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Toxicological Effects of Fluctuating Contaminant Exposures in Relation to Water QualityCriteria and NPDES Permit Limits

机译:与水质有关的污染物暴露波动的毒理学标准和NPDES许可限值

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Water quality criteria for protecting aquatic life are based primarily on laboratory testing thatused constant exposure concentrations. However, actual impacts of toxics vary depending onchemical and flow characteristics of the waterbody and effluent. Typical effluent and nonpointsource exposure concentrations fluctuate in frequency, magnitude, and duration, often resultingin different toxicological impacts than experienced in constant concentration tests. There is acritical need to improve our understanding of the link between exposure and effects in real-worldfluctuating exposure scenarios in order to improve the predictive accuracy of pollutant limitcalculations and enable more appropriate, site-specific permit limits. Tetra Tech has currentlyreviewed over 30 toxicological studies that used either time-dose response or pulsed/intermittentexposure designs representing over 15 contaminants and 10 species. Most of these studies wereconducted using freshwater species and acute exposures. Our analyses of these studies showsthat pulsed or fluctuating exposures are often less toxic than continuous exposures, given thesame peak contaminant concentration, assuming that the contaminant is accumulated internallyby the organism or that damage to the organism is “accumulated” at a faster rate than tissuerepair. Current models for dealing with acute exposures appear to be fairly robust underfluctuating exposures, particularly if kinetic constants are based on normalized time and effectsdata. However, many fast-acting pollutants, that can cause immediate damage to gills and otherorgans, may have under-protective criteria if based on an average concentration over a 2-4 dayexposure. To test this possibility we examined daily ammonia data and multiple chronicCeriodaphnia WET tests for two California wastewater facilities. We observed that peakammonia concentration was related to Ceriodaphnia chronic endpoints, consistent with the fastactingnature of this contaminant. Experimental chronic tests conducted using fathead minnowsand either nitric acid or sodium chloride, also exhibited results consistent with fast-actingsubstances and little lag effect on mortality. In general, effects were observed within 48 hours ofpulse exposure and chronic or sublethal effects were not observed. Our results suggest thatchronic effects of fluctuating exposures of fast-acting contaminants can be predicted based oncurrent acute toxicological models.
机译:保护水生生物的水质标准主要基于使用恒定暴露浓度的实验室测试。但是,有毒物质的实际影响取决于水体和废水的化学和流量特性。典型的废水和非点源暴露浓度在频率,大小和持续时间上会发生波动,通常会产生与恒定浓度测试不同的毒理学影响。迫切需要提高我们对现实世界中波动的暴露场景中暴露与影响之间联系的理解,以提高污染物限值计算的预测准确性并实现更适当的针对特定地点的许可证限值。 Tetra Tech目前已审查了30多项毒理学研究,这些研究使用了时间剂量反应或脉冲/间歇性暴露设计,代表了15种以上的污染物和10种物质。这些研究大多数是使用淡水物种和急性暴露进行的。我们对这些研究的分析表明,在相同的污染物峰值浓度的情况下,假设污染物是由生物体内部积累的,或者以比组织修复更快的速度“积累”对生物的损害,那么脉冲或波动的暴露通常比连续暴露的毒性更小。当前用于处理急性暴露的模型似乎是相当稳定的低波动暴露,尤其是如果动力学常数基于标准化时间和效应数据时。但是,如果基于2-4天的平均暴露浓度,许多速效污染物可能会立即导致腮和其他器官受损,因此可能具有保护不足的标准。为了测试这种可能性,我们检查了每日的氨气数据和两个加利福尼亚废水处理厂的慢性慢性氧化蚤的WET测试。我们观察到,峰值氨浓度与色尾藻慢性终点有关,与这种污染物的速效性质相一致。使用黑头min鱼和硝酸或氯化钠进行的实验性慢性试验也显示出与速效物质一致的结果,并且对死亡率的影响很小。通常,在脉冲暴露后48小时内观察到影响,而未观察到慢性或亚致死作用。我们的结果表明,可以基于当前的急性毒理学模型预测速效污染物的波动暴露的长期影响。

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