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Additivity and Interactions in Ecotoxicity of Pollutant Mixtures: Some Patterns, Conclusions, and Open Questions

机译:污染物混合物在生态毒性中的可加性和相互作用:一些模式,结论和未解决的问题

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Understanding the effects of exposure to chemical mixtures is a common goal of pharmacology and ecotoxicology. In risk assessment-oriented ecotoxicology, defining the scope of application of additivity models has received utmost attention in the last 20 years, since they potentially allow one to predict the effect of any chemical mixture relying on individual chemical information only. The gold standard for additivity in ecotoxicology has demonstrated to be Loewe additivity which originated the so-called Concentration Addition (CA) additivity model. In pharmacology, the search for interactions or deviations from additivity (synergism and antagonism) has similarly captured the attention of researchers over the last 20 years and has resulted in the definition and application of the Combination Index (CI) Theorem. CI is based on Loewe additivity, but focused on the identification and quantification of synergism and antagonism. Despite additive models demonstrating a surprisingly good predictive power in chemical mixture risk assessment, concerns still exist due to the occurrence of unpredictable synergism or antagonism in certain experimental situations. In the present work, we summarize the parallel history of development of CA, IA, and CI models. We also summarize the applicability of these concepts in ecotoxicology and how their information may be integrated, as well as the possibility of prediction of synergism. Inside the box, the main question remaining is whether it is worthy to consider departures from additivity in mixture risk assessment and how to predict interactions among certain mixture components. Outside the box, the main question is whether the results observed under the experimental constraints imposed by fractional approaches are a de fide reflection of what it would be expected from chemical mixtures in real world circumstances.
机译:了解接触化学混合物的影响是药理学和生态毒理学的共同目标。在以风险评估为导向的生态毒理学中,定义可加性模型的应用范围在过去20年中受到了最大的关注,因为它们有可能使人们仅依靠单独的化学信息来预测任何化学混合物的效果。生态毒理学中可加性的金标准已证明是Loewe可加性,它是由所谓的浓度加法(CA)可加性模型产生的。在药理学中,寻找可加性或协同作用(协同作用和拮抗作用)的相互作用或偏差在过去20年中同样引起了研究人员的注意,并导致了组合指数(CI)定理的定义和应用。 CI基于Loewe可加性,但专注于协同作用和拮抗作用的鉴定和定量。尽管加性模型在化学混合物风险评估中显示出令人惊讶的良好预测能力,但由于在某些实验情况下会发生不可预测的协同作用或拮抗作用,因此仍然存在担忧。在当前的工作中,我们总结了CA,IA和CI模型开发的并行历史。我们还总结了这些概念在生态毒理学中的适用性,以及如何整合它们的信息,以及预测协同作用的可能性。在方框内,剩下的主要问题是在混合物风险评估中是否值得考虑与可加性的偏离以及如何预测某些混合物成分之间的相互作用。在盒子外面,主要的问题是在分数方法施加的实验约束下观察到的结果是否正确反映了现实世界中化学混合物的预期结果。

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