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Indicator Assessment
Percentage change in PM2.5 and PM10 emissions 1990-2009 (EEA member countries)
Note: The reported change in primary PM2.5 and PM10 particulate matter for each country, 1990-2009.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution. Where emissions of primary PM10 were not reported by countries, emission estimates have been obtained from the RAINS PM10 model (IIASA).
Emissions of primary particulate matter (PM10) have reduced by 27% across the EEA-32 region between 1990 and 2009 (Figure 1), with significant reductions having occurred within most individual countries. The largest reductions have been reported by Estonia (-65%), Belgium (-60%) and Slovakia (-58%). In contrast emissions have increased in 7 countries since 1990; the greatest increases have been reported in Malta (112%), Finland (580%) and Romania (609%).
The reductions in total emissions of particulate matter between 1990 and 2009 have been mainly due to the introduction or improvement of abatement measures across the energy, road transport, and industry sectors coupled with other developments in industrial sectors such as fuel switching from high-sulphur containing fuels to low-sulphur fuels (which have also contributed to decreased formation of secondary particulate matter in the atmosphere). Emissions of primary PM10 are expected to decrease in the future as vehicle technologies are further improved and stationary fuel combustion emissions are controlled through abatement or use of low sulphur fuels such as natural gas. Despite this, it is expected that within many of the urban areas across the EU, PM10 concentrations will still be well above the EU air quality limit value. Substantial further reductions in emissions will therefore be needed if the limit value set in the EU's Air Quality Directive is to be reached.
There are no specific EU emission targets for primary PM10. However the EU National Emission Ceilings Directive (NECD) and the Gothenburg protocol to the UNECE LRTAP Convention both set ceilings (i.e. limits) for the secondary particulate matter precursors NH3, NOX and SO2 that countries must meet by 2010 [1]. Further details concerning the overall progress toward the 2010 ceilings for these pollutants may be found in the indicator fact sheet CSI 001 Emissions of acidifying substances, with additional details concerning the individual secondary particulate matter precursor pollutants available in the following indicator fact sheets:
[1] The NECD and Gothenburg protocol also set an emission ceiling for non-methane volatile organic compounds (NMVOCs) which contribute to ground-level ozone formation.
Sector contributions of emissions of primary particulate matter and secondary precursors (EEA member countries)
Note: The contribution made by different sectors to emissions of primary PM2.5 and PM10, and to emissions of the secondary particulate matter precursors.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution and the UNFCCC.
Change in PM2.5 emissions for each sector and pollutant 1990-2009 (EEA member countries)
Note: Percentage change in primary PM2.5 particulate matter emissions for each sector and pollutant between 1990 and 2009.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution.
Change in PM10 emissions for each sector and pollutant between 1990 and 2009 (EEA member countries)
Note: Percentage change in primary PM10 particulate matter emissions for each sector and pollutant between 1990 and 2009.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution.
Contribution to total change in PM2.5 emissions for each sector and pollutant between 1990 and 2009 (EEA member countries)
Note: The contribution made by each sector to the total change in primary PM2.5 particulate matter emissions between 1990 and 2009.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution.
Contribution to total change in PM10 emissions for each sector and pollutant between 1990 and 2009 (EEA member countries)
Note: The contribution made by each sector to the total change in primary PM10 particulate matter emission between 1990 and 2009.
Data from 2011 officially reported national total and sectoral emissions to UNECE/EMEP Convention on Long-Range Transboundary Atmospheric Pollution.
The most important sources of primary PM10 emissions in 2009, across the EEA-32 region, were the 'Commercial, institutional and households' (38%), 'Industrial processes' (15%), 'Road transport' (14%) and 'Agriculture' (13%) sectors. The ‘Commercial, institutional and households’ sector includes combustion-related emissions from e.g. heating of residential and commercial properties.
Since 1990, emissions of primary PM10 from most sectors have decreased (Figure 5), with the exception of the 'Other' and 'Agriculture' sectors, in which emissions have risen by (14%) and (6%) respectively.
Since 1990, emissions from the combustion-related sectors 'Energy production and distribution', 'Energy use in industry' and 'Road Transport' have in particular reduced significantly, contributing 37%, 18% and 16% respectively of the total reduction of particulate matter emissions (Figure 7). As described in the main assessment, a combination of factors has contributed to the reduction of both primary PM and secondary particulate matter emissions in these sectors between 1990 and 2009. These include for primary PM:
ktonnes (1000 tonnes)
There are no specific EU emission targets set for primary particulate matter, as with respect to PM emissions, measures are currently focused on controlling emissions of the secondary PM precursors. However, there are several Directives that affect the emissions of primary PM, including the 2008 Air Quality Directive and emission standards for specific mobile and stationary sources for primary PM10 and secondary precursor emissions.
Within the European Union, the National Emission Ceilings Directive (NEC Directive) imposes emission ceilings (or limits) for emissions of the particulate matter precursors pollutants nitrogen oxides, sulphur dioxide and ammonia that harm human health and the environment (the NEC Directive also sets emissions ceilings for a fourth pollutant - non-methane volatile organic compounds).
Other key EU legislation is targeted at reducing emissions of air pollutants from specific sources, for example:
Internationally, the issue of air pollution emissions is also being addressed by the UNECE Convention on Long-range Transboundary Air Pollution (the LRTAP Convention) and its protocols. A key objective of the protocol is to regulate emissions on a regional basis within Europe and to protect eco-systems from transboundary pollution by setting emission reduction ceilings to be reached by 2010 for the same four pollutants as addressed in the NECD (i.e. SO2, NOX, NH3 and NMVOCs). Overall for the EU Member States, the ceilings set within the Gothenburg protocol are generally either slightly less strict or the same as the emission ceilings specified in the NECD.
There are presently no European national ceilings for emissions of particulate matter.
Emissions of the secondary PM precursors SO2, NOX and NH3 are covered by the EU National Emission Ceilings Directive (NECD) (2001/81/EC) and the Gothenburg protocol under the United Nations Convention on Long-Range Transboundary Air Pollution (LRTAP Convention) (UNECE 1999). The NECD generally involves slightly stricter emission reduction targets than the Gothenburg Protocol for EU-15 Member States for 2010.
Table: 2010 Targets under the NEC Directive and the Gothenburg Protocol, in kt
2010 NECD ceilings |
2010 CLRTAP Gothenburg Protocol ceilings |
|||||
NOX |
SOX |
NH3 |
NOX |
SOX |
NH3 |
|
Austria | 103 | 39 | 66 | 107 | 39 | 66 |
Belgium | 176 | 99 | 74 | 181 | 106 | 74 |
Bulgaria | 247 | 836 | 108 | 266 | 856 | 108 |
Cyprus | 23 | 39 | 9 | |||
Czech Republic | 286 | 265 | 80 | 286 | 283 | 101 |
Denmark | 127 | 55 | 69 | 127 | 55 | 69 |
Estonia | 60 | 100 | 29 | |||
Finland | 170 | 110 | 31 | 170 | 116 | 31 |
France | 810 | 375 | 780 | 860 | 400 | 780 |
Germany | 1051 | 520 | 550 | 1081 | 550 | 550 |
Greece | 344 | 523 | 73 | 344 | 546 | 73 |
Hungary | 198 | 500 | 90 | 198 | 550 | 90 |
Iceland* | ||||||
Ireland | 65 | 42 | 116 | 65 | 42 | 116 |
Italy | 990 | 475 | 419 | 1000 | 500 | 419 |
Latvia | 61 | 101 | 44 | 84 | 107 | 44 |
Liechtenstein | 0.37 | 0.11 | 0.15 | |||
Lithuania | 110 | 145 | 84 | 110 | 145 | 84 |
Luxembourg | 11 | 4 | 7 | 11 | 4 | 7 |
Malta | 8 | 9 | 3 | |||
Netherlands | 260 | 50 | 128 | 266 | 50 | 128 |
Norway | 156 | 22 | 23 | |||
Poland | 879 | 1397 | 468 | 879 | 1397 | 468 |
Portugal | 250 | 160 | 90 | 260 | 170 | 108 |
Romania | 437 | 918 | 210 | 437 | 918 | 210 |
Slovakia | 130 | 110 | 39 | 130 | 110 | 39 |
Slovenia | 45 | 27 | 20 | 45 | 27 | 20 |
Spain | 847 | 746 | 353 | 847 | 774 | 353 |
Switzerland | 79 | 26 | 63 | |||
Sweden | 148 | 67 | 57 | 148 | 67 | 57 |
Turkey* | ||||||
United Kingdom | 1167 | 585 | 297 | 1181 | 625 | 297 |
* Iceland and Turkey do not have a ceiling under either the NEC Directive or the Gothenburg protocol.
This indicator is based on officially reported national total and sectoral emissions to EEA and UNECE/EMEP (United Nations Economic Commission for Europe/Co-operative programme for monitoring and evaluation of the long-range transmission of air pollutants in Europe) Convention on Long-range Transboundary Air Pollution (LRTAP Convention), submission 2011. For the EU-27 Member States, the data used is consistent with the emissions data reported by the EU in its annual submission to the LRTAP Convention.
Recommended methodologies for emission inventory estimation are compiled in the EMEP/EEA Air Pollutant Emission Inventory Guidebook, (EMEP/EEA, 2013). Base data are available from the EEA Data Service (http://dataservice.eea.europa.eu/dataservice/metadetails.asp?id=1096) and the EMEP web site (http://www.ceip.at/). Where necessary, gaps in reported data are filled by ETC/ACC using simple interpolation techniques (see below). The final gap-filled data used in this indicator are available from the EEA Data Service (http://dataservice.eea.europa.eu/PivotApp/pivot.aspx?pivotid=478).
Base data, reported in the UNECE/EMEP Nomenclature for Reporting (NFR) sector format are aggregated into the following EEA sector codes to obtain a consistent reporting format across all countries and pollutants:
The following table shows the conversion of Nomenclature for Reporting (NFR) sector codes used for reporting by countries into EEA sector codes:
EEA classification |
Non-GHGs (NFR) |
|
National totals |
National total |
|
Energy production and distribution |
1A1, 1A3e, 1B |
|
Energy use in industry |
1A2 |
|
Road transport |
1A3b |
|
Non-road transport (non-road mobile machinery) |
1A3 (exl 1A3b) |
|
Industrial processes |
2 |
|
Solvent and product use |
3 |
|
Agriculture |
4 |
|
Waste |
6 |
|
Commercial, institutional and households |
1A4ai, 1A4aii, 1A4bi, 1A4bii, 1A4ci, 1A4cii, 1A5a, 1A5b |
|
Other |
7 |
An improved gap-filling methodology was implemented in 2010 that enables a complete time series trend for the main air pollutants (eg NOX, SOX, NMVOC, NH3 and CO) to be compiled. In cases where countries did not report emissions for any year, it meant that gap-filling could not be applied. For these pollutants, therefore, the aggregated data are not yet complete and are likely to underestimate true emissions. Further methodological details of the gap-filling procedure are provided in section 1.4.2 Data gaps and gap-filling of the European Union emission inventory report 1990–2009 under the UNECE Convention on Long-range Transboundary Air Pollution (LRTAP).
No methodology references available.
The use of gap-filling for when countries have not reported emissions for one of more years can potentially lead to artificial trends, but it is considered unavoidable if a comprehensive and comparable set of emissions data for European countries is required for policy analysis purposes.
Primary PM2.5 and PM10 data is of relatively higher uncertainty compared to emission estimates for the secondary PM precursors. The contribution of secondary particulate matter precursor emissions to PM formation varies considerably across different emission sources and geographical region (meteorology etc).
Overall scoring: (1-3, 1=no major problems, 3=major reservations)
This indicator is regularly updated by EEA and is used in state of the environment assessments. The uncertainties related to methodology and data sets are therefore of importance.
For references, please go to https://www.eea.europa.eu/data-and-maps/indicators/emissions-of-primary-particles-and-5/assessment-1 or scan the QR code.
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