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Liver antioxidant and plasma immune responses in juvenile golden grey mullet (Liza aurata) exposed to dispersed crude oil

机译:暴露于分散原油的幼年金gray鱼(Liza aurata)的肝脏抗氧化剂和血浆免疫反应

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Dispersants are often used after oil spills. To evaluate the environmental cost of this operation in nearshore habitats, the experimental approach conducted in this study exposed juvenile golden grey mullets (Liza aurata) for 48h to chemically dispersed oil (simulating, in vivo, dispersant application), to dispersant alone in seawater (as an internal control of chemically dispersed oil), to mechanically dispersed oil (simulating, in vivo, natural dispersion), to the water-soluble fraction of oil (simulating, in vivo, an oil slick confinement response technique) and to seawater alone (control condition). Biomarkers such as fluorescence of biliary polycyclic aromatic hydrocarbon (PAH) metabolites, total glutathione liver content, EROD (7-ethoxy-resorufin-O-deethylase) activity, liver antioxidant enzyme activities, liver lipid peroxidation and an innate immune parameter (haemolytic activity of the alternative complement pathway) were measured to assess the toxicity of dispersant application. Significant responses of PAH metabolites and total glutathione content of liver to chemically dispersed oil were found, when compared to water-soluble fraction of oil. As was suggested in other studies, these results highlight that priority must be given to oil slick confinement instead of dispersant application. However, since the same patterns of biomarker responses were observed for both chemically and mechanically dispersed oil, the results also suggest that dispersant application is no more toxic than the natural dispersion occurring in nearshore areas (due to, e.g. waves). The results of this study must, nevertheless, be interpreted cautiously since other components of nearshore habitats must be considered to establish a framework for dispersant use in nearshore areas.
机译:漏油后经常使用分散剂。为了评估在近海生境中进行此操作的环境成本,本研究中进行的实验方法是将幼稚金gray鱼(Liza aurata)暴露于化学分散油中(模拟,体内,分散剂施用)48h,然后单独分散在海水中(作为化学分散油的内部控制),机械分散的油(模拟体内,自然分散),油的水溶性部分(体内模拟浮油限制反应技术)以及仅海水(控制条件)。生物标记物,例如胆汁多环芳烃(PAH)代谢物的荧光,谷胱甘肽总肝含量,EROD(7-乙氧基-resorufin-O-去乙基酶)活性,肝抗氧化酶活性,肝脂质过氧化作用和先天免疫参数(溶血活性测量了替代补体途径)以评估分散剂应用的毒性。与油中的水溶性成分相比,发现PAH代谢产物和肝脏中总谷胱甘肽含量对化学分散油有重要反应。正如其他研究所建议的那样,这些结果表明必须优先考虑浮油的限制而不是分散剂的应用。但是,由于在化学和机械分散的油中都观察到了相同的生物标志物响应模式,因此该结果还表明,分散剂的应用没有比近海区域(由于波浪)产生的天然分散体更具毒性。但是,由于必须考虑近岸生境的其他组成部分以建立在近岸地区使用分散剂的框架,因此必须谨慎地解释本研究的结果。

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