水生生态毒理学生物诊断方法

G. Chuiko, I. Tomilina, Nadezda Vladimirovna Kholmogorova
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引用次数: 3

摘要

介绍。现代生态毒理学对环境和生物体中有毒物质的含量进行检测、定量和定性评估,使用全谱的化学分析方法。然而,生物诊断学的方法是专门针对这门科学的。材料和方法。本文综述了现代生物诊断方法在水生生态毒理学中的应用:生物标记、生物检测和生物适应症。结果。与物理化学分析方法相比,生物诊断学的主要优点是能够识别单个应激因子或其组合作用的生物学后果。同时,生物诊断方法允许确定其联合作用的可加性、拮抗性和协同性。生物标记与其他生物诊断方法的不同之处在于,反应时间从几分钟到几天不等,具有高灵敏度和足够的特异性,因为它能够在低强度因素作用的早期阶段记录生物系统中发生的变化,同时识别压力因素的性质。生物检测的反应时间比生物标记慢(从几小时到几周),但在个体层面上的生态意义更为明显:生物体死亡,繁殖能力下降直至停止繁殖,生长发育中断,各种类型的行为等。生物适应症的特点是超生物系统对应激因子的反应有足够长的延迟,从几周到几年不等。同时,它使更充分和可靠地评估长期以来压力因素作用所发生的变化成为可能,以便预测生态系统进一步发展的备选办法。的局限性。水生生态毒理学中生物诊断方法的使用不受限制。然而,与物理化学分析方法不同,它们不允许对压力因素进行定量的,有时是定性的评估。因此,它们应与定性和定量物理化学分析方法结合使用。结论。因此,生物诊断方法,包括生物标记、生物检测和生物指示,以及物理和化学分析在现代综合系统中评估水体生态状态和人为影响发挥着重要作用。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Methods of biodiagnostics in aquatic ecotoxicology
Introduction. Modern ecotoxicology for the detection, quantitative and qualitative assessment of the content of toxicants in the environment and living organisms uses the entire spectrum of chemical-analytical methods. However, methods of biodiagnostics are specific to this science. Materials and methods. The paper summarizes information on the use of modern methods of biodiagnostics in aquatic ecotoxicology: biomarking, biotesting and bioindication. Results. The main advantage of biodiagnostics over physicochemical methods of analysis is the ability to identify the biological consequences of the action of a single stress factor or their combination. At the same time, biodiagnostic methods allow fixing the additivity, antagonism and synergy of their joint action. Biomarking differs from other biodiagnostic methods in response time from several minutes to several days, high sensitivity and sufficient specificity, since it gives the ability to register the changes occurring in the biological system at the early stages of the action of factors at their low intensity and at the same time identify the nature of the stress factor. Biotesting has a slower response time than biomarking (from several hours to several weeks), but the ecological significance at the level of an individual is more obvious: the death of an organism, a decrease in reproductive ability up to the cessation of reproduction, disruption of growth, development, various types of behavior, etc. Bioindication is characterized by a sufficiently long-time delay of responses of supraorganismal biosystems to the action of a stress factor from several weeks to several years. At the same time, it makes possible assess more adequately and reliably the changes that have occurred over a long period of timeof stress factor action in order to predict options for the further development of ecosystems. Limitations. Methods of biodiagnostics in aquatic ecotoxicology have no restrictions on their use. However, unlike the methods of physicochemical analysis, they do not allow a quantitative, and sometimes a qualitative assessment of the stress factor. Therefore, they should be used in conjunction with the methods of qualitative and quantitative physicochemical analysis. Conclusion. Thus, the biodiagnostic approach, including biomarking, biotesting, and bioindication, together with physics and chemicals analysis plays an important role in the modern integrated system for assessing the ecological state of water bodies and anthropogenic impact on them.
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