首页> 外文期刊>Environmental toxicology and chemistry >DEVELOPMENT OF A SHORT-TERM REPRODUCTIVE ENDOCRINE BIOASSAY USING STEROID HORMONE AND VITELLOGENIN END POINTS IN THE ESTUARINE MUMMICHOG (FUNDULUS HETEROCLITUS)
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DEVELOPMENT OF A SHORT-TERM REPRODUCTIVE ENDOCRINE BIOASSAY USING STEROID HORMONE AND VITELLOGENIN END POINTS IN THE ESTUARINE MUMMICHOG (FUNDULUS HETEROCLITUS)

机译:利用雌性激素(异形性耳鼻喉)中的甾体激素和玻璃体素端点开发短期生殖内分泌生物测定法

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摘要

We have developed a short-term gonadal recrudescence test with the estuarine mummichog (Fundulus heteroclitus) and determined endocrine end points sensitive to a strong estrogen agonist (ethynylestradiol; EE_2) and an antiestrogen (ZM 189,154; ZM) at concentrations of 0 to 1,000 ng/L in three separate experiments. A protocol was developed to ensure a year-round supply of recrudescing fish. A protocol for determining steroid production (testosterone and 11-ketotestosterone [11-KT] in incubated testes tissue and testosterone and 17-estradiol [E_2] in incubated prematurational follicles) was optimized. Recrudescing fish (males, gonadosomatic index = 2%; females = 10%) were exposed to graded doses of EE_2 or ZM for 7 to 15 d using a static daily-renewal protocol. At high EE_2 (>250 ng/L), the effect on males was depression of androgen steroidogenesis and plasma steroid levels. In females, high EE_2 depressed gonadal production and circulating E_2 levels; however, EE_2 concentrations < 100 ng/L caused increased gonadal production and plasma E_2. Low ZM (<100 ng/L) had little effect on male and female fish, while higher concentrations (>250 ng/L) increased E_2 and 11-KT production while decreasing plasma 11-KT and E_2 (1,000 ng/L only). Male and female plasma vitellogenin responded in a concentration-dependent fashion to EE_2 with no effect by ZM. The low observable effect concentrations for the endocrine parameters were 1 ng/L for EE_2 and 250 ng/L for ZM. The bioassay and results encompassing the environmentally relevant exposure range (1-100 ng/L) will be useful for assessing effects of endocrine-active contaminants in estuarine environments.
机译:我们已经开发了一项短期性腺再发试验,使用河口mummichog(异香und)并确定了对强雌激素激动剂(乙炔雌二醇; EE_2)和抗雌激素药(ZM 189,154; ZM)敏感的内分泌终点,其浓度为0至1,000 ng / L在三个独立的实验中。制定了一项协议,以确保全年提供回用鱼。优化了用于确定类固醇生成的方案(孵育的睾丸组织中的睾丸激素和11-酮睾丸酮[11-KT]以及孵育的成熟前卵泡中的睾丸激素和17-雌二醇[E_2])。使用静态每日更新方案,将鱼(雄性,性腺激素指数= 2%;雌性= 10%)暴露于EE_2或ZM分级剂量,持续7到15 d。在高EE_2(> 250 ng / L)时,对雄性的影响是抑制雄激素类固醇生成和血浆类固醇水平。在女性中,高的EE_2抑制了性腺的产生和循环的E_2的水平。但是,EE_2浓度<100 ng / L导致性腺产量增加和血浆E_2升高。低ZM(<100 ng / L)对公鱼和雌鱼几乎没有影响,而更高的浓度(> 250 ng / L)增加E_2和11-KT产量,同时降低血浆11-KT和E_2(仅1,000 ng / L) 。男性和女性血浆卵黄蛋白原素以浓度依赖的方式对EE_2产生反应,而ZM则没有作用。内分泌参数的低可观察到的效应浓度对于EE_2为1 ng / L,对于ZM为250 ng / L。涵盖环境相关暴露范围(1-100 ng / L)的生物测定和结果将有助于评估河口环境中内分泌活性污染物的影响。

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