1. Topic

  How to deal with contributions from outside the city?

2. Introduction

   

The air pollution concentrations in an urban area are the combined result from emissions within the urban area itself, and the air pollution coming from outside. The contribution from outside – the extra-urban contribution – is the result of man-made emissions from near-by activities, from neighbouring cities, as well as the combined effect of emissions from upwind areas sometimes up to several thousand km away. Even contributions from the hemispheric/global scale may be important, which is the case for instance for ozone. Natural pollutants may also be important, such as for particulate matter (e.g. Saharan dust, marine aerosols-"sea spray") and for ozone (influx of stratospheric ozone into the troposphere and boundary layer).

The extra-urban (often called "regional") pollution contribution is particularly important for particulate matter PM (PM2.5, PM10) and for ozone. The high regional PM and ozone is mainly a result of secondary particle formation from precursor gases (for PM: mainly SO2, NOX, NH3 and VOC; for ozone: mainly NOX and VOC). Considerable secondary PM and ozone formation is due to extensive precursor gas emissions in large upwind areas with air flow transport over several hours and more, such as between European regions. During the air transport certain meteorological conditions must prevail, such as strong sunshine for ozone formation, and no precipitation.

Apart from this contribution from secondary formation of pollution, large sources/emitters/industrial areas of primary pollutants (primary PM, NOX, etc.) quite near, but outside the urban area may, when it is upwind, of course contribute significantly to the urban concentrations.

The importance of the extra-urban (regional) contribution is demonstrated in Figure 1. The figure shows statistics from the data in AirBase http://air-climate.eionet.eu.int/databases/airbase.html, the air pollutant data base held by the European Topic Centre for Air Quality and Climate Change (ETC/ACC) for the European Environment Agency (EEA) http://org.eea.eu.int/. AirBase contains data from several hundreds of monitoring stations across Europe, of different types (Rural, Urban, Traffic, etc.). The figure represents data for the year 2000 and shows, for each compound (NO2, PM10, Ozone) the average, and 10th and 90th percentile of concentrations for all of each of the station types (rural, urban, traffic).

Figure 1: Data in AirBase on pollutant concentrations at monitoring stations in Europe, 2000, showing the typical concentrations at rural, urban and traffic stations, annual average and short-term percentiles (LV: limit value; TV: target value; NO2 max19: 19th highest hour in a year; PM10 max36: 36th highest day in a year; Ozone max26: 26th highest daily max 8-hour average)..

Note that the rural, urban background and traffic stations do not in general represent adjacent areas (that is, not for all cities there is a near-by rural station), although in many cases this is true. Still, the large number of stations implies that the figures give a good indication of the average rural, urban and traffic concentrations in Europe.

The information in the figure can be summarised as follows:

For NO2, the average rural background concentrations in Europe are typically 50-60% of the average urban concentrations. For PM10, the rural contribution is about 90%! For ozone, the figure demonstrates the well-known effect that the urban concentrations are typically lower than the rural ones, since ozone is most often reduced due to chemical reaction with NO inside the city, which produces NO2.

In order to work effectively on the air pollution situation in the city, it is thus obviously important for local authorities and air pollution control departments to know how to assess the extra-urban contribution and to consider the possibilities to abate the extra-urban contribution (by contacting/working with regional/national authorities).


3. Discussion

   

How to assess the extra-urban contribution

By monitoring:

Ideally the monitoring network of an urban area should include stations outside the urban area, located such that the influx of air pollution from outside can be determined. Since the extra-urban contribution varies considerably with the season, the monitoring at such stations should be year-round.

The number of extra-urban stations, and their location, obviously depends on the source situation near-by, and the geographical location relative to large-scale regional background, such as whether the high regional background contributions would come predominantly from one or several geographical sectors.

The following considerations would be important regarding extra-urban stations:

· The location(s) must be upwind of the urban area itself, when looking towards the main sector(s) of influx of regional pollution, and outside the populated areas of the city itself;

· If there are major (industrial or urban) source areas nearby, the location of the station(s) should reflect where the major impact from the sources is expected. To determine this, dispersion modelling exercises if often needed. However, if the distance to the source area is more than 10 km, the background station can be located similar as indicated above. If the distance is shorter, and there are industrial stacks, dispersion modelling would be recommended to find the areas of maximum impact from the sources.

· For regional air pollution, compounds to be covered should be NO2, PM and ozone.

· For nearby source areas, relevant compounds from the sources should be covered.

The Guidance to the Annexes of the Exchange of Information Decision give some guidance as to location of so-called "near-city" monitoring stations, Commision Decision 2001/752/EC Guidance report on the Annexes to Decision 97/101/EC (choose the pdf files).

By modelling:

Regional chemistry transport models can be used to help determine the extra-urban contribution to an urban area. Such models, e.g. EMEP http://www.emep.int/index_mscw.html, CHIMERE http://euler.lmd.polytechnique.fr/chimere/ and MATCH http://www.smhi.se/ use grid resolutions from 10 – 100 km and can determine the transport and chemistry of many pollutants. The calculations are based on meteorological input data, usually taken from global or regional models, e.g. ECMWF http://www.ecmwf.int//, HIRLAM http://hirlam.knmi.nl/ and griddled emission data, e.g. EMEP http://webdab.emep.int/. As a result, the quality of the regional model results will be dependent on both these input factors. Such models are complicated to run and not readily accessible for general use, but results from some of these models are available, e.g. EMEP http://www.emep.int/Model_data/model_data.html and CHIMERE http://euler.lmd.polytechnique.fr/chimere/output.200108/index.html.

In-country institutions carrying out regional air pollution modelling could also be contacted when there is a need for modelling of the regional air pollution outside your city.

Regional models can be used directly to estimate extra-urban contributions, but they are also useful when helping to plan the placement of background stations and to access the geographic regions and source sectors responsible for the measured extra-urban contribution.

How to abate the extra-urban contribution

In the case of large-scale regional air pollution affecting the urban area, the abatement of this "source" would be a European responsibility, which is handled by the UN-ECE Conventions on Long-Range Transboundary Air Pollution and by the Commission.

In case of nearby source areas with considerable influence on the urban area under consideration, the "zones" which have been established by each Member State under the EU Air Quality Directives (see e.g. the Topics Terms in the EC Air Quality Directives: What do they mean? and How to do Urban AQ assessments? Overview of structure and methods) should, in principle, already include all nearby emission areas affecting urban areas. They should be regarded as "Air Quality management zones" selected such as to make air pollution abatement in polluted areas as effective and integrated as possible.

4. Recommendation / Conclusion

   

It is clear that the extra-urban air pollution concentrations often give significant and sometimes dominating contributions to the urban air pollution levels. It is very important for local authorities to deal with this contribution, both to assess its importance and variations, and to try to manage it in terms of abatement, then in a broader (national or European) context.

The size and variations in the contribution must be assessed either by monitoring station(s), located such that they can determine the extra-urban contribution, and/or by using modelling techniques.

5. Examples / Further Reading

   

6. Additional Documents / Web Links

   

Airbase contains (2002 data) more than 300 rural SO2 and NO2 stations, and about 160 rural PM10 stations. The stations, their location, and monitoring data can be viewed using the AirView tool: http://air-climate.eionet.eu.int/databases/airview.html

Last Updated


 

25th January 2005

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