Zurita J L, Repetto G, Jos A, Del Peso A, Salguero M, López-Artíguez M, Olano D, Cameán A
National Institute of Toxicology and Forensic Sciences, Av. Dr Fedriani s/n, 41009 Sevilla, Spain.
Toxicol In Vitro. 2005 Oct;19(7):879-86. doi: 10.1016/j.tiv.2005.06.035. Epub 2005 Aug 10.
In order to investigate the potential ecotoxicity of diethanolamine (DEA), a battery of model systems was developed. DEA is widely used as a chemical intermediate and as a surface-active agent in cosmetic formulations, pharmaceuticals and agricultural products. DEA was studied using ecotoxicological model systems, representing four trophic levels, with several bioindicators evaluated at different exposure time periods. The battery included bioluminescence inhibition of the bacterium Vibrio fischeri, growth inhibition of the alga Chlorella vulgaris and immobilization of the cladoceran Daphnia magna. Cell morphology, total protein content, neutral red uptake, MTS metabolization, lysosomal function, succinate dehydrogenase activity, G6PDH activity, metallothionein levels and EROD activity were studied in the hepatoma fish cell line PLHC-1, derived from Poeciliopsis lucida. The systems most sensitive to DEA were both D. magna and V. fischeri, followed by C. vulgaris and the fish cell line PLHC-1. The most prominent morphological effect observed in PLHC-1 cultures exposed to DEA was the induction of a marked steatosis, followed by death at high concentrations, in some cases by apoptosis. The main biochemical modification was a nearly three-fold increase in metallothionein levels, followed by the stimulations of lysosomal function and succinate dehydrogenase and G6PDH activities. Judging by the EC(50) values in the assay systems, DEA is not expected to produce acute toxic effects in the aquatic biota. However, chronic and synergistic effects with other chemicals cannot be excluded.
为了研究二乙醇胺(DEA)的潜在生态毒性,开发了一系列模型系统。DEA在化妆品配方、药品和农产品中广泛用作化学中间体和表面活性剂。使用代表四个营养级的生态毒理学模型系统对DEA进行了研究,并在不同暴露时间段评估了几种生物指示剂。该系列包括费氏弧菌的生物发光抑制、普通小球藻的生长抑制以及大型溞的固定化。对源自亮体食蚊鱼的肝癌细胞系PLHC-1的细胞形态、总蛋白含量、中性红摄取、MTS代谢、溶酶体功能、琥珀酸脱氢酶活性、G6PDH活性、金属硫蛋白水平和EROD活性进行了研究。对DEA最敏感的系统是大型溞和费氏弧菌,其次是普通小球藻和鱼类细胞系PLHC-1。在暴露于DEA的PLHC-1培养物中观察到的最显著形态学效应是诱导明显的脂肪变性,在高浓度下随后死亡,在某些情况下是通过凋亡。主要的生化改变是金属硫蛋白水平增加近三倍,其次是溶酶体功能以及琥珀酸脱氢酶和G6PDH活性的刺激。根据测定系统中的EC(50)值判断,预计DEA不会对水生生物群产生急性毒性作用。然而,不能排除与其他化学物质的慢性和协同效应。