Uptake, tissue distribution and accumulation of microcystin-RR in Corydoras paleatus, Jenynsia multidentata and Odontesthes bonariensis -: A field and laboratory study

被引:165
作者
Cazenave, J
Wunderlin, DA
Bistoni, MDL
Amé, MV
Krause, E
Pflugmacher, S
Wiegand, C
机构
[1] Leibniz Inst Freshwater Ecol & Inland Fisheries, D-12857 Berlin, Germany
[2] Humboldt Univ, Dept Biol, D-10099 Berlin, Germany
[3] Univ Nacl Cordoba, Fac Ciencias Exactas Fis & Nat, Catedra Div Anim 2, RA-5000 Cordoba, Argentina
[4] Univ Nacl Cordoba, CONICET, Fac Ciencias Quim, Dto Bioquim Clin,CIBICI, RA-5000 Cordoba, Argentina
[5] Inst Mol Pharmacol, D-13125 Berlin, Germany
关键词
cyanotoxin; fish; distribution; brain;
D O I
10.1016/j.aquatox.2005.08.002
中图分类号
Q17 [水生生物学];
学科分类号
071004 ;
摘要
The uptake and accumulation of microcystin-RR (MC-RR) in fish was investigated under laboratory conditions and in wild fish. Jenynsia multidentata and Corydoras paleatus were exposed for 24 h to 50 mu g/L MC-RR dissolved in water. After exposure, liver, gill, brain, intestine, gall bladder, blood and muscle were analyzed for MC-RR by HPLC and analysis confirmed by LC-ESI-TOF-MS spectrometry. Furthermore, wild individuals of Odontesthes bonariensis were sampled from the eutrophic, cyanobacteria-containing San Roque reservoir, and analyzed for the presence of MC-RR in liver, gill, intestine, and muscle. MC-RR was found in liver, gills, and muscle of all exposed and wild fish, while in C. paleatus MC-RR was also present in the intestine. Moreover, we found presence of MC-RR in brain of J multidentata. Results indicate that MC-RR uptake might occur at two different organs: intestine and gills, through either feeding (including drinking) or respiratory activities. This suggests that MC-RR is taken into the blood stream after absorption, and distributed to different tissues. The liver showed the major bioaccumulation of MC-RR in both experimentally exposed and wild individuals, with muscle of wild fish showing relative high amounts of this toxin in comparison with those exposed in the laboratory; though MC-RR was present in muscle of fish exposed for 24 h. The amount of MC-RR in muscle of O. bonariensis exceeded the value suggested by WHO to be safe, thus causing a health risk to persons consuming fish as a result of chronic exposure to microcystin. Gills also showed bioaccumulation of MC-RR, raising questions on the mechanism involved in the possible uptake of MC-RR through gills as well as on its accumulation in this organ. Although MC-LR has been reported in brain of fish, this is the first report confirming the presence of MC-RR in this organ, which means that both toxins are able to cross the blood-brain barrier. These findings also raise questions on the probable neurotoxicity of microcystins. (c) 2005 Elsevier B.V. All rights reserved.
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页码:178 / 190
页数:13
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