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  • 06 June 2024

What’s the best way to tackle climate change? An ‘evidence bank’ could help scientists find answers

  • Helen Pearson

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Five different coloured Tesla electric cars plugged in to charge at an outdoor charging station in California.

Policies that encourage the use of electric vehicles are among the thousands of approaches that governments worldwide have implemented to curb emissions. Credit: Jeff Gritchen/MediaNews Group/Orange County Register via Getty

Researchers are developing a bold plan to tackle one of the most urgent challenges in climate science: working out the most effective ways to tackle climate change . If it comes to pass, researchers and artificial intelligence (AI) would build a bank of evidence syntheses — reviews of a body of science — to reveal how well policies work to cut emissions or help societies adapt to global warming.

“This ‘what works?’ question is now the central question in climate policy,” says Jan Minx, a climate researcher at the Mercator Research Institute on Global Commons and Climate Change in Berlin, who is leading the effort.

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Countries worldwide have introduced thousands of policies to tackle climate change over the past three decades — from carbon taxes to the promotion of electric vehicles. But it’s unclear which ones work best. The evidence bank would fill that gap. It could help governments to tackle climate change and feed into the next scientific assessment of the Intergovernmental Panel on Climate Change (IPCC), which is getting under way and scheduled to be published by 2029. A meeting in Berlin next week — the What Works Climate Solutions Summit — will be the first to bring together specialists in climate, policy and evidence synthesis to discuss the idea.

“I really think scientific policy advice could be largely dysfunctional,” if scientists don’t do this, says Minx.

Jim Skea, who chairs the IPCC and is based at the International Institute for Environment and Development in London, is enthusiastic about the summit and evidence-bank idea. Governments are asking the IPCC to include more guidance on climate policy and actions in its next cycle, he says. “Getting an evidence-based approach to interventions”, he says, “is absolutely aligned with that.”

But some researchers have concerns. Navroz Dubash, a climate-policy researcher at the Sustainable Futures Collaborative in New Delhi, says that although the effort is important, it risks “missing some of the most important approaches to climate policymaking”.

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Evidence explosion

Minx was an author of the IPCC’s latest assessment, published in 2021–23. He says that the body, which is tasked with assessing the science on climate change, has been hugely successful, but “to make the IPCC work in the future, we need to operate differently”.

The organization has so far said little, says Minx, on how well different policies work to address climate change, and under what conditions. These include carbon taxes, carbon pricing and policies that promote energy efficiency and cleaner transport. The IPCC’s reports have discussed such policies and a growing number of studies assess their effectiveness. But what’s missing is a systematic attempt to synthesize all the research and compare approaches. “The main point is, for most of the available policies we do not have a clear view on the evidence — and a cacophony of opinions,” says Minx.

One barrier is the explosive growth of climate science 1 (see ‘Mountain of evidence’). In the period leading up to the IPCC's first scientific assessment, in 1990, researchers published fewer than 1,100 climate-change studies. For the sixth and latest assessment, the figure exceeded 400,000, according to an analysis by Minx’s team. Growth of the literature is “a major, major challenge”, Skea says. And rather than being academic publications, many studies that evaluate the impact of climate policies are hidden in ‘grey’ literature that is hard to unearth, such as government reports.

MOUNTAIN OF EVIDENCE. Chart shows the annual number of scientific publications related to climate change has soared.

Source: J. Minx & M. Callaghan/Ref. 1

Minx’s solution is to take a leaf out of medicine’s book. Medical researchers have for decades searched for and combined studies in systematic reviews to show whether treatments help or harm. Minx wants climate scientists to adopt this approach to assess whether policies help or not. “We need to provide small bundles of knowledge that can be picked up by the IPCC,” he says.

Make electric vehicles lighter to maximize climate and safety benefits

Some such reviews already exist. A study published this month 2 by Minx’s team reviewed research on the effectiveness of carbon pricing, which typically shifts the cost of carbon emissions on to polluting industries. These initiatives are used worldwide, but their effectiveness in reducing emissions is debated. The study shows that carbon-pricing schemes cut emissions by around 4–15%, but highlighted that many schemes had not been evaluated. Minx wants future reviews to assess other impacts of policies such as carbon pricing — for example, their cost-effectiveness and impact on jobs.

Health effects

Minx is drumming up support for the evidence bank from climate researchers and funders. He envisions that reviews would build up in the literature and in existing databases, such as the Campbell Collaboration, which collects evidence syntheses on policies in one place.

Alan Dangour, who leads the climate and health team at research funder Wellcome in London, says the effort “couldn’t be more important”. Dangour wants to build evidence on the impacts of climate change and climate policies on human health — a priority area for Wellcome. Right now, “we’re asking policymakers to deliver adaptation actions with no understanding of what impact they’re going to have on health. It’s crazy”, he says.

A number of delegates on stage in front of a large audience during the opening ceremony of the COP21 climate change conference that took place in Paris in 2015.

The 2015 Paris climate agreement was influenced by assessments of science by the Intergovernmental Panel on Climate Change. Credit: Carl Court/Getty

Dangour and other researchers think that AI will accelerate the once-laborious process of synthesizing evidence. Many scientists already use machine-learning tools to screen and sort relevant studies. Wellcome has committed to spend £10 million (US$13 million) before October 2024 to support new approaches to evidence synthesis for climate and health, Dangour says. The dream, he says, is an open-access AI tool that automatically updates evidence syntheses as studies are published. “That’s the sort of thing I would love us to be able to deliver.”

Skea says that in previous IPCC discussions, greater use of systematic reviews has drawn a mixed reception. In systematic reviewing, scientists typically start by collecting hundreds of studies and then whittle them down to those that are most relevant and rigorous. But the IPCC is under pressure to bring in wider perspectives, including Indigenous people’s knowledge — information that is seldom documented in studies and risks being excluded from a systematic review. “We need to be a bit cautious about it,” Skea says.

Dubash says that focusing through evidence syntheses “on narrow and concrete climate policies may crowd out attention to broader policies that are harder to categorize but may be used more in developing countries”. For instance, policies such as fuel taxes or green-job creation might not be classified as climate policies but they still cut emissions indirectly; and many countries are embracing bespoke policy packages as they move to low-carbon economies. The challenge, he says, is often designing policies tailored to a country’s particular situation.

Minx agrees that it’s important to work with a broad definition of climate policies. He hopes that momentum behind the IPCC’s next assessment will motivate people to back the evidence bank. “This is urgent,” he says. “We cannot afford to take bad decisions.”

doi: https://doi.org/10.1038/d41586-024-01683-4

Minx, J. C., Callaghan, M., Lamb,W. F., Garard, J. & Edenhofer, O. Environ. Sci. Policy 77 , 252–259 (2017).

Article   Google Scholar  

Döbbeling-Hildebrandt, N. et al. Nature Commun. 15 , 4147 (2024).

Article   PubMed   Google Scholar  

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Europe’s air quality status 2024, key messages.

  • Despite ongoing overall improvements in air quality, current EU standards are still not met across Europe.   
  • 96% of the EU’s urban population is exposed to unsafe concentrations of fine particulate matter (PM 2.5 ).
  • The new EU air quality standards introduced in the revised ambient air quality directive — proposed to come into force in 2030 — are more ambitious than the current ones.

This briefing is one in a series to be published by the EEA as part of the Air quality in Europe 2024 package.

It assesses concentrations of air pollutants in ambient air across Europe, comparing them against current EU standards and the 2021 WHO global air quality guidelines . The EU standards were set out in the 2004 and 2008 ambient air quality directives .

Under the European Green Deal (EGD)’s zero pollution action plan , the European Commission set the interim 2030 goal of reducing the number of premature deaths caused by fine particulate matter (PM 2.5 , a key air pollutant) by at least 55% compared with 2005 levels. The ultimate objective is for air pollution to have no significant impact on health by 2050. To this end, the Commission published a proposal to review the ambient air quality directives in 2022. Among other things, it aimed to align the air quality standards more closely with WHO recommendations.

Co-legislators agreed to more ambitious EU air quality standards in February 2024. However, they are still less strict for all pollutants than what the WHO outlines in their air quality guideline levels .

In 2022, despite ongoing reductions in emissions , most of the EU’s urban population continued to be exposed to levels of key air pollutants that are damaging to health (see Figure 1). In particular, almost all of the urban population was exposed to concentrations of PM 2.5 above the 2021 WHO annual guideline level of 5µg/m 3 and to concentrations of ozone (O 3 ) above the short-term guideline level of 100µg/m 3 .

Figure 1. Share of the EU urban population exposed to air pollutant concentrations above certain EU standards and WHO guidelines in 2022

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Notes : Exposure above EU standards: the EU urban population is exposed to PM 2.5 annual concentrations above 25µg/m 3 ; PM 10 daily concentrations above 50µg/m 3 for more than 35 days per year; O 3 maximum daily 8-hour mean concentrations above 120µg/m 3 for more than 25 days per year; NO 2 annual concentrations above 40µg/m 3 ; Benzo[a]pyrene (BaP) annual concentrations above 1ng/m 3 ; and sulphur dioxide (SO 2 ) daily concentrations above 125µg/m 3 for more than three days per year. Exposure above WHO guidelines: the EU urban population is exposed to PM 2.5 annual concentrations above 5µg/m 3 ; PM 10 annual concentrations above 15µg/m 3 ; O 3 maximum daily 8-hour mean concentrations exceeding 100µg/m 3 for more than 3-4 days per year; NO 2 annual concentrations above 10µg/m 3 ; BaP annual concentrations above 0.12ng/m 3 ; and SO 2 daily concentrations above 40µg/m 3 for more than three or four days per year. Source : EEA, 2024 .

Methodology

This analysis highlights pollutants deemed most harmful to human health and those that most frequently exceed the current EU air quality standards and WHO guideline levels.

The concentrations are obtained from monitoring station measurements and are officially reported to the EEA by its members and other collaborating countries [1] . The classification of the monitoring stations and the criteria used to determine their inclusion in the analysis are described here . The number of countries that submitted data and the number of monitoring stations with the minimum data coverage required vary for each pollutant. This is summarised in Table 1 for 2022 and Table 2 for 2023. When referring to countries reporting data above certain levels, it means that they reported at least one station with concentrations that surpassed them.

Data for 2022 and 2023 were extracted from the EEA’s reporting system on 5 March 2024.

The analysis for 2022 is based on officially validated data reported by countries. The analysis for 2023 is based on provisional up-to-date (UTD) data. It may change once fully validated data is received by the EEA and more countries are considered. Validated data for 2023 will only be available later in 2024 and will be presented in the 2025 briefing.

Additional information and further analysis are available in the Eionet status reports ETC/HE 2024/3 (Targa et al., 2024a) and ETC/HE 2024/5 (Targa et al., 2024b), prepared by the European Topic Centre on Human Health and the Environment (ETC HE) .

Further information on the concentrations of air pollutants, including those for previous years, can be found at the EEA’s statistics viewer . Data can be downloaded here .

Apart from the measurements from monitoring stations, some countries also reported 2022 official data from modelling applications, which are available from the Air Quality Modelling Viewer . The results from these modelling applications have been included in this analysis where they implied concentrations above the EU standards.

Navigate the tabs for information on each pollutant: 

  • Other pollutants

PM 10 stands for particulate matter with a diameter of 10µm or less. PM 10 is emitted mainly by the combustion of solid fuels for domestic heating, although industrial activities, agriculture and road transport are also important sources. Some also come from natural sources such as sea salt, Saharan dust or volcanoes, and some (secondary PM) form in the atmosphere as a combination of different gases (for instance, ammonia and nitrogen dioxide). Member States can discount the contribution of natural sources to the total concentrations for compliance assessments as these sources are out of their control, but we do not exclude these sources in this status analysis.

Concentrations above the EU daily limit value for PM 10 are seen mainly in Italy and some eastern European countries (Map 1 and Figure 3). In most central and eastern European countries, solid fuels such as coal and wood are widely used for heating households and in some industrial facilities and power plants. The Po Valley in northern Italy is a densely populated and industrialised area with specific meteorological and geographical conditions that favour the accumulation of air pollutants in the atmosphere. Some concentrations are also above the EU daily limit value in southern Spain and the Canary Islands, mainly due to the natural contributions of Saharan dust ( MITECO, 2023 ).

Map 1. Concentrations of PM 10 in 2022 and 2023 in relation to the EU daily limit value

Note: The map shows the 90.4th percentile of the PM 10 daily mean concentrations, representing the 36th-highest value in a complete series. It is related to the PM 10 daily limit value, allowing 35 exceedances of the 50µg/m 3 threshold over one year. Source: EEA’s AQ e-reporting database.

Table 3. Country status for PM 10 in 2022 and 2023

Number of countries/Member States > EU daily limit value (50µg/m )      23/16      15/12
Number of countries/Member States > EU annual limit value (40µg/m )      9/4        6/3  
Number of countries/Member States > WHO daily guideline level (45µg/m ) 37 ( )/27 34 ( )/26
Number of countries/Member States > WHO annual guideline level (15µg/m ) 35 ( )/26 35 ( )/27

Note: ( a ) all the reporting countries; ( b ) all the reporting countries except Estonia and Iceland; ( c ) all the reporting countries except Luxembourg. Source: EEA’s AQ e-reporting database.

Figure 2. Percentage of reporting monitoring stations registering PM 10 concentrations above the EU limit values and the WHO guideline levels in 2022 and 2023

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In 2022, 16% of monitoring stations measured concentrations of PM 10  above the EU daily limit value (Figure 2), 84% of which were urban and 12% suburban.

Furthermore, Italy and Poland reported 2022 exceedances of the PM 10  daily limit value based on  assessment models  for 7 and 13 air quality zones, respectively.

Figure 3.  PM 10  concentrations in 2022 by country in relation to the EU daily limit value

Note:  The figure shows, per country, the concentrations of each reported station; the minimum and maximum concentrations; the median and the 25th and 75th percentiles of all the measurements (90.4th percentile of the PM 10  daily mean concentrations).

PM 2.5 stands for particulate matter with a diameter of 2.5µm or less. These particles are emitted mainly from the combustion of solid fuels for domestic heating, industrial activities and road transport. As with PM 10 , they can also come from natural sources and can form in the atmosphere. For compliance assessments, Member States can discount the contribution of natural sources to the total concentrations as these sources are out of their control, but in this status analysis, we do not exclude them. Agricultural emissions of ammonia significantly contribute to forming fine particulate matter in the atmosphere.

PM 2.5 concentrations above the EU annual limit value were seen in Italy and some eastern European countries (Map 2 and Figure 5). As for PM 10 , solid fuel use is the main reason for the situation in central and eastern Europe, together with an older vehicle fleet. In northern Italy, the high concentrations are due to the combination of a high density of anthropogenic emissions and also meteorological and geographical conditions that favour the accumulation of air pollutants in the atmosphere and the formation of secondary particles.

Map 2. Concentrations of PM 2.5 in 2022 and 2023 in relation to the EU annual limit value and the WHO annual guideline level

Source: EEA’s AQ e-reporting database .

Table 4. Country status for PM 2.5 in 2022 and 2023

Number of countries/Member States > EU annual limit value (25µg/m )         6/3          5/2  
Number of countries/Member States > WHO annual guideline level (5µg/m ) 36 ( )/27 34 ( )/27
Number of countries/Member States > WHO daily guideline level (15µg/m ) 37 ( )/27  35 ( )/27

Notes : ( a ) all the reporting countries, except Iceland; ( b ) all the reporting countries. Source: EEA’s AQ e-reporting database .

Figure 4. Percentage of reporting monitoring stations registering PM 2.5  concentrations above the EU annual limit value and the WHO guideline levels in 2022 and 2023

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In 2022, 2% of monitoring stations registered concentrations of PM 2.5  above the EU annual limit value (Figure 4), 78% of which were urban and 15% suburban. In contrast, 95% of the PM 2.5 reporting stations registered concentrations above the WHO annual guideline level, 76% of which were urban and 20% suburban.

Furthermore, Italy and Poland reported exceedances of the PM 2.5  annual limit value based on  assessment models  for three and one air quality zones, respectively.

Regarding the EU standards related to the Average Exposure Indicator [2] for PM 2.5 , which assesses the general population’s long-term exposure in urban areas, all EU Member States continued to meet the exposure concentration obligation of 20µg/m 3 in 2022, set as a 2015 target under the  ambient air quality directive [3] . Furthermore, for the first time, all Member States [4] met the national exposure reduction target set for 2020.

Figure 5. PM 2.5  concentrations in 2022 by country in relation to the EU annual limit value and the WHO annual guideline level

Note:  The figure shows, per country, the concentrations of each reported station, the minimum and maximum concentrations, the median and the 25th and 75th percentiles of all the measurements (annual mean PM 2.5. concentrations).

Ozone (O 3 ) is a pollutant formed in the atmosphere when heat and light cause chemical reactions between nitrogen oxides and volatile organic compounds (VOCs), including methane (which is also a powerful greenhouse gas ). Emissions of these gases occur from anthropogenic sources and, in the case of VOCs, also biogenic. Ozone is also transported to Europe from other parts of the northern hemisphere and the upper atmosphere. Meteorology plays an important role in forming and dispersing air pollution, and interannual variations in concentrations. This effect is especially significant for ozone.

Map 3. Concentrations of O 3  in 2022 and 2023 in relation to the EU target value

Notes:  The map shows the 93.2nd percentile of the O 3  maximum daily eight−hour mean, representing the 26th-highest value in a complete series. It is related to the O 3  target value. Data are presented here for one year only instead of the average over a three-year period, as stated in the definition of the EU target value for O 3 . Source : EEA’s AQ e-reporting database .

The highest concentrations in 2022 were found in some Mediterranean and central European countries (Map 3 and Figure 7).

Table 5. Country status for O 3  in 2022 and 2023  

Number of countries/Member States > EU target value threshold (120µg/m )      22/18      20/16
Number of countries/Member States > EU long-term objective (120µg/m ) 35 ( )/27 33 ( )/27
Number of countries/Member States > WHO short-term guideline level (100µg/m ) 35 ( )/27 33 ( )/27
Number of countries/Member States > WHO peak season guideline level (60µg/m ) 35 ( )/27 33 ( )/27

Notes : ( a ) all the reporting countries.  The stations in Kosovo, although reported, did not get the minimum data coverage to estimate the relevant ozone statistics. Source : EEA’s AQ e-reporting database .

Figure 6. Percentage of reporting monitoring stations registering O 3  concentrations above the EU target value and the WHO guideline levels in 2022 and 2023

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The long-term EU objective for ozone of 120µg/m 3  was met at 16% of monitoring stations in 2022.

Italy reported exceedances of the O 3  target value for the protection of health based on  assessment models  for three air quality zones. Italy and Poland reported exceedances of the O 3  long-term objective for the protection of health in 9 and 46 air quality zones, respectively.

Figure 7. O 3  concentrations in 2022 by country in relation to the EU target value

Note:  The figure shows, per country, the concentrations of each reported station, the minimum and maximum concentrations, the median and the 25th and 75th percentiles of all the measurements (93.2nd percentile of O 3 maximum daily eight-hour mean). Data are presented here for one year only, not the average over a three-year period as stated in the definition of the EU target value for O 3 .

In 2023, the long-term EU objective for ozone was met at 14% of monitoring stations.

The leading source of nitrogen dioxide (NO 2 ) is road transport, which emits NO 2 close to the ground, mostly in densely populated areas, contributing to population exposure. Other important sources are combustion processes in industry and energy supply.

Concentrations above the annual limit value were found in many Turkish cities and some big cities with a high volume of traffic (Map 4 and Figure 9).

Map 4. Concentrations of NO 2  in 2022 and 2023 in relation to the EU annual limit value and the WHO annual guideline level

Source :   EEA´s AQ e-reporting database .

Table 6. Country status for NO 2  in 2022 and 2023

Number of countries/Member States > EU annual limit value (40µg/m )      11/10      8/8
Number of countries/Member States > EU hourly limit value (200µg/m )      2/1      2/1
Number of countries/Member States > WHO annual guideline level (10µg/m ) 37 ( )/27 34 ( )/27
Number of countries/Member States > WHO daily guideline level (25µg/m ) 37 ( )/27 34 ( )/27

Notes : ( a ) all the reporting countries; ( b ) all the reporting countries, except Kosovo; ( c ): all the reporting countries. The stations from Kosovo, although reported, did not get the minimum data coverage to estimate the NO 2 statistics related to the WHO air quality daily guideline level. Source : EEA’s AQ e-reporting database .

Figure 8. Percentage of reporting monitoring stations registering NO 2  concentrations above the EU limit values and the WHO guideline levels in 2022 and 2023

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In 2022, 2% of monitoring stations registered concentrations of NO 2  above the EU annual limit value (Figure 8), 76% of which were traffic stations. Concentrations above the NO 2 WHO annual guideline level were registered at 74% of all monitoring stations, 45% of which were traffic stations.

Belgium, Italy and Poland reported exceedances of the NO 2  annual limit value based on  assessment models  for three, two and four air quality zones, respectively.

Figure 9. NO 2  concentrations in 2022 by country and in relation to the EU annual limit value and the WHO annual guideline level

Note:  The figure shows, per country, the concentrations of each reported station, the minimum and maximum concentrations, the median and the 25th and 75 th percentiles of all the measurements (annual mean NO 2 concentrations).

In 2023, 1% of monitoring stations registered concentrations of NO 2  above the annual limit value, all of which were traffic stations. 68% of monitoring stations registered concentrations above the WHO annual guideline level, 46% of which were traffic stations.

Benzo(a)pyrene (BaP)  is a carcinogenic pollutant emitted mainly from the combustion of coal and wood for heating and, to a lesser extent, from industrial installations and the combustion of agricultural waste.

The highest concentrations  were found in Italy and eastern Europe (Map 5 and Figure 10), where the use of coal and other solid fuels for residential heating is widespread.

Map 5. Concentrations of BaP in 2022

Source: EEA’s AQ e-reporting database

Country status for BaP in 2022: 12 out of 27 reporting countries, all of which were EU Member States, registered values above 1.0 ng/m 3 . Concentrations above 1.0 ng/m 3  were registered at 25% of the reported monitoring stations, the majority of which were urban (78%) or suburban (18%). Greece and Poland reported exceedances of the BaP target value based on  assessment models  for one and 32 air quality zones, respectively.

Figure 10. BaP concentrations in 2022 by country

Note:  The figure shows, per country, the concentrations of each reported station, the minimum and maximum concentrations, the median and the 25th and 75th percentiles of all the measurements (annual mean BaP concentrations).

Country status for  sulphur dioxide (SO 2 )  in 2022:

  • 4 out of 37 reporting countries (Bosnia and Herzegovina, Türkiye, North Macedonia and Serbia) — none of them EU Member States — registered levels above the EU daily limit value of 125µg/m 3 ;
  • 17 countries, including nine EU Member States, registered values above the WHO daily guideline level of 40µg/m 3 [5] .

In 2022, 1% of reporting monitoring stations registered concentrations above the EU daily limit value and 6% of stations registered concentrations above the WHO daily guideline level.

In 2023, 11 reporting stations outside the EU (nine in Bosnia and Herzegovina and two in North Macedonia) registered concentrations of SO 2  above the EU daily limit value. In the same year, concentrations above the WHO daily guideline level were registered in 13 countries (including 10 EU Member States) out of 33 reporting countries.

Concentrations above the corresponding EU limit or target values were also registered in 2022 for the following pollutants:

  • carbon monoxide (CO) at one station, located in the non-EU Member State of Serbia, out of 35 reporting countries;
  • for benzene and lead, no stations reported concentrations above EU annual limit values in the 28 and 30 reporting countries, respectively. Italy reported exceedances of the benzene annual limit value based on  assessment models  for one air quality zone;
  • arsenic in six stations across three EU Member States (Belgium, Finland and Poland, with two stations each) out of 29 reporting countries. Poland reported exceedances of the arsenic annual target value based on  assessment models  for two air quality zones;
  • cadmium at one station, located in the EU Member State of Bulgaria, out of 30 reporting countries;
  • nickel in four stations located in four EU Member States (Finland, France, Germany and Italy) out of 29 reporting countries.

[1]  The 27 European Union Member States, plus Iceland, Liechtenstein, Norway, Switzerland and Türkiye. The six West Balkan countries are cooperating countries. These include Albania, Bosnia and Herzegovina, North Macedonia, Montenegro, Serbia and Kosovo (the designation is without prejudice to position on status, and is in line with UNSCR 1244/99 and the ICJ Opinion on the Kosovo Declaration of Independence). Andorra reports data on a voluntary basis.

[2]  The Average Exposure Indicator (AEI) is based on a three-year average measured at urban background stations. The AEI for 2022 is based on 2020-2022. It assesses the general population’s long-term exposure in urban areas.

[3]  As well as the EU-27, Iceland and Norway also reported an AEI2022 below the exposure concentration obligation. The AEI2022 estimated for Switzerland, Andorra, Kosovo, Türkiye and Montenegro was also below the exposure concentration obligation. On the contrary, the estimated AEI2022 for Serbia, North Macedonia, and Bosnia and Herzegovina was above the exposure concentration obligation.

[4]  Plus Iceland and Norway.

[5]  The 99.18th percentile of the daily values has been considered, meaning three days of exceedance per year.

EEA, 2024. Indicator AIR003 'Exceedance of air quality standards in Europe'

Targa, J., Colina, M., Banyuls, L., González Ortiz, A., Soares, J. (2024a). Status report of air quality in Europe for year 2022, using validated data (ETC-HE Report 2024/3)

Targa, J., Colina, M., Banyuls, L., González Ortiz, A., Soares, J. (2024b). Status report of air quality in Europe for year 2023, using validated and up-to-date data (ETC-HE Report 2024/5).

MITECO, 2023. Evaluación de la Calidad del Aire en España 2022, Ministerio para la Transición Ecológica y el Reto Demográfico Secretaría General Técnica. Centro de Publicaciones., NIPO: 665-21-045-X

Identifiers

Briefing no. 06/2024 Title: Europe’s air quality status 2024 EN HTML: TH-AM-24-009-EN-Q - ISBN: 978-92-9480-650-5 - ISSN: 2467-3196 - doi: 10.2800/5970

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For references , please go to https://www.eea.europa.eu/publications/europes-air-quality-status-2024/europes-air-quality-status-2024 or scan the QR code.

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