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首页> 外文期刊>The Science of the Total Environment >Assessing the acute and chronic toxicity of exposure to naturally occurring oil sands deposits to aquatic organisms using Daphnia magna
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Assessing the acute and chronic toxicity of exposure to naturally occurring oil sands deposits to aquatic organisms using Daphnia magna

机译:利用Daphnia Magna评估暴露于天然存在的油砂对水生生物的急性和慢性毒性

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In the Athabasca region, the oil sands are located at or near the surface making open-pit mining viable. In addition, the Athabasca River and its tributaries flow through these oil sands deposits, thereby receiving bitumen-associated contaminants through natural fluvial erosional and weathering processes. A key knowledge gap has been related to understanding both the magnitude and significance of the toxicological and ecological effects on aquatic organisms exposed to naturally occurring bitumen entering fluvial systems. Using the Daphnia magna model system, this study assessed the ecotoxicological effects of exposure to bitumen-elutriate treatments that simulated the early stages of fluvial/erosional exposure conditions. No significant among-site differences were observed in the survival of D. magna after 48 h exposure to elutriates produced from a 24 h extraction cycle, and chemical analysis indicated low concentration of a complex mixture of hydrocarbon and metal contaminants. In contrast, the same elutriates impaired reproduction and growth after a 21-day chronic exposure. F1 neonates from the chronic tests were tested for sensitivity to the reference substance potassium dichromate, revealing a decrease in their sensitivity. Inter-generational effects were also observed, with a significant decrease in subsequent neonate production, when daphnids were moved to a clean medium. Supplemental acute toxicity assays using 48 and 72 h bitumen extraction cycles progressively increased daphnid mortality after a 48-h exposure to the respective elutriates. This indicates that bitumen-associated contaminants are being liberated after initial input and fluvial washing (24 h), highlighting the need for future work to assess toxicity responses and associated elutriate water chemistry of a longer fluvial exposure time-series. This work contributes to our understanding of the possible effects of natural bitumen exposure on riverine aquatic ecosystems, providing new information to inform the delineation of baseline conditions to assess environmental change and the design of future regional effects-based monitoring programs.
机译:在Athabasca地区,石油砂位于表面上或附近的露天坑开采可行。此外,Athabasca河及其支流通过这些油砂沉积物流过,从而通过天然河流侵蚀和风化过程接受沥青相关污染物。关键知识差距与理解毒理学和生态效应对暴露于自然发生的沥青进入河流系统的水生生物的幅度和意义。本研究评估了Daphnia Magna模型系统,评估了暴露于沥青露出治疗的生态毒理学作用,这些处理模拟氟尿/侵蚀暴露条件的早期阶段。在48小时内暴露于24小时提取循环产生的浇口后,在D. Magna的存活中没有显着差异。化学分析表明低浓度的烃和金属污染物混合物。相比之下,在21天的慢性暴露后,相同的淡种血液繁殖和生长受损。从慢性试验中进行F1新生儿进行敏感性对参考物质二聚值钾,揭示其敏感性降低。当Daphnids移动到清洁介质时,随后的新生儿生产也显着降低了代际效果。使用48和72h沥青提取循环的补充急性毒性测定在48小时暴露于相应的露天度后逐渐增加了Daphnid死亡率。这表明在初始输入和河流洗涤(24小时)后被释放出沥青相关污染物,突出了未来工作的需要评估毒性反应和相关的液体暴露时间系列的禁区水化学。这项工作有助于我们了解天然沥青暴露对河流水生生态系统可能的影响,提供新信息,以告知划分基线条件,以评估环境变化和基于区域效应的监测计划的设计。

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