| Literature DB >> 34807387 |
Patrick Amoatey1, Issa Al-Harthy2, Khalifa Al-Jabri1, Abdullah Al-Mamun1, Mahad Said Baawain3, Ahmed Al-Mayahi4.
Abstract
This study aimed at investigating aircraft noise exposure levels, their annoyance, and potential health effects among communities living within airport catchment areas during the COVID-19 pandemic. Both field measurements and an online survey approach were used to investigate aircraft noise exposure levels, annoyance, and general health effects among residents living near Muscat International Airport (MCT) in Muscat, Oman, amid the COVID-19 period. The study found a drastic decline in aircraft noise levels due to the introduction of COVID-19 intervention measures such as lockdowns, social distancing, and closure of airports. In June 2020, during the COVID-19 pandemic, average daily aircraft noise levels of LAeq (39.9 dB(A)) and Lmax (49.7 dB(A)) was observed compared to the previous year (April-May 2019) of 58.5 and 76.8 dB(A), indicating aircraft noise reductions level of 32% and 35%, respectively. The results of the online social survey among 187 participants showed that most (58.8%) of the respondents did not feel that the level of noise produced by aircraft causes annoyance. During the day, the vast majority of the interviewees did not complain of any annoyance during the morning (45.5%), afternoon (39.6%), and evening (31%) with only < 4% of residents have reported a very high degree of annoyance of during COVID-19 pandemic period. Very few people (17%) did complain of experiencing general health problems while 29% did not know of any potential health effects that could be attributed to aircraft noise exposures. Aircraft noise annoyance complaints among the As-Seeb residents during the pre-COVID-19 pandemic periods were reported to be extremely high reaching about 84% compared to 41% during this current COVID-19 pandemic period. These findings support the need to develop future sustainable noise mitigation policies in order to help reduce noise exposures and improve human health during post-COVID-19 pandemic periods.Entities:
Keywords: Aircraft noise; Annoyance; COVID-19; Health effects; Muscat; Oman
Mesh:
Year: 2021 PMID: 34807387 PMCID: PMC8607223 DOI: 10.1007/s11356-021-17514-2
Source DB: PubMed Journal: Environ Sci Pollut Res Int ISSN: 0944-1344 Impact factor: 5.190
Fig. 1A map showing the location of the study area and noise measurement points
COVID-19 cases for top six governorates in Oman as of June 2020 when the noise exposure assessment was conducted and as of August 2021 during the peak period of the pandemic and also when about 50% of the population has received double doses of vaccination
| Location | June 2020 | August 2021 | ||||
|---|---|---|---|---|---|---|
| Cases | Recovery | Death | Cases | Recovery | Death | |
| Muscat (including As-Seeb) | 43,981 | 41,694 | 288 | 150,124 | 146,455 | 1,371 |
| North Batinah | 15,616 | 14,293 | 184 | 44,723 | 42,558 | 826 |
| South Batinah | 10,170 | 9687 | 111 | 26,573 | 25,521 | 446 |
| Al Dakhliyah | 5880 | 5283 | 51 | 19,649 | 19,264 | 370 |
| Dhofar | 3760 | 3221 | 39 | 19,652 | 19,264 | 344 |
| Al Wusta | 1739 | 1664 | 4 | 6,373 | 6,036 | 36 |
| National (Oman) Total | 89,746 | 83,771 | 780 | 303,673 | 296,917 | 4,095 |
Sources: (Ministry of Health 2020; WHO 2020).
Fig. 2Aircraft traffic levels at MCT during COVID-19 pandemic (March–July 2020) compared to the same months of the previous years (2018 and 2019),
source: PACA (2020)
Daily measured aircraft equivalent sound pressure levels LAeq expressed as dB(A) amid COVID-19 pandemic near MCT, Muscat, June 2020
| Measured Points | Average, dB(A) | Median, dB(A) | Maximum, dB(A) | Minimum, dB(A) |
|---|---|---|---|---|
| M01 | 37.5 | 38.0 | 44.0 | 32.0 |
| M02 | 39.4 | 40.0 | 44.0 | 33.0 |
| M03 | 40.6 | 41.0 | 46.0 | 34.0 |
| M04 | 40.7 | 41.5 | 49.0 | 30.0 |
| M05 | 39.2 | 39.5 | 47.0 | 32.0 |
| M06 | 40.1 | 40.0 | 45.0 | 35.0 |
| M07 | 40.6 | 40.0 | 49.0 | 32.0 |
Daily measured aircraft maximum sound pressure levels Lmax expressed as dB(A) amid COVID-19 pandemic near MCT, Muscat, June 2020
| Measured points | Average, dB(A) | Median, dB(A) | Maximum, dB(A) | Minimum, dB(A) |
|---|---|---|---|---|
| M01 | 47.5 | 46.5 | 60.0 | 38.0 |
| M02 | 46.7 | 45.5 | 58.0 | 37.0 |
| M03 | 49.4 | 48.0 | 60.0 | 40.0 |
| M04 | 51.9 | 54.0 | 60.0 | 41.0 |
| M05 | 51.9 | 53.0 | 59.0 | 43.0 |
| M06 | 48.0 | 47.5 | 58.0 | 38.0 |
| M07 | 46.1 | 47.5 | 54.0 | 37.0 |
Fig. 3Hourly noise levels (LAeq, Lmax) near MCT, Muscat amid COVID-19 pandemic
Aircraft noise levels of current and historical durations measured near MCT, Muscat of Oman COVID-19 pandemic for average daily LAeq and Lmax in dB(A)
| Measured noise | Current | Historical | Differences (%change) |
|---|---|---|---|
| LAeq | 39.72(1.15) | 58.55(3.81) | − 18.83 (− 32.16%) |
| Lmax | 49.78(2.36) | 76.81(5.42) | − 27.03 (− 35.19%) |
The historical noise levels were acquired from Al-Harthy et al. (2021). The historical (measured in April–May 2019) and the current noise (measured in June 2020) levels consisted of 15 and 7 measured points, respectively. SD, standard deviation.
Sociodemographic features and perception of noise sources during the COVID-19 pandemic were reported by residents living closer proximity to MCT in Muscat, Oman, June 2020 (n = 187)
| Variable | % | ||
|---|---|---|---|
| Gender | 0.023 | ||
| Male | 78 | 41.7 | |
| Female | 109 | 58.3 | |
| Age (years) | < 0.001 | ||
| < 25 | 37 | 19.8 | |
| 25–50 | 96 | 51.3 | |
| > 50 | 55 | 28.9 | |
| Sources of Noise at home | |||
| Industrial noise | < 0.001 | ||
| Not at all | 115 | 61.5 | |
| Low | 55 | 29.4 | |
| Moderate | 9 | 4.8 | |
| High | 4 | 2.1 | |
| Very high | 4 | 2.1 | |
| Construction noise | < 0.001 | ||
| Not at all | 68 | 36.4 | |
| Low | 65 | 34.8 | |
| Moderate | 41 | 21.9 | |
| High | 11 | 5.9 | |
| Very high | 02 | 1.1 | |
| Neighborhood | < 0.001 | ||
| Not at all | 73 | 39 | |
| Low | 78 | 41.7 | |
| Moderate | 22 | 11.8 | |
| High | 07 | 3.7 | |
| Very high | 07 | 3.7 | |
| Road traffic | < 0.001 | ||
| Not at all | 70 | 37.4 | |
| Low | 57 | 30.5 | |
| Moderate | 33 | 17.6 | |
| High | 15 | 8.0 | |
| Very high | 12 | 6.4 | |
| Aircraft | < 0.001 | ||
| Not at all | 45 | 24.1 | |
| Low | 72 | 38.5 | |
| Moderate | 32 | 17.1 | |
| High | 23 | 12.3 | |
| Very high | 15 | 8.0 |
Aircraft noise annoyance levels and related health impacts during COVID-19 pandemic era reported by residents living closer proximity to MCT in Muscat, Oman, June 2020 (n = 187)
| Variable | % | ||
|---|---|---|---|
| Aircraft annoyance | 0.016 | ||
| Yes | 77 | 41.2 | |
| No | 110 | 58.8 | |
| Degree of aircraft annoyance | 0.003 | ||
| Not at all | 53 | 28.3 | |
| Slightly | 63 | 33.7 | |
| Moderate | 42 | 22.5 | |
| Extremely | 29 | 15.5 | |
| Duration of annoyance | |||
| Morning | < 0.001 | ||
| Not at all | 85 | 45.5 | |
| Low | 51 | 27.3 | |
| Moderate | 35 | 18.7 | |
| High | 10 | 5.3 | |
| Very high | 06 | 3.2 | |
| Afternoon | < 0.001 | ||
| Not at all | 74 | 39.6 | |
| Low | 55 | 29.4 | |
| Moderate | 30 | 16.0 | |
| High | 23 | 12.3 | |
| Very high | 05 | 2.7 | |
| Evening | < 0.001 | ||
| Not at all | 58 | 31 | |
| Low | 57 | 30.5 | |
| Moderate | 41 | 21.9 | |
| High | 24 | 12.8 | |
| Very high | 07 | 3.7 | |
| Health effects from aircraft noise | < 0.001 | ||
| Yes | 33 | 17.6 | |
| No | 100 | 53.4 | |
| Don’t know | 54 | 29.0 |
Reported pre-COVID-19 pandemic airport noise annoyance perception levels (%) in As-Seeb, Oman, in December 2018 to February 2019 (n = 876) (Al-Harthy et al. (2021))
| Parameters | Response (%) | |
|---|---|---|
| Perception of aircraft annoyance | ||
| Yes | 740 | 84 |
| No | 136 | 16 |
| Degree of aircraft noise annoyance | ||
| No noise | 27 | 3 |
| Low | 88 | 10 |
| Medium | 120 | 14 |
| High | 235 | 24 |
| Very high | 406 | 46 |
| Degree of neighborhood noise annoyance | ||
| No noise | 241 | 28 |
| Low | 391 | 45 |
| Medium | 167 | 19 |
| High | 44 | 5 |
| Very high | 33 | 4 |