首页> 外文期刊>Journal of environmental monitoring: JEM >One-year monitoring survey of organic compounds (PAHs, PCBs, TBT), heavy metals and biomarkers in blue mussels from the Arcachon Bay, France
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One-year monitoring survey of organic compounds (PAHs, PCBs, TBT), heavy metals and biomarkers in blue mussels from the Arcachon Bay, France

机译:为期一年的法国阿卡雄湾蓝贻贝中的有机化合物(PAHs,PCBs,TBT),重金属和生物标志物的监测调查

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Marine mussels Mytilus sp. were transplanted on a monthly basis in cages over one year to oyster farms and harbours in the Arcachon Bay ( France) in order to assess the water quality of the bay. Contaminant levels (organotin compounds, trace metals, PCBs and PAHs) were measured in tissues of transplanted mussels and mussels from a reference station, along with physiological parameters of the mussels ( condition indexes, lipid content and dry weight). Four biomarkers (AChE: acetylcholinesterase activity, GST: gluthathione S-transferase activity, CAT: catalase activity and TBARS: thiobarbituric acid-reactive substance content) were also monitored. The remote stations monitored ( oyster parks) exhibited no accumulation pattern of pollutants. Their respective concentrations therefore constitute a background level of the contamination in the bay ([TBT] = 30 ng Sn g(-1) dw, [SigmaHAPs] = 100 ng g(-1) dw, [SigmaPCBs] = 35 ng g(-1) dw). The elevated chemical contamination of the largest harbour of the bay, the Arcachon harbour, can be interpreted in terms of persistence of organotin compounds ([SigmaOTs] = 1500 - 2000 ng Sn g(-1) dw) and PAHs ([SigmaHAPs] = 4500 - 5000 ng g(-1) dw) in sediments and, to a lesser extent, of direct inputs of copper ([Cu] = 20 mug g(-1) dw in harbours versus 7 in oyster parks) and petrogenic PAHs ([methylphenanthrenes] = 1600 ng g(-1) dw in the dockyard versus 170 at the gas stations), related to the use of copper-based antifouling paints and to dockyard activity, respectively. However, the Arcachon Bay presents a low contamination level by PCBs and metals, including harbour stations. Furthermore, higher levels of other PAHs ( particularly alkyl PAHs such as methylphenanthrenes/1600 ng g(-1) dw) not included in the 16 PAHs from the EPA priority list ( usually studied in biomonitoring programmes/ 1500 ng g(-1) dw) in the Arcachon harbour underline the need to integrate these compounds in biomonitoring of highly PAH-polluted areas such as harbours in order to avoid misinterpretation of the biological responses observed. Biomarker responses were not able to discriminate the different chemical contamination levels recorded in the Arcachon Bay and rather reflected changes in environmental factors. Furthermore, the strong intraspecies variability of biological responses could be due to genetic differences of mussels from the Arcachon Bay. It is the first time that such an integrated monitoring is performed in the Arcachon Bay, also taking into account seasonal variations of chemical contents and biomarkers levels in mussel tissues.
机译:海洋贻贝Mytilus sp。为了评估该海湾的水质,每月将其在网箱中每月移交给法国阿尔卡雄湾的牡蛎养殖场和港口。在已移植贻贝和参考站贻贝的组织中测量了污染物水平(有机锡化合物,痕量金属,PCB和PAHs),以及贻贝的生理参数(条件指标,脂质含量和干重)。还监测了四个生物标志物(AChE:乙酰胆碱酯酶活性,GST:谷硫硫醚S-转移酶活性,CAT:过氧化氢酶活性和TBARS:硫代巴比妥酸反应性物质含量)。所监测的远程站(牡蛎公园)没有显示污染物的积累方式。因此,它们各自的浓度构成海湾中污染物的背景水平([TBT] = 30 ng Sn g(-1)dw,[SigmaHAPs] = 100 ng g(-1)dw,[SigmaPCBs] = 35 ng g( -1)dw)。海湾最大港口阿尔卡雄港的化学污染升高可以用有机锡化合物([SigmaOTs] = 1500-2000 ng Sn g(-1)dw)和PAHs([SigmaHAPs] =沉积物中的铜含量为4500-5000 ng g(-1)dw,在较小程度上,是铜的直接输入([Cu] = 20杯g(-1)dw,港口是牡蛎公园中的7 dg),而成岩的PAHs( [甲基菲]在船坞中为1600 ng g(-1)dw,而在加油站为170 dw),分别与铜基防污漆的使用和船坞的活性有关。但是,阿卡雄湾的多氯联苯和金属(包括港口站)的污染水平较低。此外,EPA优先列表中的16种PAH中未包括的其他PAH含量较高(尤其是烷基PAH,例如甲基菲/ 1600 ng g(-1)dw)(通常在生物监测计划中研究/ 1500 ng g(-1)dw) )在阿卡雄港中强调了将这些化合物整合到PAH高度污染地区(如港口)的生物监测中的必要性,以避免对所观察到的生物反应产生误解。生物标志物的反应无法区分在Arcachon湾中记录的不同化学污染水平,而是反映了环境因素的变化。此外,生物反应的强烈种内变异性可能是由于来自阿卡雄湾的贻贝的遗传差异所致。这是第一次在阿尔卡雄湾进行这种综合监测,同时考虑到贻贝组织中化学成分和生物标志物水平的季节性变化。

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