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Proceeding Paper

Nanomembranes and Urban Vehicles: A Simple Way to Minimize Urban Noise †

by
Elvis C. Monteiro
1,2 and
Antonio F. Avila
2,3,*
1
Stellantis Materials Technical Expertise (MTE) Division, 3455 Contorno Avenue, Paulo Camilo, Betim 32669-900, MG, Brazil
2
Mechanical Engineering Graduate Studies Program, Universidade Federal de Minas Gerais, Belo Horizonte 31270-901, MG, Brazil
3
Department of Mechanical Engineering, Universidade Federal de Minas Gerais, Belo Horizonte 31270-901, MG, Brazil
*
Author to whom correspondence should be addressed.
Presented at the 21st International Conference on Advanced Nanomaterials, ANM 2024, Aveiro, Portugal, 24–26 July 2024.
Mater. Proc. 2025, 21(1), 3; https://doi.org/10.3390/materproc2025021003
Published: 18 February 2025
(This article belongs to the Proceedings of The International Conference on Advanced Nano Materials)

Abstract

:
Urban noise is considered a growing problem in major cities around the world. This paper explores the development of a nanomembrane-based material for noise attenuation. The experimental results show that a combination of acoustic foam and nanomembranes can act as a Helmholtz resonator. The average sound absorption coefficient was around 90%, with peak frequencies varying from 2400 Hz to 4000 Hz. The average thickness of the nanomembranes was approximately 5.0 µm, while the acoustic foam was 13 mm thick. The mean noise reduction, around 10 dB, depends on the morphology of the nanomembranes, their thickness, and their pore size.

1. Introduction

As noted by de Paiva Vianna et al. [1], the World Health Organization (WHO) identified urban noise as a pollutant and potential health hazard in the early 1970s. The primary source of urban noise is road traffic, as examined by Hao et al. [2], who observed its link to sleep deprivation. Sorensen et al. [3] connected long-term exposure to urban noise with an increased risk of type 2 diabetes. McBride et al. [4] identified the spectral content of tire–pavement noise as falling within the 500 to 1500 Hz range. Van Renterghem et al. [5] found that urban park noise frequencies range from 2500 Hz to 8000 Hz, influenced by traffic. Shin et al. [6] associated road traffic noise, common in Toronto, with cardiovascular diseases, hypertension, and diabetes among residents.
Calixto et al. [7] defined allowable noise levels in various urban locations, based on factors such as construction type and traffic flow. Faulkner and Murphy [8] measured noise levels across different urban areas in Dublin. Similarly, Nascimento et al. [9] conducted a comparable study in Goiânia, Brazil, a city with a population of 1.3 million and noise levels greater than 60 dB (A). Dublin recorded road noise levels exceeding 55 dB (A).
Urban noise’s harmful effects on humans requires mitigation strategies, such as developing novel noise attenuation materials for urban areas. This paper discusses the development of a hybrid material, which combines two dissimilar microstructures to tailor acoustic behavior, potentially reducing health issues among urban populations.

2. Materials and Methods

The technique utilized for synthesizing nanomembranes in this study was electrospinning. In this research, the polymeric solution used during electrospinning consisted of poly (vinylidene fluoride-co-hexafluoropropylene) (PVdF-HFP) at a concentration of 12% w/w. Acetone and dimethyl–formamide (DMF) were mixed at a ratio of 40/60 w/w as solvents. This solvent combination not only reduced the solution’s viscosity but also facilitated rapid solvent evaporation. The flow rate of the polymeric solution through the 18G needle was maintained at 1.0 mL/h. The optimal voltage-to-distance gap ratio was determined to be 10 kV/cm for effective nanofiber formation [10]. A morphological analysis of the nanofibers was conducted using a high-resolution scanning electron microscope (SEM), FEG-Quanta 200 FEI. The experimental matrix outlined in Table 1 was designed not only to examine the impact of carbon nanotubes (CNTs) and surfactant (SDBS), but also to investigate the influence of surface tension reduction on the morphology of the nanofibers. The acoustic material used in this study was Basotect® UL (BASF Corporation, Florham Park, USA), specifically melamine foam with a density of 6 kg/m3 and a thickness of approximately 0.5 inches (around 13.0 mm). The melamine foam was combined in series with the nanomembranes. Acoustic tests were conducted following ASTM C 384 standards [10] using an impedance tube to evaluate frequencies ranging from 0 to 5000 Hz, chosen to encompass the urban noise spectrum, typically between 500 and 4500 Hz.

3. Results and Discussion

Leão et al. [11] discussed how acoustic properties are directly linked to the microstructural morphology of materials. To investigate these correlations between nanomembrane microstructure and overall acoustic response, a detailed morphological analysis was conducted; see Table 2. SEM observations from groups E1 to E4 are depicted in Figure 1a–d.
The addition of CNTs leads to a decrease in fiber diameter due to the increase in electrical conductivity. However, as discussed by Leão et al. [11], the bead formation was due to the increase in viscosity due to CNT addition. Bead formation was not observed in Figure 1c,d. This phenomenon occurs due to a reduction in surface tension between the needle’s internal walls and the solution, induced by the addition of the surfactant SDBS. As discussed by Mahesh and Mini [12], nanomembranes’ morphological changes can influence the overall system (foam + nanomembrane)’s acoustic behavior, as the combined materials act as a Helmholtz resonator. Table 3 shows the results obtained, while Figure 2a,b describe each group’s acoustic behavior over a wide frequency range.
According to Roca-Barcelo et al. [13], the noise map ranged from 45 dB to 65 dB near the Congonhas airport. By using such new material as acoustic insulation for public transportation, e.g., buses, it is possible to reduce the noise inside by at least 10 dB. The reason for such good performance is the combination of melamine foams and nanomembranes, which acts as a Helmholtz resonator, making it an an innovative and cost-effective solution, as nanomembranes are easy to create.

4. Conclusions

The concept of a Helmholtz resonator was successfully applied to create a new class of material with high capacity of sound absorption. This new innovative concept based on the series association of nanomembranes (~5.0 µm) and acoustic foam (13 mm) not only provided an average sound absorption coefficient around 89%, but also peak frequencies varying from 2400 Hz to 4000 Hz. The mean noise drop, around 10 dB, is dependent on the nanomembranes’ morphology, their thickness, and their pore size. By applying this new material to urban buses in downtown São Paulo, the average noise in a radius of 5 km from Congonhas airport can be reduced from 55 dB (A) to <45 dB (A). The environmental benefits of such a material are clear.

Author Contributions

E.C.M.: conceptualization; data curation; formal analysis; investigation; methodology; resources; validation; visualization. A.F.A.: conceptualization; formal analysis; funding acquisition; methodology; project administration; supervision; roles/writing—original draft; and writing—review and editing. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Brazilian Research Council grants number 406040/2021-4 and 307385/2022-1 and by the CAPES Foundation under grant 001. The APC was funded by ANM 2024.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

All data are available upon request to the corresponding author.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. De Paiva Vianna, K.M.; Alves Cardoso, M.R.; Rodrigues, R.M.C. Noise Pollution and Annoyance: An Urban Soundscapes Study. Noise Health 2015, 17, 125–133. [Google Scholar] [CrossRef]
  2. Hao, G.; Zuo, L.; Weng, X.; Fei, Q.; Zhang, Z.; Chen, L.; Wang, Z.; Jing, C. Associations of Road Traffic Noise with Cardiovascular Diseases and Mortality: Longitudinal Results from UK Biobank and Meta-Analysis. Environ. Res. 2022, 212, 113129. [Google Scholar] [CrossRef] [PubMed]
  3. Sørensen, M.; Hvidtfeldt, U.A.; Poulsen, A.H.; Thygesen, L.C.; Frohn, L.M.; Khan, J.; Raaschou-Nielsen, O. Long-Term Exposure to Transportation Noise and Risk of Type 2 Diabetes: A Cohort Study. Environ. Res. 2023, 217, 114795. [Google Scholar] [CrossRef]
  4. McBride, S.; Burdisso, R.; Sandu, C. Modeling Vibration-Induced Tire-Pavement Interaction Noise in the Mid-Frequency Range. Tire Sci. Technol. 2021, 49, 146–169. [Google Scholar] [CrossRef]
  5. Van Renterghem, T.; Vanhecke, K.; Filipan, K.; Sun, K.; De Pessemier, T.; De Coensel, B.; Joseph, W.; Botteldooren, D. Interactive Soundscape Augmentation by Natural Sounds in a Noise Polluted Urban Park. Landsc. Urban Plan. 2020, 194, 103705. [Google Scholar] [CrossRef]
  6. Shin, S.; Bai, L.; Oiamo, T.H.; Burnett, R.T.; Weichenthal, S.; Jerrett, M.; Kwong, J.C.; Goldberg, M.S.; Copes, R.; Kopp, A.; et al. Association between Road Traffic Noise and Incidence of Diabetes Mellitus and Hypertension in Toronto, Canada: A Population-Based Cohort Study. J. Am. Heart Assoc. 2020, 9, e013021. [Google Scholar] [CrossRef] [PubMed]
  7. Soni, A.R.; Makde, K.; Amrit, K.; Vijay, R.; Kumar, R. Noise Prediction and Environmental Noise Capacity for Urban Traffic of Mumbai. Appl. Acoust. 2022, 188, 108516. [Google Scholar] [CrossRef]
  8. Faulkner, J.P.; Murphy, E. Road Traffic Noise Modelling and Population Exposure Estimation Using CNOSSOS-EU: Insights from Ireland. Appl. Acoust. 2022, 192, 108692. [Google Scholar] [CrossRef]
  9. do Nascimento, E.O.; de Oliveira, F.L.; de Oliveira, L.N.; Zannin, P.H.T. Noise Prediction Based on Acoustic Maps and Vehicle Fleet Composition. Appl. Acoust. 2021, 174, 107803. [Google Scholar] [CrossRef]
  10. ASTM C384-04; Standard Test Method for Impedance and Absorption of Acoustical Materials by Impedance Tube Method. ASTM International: West Conshohocken, PA, USA, 2022.
  11. Leão, S.G.; Monteiro, E.C.; dos Reis, M.O.; Mapa, L.P.P.; Avila, A.F. Noise Attenuation inside Airplane Cabin: Preliminary Results on Combined Porous/Nano-Fibrous Materials. Appl. Acoust. 2022, 199, 109009. [Google Scholar] [CrossRef]
  12. Mahesh, K.; Mini, R.S. Helmholtz Resonator Based Metamaterials for Sound Manipulation. J. Phys. Conf. Ser. 2019, 1355, 012031. [Google Scholar] [CrossRef]
  13. Roca-Barceló, A.; Nardocci, A.; de Aguiar, B.S.; Ribeiro, A.G.; Failla, M.A.; Hansell, A.L.; Cardoso, M.R.; Piel, F.B. Risk of Cardiovascular Mortality, Stroke and Coronary Heart Mortality Associated with Aircraft Noise around Congonhas Airport, São Paulo, Brazil: A Small-Area Study. Environ. Health 2021, 20, 59. [Google Scholar] [CrossRef] [PubMed]
Figure 1. SEM observations: Cases E1–E4. (a) Case E1; (b) Case E2; (c) Case E3; (d) Case E4.
Figure 1. SEM observations: Cases E1–E4. (a) Case E1; (b) Case E2; (c) Case E3; (d) Case E4.
Materproc 21 00003 g001
Figure 2. Sound absorption coefficient as function of frequency. (a) Case E01 and foam; (b) Cases E02, E03, E04.
Figure 2. Sound absorption coefficient as function of frequency. (a) Case E01 and foam; (b) Cases E02, E03, E04.
Materproc 21 00003 g002
Table 1. Nanomembranes’ manufacturing features.
Table 1. Nanomembranes’ manufacturing features.
Group IDPVdF-HFP
[% w/w]
CNT
[% w]
SDBS
[ppm]
SDBS
[%w]
E1120.00----
E2120.20----
E3120.20100--
E4120.20--0.20
Table 2. Key dimensions for each nanomembrane group.
Table 2. Key dimensions for each nanomembrane group.
Group IDFiber Diameter [nm]Porous Diameter [µm]Thickness [µm]
E1216.68 ± 55.711.36 ± 0.277.80
E2130.01 ± 23.231.24 ± 0.324.68
E3188.67 ± 20.041.72 ± 0.476.79
E4146.68 ± 26.661.76 ± 0.455.28
Table 3. Acoustic properties of each nanomembrane group.
Table 3. Acoustic properties of each nanomembrane group.
Group IDPeak Absorption Coefficient [a.u.]Peak Frequency
[Hz]
Peak Noise
Drop [dB]
Mean Noise
Drop [dB]
E10.85238819.8111.16
E20.89300620.3411.45
E30.90343520.4411.21
E40.91399621.5810.27
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MDPI and ACS Style

Monteiro, E.C.; Avila, A.F. Nanomembranes and Urban Vehicles: A Simple Way to Minimize Urban Noise. Mater. Proc. 2025, 21, 3. https://doi.org/10.3390/materproc2025021003

AMA Style

Monteiro EC, Avila AF. Nanomembranes and Urban Vehicles: A Simple Way to Minimize Urban Noise. Materials Proceedings. 2025; 21(1):3. https://doi.org/10.3390/materproc2025021003

Chicago/Turabian Style

Monteiro, Elvis C., and Antonio F. Avila. 2025. "Nanomembranes and Urban Vehicles: A Simple Way to Minimize Urban Noise" Materials Proceedings 21, no. 1: 3. https://doi.org/10.3390/materproc2025021003

APA Style

Monteiro, E. C., & Avila, A. F. (2025). Nanomembranes and Urban Vehicles: A Simple Way to Minimize Urban Noise. Materials Proceedings, 21(1), 3. https://doi.org/10.3390/materproc2025021003

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