FN Archimer Export Format PT J TI Metals concentrations in transitional and coastal waters by ICPMS and voltammetry analysis of spot samples and passive samplers (DGT) BT AF Caetano, Miguel Correia dos Santos, Margarida M. Rosa, Nuno Carvalho, Inês Rodríguez, Jose germain Belzunce-Segarra, María Jesús Menchaca, Iratxe Larreta, Joana Sanz, Marta Rodrigo Millán-Gabet, Vanessa Gonzalez, Jean-Louis Amouroux, Isabelle Guesdon, Stephane Menet-Nédélec, Florence White, Blánaid Regan, Fiona Nolan, Martin McHugh, Brendan Bersuder, Philippe Bolam, Thi Robinson, Craig D. Fones, Gary R. Zhang, Hao Schintu, Marco Montero, Natalia Marras, Barbara AS 1:1;2:2;3:1;4:;5:3;6:3;7:3;8:3;9:4;10:4;11:5;12:6;13:7;14:8;15:9;16:9;17:9;18:10;19:11;20:11;21:12;22:13;23:14;24:15;25:15;26:15; FF 1:;2:;3:;4:;5:;6:;7:;8:;9:;10:;11:PDG-ODE-LITTORAL-LERPAC;12:PDG-RBE-CCEM;13:PDG-ODE-LITTORAL-LERPC;14:PDG-ODE-LITTORAL-LERN;15:;16:;17:;18:;19:;20:;21:;22:;23:;24:;25:;26:; C1 IPMA, Portuguese Institute of Sea and Atmosphere, Rua Alfredo Magalhães Ramalho, 6, 1495-165 Lisbon, Portugal Centro de Química Estrutural, Institute of Molecular Sciences, Instituto Superior Técnico, Av. Rovisco Pais, 1049-001 Lisbon, Portugal AZTI, Marine Research, Basque Research and Technology Alliance (BRTA), Herrera Kaia, Portualdea z/g, 20110 Pasaia, Gipuzkoa, Spain ITC, Instituto Tecnológico de Canarias, Playa de Pozo Izquierdo, s/n., CP: 35119, Sta. Lucía, Las Palmas, Spain Ifremer, LITTORAL unit, Provence-Azur-Corse environmental resources laboratory Zone Portuaire de Brégaillon, CS20330 83507 La Seyne/mer cedex, France Ifremer, Unit of Biogeochemistry and Ecotoxicology, Chemical Risk assessment, Rue de l'Ile d'Yeu, 44300 Nantes, France Ifremer, LITTORAL unit, Laboratoire Environnement Ressources des Pertuis Charentais, Avenue de Mus de Loup, 17390 La Tremblade, France Ifremer, LITTORAL unit, Laboratoire Environnement Ressources de Normandie, Avenue du Général de Gaulle, 14520 Port-en-Bessin, France DCU Water Institute, Dublin City University, Dublin 9, Ireland Marine Institute, Rinville, Oranmore, Galway, Ireland CEFAS, Centre for Environment, Fisheries and Aquaculture Science, Lowestoft Laboratory, Pakefield Road, Lowestoft, Suffolk NR33 0HT, United Kingdom MSS, Marine Scotland Science, Marine Laboratory, 365 Victoria Road, Aberdeen AB11 9DB, United Kingdom University of Portsmouth, School of the Environment Geography and Geosciences, Burnaby Road, Portsmouth PO1 3QL, United Kingdom Lancaster University, Lancaster Environment Centre, Lancaster LA1 4YQ, United Kingdom UNICA, Dipartimento di Scienze Mediche e Sanità Pubblica, Università degli studi di Cagliari, 09124 Cagliari, Italy C2 IPMA, PORTUGAL CQE, PORTUGAL AZTI, SPAIN ITC, SPAIN IFREMER, FRANCE IFREMER, FRANCE IFREMER, FRANCE IFREMER, FRANCE UNIV DUBLIN CITY, IRELAND MARINE INST GALWAY, IRELAND CEFAS, UK MSS, UK UNIV PORTSMOUTH, UK UNIV LANCASTER, UK UNIV CAGLIARI, ITALY SI TOULON NANTES LA TREMBLADE PORT-EN-BESSIN SE PDG-ODE-LITTORAL-LERPAC PDG-RBE-CCEM PDG-ODE-LITTORAL-LERPC PDG-ODE-LITTORAL-LERN IN WOS Ifremer UPR copubli-europe IF 5.8 TC 6 UR https://archimer.ifremer.fr/doc/00769/88088/93645.pdf https://archimer.ifremer.fr/doc/00769/88088/93646.docx https://archimer.ifremer.fr/doc/00769/88088/93647.xlsx https://archimer.ifremer.fr/doc/00769/88088/93691.pdf LA English DT Article DE ;Priority metals;Broad geographical scale;European coastal and transitional waters;DGT;Voltammetry AB This study investigates the relationships among Ni, Cd and Pb's different chemical forms determined by different methodologies in coastal and transitional waters across a broad geographical scale. Concentrations were measured in spot samples and through passive sampling (DGT). High variability of metal concentrations was found among sampling sites and methodologies due to natural water fluctuations rather than to a given metal or method. Total dissolved metal concentrations in spot samples were lower than the EQS-WFD values. The labile fractions of Cd and Pb, measured in spot samples by Anodic Stripping Voltammetry and by DGT-ICPMS, were highly correlated. Similar labilities were found for Cd, while for Pb, the ASV labile fraction was ≈50% lower. These results reflect the pool of mobile and labile species available towards each technique kinetic window, and they seem not to be affected by discrete sampling flaws. PY 2022 PD JUL SO Marine Pollution Bulletin SN 0025-326X PU Elsevier BV VL 179 UT 000802997300003 DI 10.1016/j.marpolbul.2022.113715 ID 88088 ER EF