Department of Terrestrial Ecology, National Environmental Research Institute, Aarhus University, Vejlsøvej 25, P.O. Box 314 DK-8600 Silkeborg, Denmark.
Sci Total Environ. 2010 Aug 15;408(18):3860-70. doi: 10.1016/j.scitotenv.2009.11.030. Epub 2009 Dec 16.
This paper illustrates, by a case study, how to apply the conceptual Worst-Case Definition (WCD) model, developed in the methodological paper in the current journal, by Sørensen et al. (2010-this issue). The case is about eco-toxicological risk assessment of pesticides under Danish conditions. Cumulative aspects are included on a conceptual basis as elements of the worst-case conditions. This defines factors that govern the risk assessment, including location in time and space of risk "hotspots". Two pillars of concern drive the conceptual modelling: (1) What to protect (denoted Protected Units (PUs)) and (2) the reason for increased risk level (denoted Causes of Risks (CRs)). Both PUs and CRs are analysed using hierarchical procedures that facilitate a complete listing of concrete factors governing increased risk for adverse effect due to agricultural usage of pesticide. The factors governing pesticide risk are combined in a context that combines the protection of relevant groupings of organisms with the factors for increased risk level for each of these. Identification of the most important relations between defined types of PUs and CRs is illustrated using expert knowledge. Existing databases are used to form spatial distributed risk indicators as estimators for a selection of important relations between PUs and CRs. This paper illustrates how the WCD model can break down the complex issue of uncertainty into fractions that are more open for evaluations. Finally, it shows application of risk indicators in a multi-criterion analysis using respectively self organizing mapping and partial order technique in a comparative analysis that highlights critical aspects of uncertainty, due to the ambiguity between single risk indicator rankings.
本文通过案例研究说明了如何应用概念上的最坏情况定义(WCD)模型,该模型由 Sørensen 等人在当前期刊的方法性论文中提出(2010 年-本期)。该案例涉及丹麦条件下农药的生态毒理学风险评估。累积方面基于概念基础被纳入最坏情况条件的元素中。这定义了控制风险评估的因素,包括风险“热点”的时间和空间位置。两个关注的支柱驱动着概念建模:(1)要保护什么(表示受保护单元(PUs))和(2)风险水平增加的原因(表示风险原因(CRs))。使用分层程序分析 PUs 和 CRs,这有助于全面列出由于农业使用农药而对不利影响增加风险的具体因素。将控制农药风险的因素组合在一个环境中,该环境将保护相关生物群体与每个生物群体的风险增加因素结合在一起。使用专家知识说明了如何识别定义的 PUs 和 CRs 类型之间最重要的关系。利用现有数据库形成空间分布风险指标,作为 PUs 和 CRs 之间重要关系的选择的估计值。本文说明了 WCD 模型如何将复杂的不确定性问题分解为更易于评估的部分。最后,它展示了风险指标在多准则分析中的应用,分别使用自组织映射和偏序技术在比较分析中突出不确定性的关键方面,由于单个风险指标排名之间的模糊性。