Nöth Julia, Michaelis Paul, Schüler Lennart, Scholz Stefan, Krüger Janet, Haake Volker, Busch Wibke
Department of Ecotoxicology, Helmholtz Centre for Environmental Research-UFZ, Permoserstraβe 15, 04318, Leipzig, Germany.
Department of Monitoring and Exploration Technologies, Helmholtz Centre for Environmental Research-UFZ, Permoserstraβe 15, 04318, Leipzig, Germany.
Arch Toxicol. 2025 Apr;99(4):1561-1578. doi: 10.1007/s00204-024-03944-7. Epub 2025 Jan 9.
Testing for developmental toxicity is an integral part of chemical regulations. The applied tests are laborious and costly and require a large number of vertebrate test animals. To reduce animal numbers and associated costs, the zebrafish embryo was proposed as an alternative model. In this study, we investigated the potential of transcriptome analysis in the zebrafish embryo model to support the identification of potential biomarkers for key events in developmental toxicity, using the inhibition of angiogenesis as a proof of principle. Therefore, the effects on the zebrafish transcriptome after exposure to the tyrosine kinase inhibitors, sorafenib (1.3 µM and 2.4 µM) and SU4312 (1 µM, 2 µM, and 5 µM), and the putative vascular disruptor compound rotenone (25 nM and 50 nM) were analyzed. An early (2 hpf-hours post fertilization) and a late (24 hpf) exposure start with a time resolved transcriptome analysis was performed to compare the specificity and sensitivity of the responses with respect to anti-angiogenesis. We also showed that toxicodynamic responses were related to the course of the internal concentrations. To identify differentially expressed genes (DEGs) the time series data were compared by applying generalized additive models (GAMs). We observed mainly unspecific developmental toxicity in the early exposure scenario, while a specific repression of vascular related genes was only partially observed. In contrast, differential expression of vascular-related genes could be identified clearly in the late exposure scenario. Rotenone did not show angiogenesis-specific response on a transcriptomic level, indicating that the observed mild phenotype of angiogenesis inhibition may represent a secondary effect.
发育毒性测试是化学法规的一个组成部分。所应用的测试既费力又昂贵,并且需要大量的脊椎动物实验动物。为了减少动物数量和相关成本,斑马鱼胚胎被提议作为一种替代模型。在本研究中,我们以血管生成抑制作为原理验证,研究了斑马鱼胚胎模型中转录组分析在支持识别发育毒性关键事件潜在生物标志物方面的潜力。因此,分析了暴露于酪氨酸激酶抑制剂索拉非尼(1.3 µM和2.4 µM)、SU4312(1 µM、2 µM和5 µM)以及假定的血管破坏剂化合物鱼藤酮(25 nM和50 nM)后对斑马鱼转录组的影响。进行了早期(受精后2小时)和晚期(受精后24小时)暴露,并进行了时间分辨转录组分析,以比较抗血管生成反应的特异性和敏感性。我们还表明,毒代动力学反应与体内浓度的变化过程有关。为了识别差异表达基因(DEG),通过应用广义相加模型(GAM)对时间序列数据进行了比较。我们在早期暴露情况下主要观察到非特异性发育毒性,而仅部分观察到血管相关基因的特异性抑制。相比之下,在晚期暴露情况下可以清楚地识别出血管相关基因的差异表达。鱼藤酮在转录组水平上未显示出血管生成特异性反应,这表明观察到的血管生成抑制的轻度表型可能是一种次要效应。