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Spatially explicit multimedia fate models for pollutants in Europe: State of the art and perspectives

机译:欧洲污染物空间明确的多媒体归类模型:最新技术和观点

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摘要

A review by Hollander et al. (in preparation), discusses the relative potentials, advantages and shortcomings of spatial and non spatial models of chemical fate, highlighting that spatially explicit models may be needed for specific purposes. The present paper reviews the state of the art in spatially explicit chemical fate and transport modeling in Europe. We summarize the three main approaches currently adopted in spatially explicit modeling, namely (1) multiple box models, (2) numerical solutions of simultaneous advection–dispersion equations (ADE) in air, soil and water, and (3) the development of meta-models. As all three approaches experience limitations, we describe in further detail geographic information system (GIS)-based modeling as an alternative approach allowing a simple, yet spatially explicit description of chemical fate.udWe review the input data needed, and the options available for their retrieval at the European scale. We also discuss the importance of, and limitations in model evaluation.udWe observe that the high uncertainty in chemical emissions and physico-chemical behavior in the environment make realistic simulations difficult to obtain. Therefore we envisage a shift in model use from process simulation to hypothesis testing, in which explaining the discrepancies between observed and computed chemical concentrations in the environment takes importance over prediction per se. This shift may take advantage of using simple models in GIS with residual uses of complex models for detailed studies. It also calls for tighter joint interpretation of models and spatially distributed monitoring datasets, and more refined spatial representation of environmental drivers such as landscape and climate variables, and better emission estimates. In summary, we conclude that the problem is not “how to compute” (i.e. emphasis on numerical methods, spatial/temporal discretization, quantitative uncertainty and sensitivity analysis…) but “what to compute” (i.e. emphasis on spatial distribution of emissions, and the depiction of appropriate spatial patterns of environmental drivers).
机译:Hollander等人的评论。 (准备中)讨论了化学命运空间模型和非空间模型的相对潜力,优点和缺点,强调了特定目的可能需要使用空间显式模型。本文回顾了欧洲在空间上明确的化学命运和运输模型方面的最新技术。我们总结了目前在空间显式建模中采用的三种主要方法,即(1)多箱模型,(2)空气,土壤和水中的同时对流扩散方程(ADE)的数值解,以及(3)元的发展-楷模。由于所有这三种方法都存在局限性,因此我们将进一步详细介绍基于地理信息系统(GIS)的建模,这是一种允许对化学成分进行简单但在空间上明确描述的替代方法。 ud我们将审查所需的输入数据以及可用于在欧洲范围内对其进行检索。我们还讨论了模型评估的重要性和局限性。 ud我们注意到,环境中化学排放物和物理化学行为的高度不确定性使得难以获得逼真的模拟。因此,我们设想将模型的使用从过程仿真转换为假设测试,在这种情况下,解释环境中观察到的和计算出的化学浓度之间的差异比预测本身重要。这种转变可能会利用在GIS中使用简单模型的优势,而对复杂模型的剩余使用将用于详细研究。它还要求对模型和空间分布的监测数据集进行更严格的联合解释,要求对环境驱动因素(例如景观和气候变量)进行更精细的空间表示,并要求更好的排放估算。总而言之,我们得出结论,问题不是“如何计算”(即强调数值方法,时空离散化,定量不确定性和敏感性分析……),而是“要计算什么”(即强调排放物的空间分布,以及环境驱动因素的适当空间模式的描述)。

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