University of Lille Nord de France, France.
Ecotoxicol Environ Saf. 2012 Jun;80:45-53. doi: 10.1016/j.ecoenv.2012.02.010. Epub 2012 Feb 29.
Juvenile turbot were exposed in laboratory conditions to a mixture of chemical contaminants associated with harbour and estuarine sediments for seven and 21 days. Several molecular biomarkers of exposure were then measured in fish liver: two biotransformation parameters [ethoxyresorufin-O-deethylase (EROD) and phase II glutathione S-transferase (GST) activities] and an antioxidant enzyme activity [catalase (CAT)]. Modifications at the histological level were analysed by the measurement of the number and size of melanomacrophage centres (MMCs) and disturbances to the immune function by the measurement of cytokine transforming growth factor-beta (TGF-β) and development of the thymus. The responses of these molecular and immunological biomarkers were correlated with metal and PAH concentrations measured in sediments and with the physiological performance of turbot analysed in a previous study on the same fish (growth rates, condition factor K, RNA:DNA ratio and lipid index). While no difference was found in thymus analysis, some molecular and immunological responses were observed in fish exposed to contaminated sediments. Weak relationships between molecular biomarkers' responses and PAH concentrations were recorded, while their responses were significantly correlated with some metals. MMC and aggregates were weakly related to chemical contaminants whereas some significant correlations were found between TGF-b1 responses and some metal concentrations. However, molecular and immunological biomarkers were weakly related to fish physiological damages since low responses were observed in the condition which led to the lowest growth and condition indices. These data suggest the complexity of cause-effect relationships between exposure to pollutants, metabolisms and health damages. Precautions should be considered in the use of molecular and immunological biomarkers alone in biomonitoring programs. Their complementary use with physiological biomarkers, such as fish growth and condition indices, could improve their utilisation.
在实验室条件下,幼年比目鱼暴露于与港湾和河口沉积物相关的化学污染物混合物中 7 天和 21 天。然后在鱼肝中测量了几种暴露的分子生物标志物:两种生物转化参数[乙氧基异吩恶唑-O-脱乙基酶(EROD)和 II 相谷胱甘肽 S-转移酶(GST)活性]和一种抗氧化酶活性[过氧化氢酶(CAT)]。通过测量黑素巨噬细胞中心(MMC)的数量和大小以及通过测量细胞因子转化生长因子-β(TGF-β)和胸腺发育来分析组织学水平的变化,从而分析免疫功能的干扰。这些分子和免疫生物标志物的反应与沉积物中测量的金属和 PAH 浓度以及在同一批鱼的先前研究中分析的比目鱼的生理性能(生长率、条件系数 K、RNA:DNA 比和脂质指数)相关。虽然在胸腺分析中没有发现差异,但在暴露于污染沉积物的鱼类中观察到一些分子和免疫反应。记录到分子生物标志物反应与 PAH 浓度之间的弱关系,而它们的反应与某些金属显著相关。MMC 和聚集体与化学污染物弱相关,而 TGF-b1 反应与某些金属浓度之间存在一些显著相关性。然而,分子和免疫生物标志物与鱼类生理损伤的相关性较弱,因为在导致生长和状况指数最低的情况下观察到低反应。这些数据表明,暴露于污染物、新陈代谢和健康损害之间的因果关系非常复杂。在生物监测计划中单独使用分子和免疫生物标志物时应谨慎考虑。它们与生理生物标志物(如鱼类生长和状况指数)的互补使用可以提高它们的利用效率。