FN Archimer Export Format PT J TI Microplastics contamination in pearl-farming lagoons of French Polynesia BT AF GARDON, Tony El Rakwe, Maria Paul-Pont, Ika Le Luyer, Jeremy THOMAS, Lena Prado, Enora Boukerma, Kada Cassone, Anne-Laure Quillien, Virgile Soyez, Claude COSTES, Louis Crusot, Margaux Dreanno, Catherine Le Moullac, Gilles Huvet, Arnaud AS 1:1;2:2;3:5;4:1;5:;6:2;7:2;8:5;9:1;10:1;11:1;12:4;13:2;14:1;15:3; FF 1:PDG-RBE-RMPF;2:PDG-REM-RDT-LDCM;3:;4:PDG-RBE-RMPF;5:PDG-REM-RDT-LDCM;6:PDG-REM-RDT-LDCM;7:PDG-REM-RDT-LDCM;8:;9:PDG-RBE-PFOM-LPI;10:PDG-RBE-RMPF;11:PDG-RBE-RMPF;12:;13:PDG-REM-RDT-LDCM;14:PDG-RBE-RMPF;15:PDG-RBE-PFOM-LPI; C1 Ifremer, ILM, IRD, Univ Polynésie française, EIO, F-98719 Taravao, Tahiti, Polynésie française, France Ifremer, Laboratoire Détection, Capteurs et Mesures (LDCM), Centre Bretagne, ZI de la Pointe du Diable, CS 10070, 29280 Plouzané, France Univ Brest, Ifremer, CNRS, IRD, LEMAR, F-29280 Plouzané, France Univ Polynésie française, Ifremer, ILM, IRD, EIO, F-98702 Faa’a, Tahiti, Polynésie française, France Univ Brest, Ifremer, CNRS, IRD, LEMAR, F-29280 Plouzané, France C2 IFREMER, FRANCE IFREMER, FRANCE IFREMER, FRANCE UNIV POLYNESIE FRANCAISE, FRANCE CNRS, FRANCE SI TAHITI BREST SE PDG-RBE-RMPF PDG-REM-RDT-LDCM PDG-RBE-PFOM-LPI UM LEMAR EIO IN WOS Ifremer UPR WOS Ifremer UMR WOS Cotutelle UMR copubli-france copubli-univ-france IF 14.224 TC 21 UR https://archimer.ifremer.fr/doc/00703/81508/85938.pdf https://archimer.ifremer.fr/doc/00703/81508/85940.pdf LA English DT Article DE ;Microplastics pollution;Atolls;Surface water;Water column;Pearl oyster AB Pearl-farming is the second most important source of income in French Polynesia. However, tropical lagoons are fragile ecosystems with regard to anthropogenic pressures like plastic pollution, which threaten marine life and the pearl oyster-related economy. Here, we investigated the spatial distribution of microplastics (MP) and concentrations in surface water (SW), water column (WC) and cultivated pearl oyster (PO) from three pearl-farming atolls with low population and tourism. Microplastics were categorized by their size class, shape, colour and polymer type identified using FTIR spectroscopy. Widespread MP contamination was observed in every study site (SW, 0.2–8.4 MP m–3; WC, 14.0–716.2 MP m–3; PO, 2.1–125.0 MP g–1 dry weight), with high contamination in the WC highlighting the need to study the vertical distribution of MP, especially as this compartment where PO are reared. A large presence of small (< 200 µm) and fragment-shaped (> 70%) MP suggests that they result from the breakdown of larger plastic debris. The most abundant polymer type was polyethylene in SW (34–39%), WC (24–32%), while in PO, polypropylene (14–20%) and polyethylene were more evenly distributed (9–21%). The most common MP identified as black-grey polyethylene and polypropylene matches the polymer and colour of ropes and collectors questioning a pearl-farming origin. PY 2021 PD OCT SO Journal Of Hazardous Materials SN 0304-3894 PU Elsevier BV VL 419 UT 000696623000004 DI 10.1016/j.jhazmat.2021.126396 ID 81508 ER EF