Eutrophication of terrestrial ecosystems due to air pollution

Briefing Published 30 Nov 2017 Last modified 01 Dec 2017
7 min read
Eutrophication of terrestrial ecosystems due to air pollution

Indicator

Indicator past trend


Selected objective to be met by 2020

Indicative outlook of the EU meeting the selected objective by 2020

Exposure of terrestrial ecosystems to eutrophication due to air pollution

EU

Green triangle: improving trend

EEA

Green triangle: improving trend

 

Reduce areas of critical load exceedance with
respect to eutrophication by 43 % from 2000 levels
— Air Pollution Thematic Strategy

 

Red circle: it is unlikely that the objective will be met by 2020

The area where ecosystems are exposed to eutrophication because of excess atmospheric nitrogen deposition has decreased. According to a scenario assuming that current legislation is fully implemented, it will, nevertheless, fall short of the 2020 objective

For further information on the scoreboard methodology please see Box I.3 in the EEA Environmental indicator report 2017


The Seventh Environment Action Programme (7th EAP) includes the objective of reducing the impact of air pollution on ecosystems and biodiversity, with the long-term aim of not exceeding critical loads and levels. Critical loads represent the upper limit of the levels of one or more air pollutants deposited to the Earth’s surface that an ecosystem can tolerate without being damaged. Currently, the most important impact of air pollution on ecosystems and biodiversity is eutrophication. The EU Thematic Strategy on Air Pollution includes a milestone for 2020 relative to 2000, of a 43 % reduction in the areas of ecosystems exposed to eutrophication as a result of air pollution, i.e. areas where eutrophication critical loads are exceeded.

The EU ecosystem area where the critical loads for eutrophication were exceeded was approximately 78 % in 2000. The area in exceedance is projected to decrease to 54 % in 2020 for the EU, assuming that current legislation is fully implemented. The reduction in ecosystem areas exposed to eutrophication as a result of air pollution is estimated to be approximately 31 % between 2000 and 2020, which is below the 43 % reduction milestone suggested by the air pollution thematic strategy for this period. The improvements are primarily a result of reductions in eutrophying nitrogen emissions to the air. However, these emissions and, in particular, ammonia (NH3) and nitrogen dioxide (NO2) emitted from the agriculture and transport sectors, respectively, will remain significant contributors to eutrophication caused by air pollution. The eutrophication reduction milestone will therefore not be met unless further specific and targeted mitigation measures are put in place. Dietary changes resulting in less meat and dairy farming and the reduced use of petrol and diesel in cars could also contribute to reductions.  


Setting the scene

The 7th EAP (EU, 2013) includes the objective of reducing the impact of air pollution on ecosystems and biodiversity, with the long-term aim of not exceeding critical levels and loads. Currently, the most important impact of air pollution on ecosystems and biodiversity is eutrophication caused by airborne nitrogen deposition to ecosystems. In certain terrestrial sensitive ecosystems such as grasslands, excessive atmospheric loads of nitrogen can alone result in loss of sensitive species, increased growth of species that benefit from high nutrient levels, changes to habitat structure and function, the homogenisation of vegetation types, etc. This briefing addresses ecosystem eutrophication from air-borne sources. There are also other sources that cause ecosystem eutrophication (e.g. use of fertilisers on cropland and pastures if not applied correctly – see AIRS_PO1.2, 2017).

Policy targets and progress

The EU Thematic Strategy on Air Pollution includes a milestone for 2020, relative to 2000, of a 43 % reduction in areas of ecosystems exposed to eutrophication, i.e. areas where eutrophication critical loads are exceeded (EC, 2005a,  2005b). This milestone is in line with the long-term objective of not exceeding critical loads.  

In 2000[1], the area of ecosystems where the critical load was exceeded was about 78 % of the total in the EU Member States (approximately 60 % in all 33 EEA member countries for which data were available, including the 28 EU Member States) and decreased in 2010 to 63 % in the EU (55 % in all 33 EEA member countries). Assuming that current legislation is fully implemented, the area in exceedance is projected to be 54 % in the EU (48 % in all 33 EEA member countries) in 2020 (EEA, 2017a). The relative reduction is approximately 31 % for the EU, as well as for all the 33 EEA member countries, between 2000 and 2020, which is below the 43 % reduction milestone suggested by the air pollution thematic strategy for this period.

Nevertheless, as illustrated in Figure 1, the magnitude (though not the area) of the exceedance is projected to decline considerably in most areas, except for a few ‘hot spot’ areas, particularly in Belgium, Germany and the Netherlands, as well as in northern Italy.

Figure 1. Exposure of ecosystems to risk of eutrophication due to airborne deposition of nutrient nitrogen – area and magnitude of exceedance in 2000 and 2020.

Sources:
a. EEA – Indicator CSI005
b. CCE (Coordination Centre for Effects), CLRTAP, UNECE.


Note: The maps show areas where critical loads for eutrophication of freshwater and terrestrial habitats are exceeded

The main sources of eutrophication are emissions of nitrogen compounds (i.e. nitrogen oxide, ammonia) to the atmosphere. Nitrogen oxide (NOx) emissions for the EU decreased by approximately 41 % between 2000 and 2015 (EEA, 2017b). This reduction was primarily due to the introduction of three-way catalytic converters for cars. However, emission reductions from modern vehicles have not been as large as was originally anticipated. Standard diesel vehicles, for example, can emit up to seven times more NOx in real‑world conditions than in official tests (EEA, 2016).

Ammonia (NH3) emissions have not fallen by as much. In 2015, they had fallen by approximately 8 % compared with their value in 2000 for the EU (EEA, 2017b). Actually, both in 2014 and 2015 EU ammonia emissions increased by 1.1 % and 1.8 % respectively (AIRS_PO3.2, 2017). Agriculture is the main source of NH3 emissions; they amount to approximately 95 % of total emissions in the EEA-33 region. Emissions primarily arise from the decomposition of urea in animal wastes and uric acid in poultry wastes.

A key driver behind the observed reductions was the implementation of the National Emission Ceilings Directive (EU, 2001), which set air pollutant emission ceilings to be achieved by 2010 for, inter alia, emissions of the eutrophying air pollutants NOx and NH3. However, eutrophying emissions primarily from the agriculture and road transport sectors, but also from shipping and air travel, have been and will remain significant contributors to eutrophication caused by air pollution.

Further reductions in eutrophying air pollutant emissions are expected by 2020, among other things, as a result of the 2012 amended Gothenburg Protocol, which set stricter air pollutant emission ceilings for 2020 (UNECE, 2012) and of the revised National Emission Ceilings Directive which, inter alia, reflected these ceilings into EU legislation (EU, 2016).

Nevertheless, as illustrated at the start of this section, the decreases anticipated for 2020, under a scenario that assumes  current legislation (including the revised National Emission Ceilings Directive) is fully implemented, are not expected to contribute sufficiently to reductions in the ecosystem area exposed to excess atmospheric nitrogen deposition and affected by eutrophication. The relative reduction over the 2000 to 2020 period is expected to be only about 31 %, which is below the EU thematic strategy’s suggested milestone of a 43 % reduction for that period. Deeper reductions could take place through additional specific and targeted (technical) mitigation measures, particularly in the agriculture and transport sectors. Dietary changes resulting in less meat and dairy farming and the reduced use of petrol and diesel in cars could also contribute to reductions.

Country level information

Figure 2 shows the percentage of the area by country where the critical loads for eutrophication were exceeded in 2010 and the areas where exceedance is expected in 2020. Although a decrease is predicted by 2020, if current legislation is implemented, the area showing exceedance will be above 50 % in most countries (see bars). Extremely high magnitudes of exceedance can be found in Denmark, Hungary, Luxembourg, the Netherlands and Switzerland, caused by high deposition rates and/or ecosystems that are very sensitive to an excess supply of nitrogen from the atmosphere (see dots), for example nutrient-poor grasslands. 

Figure 2. The ecosystem area at risk of eutrophication due to airborne nitrogen deposition and the magnitude of exceedance in each country

Note: AAE is the average accumulated exceedance, showing the magnitude of exceedance in equivalents (mol nitrogen/ha per year). The data are based on the revised Gothenburg Protocol emission reduction agreements of 2012 (assuming for the 2020 scenario that current legislation is fully implemented). Data for Serbia and Montenegro are presented as aggregated data.

Outlook beyond 2020

The updated EU air pollution strategy aims, inter alia, to achieve a situation in which the EU ecosystem area exceeding critical loads for eutrophication is reduced by 35 % by 2030, relative to 2005 (EC, 2013a).

The revised National Emission Ceilings Directive not only transposed the amended Gothenburg Protocol 2020 air pollutant reduction commitments, it also set more ambitious air pollutant reduction commitments for 2030. These commitments – in particular the reduction commitments for the two eutrophying air pollutants, NOx and NH3 – will contribute to the achievement of the objective of 35 % by 2030.

However, this objective would not be met if only current legislation was fully implemented.

It would be met if the maximum number of technically feasible reduction measures was implemented (EC, 2013b).

Beyond  2030, the EU aspires towards ‘achieving levels of air quality that do not give rise to significant negative impacts on and risks to human health and the environment’ (EU, 2002). 

About the indicator

The indicator shows area and quantitative information for ecosystems where atmospheric nutrient nitrogen deposition is above the critical load. A critical load is a 'quantitative estimate of an exposure to one or more pollutants, below which significant harmful effects on specified sensitive elements of the environment do not occur according to present knowledge' (UNECE, 2015). Deposition loads of eutrophying airborne pollutants above the critical loads are termed an 'exceedance'. 

Exposure in an ecosystem for which information on critical loads is available, is calculated as the average accumulated exceedance (AAE). The AAE is the area-weighted average of exceedances, accumulated over all sensitive habitats (or ecosystem points) defined in a grid cell.

Footnotes and references

[1] The 2000 data presented here were provided by the Coordination Centre for Effects, a data centre under the UNECE Convention on Transboundary Air Pollution, on 21 November 2014 and can be obtained on demand from the EEA. Similarly, the 2010 and 2020 data presented here and in the related EEA indicator (EEA, 2017a) are from the same source and time stamp.

 

CCE, 2016, ‘Coordination Centre for Effects’, a data centre under the Convention on Long-range Transboundary Air Pollution (CLRTAP) of the United Nations Economic Commission for Europe (UNECE) (http://wge-cce.org), accessed 27 June 2017.

EC, 2005a, Communication of 21 September 2005 from the Commission to the Council and the European Parliament ‘Thematic strategy on air pollution’ (COM(2005) 446 final of 21 September 2005) (http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=URISERV%3Al28159) accessed 27 June 2017.

EC, 2005b, Commission staff working paper - Annex to the Communication from the Commission to the Council and the European Parliament ‘Thematic strategy on air pollution’ {COM(2005) 446 final} (SEC(2005) 1132 (http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A52005SC1132) accessed 27 June 2017.

EC, 2013a, ‘The Clean Air Policy Package’, adopted 18.12.2013 (http://ec.europa.eu/environment/air/clean_air_policy.htm) accessed 27 June 2017.

EC, 2013b, Commission staff working paper -  Executive Summary of the impact assessment of ‘The Clean Air Policy Package’, SWD(2013) 532 final of 18.12.2013 (http://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:52013SC0532&from=EN) accessed 5 November  2017.

EEA, 2016, Explaining road transport emissions — A non-technical guide (http://www.eea.europa.eu/publications/explaining-road-transport-emissions) accessed 27 June 2017.

EEA, 2017a, ‘Exposure of ecosystems to acidification, eutrophication and ozone (CSI 005)’ (http://www.eea.europa.eu/data-and-maps/indicators/exposure-of-ecosystems-to-acidification-3/assessment-2), accessed 6 November 2017.

EEA, 2017b, ‘Emissions of the main air pollutants in Europe (CSI 040)’ (http://www.eea.europa.eu/data-and-maps/indicators/main-anthropogenic-air-pollutant-emissions/assessment-1) accessed 6 November 2017. 

EU, 2001, Directive 2001/81/EC of the European Parliament and of the Council of 23 October 2001 on national emission ceilings for certain atmospheric pollutants (OJ L 309, 27.11.2001, p. 22–30) (http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=celex%3A32001L0081) accessed 27 June 2017.

EU, 2002, Decision No 1600/2002/EC of the European Parliament and of the Council of 22 July 2002 laying down the Sixth Community Environment Action Programme (OJ L 242, 10.9.2002) (http://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32002D1600&from=EN) accessed 27 June 2017.  

EU, 2013, Decision No 1386/2013/EU of the European Parliament and of the Council of 20 November 2013 on a General Union Environment Action Programme to 2020 ‘Living well, within the limits of our planet’ (OJ L 354, 28.12.2013, p. 171–200) (http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32013D1386) accessed 27 June 2017.

EU, 2016, Directive (EU) 2016/2284 of the European Parliament and of the Council of 14 December 2016 on the reduction of national emissions of certain atmospheric pollutants, amending Directive 2003/35/EC and repealing Directive 2001/81/EC (OJ L 344, 17.12.2016, p. 1–31) (http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=uriserv%3AOJ.L_.2016.344.01.0001.01.ENG) accessed 27 June 2017.

UNECE, 2012, ‘The 1999 Gothenburg protocol to abate acidification, eutrophication and ground-level ozone’, United Nations Economic Commission for Europe (http://www.unece.org/env/lrtap/multi_h1.html) accessed 27 June 2017.

UNECE, 2015, Manual on methodologies and criteria for modelling and mapping critical loads and levels and air pollution effects, risks and trends, United Nations Economic Commission for Europe, International Cooperative Programme on Modelling and Mapping (http://icpmapping.org/Latest_update_Mapping_Manual) accessed 27 June 2017.

 

AIRS briefings

AIRS_PO3.2, 2017, Air pollutant emissions

 

Environmental indicator report 2017 – In support to the monitoring of the 7th Environment Action Programme, EEA report No21/2017, European Environment Agency

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Based on indicators

Exposure of ecosystems to acidification, eutrophication and ozone Exposure of ecosystems to acidification, eutrophication and ozone In the EU-28, critical loads for acidification were exceeded in 7 % of the ecosystem area in 2010, down from 43 % in 1980 (and decreased to 7 % of the ecosystem area  across all EEA member countries). There are still some areas where the interim objective for reducing acidification, as defined in the EU's National Emission Ceilings Directive, has not been met.  The EU-28 ecosystem area in which the critical loads for eutrophication were exceeded peaked at 84 % in 1990 and decreased to 63 % in 2010 (55 % in the EEA member countries). The area in exceedance is projected to further decrease to 54 % in 2020 for the EU-28 (48 % in the EEA member countries), assuming current legislation is implemented. The magnitude of the exceedances is also projected to decline considerably in most areas, except for a few 'hot spot' areas in western France and the border areas between the Belgium, Germany and the Netherlands, as well as in northern Italy. Looking forward, only 4 % of the EU-28 ecosystem area (3 % in EEA member countries) is projected to exceed acidification critical loads in 2020 if current legislation is fully implemented. The eutrophication reduction target set in the updated EU air pollution strategy proposed by the European Commission in late 2013, will be met by 2030 if it is assumed that all maximum technically feasible reduction measures are implemented, but it will not be met by current legislation. For ozone, most of Europe's vegetation and agricultural crops are exposed to ozone levels that exceed the long term objective specified in the EU's Air Quality Directive. A significant fraction is also exposed to levels above the target value threshold defined in the directive. During the past five years, the fractions of agricultural crops above the target value were the lowest since 1996. In 2013, the fraction decreased to around the 21 %, compared with a relative peak of 27 % in 2012 . The effect-related concentrations show large year-to-year variations. Over the period 1996-2013, exposure increased until 2006, after which it decreased. During the past five years, around two-thirds of the forest area was exposed to ozone concentrations above the critical level set by the United Nations Economic Commission for Europe ( UNECE) for the protection of forests. 
Emissions of the main air pollutants in Europe Emissions of the main air pollutants in Europe Anthropogenic emissions of the main air pollutants decreased significantly in most EEA-33 member countries between 1990 and 2013: Nitrogen oxides (NO x ) emissions decreased by 49 % (54 % in the EU-28); Sulphur oxides (SO x ) emissions decreased by 80 % (87 % in the EU-28); Non-methane volatile organic compounds (NMVOC) emissions decreased by 57 % (59 % in the EU-28); Ammonia (NH 3 ) emissions decreased by 15 % (27 % in the EU-28); and Fine particulate matter (PM 2.5 ) emissions decreased by 34 % (34 % in the EU-28). The EU-28 met its continuing obligation to maintain emissions of NO x , SO x , NH 3  and NMVOC below legally binding targets as specified by the National Emission Ceilings Directive (NECD). However, a number of individual Member States reported emissions above their NECD emission ceilings: six for NO X (Austria, Belgium, France, Germany, Ireland and Luxembourg), six for NH 3 (Austria, Denmark, Finland, Germany, Netherlands and Spain) and three for NMVOCs (Denmark, Germany and Ireland). There are no emission ceilings for primary PM 2.5 . Three additional EEA member countries have emission ceilings for 2010 set in the Gothenburg Protocol under the 1979 UNECE Convention on Long-range Transboundary Air Pollution (Liechtenstein, Norway and Switzerland). Liechtenstein reported emissions above their NO x ceiling. Liechtenstein and Norway reported emissions above their NH 3 ceiling. Emissions reduction commitments for 2020 have been set under the 2012 amended Gothenburg Protocol for NO x , SO 2 , NMVOC, NH 3 , and PM 2.5 . The EU-28 as a whole is on track to meet its reduction commitments.
Exposure of ecosystems to acidification, eutrophication and ozone Exposure of ecosystems to acidification, eutrophication and ozone In the EU-28 countries, the ecosystem area where acidification critical loads were exceeded decreased from 43% in 1980 to 7% in 2010 (it also decreased by 7% across all EEA member countries). There remain some areas where the EU's interim objective for reducing acidification, as defined in the National Emission Ceilings Directive, has not been met.  The EU28 ecosystem area, where the critical loads for eutrophication were exceeded, peaked at 84% in 1990 and decreased to 63% in 2010 (55% in EEA member countries). The area in exceedance is projected to further decrease to 54% in 2020 for the EU28 (48% in EEA member countries), assuming current legislation is implemented. The magnitude of the exceedances is projected to reduce considerably in most areas, except for a few 'hot spot' areas in western France and the border areas between the Belgium, Germany and the Netherlands as well as in northern Italy. Only 4% of the EU-28 ecosystem area (3% in EEA member countries) is still projected to be in exceedance of acidification critical loads in 2020 if current legislation is fully implemented. The eutrophication reduction target set in the updated EU air pollution strategy proposed by the European Commission in late 2013, will be met by 2030 if it is assumed that all maximum technically feasible reduction measures are implemented, but it will not be met by current legislation. Most of Europe's vegetation and agricultural crops are exposed to ozone levels that exceed the long term objective specified in the EU Air Quality Directive. A significant fraction is also exposed to levels above the target value threshold defined in the directive. In 2012, the agricultural area exposed to concentrations above the target value threshold increased to 27% of the total area, representing an increase compared to the previous three years. With regard to forest ozone exposure, between 2004 and 2012, 60% or more of the forest area was exposed to concentrations above the critical level set by the UNECE Convention on Long Range Transboundary Air Pollution.  

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