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Passive dosing of triclosan in multi-generation tests with copepods - Stable exposure concentrations and effects at the low µg l-1 range

机译:在使用桡足类的多代测试中被动剂量的三氯生 - 在低μgl -1 范围内稳定的暴露浓度和效应

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摘要

Ecotoxicity testing is a crucial component of chemical risk assessment. Still, due to methodological difficulties related to controlling exposure concentrations over time, data on long-term effects of organic chemicals at low concentrations are limited. The aim of the present study was therefore to test the applicability of passive dosing to maintain stable concentrations of the organochlorine bacteriocide triclosan in the water phase during a 6-week multi-generation population development test with the harpacticoid copepod Nitocra spinipes. Triclosan was loaded into silicone (1000 mg), which was used as passive dosing phase in the exposure vials. The distribution ratio for triclosan between silicone and water (Dsilicone-water ) was 10466 ± 1927. A population development test was conducted at three concentration levels of triclosan that were measured to be 3-5 µg L(-1) , 7-11 µg L(-1) and 16-26 µg L(-1) . Our results demonstrate that passive dosing is applicable for long-term ecotoxicity testing of organic chemicals, including during significant growth of the test organism population. Shifts in the demographic structure of the population during exposure suggest the most severe effects were exerted on juvenile development. Progressively lower development index values in the populations exposed to increasing triclosan concentrations suggest developmental retardation. Our results further stress the need for chronic exposure during ecotoxicity testing in chemical risk assessment as even the most sensitive endpoint was not significant until after 7 days of exposure. This article is protected by copyright. All rights reserved.
机译:生态毒性测试是化学风险评估的关键组成部分。但是,由于与控制随时间变化的暴露浓度有关的方法上的困难,有关低浓度有机化学品长期影响的数据仍然有限。因此,本研究的目的是在用类立足类co足类Ni足类Nitocra菠菜进行为期6周的多代种群发育测试期间,测试被动给药在维持水相中稳定浓度有机氯杀菌剂三氯生的适用性。将三氯生加载到有机硅(1000μg)中,该硅酮用作曝光瓶中的被动加料阶段。三氯生在硅酮和水(Dsilicone-水)之间的分配比率为10466±1927。在三氯生的三个浓度水平(分别为3-5μgL(-1)和7-11μg)下进行了种群发展测试。 L(-1)和16-26μgL(-1)。我们的结果表明,被动剂量适用于有机化学品的长期生态毒性测试,包括在受试生物种群大量增长期间。在接触过程中人口的人口结构变化表明,对青少年发育的影响最为严重。在三氯生浓度增加的人群中,逐渐降低的发展指数值表明发育迟缓。我们的结果进一步强调了在化学风险评估中进行生态毒性测试期间需要长期暴露的原因,因为即使最敏感的终点也要等到暴露7天后才有意义。本文受版权保护。版权所有。

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