This briefing provides information about the effect of environmental noise from road, rail and air transport on children’s reading ability and behaviour in Europe, to support EU policy responses. It is based on data submitted by EEA member countries under the EU’s Environmental Noise Directive (END).

Key messages

Children living or attending school in areas impacted by transport noise tend to score lower on reading comprehension and face more behavioural challenges.

Over half a million children in Europe experience impaired reading ability due to environmental noise from road, rail and air transport.

Almost 60,000 cases in Europe of behavioural difficulties in children are due to environmental noise generated from transport.

Those cases of impaired reading ability and behavioural difficulties can be largely prevented through interventions to reduce environmental noise at homes and schools.

Health effects from transport noise on children

Environmental noise from transport sources such as vehicles, trains and aircraft is among the most damaging environmental factors to health in Europe after air pollution (Hänninen et al., 2014). Living in an area affected by transport noise is associated with an increased risk of developing a wide range of health issues, including cardiovascular, metabolic and mental health diseases. Chronic exposure to transport noise can also negatively affect children, especially because they are in an important learning and developmental phase (Clark and Paunovic, 2018). Growing evidence suggests that children that are exposed to transport noise at school or at home are more likely to suffer certain types of cognitive, learning, behavioral problems and obesity (ETC HE, 2024). In addition, recent work on cognitive development in adolescents found that traffic noise was associated with anxiety (Thompson et al., 2024) and that early life exposure to transport noise could also lead to mental health issues in adulthood (Newbury et al., 2024). Based on the latest evidence, this briefing presents the estimated impact of transport noise (road, rail and air) on the reading and behaviour of children in Europe. The full findings and methodology are described in the report Health effects of transportation noise for children and adolescents: an umbrella review and burden of disease estimation from the European Topic Center on Human Health and the Environment (ETC HE) (ETC HE, 2024).

Exposure of Europe’s population to transport noise

Exposure to noise from transport sources, in particular road traffic noise, is a major environmental problem in Europe. Over 20% of the EU’s population, including children, live in areas where traffic noise levels are harmful to health (EEA, 2021). In many urban areas, this percentage is much higher, reaching 50%. Approximately 14 million children aged 6-17 in Europe (including Iceland, Norway and Switzerland) are exposed to average transport noise levels of 55dB or higher. Recent evidence indicates that the risk of cognitive and behavioural problems in children begins to increase at schools where the outdoor levels are even below this threshold (Clark and Paunovic, 2018; Clark et al., 2021; Schubert et al., 2019; Thompson et al., 2022). Additionally, other studies have found negative effects associated with children’s exposure to traffic noise at home (Hjortebjerg et al., 2016; Tangermann et al., 2022).

Assessing the impacts of transportation noise on children’s health

The methodology used in this assessment is described by the ETC HE (ETC HE, 2024). This analysis incorporates data on the population exposed to noise levels exceeding 55dB Lden (day-evening-night level) from major roads, railways and airports as well as from roads, railways and airports within urban agglomerations of over 100,000 inhabitants as outlined in the END. Table 1 presents the key aspects of the noise health risk assessment for children in Europe.

Table 1. Overview of methodology used for estimating children’s health risks from transport noise exposure

Please select a resource that has a preview image available.

Impact of transport noise on children’s reading ability and behaviour in Europe

Based on current figures, the ETC HE has estimated the extent to which exposure to road, rail and air transport noise affect the reading ability and behaviour of children in Europe. The results are summarised in Table 2 below.

Table 2. Estimated number of children aged 6-17 suffering from reading and behavioural problems due to noise from road, rail and air transport in 2022, EEA-32 (excluding Turkey)

Please select a resource that has a preview image available.

Almost 550,000 cases of reading ability impairment a year are estimated to be due to environmental transport noise in Europe. Most of these cases (84%) are due to noise from road traffic, especially inside urban areas, followed by rail traffic (15%) and air transport (about 1%). In addition, almost 60,000 cases of behavioural difficulties annually are due to environmental transport noise in Europe, where again, a majority (about 86%) of cases are due to road traffic noise, mostly inside urban areas.

Uneven and incomplete coverage leads to underestimating the impacts of noise

The calculated impact of 550,0000 cases of impaired reading and 60,000 cases of behavioural difficulties from environmental noise should be considered an underestimate. This is primarily because the data reported under the END do not comprehensively cover all roads, rail networks, airports and agglomerations. They only cover roads transited by more than three million vehicles a year, railways with more than 30,000 trains a year, airports with more than 50,000 movements a year and agglomerations of more than 100,000 inhabitants.

In addition to this restricted coverage, not all cities map road and rail noise across all, or even most, streets. Some cities map the majority of their streets while others map only the busiest streets. As a result, there is not only an underestimation of impacts due to the coverage limitations of the END, but also a significant underestimation in certain urban areas resulting from incomplete noise mapping. Countries that conduct a comprehensive mapping of urban roads and streets are better positioned to capture the true extent of the impacts of environmental transport noise. The street coverage of each city can be seen in the EEA’s noise viewer.

Finally, the impacts of transport noise on children may start at levels below the END thresholds used in this assessment.

Possible interventions

Currently, there is a limited number of policy measures that limit children’s exposure to noise from transport. WHO has made the most relevant recommendations. WHO guidelines for community noise (Bjerglund, 1999) recommend that noise levels in school playgrounds should not exceed 55dB(A), while indoor classroom noise levels should not exceed 35dB(A) (EEA, 2020).

Reducing children’s exposure to environmental noise from road, railway and air transport at home and at school can help decrease cases of reading impairment and behavioural problems. Studies have found that reduced levels of transport noise can help mitigate the adverse effects on children, which include deficits in cognitive functions, elevated stress biomarkers and lower perceived quality of life (Evans et al., 1998; Hygge et al., 2002), highlighting the potential benefits of noise abatement strategies. Importantly, some research also shows that cognitive deficits may diminish over time once the source of noise is eliminated  (Hygge et al., 2002). This emphasises the necessity for timely actions and long-term planning in areas where children can be exposed to transportation noise. Additionally, studies evaluating interventions such as building modifications in schools have demonstrated improvements in terms of enhanced student concentration and decreased aggression (Polewczyk and Jarosz, 2020). Awareness interventions have also showed positive results in children in terms of understanding noise as a pollutant (Gilles and Paul, 2014; Christidou et al., 2015).

Table 3 shows a compilation of possible mitigation measures that can be implemented at schools and in the home environment to reduce the impact of transportation noise on children’s health.

To effectively minimise noise exposure from transportation sources, particularly for vulnerable populations such as children, it is crucial to focus on upstream measures aimed at reducing noise at source. Implementing strategies such as lowering speed limits, reducing motor and tyre noise, and targeting high-emission noise sources can significantly benefit a larger segment of the population. In contrast, localised interventions like constructing noise barriers primarily benefit those in a specific area (EEA, 2022; ETC HE, 2022). Additionally, a long-term strategy to reduce exposure to transport noise should also consider improved urban and transportation planning. This includes developing buffer zones, orienting buildings to minimise exposure and designing noise-sensitive areas within structures. Some measures, like the creation of green quiet areas, may have clear co-benefits in terms of air quality improvement, climate change adaptation and wellbeing. Previous studies indicate that to significantly decrease the number of individuals exposed to high levels of harmful noise, a comprehensive approach is essential. This approach should combine source-based measures, enhanced urban and transportation planning and substantial reductions in road traffic within urban areas (EEA, 2022; ETC HE, 2022).

Table 3. Interventions to reduce the impact of road, rail and aircraft noise on children’s health

School

Home

Building orientation and layout: designing school buildings to minimise exposure to outdoor noise by positioning classrooms away from busy roads or implementing buffers that can reduce noise levels inside schools.

Interventions/policies aiming at reducing emissions from road, rail and aircraft noise in residential areas: this includes lower speed limits, traffic calming measures and operational restrictions at airports and for railways.

Landscaping and green buffers: planting trees, shrubs or installing earth berms around school buildings can act as a natural noise barrier, absorbing and deflecting noise from transportation sources.

Engineering measures: using noise-reduction technologies in transportation infrastructure such as low-noise pavements, low-noise aircraft, quiet tyres, etc.

Quiet zones: creating designated quiet areas around schools. This can involve pacification of nearby streets by reduced traffic and lower speed limits, among others.

Urban planning measures: creating buffer zones around residential buildings and orienting buildings to minimise exposure to transport noise.

Engineering measures: using noise-reduction technologies in transportation infrastructure such as low-noise pavements, low noise tyres, low-noise aircraft, etc.

Landscaping and green areas: creating green areas around residential areas to provide quiet places away from transport sources. Planting trees, shrubs or installing earth berms around residential buildings can act as a natural noise barrier, absorbing and deflecting noise from transportation sources.

Insulation and acoustic treatment: soundproof windows, noise barriers, insulated doors and acoustic panels can reduce transportation noise inside classrooms. However, it is important to consider that some of these measures may also lead to potential issues, such as overheating or reduced ventilation.

Location of children’s bedroom and play areas: place away from areas affected by transportation noise to avoid exposure to transportation noise during nighttime

Educational measures: implementing noise awareness programmes for students and staff can help raise awareness about noise pollution and its effects, encouraging practices that contribute to a quieter learning environment.

Soundproofing of windows and doors, as well as sound absorbing insulation in walls and ceilings facing roads, railways or airports: it is important, however, to consider that some of these measures may also lead to potential issues, such as overheating or reduced ventilation

Sources: Based on (EEA, 2020), (ETC HE, 2024) and (Brown and van Kamp, 2017).

Conclusions

A very large proportion of the population in Europe — more than 20% — is exposed to long-term levels of transportation noise that are considered to be harmful to health. Consequently, it is estimated that the same proportion of children is also exposed to levels of noise that can have detrimental effects in their learning development. It is conservatively estimated that there are more than 500,000 children with impaired reading ability due to transportation noise from road, rail and air transport. In addition to this, almost 60,000 could also be having behavioural difficulties. Given the large number of children exposed to transport noise in residential environments and at schools, implementing policies to reduce transport noise could help in mitigating the detrimental effects of noise on learning.

Reducing exposure both at home and at schools would minimise these adverse outcomes for children, which may affect their lifelong opportunities and quality of life. There is a wide range of interventions that can be applied to reduce noise exposure and increase related community health outcomes, including for children.

Web report no. 16/2024
Title: The effect of environmental noise on children’s reading ability and behaviour in Europe
EN HTML: TH-01-24-025-EN-Q - ISBN: 978-92-9480-703-8 - ISSN: 2467-3196 - doi: 10.2800/2429067

Bjerglund, B., 1999, Guidelines for community noise, World Health Organization, Geneva,  Switzerland (http://apps.who.int/iris/handle/10665/66217) accessed 28 November 2018.

Brown, A. L. and van Kamp, I., 2017, ‘WHO Environmental Noise Guidelines for the European Region: A Systematic Review of Transport Noise Interventions and Their Impacts on Health’, International Journal of Environmental Research and Public Health 14(8), p. 873 (DOI: 10.3390/ijerph14080873).

Christidou, V., et al., 2015, ‘“Young noise researchers”: an intervention to promote noise awareness in preschool children’, Journal of Baltic Science Education 14(5), p. Continuous (DOI: https://doi.org/10.33225/jbse/15.14.569).

Clark, C., et al., 2021, ‘A meta-analysis of the association of aircraft noise at school on children’s reading comprehension and psychological health for use in health impact assessment’, Journal of Environmental Psychology 76, p. 101646 (DOI: 10.1016/j.jenvp.2021.101646).

Clark, C. and Paunovic, K., 2018, ‘WHO environmental noise guidelines for the European region: a systematic review on environmental noise and cognition’, International Journal of Environmental Research and Public Health 15(2), p. 285 (DOI: https://doi.org/10.3390/ijerph15020285).

EEA, 2020, Environmental noise in Europe — 2020, EEA Report No 22/2019, European Environment Agency.

EEA, 2021, Exposure of Europe’s population to environmental noise (https://www.eea.europa.eu/ims/exposure-of-europe2019s-population-to) accessed 23 September 2022.

EEA, 2022, Outlook to 2030 — can the number of people affected by transport noise be cut by 30%?, EEA Briefing (https://www.eea.europa.eu/publications/outlook-to-2030/outlook-to-2030-can-the) accessed 23 September 2022.

ETC HE, 2024, Health effects of transportation noise for children and adolescents: an umbrella review and burden of disease estimation, Report number 2024/11, European Topic Centre on Human Health and the Environment (Link pending).

ETC/HE, 2022, Projected health impacts from transportation noise – Exploring two scenarios for 2030, ETC/HE Report 2022/5, European Topic Centre on Human Health and the Environment (https://www.eionet.europa.eu/etcs/etc-he/products/etc-he-products/etc-he-reports/etc-he-report-2022-5-projected-health-impacts-from-transportation-noise-2013-exploring-two-scenarios-for-2030) accessed 22 June 2022.

Evans, G. W., et al., 1998, ‘Chronic Noise Exposure and Physiological Response: A Prospective Study of Children Living Under Environmental Stress’ (https://journals.sagepub.com/doi/10.1111/1467-9280.00014) accessed 29 November 2024.

Gilles, A. and Paul, V. de H., 2014, ‘Effectiveness of a preventive campaign for noise-induced hearing damage in adolescents’, International Journal of Pediatric Otorhinolaryngology 78(4), pp. 604-609 (DOI: 10.1016/j.ijporl.2014.01.009).

Hänninen, O., et al., 2014, ‘Environmental Burden of Disease in Europe: Assessing Nine Risk Factors in Six Countries’, Environmental Health Perspectives 122(5), pp. 439-446 (DOI: 10.1289/ehp.1206154).

Hjortebjerg, D., et al., 2016, ‘Exposure to Road Traffic Noise and Behavioral Problems in 7-Year-Old Children: A Cohort Study’, Environmental Health Perspectives 124(2), pp. 228-234 (DOI: 10.1289/ehp.1409430).

Hygge, S., et al., 2002, ‘A prospective study of some effects of aircraft noise on cognitive performance in schoolchildren’, Psychological Science 13(5), pp. 469-474 (DOI: 10.1111/1467-9280.00483).

Newbury, J. B., et al., 2024, ‘Air and Noise Pollution Exposure in Early Life and Mental Health From Adolescence to Young Adulthood’, JAMA Network Open 7(5), p. e2412169 (DOI: 10.1001/jamanetworkopen.2024.12169).

Polewczyk, I. and Jarosz, M., 2020, ‘Teachers’ and Students’ Assessment of the Influence of School Rooms Acoustic Treatment on Their Performance and Wellbeing’, Archives of Acoustics 45(3), p. 401 (DOI: 10.24425/aoa.2020.134057).

Schubert, M., et al., 2019, ‘Behavioral and Emotional Disorders and Transportation Noise among Children and Adolescents: A Systematic Review and Meta-Analysis’, IJERPH 16(18), pp. 1-16.

Tangermann, L., et al., 2022, ‘The association of road traffic noise with problem behaviour in adolescents: A cohort study’, Environmental Research 207, p. 112645 (DOI: 10.1016/j.envres.2021.112645).

Thompson, R., et al., 2022, ‘Noise pollution and human cognition: An updated systematic review and meta-analysis of recent evidence’, Environment International 158, p. 106905 (DOI: 10.1016/j.envint.2021.106905).

Thompson, R., et al., 2024, ‘Air pollution, traffic noise, mental health, and cognitive development: A multi-exposure longitudinal study of London adolescents in the SCAMP cohort’, Environment International 191, p. 108963 (DOI: 10.1016/j.envint.2024.108963).

WHO Europe, 2018, Environmental noise guidelines for the European region, World Health Organization Regional Office for Europe, Copenhagen (https://www.who.int/europe/publications/i/item/9789289053563) accessed 5 May 2022.