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SPECIFYING THE DIMENSIONS OF AQUATIC LIFE BENCHMARK VALUES IN CLEAR COMPLETE JUSTIFIED PROBLEM FORMULATIONS

机译:在清晰完整确定的问题公式中指定水生生命基准值的维数

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摘要

Nations that develop water quality benchmark values have relied primarily on standard data and methods. However, experience with chemicals such as Se, ammonia, and tributyltin has shown that standard methods do not adequately address some taxa, modes of exposure and effects. Development of benchmark values that are protective requires an explicit description of the issues, a problem formulation. In particular, the assessment endpoints and other dimensions should be specified for each chemical so that the necessary data will be obtained and appropriate analyses will be performed. Assessment endpoints specify the entity and attribute to be protected. In addition, the level of protection, including the magnitude of effect and the proportion affected is specified. Magnitude and proportion are included, because they are used to calculate the benchmark concentration. If uncertainty is considered in the benchmark, the proportion of the uncertainty distribution that is protected should be specified. Because effects are related to the duration of exposure and time for recovery, temporal dimensions should be specified. Clearly described exposure metrics are also needed, because the relevant exposure parameter is not always total aqueous concentration. Finally, the benchmark may be applicable to particular geographic or climatological areas, water chemistries, taxa, or habitat types. Considering and justifying all the dimensions is likely to result in protective and more easily communicated benchmarks.
机译:制定水质基准值的国家主要依靠标准数据和方法。但是,有关硒,氨和三丁基锡等化学物质的经验表明,标准方法不能充分解决某些分类,暴露方式和影响。开发具有保护性的基准值需要对问题进行明确的描述,并提出问题。特别是,应为每种化学品规定评估终点和其他尺寸,以便获得必要的数据并进行适当的分析。评估端点指定要保护的实体和属性。此外,还规定了保护级别,包括影响的大小和受影响的比例。包括幅度和比例,因为它们用于计算基准浓度。如果基准中考虑了不确定性,则应指定受保护的不确定性分布的比例。由于影响与暴露时间和恢复时间有关,因此应指定时间范围。还需要明确描述的暴露指标,因为相关的暴露参数并不总是总水浓度。最后,该基准可能适用于特定的地理或气候区域,水化学,生物分类或栖息地类型。考虑和证明所有方面的合理性可能会导致保护性基准和更易于传达的基准。

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