Hinton David E, Kullman Seth W, Hardman Ron C, Volz David C, Chen Pei-Jen, Carney Michael, Bencic David C
Laboratory of Molecular Aquatic Toxicology, Division of Environmental Sciences and Policy, Nicholas School of the Environment and Earth Sciences, Duke University Durham, NC 277-8-0328, USA.
Mar Pollut Bull. 2005;51(8-12):635-48. doi: 10.1016/j.marpolbul.2005.07.020. Epub 2005 Sep 9.
In this age of modern biology, aquatic toxicological research has pursued mechanisms of action of toxicants. This has provided potential tools for ecotoxicologic investigations. However, problems of biocomplexity and issues at higher levels of biological organization remain a challenge. In the 1980s and 1990s and continuing to a lesser extent today, organisms residing in highly contaminated field sites or exposed in the laboratory to calibrated concentrations of individual compounds were carefully analyzed for their responses to priority pollutants. Correlation of biochemical and structural analyses in cultured cells and tissues, as well as the in vivo exposures led to the production and application of biomarkers of exposure and effect and to our awareness of genotoxicity and its chronic manifestations, such as neoplasms, in wild fishes. To gain acceptance of these findings in the greater environmental toxicology community, "validation of the model" versus other, better-established often rodent models, was necessary and became a major focus. Resultant biomarkers were applied to heavily contaminated and reference field sites as part of effects assessment and with investigations following large-scale disasters such as oil spills or industrial accidents. Over the past 15 years, in the laboratory, small aquarium fish models such as medaka (Oryzias latipes), zebrafish (Danio rerio), platyfish (Xiphophorus species), fathead minnow (Pimephales promelas), and sheepshead minnow (Cyprinodon variegatus) were increasingly used establishing mechanisms of toxicants. Today, the same organisms provide reliable information at higher levels of biological organization relevant to ecotoxicology. We review studies resolving mechanisms of toxicity and discuss ways to address biocomplexity, mixtures of contaminants, and the need to relate individual level responses to populations and communities.
在这个现代生物学时代,水生毒理学研究一直在探寻毒物的作用机制。这为生态毒理学研究提供了潜在工具。然而,生物复杂性问题以及生物组织更高层面的问题仍然是一项挑战。在20世纪80年代和90年代,并且在如今仍在较小程度上持续,居住在高度污染现场的生物或在实验室中暴露于校准浓度的单一化合物的生物,被仔细分析其对优先污染物的反应。培养细胞和组织中的生化与结构分析以及体内暴露的相关性,导致了暴露和效应生物标志物的产生与应用,也让我们意识到了野生鱼类中的遗传毒性及其慢性表现,如肿瘤。为了让这些发现在更广泛的环境毒理学界获得认可,与其他更成熟的常被使用的啮齿动物模型相比,“模型的验证”是必要的,并且成为了一个主要焦点。由此产生的生物标志物被应用于重度污染和对照现场,作为效应评估的一部分,并用于诸如石油泄漏或工业事故等大规模灾难后的调查。在过去15年里,在实验室中,诸如青鳉(Oryzias latipes)、斑马鱼(Danio rerio)、剑尾鱼(Xiphophorus species)、黑头软口鲦(Pimephales promelas)和湾口无须鲷(Cyprinodon variegatus)等小型水族箱鱼类模型越来越多地被用于确定毒物的作用机制。如今,同样的生物在与生态毒理学相关的生物组织更高层面上提供了可靠信息。我们回顾了解决毒性机制的研究,并讨论了应对生物复杂性、污染物混合物以及将个体水平反应与种群和群落联系起来的必要性的方法。