Current and Future Perspectives Using Biomarkers to Assess Pollution in Aquatic Ecosystems

José María Monserrat, L. Geracitano, A. Bianchini
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引用次数: 32

Abstract

The possibility of detecting aquatic pollution problems to take corrective decisions is intimately related to the organization levels of the living matter. Measurements at the biochemical or physiological levels detect more quickly and specifically the presence of several toxic compounds, allowing its utilization in a prospective way, until that deleterious effect reaches higher organization levels. The detection of environmental “hot spots” needs general nonspecific biomarkers if no previous information about the presence of specific pollutants exist. Since several xenobiotics can modify directly or indirectly the balance between pro-oxidant and antioxidant concentration, the determination of oxidative stress (DNA damage, protein oxidation, lipid peroxidation) in aquatic species is commonly used as a nonspecific biomarker. On the other hand, acetylcholinesterase activity or determination of metallothionein concentration (or expression) represents specific biomarkers that indicate the presence of anticholinesterasic compounds (organophosphorus pesticides or neurotoxins, for instance) and metals, respectively. The fact that animal populations inhabiting polluted areas can express responses qualitatively and quantitatively different from those of reference areas has lead to the “pollution induced community tolerance” approach that seems to be a valuable tool to compare toxicological responses of different aquatic populations.
利用生物标志物评估水生生态系统污染的现状和未来展望
检测水生污染问题以采取纠正决策的可能性与生物物质的组织水平密切相关。在生化或生理水平上的测量可以更快、更具体地检测到几种有毒化合物的存在,从而允许以一种有预期的方式利用它,直到有害影响达到更高的组织水平。如果之前没有关于特定污染物存在的信息,环境“热点”的检测需要一般的非特异性生物标志物。由于几种外源生物可以直接或间接地改变促氧化剂和抗氧化剂浓度之间的平衡,因此水生物种氧化应激(DNA损伤,蛋白质氧化,脂质过氧化)的测定通常被用作非特异性生物标志物。另一方面,乙酰胆碱酯酶活性或金属硫蛋白浓度(或表达)的测定分别代表了表明抗胆碱酯化合物(例如有机磷农药或神经毒素)和金属存在的特定生物标志物。由于生活在污染地区的动物种群在质量和数量上都不同于参考地区的动物种群,因此“污染诱导的群落容忍”方法似乎是比较不同水生种群毒理学反应的一个有价值的工具。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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