长期暴露于全氟十三酸的青鳉鱼体内分布和生物富集

研究了将青鳉鱼长期暴露于不同浓度的全氟羧酸类物质全氟十三酸(PFTriDA)后的器官分布和富集系数.结果显示, PFTriDA最高富集在性腺;其次是卵、肝脏;浓度最低的部分是残体.除了性腺之外,该器官分布与野生中华鲟的一致.在相同暴露浓度下,雄鱼体内各器官的PFTriDA的含量高于雌鱼,机理模型计算进一步表明高母子传递系数是造成雌雄差异的可能原因.随着PFTriDA暴露浓度的升高,鱼体内同一器官的生物富集系数(BCF)呈现下降趋势.     

实时定量RT-PCR方法检测雌二醇诱导原代培养青鳉鱼肝细胞的基因表达

利用原代培养的雄性青鳉鱼肝细胞进行了相同雌二醇(E2)浓度(100 nmol·L-1)下的不同时间(2、4、6、8d)和相同暴露时间(4d)下的不同浓度(1、10、100、1000、10000 nmol·L-1)的雌二醇(E2)实验,采用实时定量RT-PCR方法对青鳉鱼VTG-Ⅰ、VTG-Ⅱ、CHG-H、CHG-L和ERα的基因表达进行了研究,结果表明,VTG-Ⅰ、VTG-Ⅱ、CHG-H、CHG-L和ERα的基因表达与E2的暴露浓度呈现很好的剂量-效应关系,且1nmol·L-1E2暴露就能显著诱导肝细胞内VTG-Ⅰ、VTG-Ⅱ、CHG-H、CHG-L和ERα的基因表达.作为生物监测雌激素活性的in vitro方法,实时定量RT-PCR的灵敏度高于其它已经发表的方法.因此,实时定量RT-PCB方法与原代培养青鳉鱼肝细胞相结合的方法在环境雌激素效应的评价上具有很大地应用潜力.     

稀有鮈鲫作为水生模式生物的研究及探讨

我国本土水生生物稀有鮈鲫(Gobiocypris rarus Ye et Fu,1983年)是一种优良的试验用鱼,具备成为模式生物必要条件。本文总结了稀有鮈鲫生物生态学研究情况,分析了稀有鮈鲫在多个应用领域与模式生物斑马鱼、青鳉存在的不足和差距,同时借鉴发达国家推动模式生物的实践经验,提出了针对性建议。     

稀有鮈鲫作为水生模式生物的研究及探讨

我国本土水生生物稀有鮈鲫(Gobiocypris rarus Ye et Fu,1983年)是一种优良的试验用鱼，具备成为模式生物必要条件。本文总结了稀有鮈鲫生物生态学研究情况，分析了稀有鮈鲫在多个应用领域与模式生物斑马鱼、青鳉存在的不足和差距，同时借鉴发达国家推动模式生物的实践经验，提出了针对性建议。     

定量RT-PCR检测雌二醇诱导的青鳉鱼基因表达

采用实时定量RT-PCR(Q-RT-PCR)方法,对暴露60d雌二醇的雄性青鳉鱼肝脏内卵黄蛋白原(VTG)和卵壳前体蛋白(CHG)基因表达进行研究.结果表明,0.1,1.0,10.0,100.0ng/L的雌二醇使肝脏内VTG-I,VTG-II,CHG-L和CHG-H基因表达被显著诱导.其中VTG-I显示出较好的剂量—效应关系,是较为理想的生物标记物基因.在0.1ng/L雌二醇暴露组中,VTG-I和VTG-II的表达量均显著高于对照组(P<0.05),表明本方法具有检测环境中低剂量雌二醇暴露的潜力.     

Toxicity Testing of Leachate from Waste Landfills Using Medaka (Oryzias Latipes) for Monitoring Environmental Safety

To investigate the environmental safety of waste disposal landfill sites and of land reclaimed from such sites, we evaluated the toxicity of leachate from these sites by a combination of bioassays in the Japanese killifish medaka Oryzias latipes. We tested for lethal toxicity in adult and larval medaka and for hatching inhibition of embryos from eggs. As biochemical evidence of the effects of leachate exposure, CYP1A (EROD activity) and vitellogenin (Vtg) were induced. We also bioassayed water-treated leachate and downstream river water. Leachate solution was lethal to larval and adult medaka. Embryo hatchability was inhibited, and abnormal hatching, spinal deformity and anisophthalmia occurred in embryos exposed to leachate solution. CYP1A was induced by exposure to leachate solution diluted to 1.0%, and EROD activity was significantly higher than in control. Vtg and unknown proteins were induced in the sera of male medaka exposed to the diluted leachate solution. Conventional water treatments worked effectively to remove toxic compounds but did not work well to remove element ions, including heavy metals. Treated leachate produced neither lethal toxicity nor hatching abnormalities during the exposure period. Fish toxicity tests for leachate would be useful for monitoring the environmental safety of landfill sites.     

利用日本青鳉早期发育阶段暴露评估排水的急、慢性毒性和内分泌干扰效应

提出一套利用日本青鳉胚胎-幼鱼阶段生长、形态学改变和雌雄比例变化的指标体系评价排水的毒性和内分泌干扰效应的方法.该方法属于活体动物的短期和部分生命阶段暴露测试,整个实验周期为21 d,测试过程不依赖复杂的仪器设备,操作简单、成本低.通过在北京市污水、工业废水及其经过生物处理后的排水进行测试,表明其能够比较准确判断排水中是否存在急性毒性、致畸和内分泌干扰效应物质.将其应用于评价不同深度处理工艺出水毒性效果,结果表明反渗透工艺能够去除大部分毒性物质.     

稀有鮈鲫和日本青鳉肝细胞原代培养及其对2,3,7,8-TCDD的敏感性比较

利用胰酶消化和机械分散相结合的方法对稀有鮈鲫和日本青鳉的肝细胞进行分离和培养,测定了不同培养时间下两种原代培养肝细胞的活力,研究了两种原代培养肝细胞受到2,3,7,8-TCDD暴露后EROD活力变化的时间-和浓度-效应关系.结果表明,稀有鮈鲫和日本青鳉的肝细胞产率分别达到2.0×107cells.g-1和1.5×107cells.g-1,稀有鮈鲫原代肝细胞的活力可以稳定地保持5d,日本青鳉原代肝细胞的活力至少可以稳定地保持1周;不同浓度TCDD暴露后,两种鱼的原代肝细胞EROD活力变化均显示良好的时间-浓度-效应关系,TCDD诱导稀有鮈鲫和日本青鳉原代肝细胞EROD活力的最低可观察效应浓度(LOEC)分别为4pg.mL-1和1pg.mL-1;TCDD诱导日本青鳉原代肝细胞EROD活力的EC50值低于稀有鮈鲫.就原代肝细胞培养操作和对毒物胁迫的敏感性而言,日本青鳉优于稀有鮈鲫.     

Toxicity evaluation of 10 oil gelling agents北大核心CSCD

Oil gelling agents are widely used in emergency response of marine oil spills. However, the biological toxicity of oil gelling agents is not well understood. This research aimed to evaluate the environmental safety of oil gelling agents used for rapid removal and cleanup of marine oil spills. We used luminescent bacteria (Acinetobacter sp. Tox2 and Acinetobacter sp. RecA) combined with exposure experiment using marine medaka (Oryzias melastigma) juveniles to detect the acute toxicity and genotoxicity of 10 oil gelling agents. As a result, a certain level of acute toxicity was detected from the oil gelling agent FOA and GMN-01 (the toxicity equivalent to 0.067 mg/L and 0.084 mg/L of HgCl2, respectively), and a certain level of genotoxicity was detected from the oil gelling agent NORSOREX (the toxicity equivalent to 0.307 mg/L of MMC) by the luminescent bacteria test. However, no obvious acute toxicity or genotoxicity was detected from the above three oil gelling agents in fish-exposure experiments. Our results suggest that the 10 oil gelling agents have no obvious acute toxicity or genotoxicity to higher organisms (including marine medaka). The luminescent bacteria test is more sensitive in detecting biological toxicity of oil gelling agents. This study provides a reference for environmental safety evaluation of the oil gelling agents used in the cleaning up of the marine oil spills.