Title: Prve
1CITY-DELTA European Modelling Exercise -
calculations with the THOR integrated air
pollution forecast and management system
Ruwim Berkowicz, Jørgen Brandt and Jesper H.
Christensen, National Environmental Research
Institute Department of Atmospheric Environment
2The THOR integrated model system
Global meteorological data from NCEP, USA
Numerical weather forecast model (Eta)
Emission and traffic models
Long range transport model (DEOM)
2000 visualizations and animations of weather
and air pollution, four times a day
Urban background model (UBM)
Street canyon model (OSPM)
Subset to decision makers, web site, the public,
etc.
3CityDelta modelling results are available for
Berlin
London
Copenhagen
4Urban emissions constitute a singularity
compared to regional emissions
5Berlin Emissions
6London Emissions
7Modelling results with 50km grid resolution
cannot reproduce the increased NOX levels within
the urban areas.
8In order to reproduce the increased NOX levels
within the urban areas the resolution of the
emission data must be at least 2km, or better.
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11- Regional scale (European) scale modelling tools
are not suitable for urban scale modelling (?) - regional scale chemical transformations,
depositions are important - urban scale atmospheric dilution of local
emissions is more important than chemical
transformations and deposition
12Urban Background Model (BUM) - High resolution
dispersion modelling but simplified chemistry.
Applied only for the urban area.
13NO2 formation
Formation of the nitrogen dioxide due to
oxidation of NO by ozone is calculated using a
simple chemical model based on assumption of a
photochemical equilibrium on the time scale of
the pollution transport across the city area.
The rate of entrainment of fresh rural ozone is
governed by this time scale.
14Emissions
15Berlin
16Berlin
17London
18London
19Copenhagen - Methods
Traffic
Emissions
Vehicle emission factors
PM10Total traffic related emissions !!- based
on street measurements and OSPM modelling!
20Copenhagen - Methods
Time variation of emissions is defined for 8 day
classes. DC1 - Monday to Thursday DC2 -
Friday DC3 - Saturday DC4 - Sunday DC5 to DC8 the
same as above but for July (summer holidays in
Denmark)
21Results
22Jagtvej, Copenhagen
23Average diurnal variation of NOX, Berlin
Average diurnal variation of PM10, Berlin
24Average diurnal variation of O3, Berlin
25Model performance is better for hours with higher
mixing heights than for hours with limited
vertical dispersion. Prediction of hourly
variation of the mixing height is crucial for
model results.
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33London NOX
34London NO2
35London O3
36London PM10
37London
38Copenhagen
39Copenhagen PM10
Measured urban backgroundMay -June 2002
Modelled urban background1999
40Copenhagen NOX
41Copenhagen NO2
42Copenhagen O3
43Copenhagen PM10