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You are here: Home / Data and maps / Indicators / Critical load exceedance for nitrogen / Critical load exceedance for nitrogen (SEBI 009) - Assessment published May 2010

Critical load exceedance for nitrogen (SEBI 009) - Assessment published May 2010

Topics: ,

Generic metadata

Topics:

Biodiversity Biodiversity (Primary topic)

Tags:
ozone | csi | biodiversity | acidification | air
DPSIR: Pressure
Typology: Performance indicator (Type B - Does it matter?)
Indicator codes
  • SEBI 009
Dynamic
Temporal coverage:
2004
 
Contents
 

Key policy question: What are the trends in nitrogen emissions and where in Europe does atmospheric nitrogen deposition threaten biodiversity?

Key messages

Nitrogen emissions and deposition of nitrogen compounds have decreased since 1990 but relatively little compared to sulphur emissions. Agriculture and transport are the main sources of nitrogen pollution (EEA, 2007c). In addition, nitrogen components can lead to eutrophication of ecosystems. When this pollution exceeds certain levels ('critical load'), it is damaging to biodiversity. Critical load exceedance is still significant(1).

(1) The critical load of nutrient nitrogen is defined as 'the highest deposition of nitrogen as NOX and/or NHY below which harmful effects in ecosystem structure and function do not occur according to present knowledge' (ICP, M&M, 2004).

Total emissions of acidifying substances (sulphur, nitrogen) and of nitrogen in the EEA-32 from 1990 to 2006

Note: How to read the graph: in 1990, the total of acidifying emissions was around 1 500 Gg, while for nitrogen fractions it was more than 500 Gg.

Data source:

EEA/ETC ACC.

Downloads and more info

Exceedance of the critical loads for eutrophication in Europe (as average accumulated exceedances), 2004

Note: How to read the map: for Norway, exceedances of the critical load for nutrient nitrogen are in general not a major problem. Size of grid-cell: 50 km x 50 km.

Data source:

CCE IMPACT Database MNP (Netherlands Environmental Assessment Agency); Coordination Centre for Effects (CCE), Data Centre of the International Cooperative Programme on Modelling and Mapping of Critical Levels and Loads and Air Pollution Effects, Risks and Trends (ICP Modelling and Mapping, ICP M&M), Convention on Long-range Transboundary Air Pollution (LRTAP) of the United Nations Economic Commission for Europe (UNECE) of the Convention on Long-range Transboundary Air Pollution. 2007.

CCE/EMEP, 2007. Personal communication, input to Air pollution in Europe 1990–2004. EEA Report No 2/2007. European Environment Agency, Copenhagen, Denmark. Available at: www.eea.europa.eu/publications/eea_report_2007_2

CCE, 2007: 'Critical Loads of Nitrogen and Dynamic Modelling', Coordination Centre for Effects Progress Report 2007, MNP Report 500090001/2007.

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Key assessment

Across the EU-25, approximately 47 % of (semi-) natural ecosystem areas were subject to nutrient nitrogen deposition leading to eutrophication in 2004. A relatively smaller 15 % of the ecosystem area received deposition of acidifying compounds including nitrogen (CCE/EMEP, 2007). Ecosystem types in use by European countries for critical load calculations are forests; marine and coastal habitats; littoral zones; mire, bog and fen habitats; grasslands and tall forb habitats; heathland, scrub and tundra habitats; inland un-vegetated or sparsely vegetated habitats; agricultural habitats; inland and surface water habitats (for details see CCE, 2007). The extent to which critical loads are exceeded varies significantly across Europe.

FURTHER INFORMATION

 

Data sources

More information about this indicator

See this indicator specification for more details.

Contacts and ownership

EEA Contact Info

Katarzyna Biala

Ownership

EEA Management Plan

2010 (note: EEA internal system)

Dates

Document Actions

Comments

European Environment Agency (EEA)
Kongens Nytorv 6
1050 Copenhagen K
Denmark
Phone: +45 3336 7100