School of Pharmaceutical Sciences of Ribeirão Preto, University of São Paulo, 14040-903 Ribeirão Preto, São Paulo, Brazil; National Institute of Science and Technology for Detection, Toxicological Evaluation and Removal of Micropollutants and Radioactive Substances (INCT-DATREM), Brazil.
School of Pharmaceutical Sciences of Ribeirão Preto, University of São Paulo, 14040-903 Ribeirão Preto, São Paulo, Brazil; Faculty of Sciences, University of Lisbon, Campo Grande, 1749-016 Lisboa, Portugal.
Sci Total Environ. 2024 Jan 15;908:168062. doi: 10.1016/j.scitotenv.2023.168062. Epub 2023 Oct 24.
Some dyes currently used by the textile, pharmaceutical, food, cosmetic, and photographic industries have been shown to be toxic and/or mutagenic to aquatic life. Most of these dyes resist degradation processes available for treating wastewater, and these processes might generate even more toxic by-products. Despite the large number of available dyes and the large quantity of dyes released into the environment, studies on their toxicity are still scarce. We evaluated and compared the effects in the animal model Danio rerio (zebrafish) of environmentally relevant concentrations of Disperse Red 60 (DR 60), 73 (DR 73), and 78 (DR 78) using the fish embryo acute toxicity (FET) test, morphometric analysis, immunofluorescence imaging, and behavioral parameters. DR 60 caused ocular modifications, while the DR 73 caused non-inflation of the swim bladder (NISB), pericardial edema (PE), scoliosis (S) and abnormal yolk sac (AYS) from at 0.125 mg/L. In behavioral tests, all the dyes induced changes in velocity and time spent swimming of exposed larvae. However, these alterations in behavior seem to be caused by different factors dependent on the dye and its concentration. Nevertheless, behavior seems to add valuable information concerning the hazards analysis of dyes, since it reveals to be the most sensitive group of parameters tested in the current study. In conclusion, of the behavioral and developmental alterations caused by these dyes should be interpreted as an alert for greater attention when registering new dyes and releasing them into the environment. In the particular case of DR 60 the possibility that directly affects the eye of larvae is of great environmental concern, but also from the human health perspective.
一些目前被纺织、制药、食品、化妆品和摄影行业使用的染料已被证明对水生生物具有毒性和/或致突变性。这些染料大多数都难以被废水处理过程中的降解,而且这些过程可能会产生更具毒性的副产品。尽管可用染料种类繁多,且有大量染料被排放到环境中,但对其毒性的研究仍然很少。我们使用鱼类胚胎急性毒性(FET)试验、形态计量分析、免疫荧光成像和行为参数,评估和比较了环境相关浓度的分散红 60(DR 60)、73(DR 73)和 78(DR 78)对动物模型斑马鱼的影响。DR 60 引起眼部畸形,而 DR 73 在 0.125 mg/L 时引起鳔不充气(NISB)、心包水肿(PE)、脊柱侧凸(S)和卵黄囊异常(AYS)。在行为测试中,所有染料都引起暴露幼虫的速度和游泳时间发生变化。然而,这些行为的改变似乎是由染料及其浓度依赖的不同因素引起的。然而,行为似乎提供了有关染料危害分析的有价值信息,因为它在当前研究中被证明是最敏感的参数组。总之,这些染料引起的行为和发育改变应被视为在登记新染料并将其释放到环境中时应更加关注的警报。在 DR 60 的特殊情况下,它直接影响幼虫眼睛的可能性引起了极大的环境关注,同时也引起了人类健康的关注。