Department of Biomedical Sciences and Veterinary Public Health, Swedish University of Agricultural Sciences, Uppsala, Sweden.
Aquat Toxicol. 2013 Jan 15;126:30-41. doi: 10.1016/j.aquatox.2012.10.008. Epub 2012 Oct 22.
Extensive use of veterinary pharmaceuticals may result in contamination of water bodies adjacent to pasture land or areas where animal manure has been applied. In order to evaluate the potential risk to fish embryos 15 veterinary pharmaceuticals were investigated by use of an extended zebrafish embryo toxicity test. Chemical analysis of the exposure medium was performed by solid phase extraction-liquid chromatography-tandem mass spectrometry (SPE-LC-MS/MS) for 11 of the compounds and potential metabolism by the embryos was studied for albendazole, febantel, fenbendazole and oxfendazole. Newly fertilized zebrafish eggs were exposed under static conditions in 96-well plates for 6 days to the pharmaceuticals: 5 antibacterials and 10 antiparasitics. Endpoints including mortality, malformations and other sublethal responses were recorded at 24, 48 and 144 h post fertilization (hpf). The pharmaceuticals causing the highest toxicity were antiparasitics whereas the tested antibacterials, danofloxacin, enrofloxacin, tylosine, trimethoprim and oxytetracyclin had a much lower toxic potency in zebrafish embryos. Most toxic were fenbendazole, albendazole and flumethrin with no observed effect concentrations (NOECs) around 0.02 mg/L. The overall NOEC was determined by lethality for the following pharmaceuticals: albendazole, fenbendazole and oxfendazole. Sublethal endpoints, including malformations, side-laying embryos, tremors, reduced movements and altered heart rate increased the sensitivity of the tests and determined the overall NOECs for febantel, doramectin, ivermectin, flumethrin and toltrazuril. Exposure to doramectin and ivermectin caused a decrease in movements at 24 hpf and a decrease in heart rate at 48 hpf. Flumethrin exposure resulted in decreased time to hatching, except at the highest concentrations, and caused an increase in heart rate at 48 hpf. In contrast, toltrazuril caused an increased time to hatching and a decrease in heart rate. Chemical analysis of the exposure medium after the tests revealed great differences between nominal and measured concentrations, emphasizing the need of including analysis of the actual exposure concentrations. The results indicated that metabolism of albendazole into its sulfoxide protected the embryos from toxicity. Albendazole was metabolized efficiently into albendazole sulfoxide at lower exposure concentrations, resulting in reduced toxicity. At higher concentrations, an increasing proportion of albendazole remained unmetabolized and embryo mortality occurred. Metabolism by the embryos of febantel into fenbendazole and oxfendazole and of fenbendazole into oxfendazole was demonstrated. It is suggested that the toxic effect of febantel in zebrafish embryos is due to metabolism into fenbendazole.
大量使用兽医药品可能导致邻近牧场或施用动物粪便的水体受到污染。为了评估对鱼类胚胎的潜在风险,使用扩展的斑马鱼胚胎毒性测试对 15 种兽医药品进行了研究。通过固相萃取-液相色谱-串联质谱法(SPE-LC-MS/MS)对 11 种化合物进行了暴露介质的化学分析,并研究了 albendazole、febantel、fenbendazole 和 oxfendazole 在胚胎中的潜在代谢情况。将新受精的斑马鱼卵在 96 孔板中以静态条件暴露 6 天,接受以下药物的处理:5 种抗菌药物和 10 种抗寄生虫药物。在受精后 24、48 和 144 小时(hpf)记录死亡率、畸形和其他亚致死反应等终点。引起最高毒性的药物是抗寄生虫药物,而测试的抗菌药物,danofloxacin、enrofloxacin、tylosin、trimethoprim 和 oxytetracyclin 在斑马鱼胚胎中的毒性要低得多。fenbendazole、albendazole 和 flumethrin 的毒性最大,未观察到效应浓度(NOEC)约为 0.02mg/L。通过致死性确定了 albendazole、fenbendazole 和 oxfendazole 的总体 NOEC。包括畸形、侧躺胚胎、震颤、运动减少和心率改变在内的亚致死终点增加了测试的灵敏度,并确定了 febantel、doramectin、ivermectin、flumethrin 和 toltrazuril 的总体 NOEC。暴露于 doramectin 和 ivermectin 会在 24 hpf 时降低运动,在 48 hpf 时降低心率。flumethrin 暴露会导致孵化时间缩短,除了在最高浓度下,并且会在 48 hpf 时增加心率。相比之下,toltrazuril 会导致孵化时间延长和心率降低。测试后对暴露介质进行的化学分析显示,名义浓度和实测浓度之间存在很大差异,这强调了需要包括实际暴露浓度的分析。结果表明,albendazole 代谢为其亚砜可保护胚胎免受毒性影响。在较低的暴露浓度下,albendazole 高效代谢为 albendazole 亚砜,从而降低了毒性。在较高的浓度下,未代谢的 albendazole 比例增加,胚胎死亡率增加。证明了 febantel 在胚胎中代谢为 fenbendazole 和 oxfendazole,以及 fenbendazole 代谢为 oxfendazole。这表明 febantel 对斑马鱼胚胎的毒性作用是由于代谢为 fenbendazole 所致。