Authors :
Jeryl Joselin P. Morales; John Lester S. Resuello; Melmar Camacho; Gececlene C. Estorico
Volume/Issue :
Volume 10 - 2025, Issue 4 - April
Google Scholar :
https://tinyurl.com/mr36su2a
Scribd :
https://tinyurl.com/4wvke223
DOI :
https://doi.org/10.38124/ijisrt/25apr266
Google Scholar
Note : A published paper may take 4-5 working days from the publication date to appear in PlumX Metrics, Semantic Scholar, and ResearchGate.
Note : Google Scholar may take 15 to 20 days to display the article.
Abstract :
Transportation noise pollution is a critical environmental and public health concern, particularly in urban areas
where increasing traffic density contributes to elevated noise levels. Prolonged exposure to excessive transport noise has
been associated with adverse health effects, including hearing impairment, sleep disturbances, increased stress levels, and
an elevated risk of cardiovascular diseases. This systematic review examines noise pollution across various transport
modes—including buses, cars, trucks, motorcycles, subways, and aircraft—and compares recorded noise levels to the World
Health Organization (WHO) standard limits. The findings indicate that several transport modes exceed recommended
thresholds, with motorcycles (88.9 dBA), heavy trucks (87.5 dBA), and auto-rickshaws (85.5 dBA) surpassing their respective
limits of 85 dBA, 85 dBA, and 82 dBA. Among public transport options, buses exhibit an average noise level of 81.91 dBA,
exceeding the standard of 80 dBA, while subways (79.8 dBA) and streetcars (71.5 dBA) remain within acceptable limits. The
highest recorded noise level was for commercial passenger aircraft at 135.0 dBA, whereas the lowest was for bicycles at
69.65 dBA, remaining below the 70 dBA threshold. The most frequently reported sources of excessive noise in urban
transport, including engine vibrations, exhaust systems, tire-road interactions, and sudden vehicle movements.
Furthermore, this review evaluates various mitigation strategies, emphasizing the role of advancements in vehicle
technology, infrastructure modifications, traffic management, and policy enforcement in reducing transportation noise. The
adoption of electric and hybrid vehicles, noise-absorbing road surfaces, urban green spaces, and stricter noise regulations
are identified as effective strategies; however, persistent high noise exposure suggests that current measures require more
robust implementation and enforcement. By providing a comprehensive assessment of urban transportation noise levels and
their health implications, this study highlights the necessity for enhanced noise regulation and mitigation efforts. Its findings
offer valuable insights for policymakers, urban planners, and public health officials in developing evidence-based strategies
to minimize noise pollution and its associated health risks. Given the increasing reliance on public and private
transportation, addressing transport noise pollution is imperative to fostering healthier and more sustainable urban
environments.
Keywords :
Environmental Noise, Noise-Induced Health Effects, Public Health, Traffic Noise Exposure, Transportation Noise.
References :
- Babisch, W. (2008). Road traffic noise and cardiovascular risk. Noise and Health, 10(38), 27–33. https://doi.org/10.4103/1463-1741.39005
- Basner, M., Babisch, W., Davis, A., Brink, M., Clark, C., Janssen, S. A., & Stansfeld, S. A. (2014). Auditory and non-auditory effects of noise on health. The Lancet, 383(9925), 1325–1332. https://doi.org/10.1016/S0140-6736(13)61613-X
- European Environment Agency. (2020). Environmental noise in Europe – 2020. Publications Office of the European Union. https://www.eea.europa.eu/publications/environmental-noise-in-europe
- European Parliament and Council. (2002). Directive 2002/49/EC relating to the assessment and management of environmental noise. Official Journal of the European Communities.
- Guski, R., Schreckenberg, D., & Schuemer, R. (2017). WHO environmental noise guidelines for the European region: A systematic review on environmental noise and annoyance. International Journal of Environmental Research and Public Health, 14(12), 1539. https://doi.org/10.3390/ijerph14121539
- International Organization for Standardization. (2016). ISO 1996-1:2016 Acoustics – Description, measurement and assessment of environmental noise – Part 1: Basic quantities and assessment procedures. ISO. https://www.iso.org/standard/59765.html
- Kamineni, A., Duda, S. K., Chowdary, V., & Prasad, C. (2019). Modelling of noise pollution due to heterogeneous highway traffic in India. Transport and Telecommunication Journal, 20(1), 22–39. https://doi.org/10.2478/ttj-2019-0003
- Karimi, A., Nasiri, S., Kazerooni, F., & Oliaei, M. (2010). Noise-induced hearing loss risk assessment in truck drivers. Noise and Health, 12(46), 49. https://doi.org/10.4103/1463-1741.59999
- Kasagıcı, B., & Ates, N. (2021). Evaluation of environmental noise pollution (Traffic, schools, hospitals) and noise perception. Energy Environment & Storage, 1(2). https://doi.org/10.52924/ywkd5166
- Kumari, S., Sharma, A., & Ghosh, A. K. (2023). Noise pollution and associated health impacts at Ganeshpeth Bus Terminus in Nagpur, India. Noise Mapping, 10(1). https://doi.org/10.1515/noise-2022-0168
- Lacerda, A., Ribas, A., Mendes, J., & Andrade, P. (2004, December 1). Noise level and its perception by commuters in urban buses of Curitiba. Journal of the Canadian Acoustical Association. https://jcaa.caa-aca.ca/index.php/jcaa/article/view/1706
- Lu, Y., Chen, L., Wu, S. F., Hu, J., & Li, H. (2022). Analyzing motorcycle low-frequency noise. Journal of Theoretical and Computational Acoustics, 30(2). https://doi.org/10.1142/s2591728522500050
- Paviotti, M., & Vogiatzis, K. (2012). On the outdoor annoyance from scooter and motorbike noise in the urban environment. Science of the Total Environment. https://www.sciencedirect.com/science/article/pii/S0048969712006560
- Schwela, D., & Zali, O. (1999). Urban traffic pollution. Spon Press.
- Sørensen, M., & Poulsen, A. H. (2021). Transportation noise and health. In S. Dzhambov & D. Dimitrova (Eds.), Noise and public health (pp. 73-95). Elsevier.
- Supriya Kumari, S., Sharma, A., & Ghosh, A. K. (2024). Noise pollution and its impact on human health. De Gruyter. https://www.degruyter.com/document/doi/10.1515/noise-2022-0180/html
- World Health Organization. (1999). Guidelines for community noise. WHO. https://apps.who.int/iris/handle/10665/66217
- World Health Organization. (2018). Environmental noise guidelines for the European region. WHO Regional Office for Europe. https://www.who.int/europe/publications/i/item/9789289053563
- World Health Organization. (2021). Noise and health impacts: WHO findings and recommendations. WHO.
- Yang, W., & Kang, J. (2005). Soundscape and sound preferences in urban squares: A case study in Sheffield. Journal of Urban Design, 10(1), 61–80.
- Yao, C. M., Cushing, S. L., & Lin, V. Y. (2017). Noise exposure while commuting in Toronto - A study of personal and public transportation. Journal of Otolaryngology - Head and Neck Surgery, 46(1). https://doi.org/10.1186/s40463-017-0239-6
- Yavuz, A., Hazar-Yavuz, A. N., & Hacıbektaşoğlu, S. E. (2024). Vehicle noise pollution awareness for human health and environmental impacts: A comprehensive review. Acta Pharmaceutica Sciencia, 62(2), 244-266. https://www.actapharmsci.com/pdf.php?id=869
- Respicio, H. (2024b, April 12). Noise pollution Philippines. RESPICIO & CO. https://www.respicio.ph/commentaries/noise-pollution-philippines?
Transportation noise pollution is a critical environmental and public health concern, particularly in urban areas
where increasing traffic density contributes to elevated noise levels. Prolonged exposure to excessive transport noise has
been associated with adverse health effects, including hearing impairment, sleep disturbances, increased stress levels, and
an elevated risk of cardiovascular diseases. This systematic review examines noise pollution across various transport
modes—including buses, cars, trucks, motorcycles, subways, and aircraft—and compares recorded noise levels to the World
Health Organization (WHO) standard limits. The findings indicate that several transport modes exceed recommended
thresholds, with motorcycles (88.9 dBA), heavy trucks (87.5 dBA), and auto-rickshaws (85.5 dBA) surpassing their respective
limits of 85 dBA, 85 dBA, and 82 dBA. Among public transport options, buses exhibit an average noise level of 81.91 dBA,
exceeding the standard of 80 dBA, while subways (79.8 dBA) and streetcars (71.5 dBA) remain within acceptable limits. The
highest recorded noise level was for commercial passenger aircraft at 135.0 dBA, whereas the lowest was for bicycles at
69.65 dBA, remaining below the 70 dBA threshold. The most frequently reported sources of excessive noise in urban
transport, including engine vibrations, exhaust systems, tire-road interactions, and sudden vehicle movements.
Furthermore, this review evaluates various mitigation strategies, emphasizing the role of advancements in vehicle
technology, infrastructure modifications, traffic management, and policy enforcement in reducing transportation noise. The
adoption of electric and hybrid vehicles, noise-absorbing road surfaces, urban green spaces, and stricter noise regulations
are identified as effective strategies; however, persistent high noise exposure suggests that current measures require more
robust implementation and enforcement. By providing a comprehensive assessment of urban transportation noise levels and
their health implications, this study highlights the necessity for enhanced noise regulation and mitigation efforts. Its findings
offer valuable insights for policymakers, urban planners, and public health officials in developing evidence-based strategies
to minimize noise pollution and its associated health risks. Given the increasing reliance on public and private
transportation, addressing transport noise pollution is imperative to fostering healthier and more sustainable urban
environments.
Keywords :
Environmental Noise, Noise-Induced Health Effects, Public Health, Traffic Noise Exposure, Transportation Noise.