中国血吸虫病防治杂志 ›› 2020, Vol. 32 ›› Issue (1): 78-.

• 实验研究 • 上一篇    下一篇

氯硝柳胺对斑马鱼幼鱼甲状腺内分泌系统的影响

朱璧然1*, 李博2   

  1. 1 湖北中医药大学基础医学院(武汉430065); 2 湖北省疾病预防控制中心
  • 出版日期:2020-03-03 发布日期:2020-03-03
  • 作者简介:朱璧然,男,博士,讲师。研究方向:预防医学和环境毒理学
  • 基金资助:
    湖北省卫生健康科研基金 (WJ 2019X006); 湖北省卫生计生科研基金 (WJ2017X010)

Effect of niclosamide on thyroid endocrine system of larval zebrafish

ZHU Bi-Ran1*, LI Bo2   

  1. 1 School of Basic Medical Sciences, Hubei University of Chinese Medicine, Wuhan 430065, China; 2 Hubei Center for Disease Control and Prevention, China
  • Online:2020-03-03 Published:2020-03-03

摘要: 目的 研究灭螺药氯硝柳胺对斑马鱼幼鱼甲状腺内分泌系统的干扰效应。方法 将受精2 h内的斑马鱼胚胎分别暴露于浓度为0、5、10、20、40 μg/L和80 μg/L的氯硝柳胺 120 h,观察不同暴露浓度下斑马鱼胚胎/幼鱼体重、胚胎孵化率、畸形率和存活率等指标;同时检测鱼体内四碘甲状腺原氨酸 (T4) 和三碘甲状腺原氨酸 (T3)水平,并采用荧光定量 PCR法检测与甲状腺激素调节相关的两个重要基因tshβ和ttr表达情况。结果 暴露于不同浓度氯硝柳胺后,各组斑马鱼幼鱼孵化率(F = 0.947, P = 0.924)和体重(F = 1.042, P = 0.409)差异无统计学意义,存活率(F = 9.309, P = 0.005)和畸形率(F = 14.900, P = 0.001)差异有统计学意义;与对照组相比,较高浓度的氯硝柳胺暴露(40 μg/L和80 μg/L)可显著降低斑马鱼幼鱼存活率 (P均 < 0.05),并显著增加斑马鱼幼鱼畸形率 (P均 < 0.05)。 随着氯硝柳胺暴露浓度的增加, 斑马鱼幼鱼体内T4含量增加 (R2 = 0.927, F = 6.858, P = 0.003)、T3含量减少 (R2 = 0.925, F = 8.212, P = 0.001),tshβ基因表达水平上调 (R2 = 0.840, F = 9.032, P = 0.002)、ttr基因表达水平下调 (R2 = 0.952, F = 9.130, P = 0.002)。结论 环境相关浓度的氯硝柳胺暴露可对斑马鱼幼鱼甲状腺内分泌系统造成干扰。

关键词: 氯硝柳胺, 斑马鱼, 环境相关浓度, 甲状腺激素, 发育毒性

Abstract: Objective To examine the effect of niclosamide on thyroid endocrine disruption in larval zebrafish. Methods   Zebrafish embryos (2 hours post?fertilization) were exposed to niclosamide at concentrations of 0, 5, 10, 20, 40 μg/L and 80 μg/L until 120 hours post?fertilization, and the body weight, hatching rate, malformation rate and survival rate of zebrafish embryos/larvae were measured. In addition, the triiodothyronine (T3) and thyroxin (T4) activities were determined in zebrafish, and the expression of tshβ and ttr genes that were associated with the regulation of thyroid hormones was quantified using a quantitative real?time PCR (qPCR) assay. Results Following exposure to niclosamide, there was no concentration?dependent hatching rate (F = 0.947, P = 0.924) or body weight of larval zebrafish (F = 1.042, P = 0.409); however, there were concentration?dependent survival rate (F = 9.309, P = 0.005) and malformation rate (F = 14.900, P = 0.001). As compared to controls, exposure to niclosamide at concentrations of 40 μg/L and 80 μg/L resulted in a significant reduction in the survival rate (both P values < 0.05), and a marked rise in the malformation rate of larval zebrafish (both P values < 0.05). In addition, the T4 activity increased (R2 = 0.927, F = 6.858, P = 0.003) and T3 activity decreased (R2 = 0.925, F = 8.212, P = 0.001) in larval zebrafish with the concentration of niclosamide. qPCR assay determined up?regulation of tshβ gene expression (R2 = 0.840, F = 9.032, P = 0.002) and down?regulation of ttr gene expression (R2 = 0.952, F = 9.130, P = 0.002). Conclusion Niclosamide exposure at environmental related concentrations may cause thyroid endocrine disruption of larval zebrafish.

Key words: Niclosamide, Zebrafish, Environmental related concentration, Thyroid hormone, Developmental toxicity

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