FN Archimer Export Format
PT J
TI Chronic dietary exposure to pyrolytic and petrogenic mixtures of PAHs causes physiological disruption in zebrafish - part I: Survival and growth
BT 
AF VIGNET, Caroline
   LE MENACH, Karyn
   MAZURAIS, David
   LUCAS, Julie
   PERRICHON, Prescilla
   LE BIHANIC, Florane
   DEVIER, Marie-Hélène
   LYPHOUT, Laura
   FRERE, Laura
   BEGOUT, Marie-Laure
   ZAMBONINO INFANTE, Jose-Luis
   BUDZINSKI, Helene
   COUSIN, Xavier
AS 1:1;2:2;3:3;4:1,4;5:1;6:2;7:2;8:1,5;9:5;10:5;11:3;12:2;13:1,6;
FF 1:;2:;3:PDG-RBE-PFOM-ARN;4:;5:PDG-RBE-BE;6:;7:;8:PDG-RBE-HGS-LRHLR;9:;10:PDG-RBE-HGS-LRHLR;11:;12:;13:;
C1 IFREMER, Lab Ecotoxicol, F-17137 Lhoumeau, France.
   Univ Bordeaux 1, EPOC, UMR CNRS 5805, F-33405 Talence, France.
   IFREMER, Unit Funct Physiol Marine Organisms, UMR LEMAR 6539, F-29280 Plouzane, France.
   Inst Littoral & Environm, UMR Littoral Environm Soc LIENSs 7266, F-17000 La Rochelle, France.
   IFREMER, Lab Ressources Halieut, F-17137 Lhoumeau, France.
   INRA LPGP, F-35042 Rennes, France.
C2 IFREMER, FRANCE
   UNIV BORDEAUX, FRANCE
   IFREMER, FRANCE
   INST LITTORAL & ENVIRONM, FRANCE
   IFREMER, FRANCE
   INRA, FRANCE
SI BREST
   LA ROCHELLE
SE PDG-RBE-PFOM-ARN
   PDG-DCN
   PDG-RBE-BE
   PDG-RBE-HGS-LRHLR
   UBO
   PDG-RBE-BE-LBEX
IN WOS Ifremer jusqu'en 2018
   copubli-france
   copubli-p187
   copubli-univ-france
IF 2.828
TC 30
UR https://archimer.ifremer.fr/doc/00188/29907/28490.pdf
LA English
DT Article
DE ;Danio rerio;Life cycle;Polycyclic aromatic hydrocarbon;Heavy oil;Light crude oil;Alkylated PAH;Jaw;Digestion
AB The release of polycyclic aromatic hydrocarbons (PAHs) into the environment has increased very substantially over the last decades leading to high concentrations in sediments of contaminated areas. To evaluate the consequences of long-term chronic exposure to PAHs, zebrafish were exposed, from their first meal at 5 days post fertilisation until they became reproducing adults, to diets spiked with three PAH fractions at three environmentally relevant concentrations with the medium concentration being in the range of 4.6–6.7 μg g−1 for total quantified PAHs including the 16 US-EPA indicator PAHs and alkylated derivatives. The fractions used were representative of PAHs of pyrolytic (PY) origin or of two different oils of differing compositions, a heavy fuel (HO) and a light crude oil (LO). Fish growth was inhibited by all PAH fractions and the effects were sex specific: as determined with 9-month-old adults, exposure to the highest PY inhibited growth of females; exposure to the highest HO and LO inhibited growth of males; also, the highest HO dramatically reduced survival. Morphological analysis indicated a disruption of jaw growth in larvae and malformations in adults. Intestinal and pancreatic enzyme activities were abnormal in 2-month-old exposed fish. These effects may contribute to poor growth. Finally, our results indicate that PAH mixtures of different compositions, representative of situations encountered in the wild, can promote lethal and sublethal effects which are likely to be detrimental for fish recruitment.
PY 2014
PD DEC
SO Environmental Science And Pollution Research
SN 0944-1344
PU Springer Heidelberg
VL 21
IS 24
UT 000345314500011
BP 13804
EP 13817
DI 10.1007/s11356-014-2629-x
ID 29907
ER

EF