos, Despo, Henriques, I., Jaeger, T., Karkman, A., Martínez, J. L., Michael, S.G., Michael-Kordatou, I., O'Sullivan, K., Rodriguez-Mozaz, S., Schwartz, T., Sheng, H., Sørum, H., Stedtfeld, R.D., Tiedje, J.M., Giustina, S.V.D., Walsh, F., Vaz-Moreira, I., Virta, M., and Manaia, Célia M.

Abstract

Integrated antibiotic resistance (AR) surveillance is one of the objectives of the World Health Organization global action plan on antimicrobial resistance. Urban wastewater treatment plants (UWTPs) are among the most important receptors and sources of environmental AR. On the basis of the consistent observation of an increasing north-to-south clinical AR prevalence in Europe, this study compared the influent and final effluent of 12 UWTPs located in seven countries (Portugal, Spain, Ireland, Cyprus, Germany, Finland, and Norway). Using highly parallel quantitative polymerase chain reaction, we analyzed 229 resistance genes and 25 mobile genetic elements. This first trans-Europe surveillance showed that UWTP AR profiles mirror the AR gradient observed in clinics. Antibiotic use, environmental temperature, and UWTP size were important factors related with resistance persistence and spread in the environment. These results highlight the need to implement regular surveillance and control measures, which may need to be appropriate for the geographic regions.

Published
2019

33. Output of GLOBAQUA WP7 ECOSYSTEM: Incorporating ecosystem functioning into river monitoring and assessment

Author

Elosegi, A., von Schiller, D., Acuna, V., Aristi, I., Arroita, M., Basaguren, A., Bellin, A., Boyero, L., Butturini, A., Ginebreda, A., Kalogianni, E., Larranaga, A., Majone, B., Martinez, A., Monroy, S., Munoz, I., Paunovic, M., Pereda, O., Petrovic, M., Pozo, J., Rodriguez-Mozaz, S., Rivas, D., Sabater, S., Sabater, F., Skoulikidis, N., Smeti, E., Solagaistua, L., and Vardakas, L.

Published
2018

47. A global multinational survey of cefotaxime-resistant coliforms in urban wastewater treatment plants

Author

Yunho Lee, Manika Choudhury, Om Prakash, Donald Morrison, Hélène Guilloteau, Heidrun Mayrhofer, María Inmaculada Polo-López, Belen Esteban, Katarzyna Slipko, Leonardo Pantoja Munoz, Samira Nahim–Granados, José Manuel Guillén-Navarro, Marco Guida, Stela Krizanovic, Hemda Garelick, Pilar Caballero, Traore Ousmane, Marcos Quintela-Baluja, Sara Rodríguez-Mozaz, Helmut Bürgmann, Nikolina Udiković-Kolić, Carsten Ulrich Schwermer, Agnieszka Kalinowska, Milena Milaković, Ester Heath, Marta Piotrowska, Andrea Di Cesare, Célia M. Manaia, Ying Yang, Amy Pruden, Anne F.C. Leonard, Erica Donner, Tanel Telson, Christophe Merlin, Karin Beck, Ana Agüera, Anhony A Adegoke, Marie-Noëlle Pons, Bastian Herzog, Joana Abreu-Silva, Leonie Henn, Norbert Kreuzinger, Younggun Yoon, Stefanie Heß, Olga C. Nunes, Alice L. Petre, Despo Fatta-Kassinos, Gianluca Brunetti, Roberto B. M. Marano, Stella Michael, Thor A. Stenström, Ayella Maile-Moskowitz, Popi Karaolia, Joshua T. Bunce, Giovanni Libralato, Jérôme Ory, Yogesh Nimonkar, Alfieri Pollice, Aneta Luczkiewicz, Carlo Salerno, Andrew Scott, Shichun Zou, Antoni Oliver, Barbara Drigo, Isabel Martínez-Alcalá, Virginia Riquelme, Veljo Kisand, Anna Baraniak, William H. Gaze, Edward Topp, Edouard Jurkevitch, Isabel Henriques, Telma Fernandes, Eddie Cytryn, José Luis Balcázar, Marta Tacão, Thomas Schwartz, Thomas Jäger, Gianluca Corno, Mailis Laht, Thomas U. Berendonk, Roberto Rosal, Magdalena Popowska, Pawel Krzeminski, Connor L. Brown, Veritati - Repositório Institucional da Universidade Católica Portuguesa, Marano, R. B. M., Fernandes, T., Manaia, C. M., Nunes, O., Morrison, D., Berendonk, T. U., Kreuzinger, N., Telson, T., Corno, G., Fatta-Kassinos, D., Merlin, C., Topp, E., Jurkevitch, E., Henn, L., Scott, A., Hess, S., Slipko, K., Laht, M., Kisand, V., Di Cesare, A., Karaolia, P., Michael, S. G., Petre, A. L., Rosal, R., Pruden, A., Riquelme, V., Aguera, A., Esteban, B., Luczkiewicz, A., Kalinowska, A., Leonard, A., Gaze, W. H., Adegoke, A. A., Stenstrom, T. A., Pollice, A., Salerno, C., Schwermer, C. U., Krzeminski, P., Guilloteau, H., Donner, E., Drigo, B., Libralato, G., Guida, M., Burgmann, H., Beck, K., Garelick, H., Tacao, M., Henriques, I., Martinez-Alcala, I., Guillen-Navarro, J. M., Popowska, M., Piotrowska, M., Quintela-Baluja, M., Bunce, J. T., Polo-Lopez, M. I., Nahim-Granados, S., Pons, M. -N., Milakovic, M., Udikovic-Kolic, N., Ory, J., Ousmane, T., Caballero, P., Oliver, A., Rodriguez-Mozaz, S., Balcazar, J. L., Jager, T., Schwartz, T., Yang, Y., Zou, S., Lee, Y., Yoon, Y., Herzog, B., Mayrhofer, H., Prakash, O., Nimonkar, Y., Heath, E., Baraniak, A., Abreu-Silva, J., Choudhury, M., Munoz, L. P., Krizanovic, S., Brunetti, G., Maile-Moskowitz, A., Brown, C., Cytryn, E., The Robert H. Smith Faculty of Agriculture, Food and Environment, Department of Animal Sciences, The Hebrew University of Jerusalem (HUJ), Institute of Soil, Water and Environmental Sciences, Agricultural Research Organization - the Volcani Center, Centro de Química Fina e Biotecnologia (CQFB), Requimte, Universidade do Porto-Departamento de Química (DQ), Faculdade de Ciências e Tecnologia = School of Science & Technology (FCT NOVA), Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Faculdade de Ciências e Tecnologia = School of Science & Technology (FCT NOVA), Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade do Porto-Departamento de Química (DQ), Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade Nova de Lisboa = NOVA University Lisbon (NOVA), Laboratory for Process Engineering, Environment, Biotechnology and Energy (LEPABE), Universidade do Porto, Edinburgh Napier University, Institute for Hydrobiology, Technische Universität Dresden = Dresden University of Technology (TU Dresden), Vienna University of Technology, Institute of Technology [Tartu, Estonia], University of Tartu, CNR Water Research Institute (IRSA), Consiglio Nazionale delle Ricerche (CNR), University of Cyprus (UCY), Laboratoire de Chimie Physique et Microbiologie pour les Matériaux et l'Environnement (LCPME), Institut de Chimie du CNRS (INC)-Université de Lorraine (UL)-Centre National de la Recherche Scientifique (CNRS), Agriculture and Agri-Food [Ottawa] (AAFC), Department of Biology, University of Western Ontario, University of Western Ontario (UWO), Estonian Environmental Research Centre (EKUK), Universidad de Alcalá - University of Alcalá (UAH), Virginia Tech [Blacksburg], Area de Quimica Inorganica - Centro de Investigacion en Energia Solar (CIESOL) (CIESOL), Universidad de Almería (UAL), Gdańsk University of Technology (GUT), University of Exeter Medical School, University of Exeter, Durban University of Technology, Universidad Nacional de Cuyo [Mendoza] (UNCUYO), Norwegian Institute for Water Research (NIVA), University of South Australia [Adelaide], Università degli studi di Napoli Federico II, Swiss Federal Insitute of Aquatic Science and Technology [Dübendorf] (EAWAG), Middlesex University [London], Universidade de Aveiro, Universidade de Coimbra [Coimbra], Universidad Católica San Antonio de Murcia (UCAM), Department of Applied Microbiology [Warsaw], Institute of Microbiology [Warsaw], Faculty of Biology [Warsaw], University of Warsaw (UW)-University of Warsaw (UW)-Faculty of Biology [Warsaw], University of Warsaw (UW)-University of Warsaw (UW), School of Engineering [Newcastle], Newcastle University [Newcastle], Plataforma Solar de Almeria – CIEMAT, Tabernas, Almeria, Laboratoire Réactions et Génie des Procédés (LRGP), Centre National de la Recherche Scientifique (CNRS)-Université de Lorraine (UL), Rudjer Boskovic Institute [Zagreb], Laboratoire Microorganismes : Génome et Environnement (LMGE), Université Clermont Auvergne [2017-2020] (UCA [2017-2020])-Centre National de la Recherche Scientifique (CNRS), CHU Clermont-Ferrand, Laboratorio EMATSA, Instituto Catalán de Investigación del Agua - ICRA (SPAIN) (ICRA), Institute of Functional Interfaces, Karlsruhe Institute of Technology (KIT), Sun Yat-Sen University [Guangzhou] (SYSU), Gwangju Institute of Science and Technology (GIST), Technische Universität Munchen - Université Technique de Munich [Munich, Allemagne] (TUM), NCMR, Jozef Stefan Institute [Ljubljana] (IJS), National Medicines Institute - Narodowy Instytut Leków [Warsaw] (NIL), Agricultural Research Organisation (ARO), Volcani Center, Universidade do Porto = University of Porto-Departamento de Química (DQ), Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade Nova de Lisboa = NOVA University Lisbon (NOVA)-Universidade do Porto = University of Porto-Departamento de Química (DQ), Universidade do Porto = University of Porto, National Research Council of Italy | Consiglio Nazionale delle Ricerche (CNR), University of Cyprus [Nicosia] (UCY), Agriculture and Agri-Food (AAFC), University of Naples Federico II = Università degli studi di Napoli Federico II, Université de Lorraine (UL)-Centre National de la Recherche Scientifique (CNRS), Marano, Robert BM, Fernandes, Telma, Manaia, Celia M, Nunes, Olga, Donner, Erica, Drigo, Barbara, Brunetti, Gianluca, and Cytryn, Eddie

Subjects
Cefotaxime, 010504 meteorology & atmospheric sciences, Coliforms, Antibiotic resistance, Sewage, Microorganismes -- Resistència als medicaments, Wastewater treatment, Wastewater, 010501 environmental sciences, 01 natural sciences, Surveys and Questionnaires, Microorganisms -- Drug resistance, ComputingMilieux_MISCELLANEOUS, lcsh:Environmental sciences, General Environmental Science, lcsh:GE1-350, 6. Clean water, Anti-Bacterial Agents, 3. Good health, Europe, Interdisciplinary Natural Sciences, Health, Sewage treatment, Biotechnology, medicine.drug, Life sciences, biology, Aigua -- Reutilització, Asia, Quantification methods, Aigües residuals -- Plantes de tractament, Culture and Communities, Water Purification, Applied microbiology, Water reuse, Environmental health, ddc:570, medicine, Microbiology Research Group, [SPI.GPROC]Engineering Sciences [physics]/Chemical and Process Engineering, antibiotic resistance, coliforms, ESBLs, wastewater treatment, wastewater reuse, Sewage disposal plants, Effluent, 0105 earth and related environmental sciences, [SDV.EE.SANT]Life Sciences [q-bio]/Ecology, environment/Health, Coliform, business.industry, Australia, Fecal coliform, Antibiotic resistance, Coliforms, ESBLs, Wastewater treatment, Water reuse, ESBL, North America, Environmental science, business
Abstract

The World Health Organization Global Action Plan recommends integrated surveillance programs as crucial strategies for monitoring antibiotic resistance. Although several national surveillance programs are in place for clinical and veterinary settings, no such schemes exist for monitoring antibiotic-resistant bacteria in the environment. In this transnational study, we developed, validated, and tested a low-cost surveillance and easy to implement approach to evaluate antibiotic resistance in wastewater treatment plants (WWTPs) by targeting cefotaxime-resistant (CTX-R) coliforms as indicators. The rationale for this approach was: i) coliform quantification methods are internationally accepted as indicators of fecal contamination in recreational waters and are therefore routinely applied in analytical labs; ii) CTX-R coliforms are clinically relevant, associated with extended-spectrum β-lactamases (ESBLs), and are rare in pristine environments. We analyzed 57 WWTPs in 22 countries across Europe, Asia, Africa, Australia, and North America. CTX-R coliforms were ubiquitous in raw sewage and their relative abundance varied significantly (

Published
2020

48. The Complex Interplay Between Antibiotic Resistance and Pharmaceutical and Personal Care Products in the Environment.

Author

Manaia CM, Aga DS, Cytryn E, Gaze WH, Graham DW, Guo J, Leonard AFC, Li L, Murray AK, Nunes OC, Rodriguez-Mozaz S, Topp E, and Zhang T

Subjects
Humans, Bacteria, Angiotensin Receptor Antagonists pharmacology, Angiotensin-Converting Enzyme Inhibitors pharmacology, Drug Resistance, Microbial genetics, Pharmaceutical Preparations, Anti-Bacterial Agents pharmacology, Genes, Bacterial, Cosmetics
Abstract

Antibiotic-resistant bacteria (ARB) and antibiotic resistance genes (ARGs) are important environmental contaminants. Nonetheless, what drives the evolution, spread, and transmission of antibiotic resistance dissemination is still poorly understood. The abundance of ARB and ARGs is often elevated in human-impacted areas, especially in environments receiving fecal wastes, or in the presence of complex mixtures of chemical contaminants, such as pharmaceuticals and personal care products. Self-replication, mutation, horizontal gene transfer, and adaptation to different environmental conditions contribute to the persistence and proliferation of ARB in habitats under strong anthropogenic influence. Our review discusses the interplay between chemical contaminants and ARB and their respective genes, specifically in reference to co-occurrence, potential biostimulation, and selective pressure effects, and gives an overview of mitigation by existing man-made and natural barriers. Evidence and strategies to improve the assessment of human health risks due to environmental antibiotic resistance are also discussed. Environ Toxicol Chem 2024;43:637-652. © 2022 SETAC., (© 2022 SETAC.)

Published
2024
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49. What is in the fish? Collaborative trial in suspect and non-target screening of organic micropollutants using LC- and GC-HRMS.

Author

Dürig W, Lindblad S, Golovko O, Gkotsis G, Aalizadeh R, Nika MC, Thomaidis N, Alygizakis NA, Plassmann M, Haglund P, Fu Q, Hollender J, Chaker J, David A, Kunkel U, Macherius A, Belova L, Poma G, Preud'Homme H, Munschy C, Aminot Y, Jaeger C, Lisec J, Hansen M, Vorkamp K, Zhu L, Cappelli F, Roscioli C, Valsecchi S, Bagnati R, González B, Prieto A, Zuloaga O, Gil-Solsona R, Gago-Ferrero P, Rodriguez-Mozaz S, Budzinski H, Devier MH, Dierkes G, Boulard L, Jacobs G, Voorspoels S, Rüdel H, and Ahrens L

Subjects
Animals, Humans, Gas Chromatography-Mass Spectrometry, Chromatography, Liquid methods, Mass Spectrometry methods, Environmental Monitoring methods, Fishes
Abstract

A collaborative trial involving 16 participants from nine European countries was conducted within the NORMAN network in efforts to harmonise suspect and non-target screening of environmental contaminants in whole fish samples of bream (Abramis brama). Participants were provided with freeze-dried, homogenised fish samples from a contaminated and a reference site, extracts (spiked and non-spiked) and reference sample preparation protocols for liquid chromatography (LC) and gas chromatography (GC) coupled to high resolution mass spectrometry (HRMS). Participants extracted fish samples using their in-house sample preparation method and/or the protocol provided. Participants correctly identified 9-69 % of spiked compounds using LC-HRMS and 20-60 % of spiked compounds using GC-HRMS. From the contaminated site, suspect screening with participants' own suspect lists led to putative identification of on average ∼145 and ∼20 unique features per participant using LC-HRMS and GC-HRMS, respectively, while non-target screening identified on average ∼42 and ∼56 unique features per participant using LC-HRMS and GC-HRMS, respectively. Within the same sub-group of sample preparation method, only a few features were identified by at least two participants in suspect screening (16 features using LC-HRMS, 0 features using GC-HRMS) and non-target screening (0 features using LC-HRMS, 2 features using GC-HRMS). The compounds identified had log octanol/water partition coefficient (K OW ) values from -9.9 to 16 and mass-to-charge ratios (m/z) of 68 to 761 (LC-HRMS and GC-HRMS). A significant linear trend was found between log K OW and m/z for the GC-HRMS data. Overall, these findings indicate that differences in screening results are mainly due to the data analysis workflows used by different participants. Further work is needed to harmonise the results obtained when applying suspect and non-target screening approaches to environmental biota samples., 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 Ltd.. All rights reserved.)

Published
2023
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50. Prospects on coupling UV/H 2 O 2 with activated sludge or a fungal treatment for the removal of pharmaceutically active compounds in real hospital wastewater.

Author

Mir-Tutusaus JA, Jaén-Gil A, Barceló D, Buttiglieri G, Gonzalez-Olmos R, Rodriguez-Mozaz S, Caminal G, and Sarrà M

Subjects
Hospitals, Hydrogen Peroxide, Oxidation-Reduction, Sewage, Ultraviolet Rays, Waste Disposal, Fluid, Wastewater, Water Pollutants, Chemical analysis, Water Purification
Abstract

Conventional active sludge (AS) process at municipal centralized wastewater treatment facilities may exhibit little pharmaceuticals (PhACs) removal efficiencies when treating hospital wastewater (HWW). Therefore, a dedicated efficient wastewater treatment at the source point is recommended. In this sense, advanced oxidation processes (AOPs) and fungal treatment (FG) have evidenced promising results in degrading PhACs. The coupling of the AOP based on UV/H 2 O 2 treatment with biological treatment (AS or FG) treating a real non-sterile HWW, was evaluated in this work. In addition, a coagulation-flocculation pretreatment was applied to improve the efficiency of all approaches. Twenty-two PhACs were detected in raw HWW, which were effectively removed (93-95%) with the combination of any of the biological treatment followed by UV/H 2 O 2 treatment. Similar removal results (94%) were obtained when placing UV/H 2 O 2 treatment before FG, while a lower removal (83%) was obtained in the combination of UV/H 2 O 2 followed by AS. However, the latest was the only treatment combination that achieved a decrease in the toxicity of water. Moreover, deconjugation of conjugated PhACs has been suggested for ofloxacin and lorazepam after AS treatment, and for ketoprofen after fungal treatment. Monitoring of carbamazepine and its transformation products along the treatment allowed to identify the same carbamazepine degradation pathway in UV/H 2 O 2 and AS treatments, unlike fungal treatment, which followed another degradation route., 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
2021
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