...
首页> 外文期刊>Environmental toxicology and chemistry >AQUATIC TOXICITY TESTS WITH SUBSTANCES THAT ARE POORLY SOLUBLE IN WATER AND CONSEQUENCES FOR ENVIRONMENTAL RISK ASSESSMENT
【24h】

AQUATIC TOXICITY TESTS WITH SUBSTANCES THAT ARE POORLY SOLUBLE IN WATER AND CONSEQUENCES FOR ENVIRONMENTAL RISK ASSESSMENT

机译:水溶解性测试,其物质在水中难溶,并且具有环境风险评估的后果

获取原文
获取原文并翻译 | 示例
           

摘要

Aquatic toxicity tests with substances that are poorly soluble in water have been conducted using different methods, and estimates of toxicity have varied accordingly. The present study illustrates differences in toxicity values resulting from variation in test designs and solution preparation methods, and offers guidance on the best way to conduct these tests. Consequences for environmental risk assessment and classification are also discussed. The present study mainly considers active ingredients of plant protection products, but is also considered relevant to other chemicals. It is recommended that toxicity tests be conducted only up to the saturation limit, dispersants avoided, and solvents used only if necessary to support handling and speed of dissolution. Analytical measurements of exposure concentrations should reflect what organisms are exposed to. If acute toxicity testing at the saturation limit yields no adverse effects, further testing should not normally be required; the toxicity value of the endpoints should be considered as the saturation limit and adverse classification should not be required. Chronic testing, if required, should then be conducted at the practical saturation limit as this is the most realistic worst-case exposure scenario. If no adverse effects occur, the risk should be acceptable because higher aqueous exposure cannot occur. This could be substantiated by testing additional species. Assessment factors on no observed effect concentration (NOEC) values at the saturation limit require careful consideration in the risk assessment to avoid unnecessarily low regulatory acceptable concentrations.
机译:已经使用不同的方法对难溶于水的物质进行了水生毒性测试,其毒性估计也相应变化。本研究说明了由于测试设计和溶液制备方法的不同而导致的毒性值的差异,并为进行这些测试的最佳方法提供了指导。还讨论了环境风险评估和分类的后果。本研究主要考虑植物保护产品的活性成分,但也被认为与其他化学品有关。建议仅在不超过饱和极限的条件下进行毒性测试,避免使用分散剂,仅在必要时使用溶剂以支持处理和溶解速度。暴露浓度的分析测量结果应反映出所暴露的生物。如果在饱和极限下进行急性毒性试验不会产生不利影响,则通常不应要求进行进一步试验;端点的毒性值应被视为饱和极限,并且不需要进行不利分类。如果需要,则应在实际的饱和极限下进行长期测试,因为这是最现实的最坏情况下的暴露情况。如果没有不良反应发生,则该风险应该可以接受,因为不会发生更多的水暴露。这可以通过测试其他物种来证实。在饱和度极限时未观察到的影响浓度(NOEC)值的评估因素需要在风险评估中仔细考虑,以避免不必要的低监管可接受浓度。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号