Abstract

Many models exist for predicting the atmospheric transport and dispersion of material following its release into the atmosphere. The purpose of these models may be to support air quality assessments and/or to predict the hazard resulting from releases of harmful materials to inform emergency response actions. In either case it is essential that the user understands the level of predictive accuracy that might be expected. However, contrary to expectation, this is not easily determined from published comparisons of model predictions against data from dispersion experiments. The paper presents and reviews the methods adopted and issues involved in comparing the predictive performance of atmospheric transport and dispersion models to experimental data, by reference to a number of experimental data sets and comparison results. It then presents an approach which is designed to make the performance of atmospheric dispersion models more transparent, through clearly defining the basis on which the comparison is made, and comparing the performance of the chosen model to that of a reference model. Such an approach establishes a clear baseline against which the accuracy of models can be evaluated and the performance benefits of more sophisticated approaches quantified. The use of a simple analytic reference model applicable to continuous ground level releases in open terrain and urban areas is shown as a proof-of-principle.

Highlights

  • The need to be able to predict urban air quality, regulate emissions from industrial plants and predict the consequences of unexpected releases of hazardous materials, has led to the development of a large number of atmospheric transport and dispersion (AT&D) models of varying levels of complexity

  • It has led to the development of initiatives, such as harmonisation within atmospheric dispersion modelling for regulatory purposes (HARMO), in order to promote the standardisation and development of AT&D models, and the development of best practice guides and model evaluation protocols, such as that developed under the Cooperation in Science and Technology

  • The range of performance metrics typically used in model evaluations; The limitations inherent in comparisons made against data obtained from field and wind tunnel experiments; How decisions in the evaluation process affect the results

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Summary

Introduction

The need to be able to predict urban air quality, regulate emissions from industrial plants and predict the consequences of unexpected releases of hazardous materials, has led to the development of a large number of atmospheric transport and dispersion (AT&D) models of varying levels of complexity. RANS and The the LES approaches appear innately superior methods, fields, are well known and solutions are less accurate for low wind speed regions [8,9] Britter and both rely on a series of modelling assumptions, commonly including the eddy-viscosity. Both RANS and the LES approaches appear innately superior to Gaussian methods, Hanna [10]. RANS methods may produce reasonable gradient-diffusion hypotheses The limitations of these approximations, even in the simplest flow both rely on a series of modelling assumptions, commonly including the eddy-viscosity and qualitative results for mean flows, their performance may be speed little better than thatBritter of simple fields, are well known and solutions areactual less accurate forapproximations, low wind regions and flow gradient-diffusion hypotheses. Regardless of the AT&D model used it is essential that robust verification and performance evaluation procedures exist that are applicable to both open terrain and complex urban environments to ‘provide assurance of the robustness of predictions and to guide improvements in the modelling techniques’ [15]

Performance Metrics
Data from Field Experiments
The layout the sampler in the Grass
Data from Wind Tunnel Experiments
Conducting a Model Comparison against Experimental Data
Making
11. Comparisons
Findings
Conclusions
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