A contribution to subprojects SATURN and GENEMIS
Clemens Mensink and Ina De Vlieger
VITO, Boeretang 200, B-2400 Mol, Belgium
1. Summary
An urban emission inventory (SO2, NOx, VOC and
HM) for the Antwerp area (Fig. 1) has been developed, which includes industrial
sources, road transport and space heating. The spatial resolution is determined
by a national emission inventory, as provided by the Flemish Environmental
Agency (VMM, 1997), containing yearly averaged emission data for point
sources, line sources, (motorways and national main roads) and 1 x 1 km²
area sources for space heating and urban road transport. The temporal emission
variations are modelled using temporal emission factors as based on various
sources of emission measurements and national statistics (eg. traffic counts
and several years of degree-days measured at different locations).
Much attention is paid to road transport emissions. They are derived by a "bottom-up" approach using chassis dynamometer tests and VITO’s on-the-road traffic emission measurements in combination with an urban traffic flow model, which is actually used by the Antwerp City authorities and includes statistics on traffic numbers and vehicle types for a network of almost 2000 road segments. The emission factors are partially derived from the on-the-road traffic emission measurements carried out for gasoline passenger cars with a closed-loop controlled three-way-catalyst (TWC) and for a carburetted non-catalyst car (De Vlieger, 1997). The emission factors for other vehicle types were derived from the joint EMEP/CORINAIR Atmospheric Emission Inventory Guidebook (Mc Innes, 1996), following the COPERT-II methodology.
Fig. 1 The urban area of Antwerp
2. Aim of the research
The urbanised triangle Antwerp-Brussels-Gent is located in Northwest Europe and can be characterised by open, flat terrain conditions. There is a dense Automatic Measurement Network to monitor the air quality. Several meteorological towers are part of the network. The use of satellite remote sensing data for this triangle will complement the data from the existing monitoring stations and will induce geographical consistency in information. For the assessment of the air quality in this triangle, the objectives are:
A methodology will be developed for the estimation of atmospheric stability based on (satellite) remote sensing and on an operational basis. Satellite derived data and continuous meteorological tower-based measurements (for calibration) are integrated in an operational scheme for the determination of atmospheric stability. The scheme will be demonstrated.
The road transport emissions of the emission inventory will be estimated with VITO’s on-the-road emission and energy measurement system in combination with national statistics on traffic numbers and vehicle types. For industrial sources and space heating a top-down approach based on a harmonised methodology will be followed.
Modelling tools will be refined to analyse source-receptor relationships and temporal variations in urban air quality. The models will also be used to control the quality of the data sets (emissions, meteorology and immissions) that will be made available for model evaluation.
3. Activities during the year
Specification of data on atmospheric stability
Evaluation of surface heat fluxes and specification of atmospheric stability using remote sensing data. Design of the procedures needed to estimate surface heat flux and atmospheric stability using remote sensing data. Implementation of the procedures and testing the method using an existing NOAA data set. Successful implementation of the methodology and testing with ground-truth data.
Development of an emission inventory for specific urban environments.
Acquisition of VOC emissions; spatial and temporal specification of
road transport emissions in the urban triangle using VITO’s on-the-road
emission and energy measurement system (VOEM) in combination with statistics
on traffic numbers and vehicle types. A detailed emission inventory was
obtained for the Antwerp area (including temporal and spatial distributions)
based on a traffic flow model provided by the City of Antwerp.
4. Principle results
The Emission Inventory for the Antwerp area (Fig. 1) can be characterised by the presence of a relatively large contribution of industrial point sources. In 1996, 72 % of the NOx(NO2) emissions and 94% of the SO2 emissions within the urban area of Antwerp could be allocated to industrial point sources. Since 1993, industrial companies are obliged to report their emission yearly. Based on these registrations and on additional calculations and estimates using statistical data and emission factors from the literature, the Flemish Environmental Agency composes a yearly emission inventory.
For the Antwerp area (20 x 20 km²) 208 point sources were registered
emitting NOx(NO2) and 174 point sources were emitting
SO2 in 1996. Fig. 2 shows the cumulative distribution of the
industrial point source emissions, both for NOx and for SO2.
It can be seen that within the Antwerp area, the largest 15% of the industrial
point sources are responsible for 95% of the industrial SO2
emissions. For the NOx(NO2) emissions, 95% of the
industrial emissions can be allocated to only 30% of the point sources.
Fig. 2 Cumulative distribution of industrial point sources in the Antwerp area
The total amount of SO2 emitted in 1996 within the urban area of Antwerp was 53561 tons, which is almost one third of the total SO2 emissions in Flanders. The largest contribution of the various source categories to the SO2 emissions is coming from industrial point sources (94%). The total amount of NOx(NO2) emitted in 1996 was 26317 tons, which is 15% of the total NOx(NO2) emissions in Flanders. With 72% and 24% respectively, the industrial point sources and traffic provide the largest contributions to the NOx(NO2) emissions in the Antwerp area.
5. Main conclusions
Extension of the methodology to determine surface heat fluxes using satellite remote sensing to a versatile scheme from which atmospheric stability parameters (o.a. Bultynck-Malet) can be derived. Comparisons with data from a meteorological tower (at Mol).
Development of an emission inventory for specific urban environments.
VOC split, detailed modelling of traffic emissions; detailed emission inventories for the Gent and Brussels area. Quality control by comparing the (modelled) inventory results with airborne and ground based measurements.
Mc Innes G. (ed.); Atmospheric emission inventory guide book, A joint EMEP/CORINAIR Production, EEA, Copenhagen (1996) B710/9-11
Vlaamse Milieumaatschappij (VMM); Lozingen in de lucht (Air emission report) 1996-1997, Flemish Environmental Agency, Aalst, (1998) (in Dutch).