Abstract

The number of cities, or parts of cities, where air quality has been computed using the PMSS 3D model now appears to be sufficient to allow assessment and understanding of performance. Two fields of application explain the growing number of sites: the first is the long-term air quality assessment required in urban areas for any building or road project. The geometric complexity found in such areas can justify the use of a 3D approach, as opposed to Gaussian ones. However, these studies have constraining rules that can make the modelling challenging: several scenarios are needed (current, future with project, future without project), the long-term impact implies a long physical time period to be computed, and the spatial extension of the domain can be large in order to cover the traffic impact zone of the project. The second type of application is dedicated to services and, essentially, to forecasting. As for impact assessments, the modelling can be challenging here because of the extension of the domain if the target area is a whole city. Forecast also adds the constraint of time, as results are requested early, and the constraint of robustness. The CPU amount needed to meet all these requirements is important. It is therefore crucial to optimize all possible parts of the modelling chain in order to limit cost and delay. The sites presented in the article have been modelled with PMSS for long periods. This allows feedback to be provided on different topics: (a) daily forecasts offer an opportunity to increase the robustness of the modelling chain; (b) quantitative validation at air quality measurement stations; (c) comparison of annual impact based on a whole year, and based on a sampling list of dates selected thanks to a classification process; (d) large calculation domains with widespread pollutant emissions offer a great opportunity to qualitatively check and improve model results on numerous geometrical configurations; (e) CPU time variations between different sites provide valuable information to select the best parametrizations, to predict the cost of the services, and to design the needed hardware for a new site.

Highlights

  • Air quality in cities results from local emissions, but is a complex system that can be described by the following simplifications [1]: the regional-scale contribution which have a uniform impact on the city; the city-scale contribution, including emissions from heating for example, that is uniformly considered within the city or within the different districts of the city according to the spatial resolution of the available emission inventory; and the street-scale contribution, which are related mainly to local traffic emissions, and are highly non-uniform

  • To consider traffic-produced turbulence (TPT) in street canyons, a formulation based on the OSPM model [14] has been added, increasing the turbulent kinetic energy field predicted by PSWIFT in these zones according to vehicles fluxes, speed, and effective area

  • The developed hybrid modelling system (HMS) couples PMSS with the Eulerian chemical transport model (CTM) and FARM [34,35]

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Summary

General Context and Motivations

Air pollution is known to impact health strongly: the World Health Organization estimates today that it kills approximatively 7 million people per year. As air quality observations provide concentration measurements of all the contributions, model validation is not performed with only the street-scale, and with the larger scale contributions that can be named “background contribution”. Modeling provides additional and complementary information to air quality monitoring networks that are limited to a given number of measurement points: exposure maps detailing spatial gradients are one of the added values of modeling. The present article deals with applications where both 3D high resolution and limited CPU time are required, and for which the PMSS modeling system is an applied solution

The PMSS Modeling System
The Different Type of High Resolution Air Quality Modeling Applications
Complex Geometry
Unsteady Meteorology and Unsteady Emissions
Purifying Systems
Numerous Scenarios
Domain Extents
Model Performance without Classification
Results with SOMs Classification
Results
Months
CPU Time Performance and Optimization
CPU Demand Analysis and Estimation
Discussion
Full Text
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