Brinke Alexandra, Buchinger Sebastian
Division of Biochemistry and Ecotoxicology, Federal Institute of Hydrology (BfG), Koblenz, 56068, Germany.
Adv Biochem Eng Biotechnol. 2017;157:159-186. doi: 10.1007/10_2016_15.
This chapter reviews the current knowledge and recent progress in the field of environmental, aquatic ecotoxicogenomics with a focus on transcriptomic methods. In ecotoxicogenomics the omics technologies are applied for the detection and assessment of adverse effects in the environment, and thus are to be distinguished from omics used in human toxicology [Snape et al., Aquat Toxicol 67:143-154, 2004]. Transcriptomic methods in ecotoxicology are applied to gain a mechanistic understanding of toxic effects on organisms or populations, and thus aim to bridge the gap between cause and effect. A worthwhile effect-based interpretation of stressor induced changes on the transcriptome is based on the principle of phenotypic-anchoring [Paules, Environ Health Perspect 111:A338-A339, 2003]. Thereby, changes on the transcriptomic level can only be identified as effects if they are clearly linked to a specific stressor-induced effect on the macroscopic level. By integrating those macroscopic and transcriptomic effects, conclusions on the effect-inducing type of the stressor can be drawn. Stressor-specific effects on the transcriptomic level can be identified as stressor-specific induced pathways, transcriptomic patterns, or stressors-specific genetic biomarkers. In this chapter, examples of the combined application of macroscopic and transcriptional effects for the identification of environmental stressors, such as aquatic pollutants, are given and discussed. By means of these examples, challenges on the way to a standardized application of transcriptomics in ecotoxicology are discussed. This is also done against the background of the application of transcriptomic methods in environmental regulation such as the EU regulation Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH).
本章回顾了环境水生生态毒理基因组学领域的现有知识和最新进展,重点是转录组学方法。在生态毒理基因组学中,组学技术用于检测和评估环境中的不良影响,因此与人类毒理学中使用的组学有所区别[Snape等人,《水生毒理学》67:143 - 154,2004年]。生态毒理学中的转录组学方法用于深入了解对生物体或种群的毒性作用机制,从而旨在弥合因果关系之间的差距。基于表型锚定原则[Paules,《环境健康展望》111:A338 - A339,2003年],对应激源诱导的转录组变化进行基于效应的有价值解释。因此,只有当转录组水平的变化与宏观水平上特定应激源诱导的效应明确相关时,才能将其识别为效应。通过整合这些宏观和转录组效应,可以得出关于应激源效应诱导类型的结论。应激源对转录组水平的特异性效应可被识别为应激源特异性诱导途径、转录组模式或应激源特异性遗传生物标志物。本章给出并讨论了宏观效应与转录效应联合应用以识别环境应激源(如水生污染物)的实例。借助这些实例,讨论了转录组学在生态毒理学中标准化应用道路上的挑战。这也是在转录组学方法应用于环境法规(如欧盟化学品注册、评估、授权和限制法规(REACH))的背景下进行的。