首页> 外文期刊>Marine Environmental Research >Semipermeable Membrane Devices Link Site-specific Contaminants To Effects: Part 1 - Induction Of Cyp1a In Rainbow Trout From Contaminants In Prince William Sound, Alaska
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Semipermeable Membrane Devices Link Site-specific Contaminants To Effects: Part 1 - Induction Of Cyp1a In Rainbow Trout From Contaminants In Prince William Sound, Alaska

机译:半透膜设备将特定地点的污染物联系起来:第1部分-从阿拉斯加威廉王子湾的污染物中诱捕虹鳟中的Cyp1a

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Extracts from semi-permeable membrane devices (SPMDs) deployed on beaches in Prince William Sound (PWS), Alaska, were used to evaluate if complex contaminant mixtures from different sources can be distinguished by the resulting cytochrome P450 1A (CYP1A) activity in exposed test animals. Deployment sites included canneries, salmon hatcheries, and beaches where lingering oil remains from discharges during the 1964 earthquake or the 1989 Exxon Valdez oil spill. Other sites were selected at random to evaluate region-wide contaminant inputs or were located in salmon streams to evaluate contaminants carried and released by migrating salmon carcasses following reproduction. Following standard deployments of approximately 28 d, an aliquot of the accumulated contaminants was intraperitoneally injected without cleanup into juvenile rainbow trout (Oncorhynchus mykiss). After 2 d and 7 d, the activity of CYP1A was measured by the ethoxyresorufin-o-deethylase (EROD) assay. Exposure to extracts from the oiled sites and one hatchery site with numerous creosote pilings elicited strong EROD responses, whereas fish exposed to salmon stream extracts elicited weak but significant responses during late summer compared to late spring. Responses from the other sites were not significant, indicating contaminants from these sources are unlikely to cause CYP1A induction in resident biota. Rather than simply assessing extant contaminants, this method evaluates the potency of the different sites for bringing about aryl hydrocarbon receptor responses in resident biota.
机译:在阿拉斯加威廉王子湾(PWS)的海滩上部署的半渗透膜装置(SPMD)的提取物用于评估暴露测试中所得的细胞色素P450 1A(CYP1A)活性是否能区分不同来源的复杂污染物混合物动物。部署地点包括罐头厂,鲑鱼孵化场和海滩,在1964年地震或1989年埃克森·瓦尔迪兹(Exxon Valdez)漏油事件中,排放的石油仍然残留。随机选择其他地点以评估整个区域的污染物输入,或将其放置在鲑鱼流中以评估繁殖后鲑鱼尸体的迁移所携带和释放的污染物。在大约28天的标准部署后,将未清除的等分试样经腹膜内注射到幼体虹鳟鱼(Oncorhynchus mykiss)中。在第2天和第7天后,通过乙氧基间苯二酚-o-脱乙基酶(EROD)测定来测量CYP1A的活性。暴露于涂油部位和一个孵化场的提取物以及大量杂酚油堆引起强烈的EROD响应,而暴露于鲑鱼流提取物的鱼在夏末相比春末引起了微弱但重要的响应。其他位点的反应不显着,表明这些来源的污染物不太可能在生物群落中引起CYP1A诱导。该方法不是简单地评估现有污染物,而是评估不同位点在常驻生物区中引起芳基烃受体响应的能力。

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