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Spatial extrapolation modeling approaches

At the regional scale, other means of parameterization are required. A typical example is the evaluation of large-scale non-point source pollution with spatially distributed modeling approaches, which very often rely on the availability of the soil s physico-chemical properties at the scale of each grid of a constructed soil information system. Unfortunately, only limited hard data are available in most soil information systems. Grid scale modeling parameters need to be generated by interpolation, extrapolation, geo-statistics, pedo-transfer functions and the like. Pedotransfer functions will play an important role in this context. [Pg.85]

A central issue for pesticide risk assessment is extrapolation from individual- to population-level effects and from small temporal and spatial scales to larger ones. Empirical methods to tackle these issues are limited. Models are thus the only way to explore the full range of ecological complexities that may be of relevance for ecological risk assessment. However, EMs are not a silver bullet. Transparency is key, and certain challenges exist, for example, translating model output to useful risk measures. To make full use of models and get them established for risk assessment, we need case studies that clearly demonstrate the added value of this approach (Chapter 10). [Pg.31]


See other pages where Spatial extrapolation modeling approaches is mentioned: [Pg.197]    [Pg.511]    [Pg.300]    [Pg.4359]    [Pg.84]    [Pg.767]    [Pg.40]    [Pg.4]    [Pg.101]    [Pg.102]    [Pg.137]    [Pg.197]    [Pg.2376]    [Pg.205]    [Pg.422]    [Pg.373]    [Pg.14]   
See also in sourсe #XX -- [ Pg.243 , Pg.246 ]




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Model approach

Model extrapolations

Spatial approach

Spatial extrapolation

Spatial extrapolation models

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