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ISSN: 2766-2276
General Science . 2022 May 10;3(5):512-515. doi: 10.37871/jbres1473.

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open access journal Mini Review

Air Pollution and Meteorological Parameters in SARS-CoV-2 Virus Spread and Transition

Mojtaba Ehsanifar1* and Mehravar Rafati2

1Anatomical Sciences Research Center, Kashan University of Medical Sciences, Kashan, Iran & Department of environmental health engineering, School of public health Iran University of medical sciences, Tehran, Iran
2Department of Medical Physics and Radiology, Faculty of Paramedicine, Kashan University of Medical Sciences, Kashan, Iran
*Corresponding author: Mojtaba Ehsanifar, Anatomical Sciences Research Center, Kashan University of Medical Sciences, Kashan, Iran & Department of environmental health engineering, School of public health Iran University of medical sciences, Tehran, Iran E-mail:
Received: 02 May 2022 | Accepted: 09 May 2022 | Published: 10 May 2022
How to cite this article: Ehsanifar M, Rafati M. Air Pollution and Meteorological Parameters in SARS-CoV-2 Virus Spread and Transition. J Biomed Res Environ Sci. 2022 May 10; 3(5): 512-515. doi: 10.37871/jbres1473, Article ID: jbres1473
Copyright:© 2022 Ehsanifar M, et al. Distributed under Creative Commons CC-BY 4.0.
Keywords
  • SARS-CoV-2
  • Air pollution
  • Meteorological parameters
  • COVID-19 infection

The purpose of this small study is to evaluate the meteorological parameters and air pollutants on the prevalence of SARS-CoV-2 in urban areas to identify conditions that can prevent or prevent future infection waves. According to studies, all meteorological parameters are significantly associated with SARS-CoV-2 cases. (Temperature, mainly affects solar radiation, UV Index (UVI), and wind speed) as well as air pollution parameters (Especially O3, SO2, and CO), but to a lesser extent. CO, SO2, and NO2 (mobility markers that refer to human interaction) it was reported all year round. It can be inferred that meteorological phenomena mainly affect the virus, both in its spread and inactivation: High relative humidity, low temperatures, low solar radiation, and low Wind speed can cause the virus to persist in the air, then, cold and dry rainy seasons can be dangerous for people who are outdoors. CO, SO2 and NO2 can be used to predict and reduce infections in the new wave of SARS-CoV-2 transmission. Adequate outdoor face masks should be considered to prevent inhalation of air pollutants and SARS-CoV-2.

The SARS-CoV-2 virus spreads relatively rapidly and infects individuals, and each type has a different rate of spread among the population. Alpha and beta variants were first identified by the WHO, followed by gamma, delta, lambda, mo, and finally, Omicron and its subsidiaries from November 2021 [1]. It has been reported to be resistant to antibodies produced by a single dose of current vaccines [2]. Therefore, new strains of SARS-CoV-2 can be expected to prevail and other waves of infection to appear worldwide [3].

WHO strategies or recommendations for minimizing or preventing SARS-CoV-2 transmission include hand hygiene, avoiding crowds, avoiding hand contact, maintaining a physical distance of at least 1 m from others, ventilated areas, wearing face masks indoors or in crowded places covering the mouth when sneezing [4], however, these measures are not sufficient because the ventilated and exhaled areas of infected people spread the virus outdoors [4,5]. Previous reports around the world indicate the effect of meteorological and atmospheric pollution parameters on the spread of SARS-CoV-2 over-pollution. Has not fully understood how it spreads outdoors in the presence of air pollutants and various meteorological conditions, where they can affect its behavior [6-10]. Parameters such as temperature and humidity have been studied [5,11,12].

In addition, the effects of particulate matter and wind speed on SARS-CoV-2 infections from March 10, 2020 to October 4, 2020 in Pakistan and its provinces were investigated. They found a positive and negative correlation between PM2.5 and infection. In addition, the wind speed had a U-shaped curved effect, was proportional at first, and when the wind speed was more than 4 km/h, the ratio was reversed (reduced cases) [13]. Another study looked at the concentrations of particulate matter and ozone on infections in Italy from February to August 2020. The findings showed that the number of infected people increased in cities that had more than PM10 or ozone for more than 100 days [14]. Analysis of data models shows that air pollution and meteorological parameters (temperature and wind speed) affected virus transmission in Saudi Arabia from March 9, 2020 to November 19, 2020 [15]. However, it is unclear whether these results are due to the disclosure of histories of pollutants that predispose individuals to health complications or airborne viruses. In another work, researchers used statistical approaches to particle analysis and SARS-CoV-2 cases in nine Asian cities and found a positive correlation between PM10 and PM2.5 for infection cases [15]. Following the COVID epidemic, major cities around the world experienced a difficult scenario that led to an increase in SARS-CoV-2 infections. In addition, the WHO and most researchers have reported that the virus is transmitted through the air [16]. Assessing environmental conditions is essential to understanding the virus's infectivity in polluted air environments and different meteorological conditions. This study seeks to investigate the role of meteorological conditions and air pollutants that affect the spread of the SARS-CoV-2 virus as a reference for exposure to new transmission waves.

SARS-CoV-2 meteorological parameters effect

One of the most important aspects of COVID-19 pandemic is its behavior over time. CO and NO2 are the primary and standard pollutants produced in incomplete fuels burned from industrial activities and engine exhaust - cars, trucks, buses, power plants and off-road equipment [17]. CO and NO2 are used as indicators to determine whether people are sheltered at home. Therefore, they can be considered as indicators of anthropogenic processes and indicators of mobility [18,19].

Recent works report that the virus decreases its infectivity when exposed to solar radiation [20] and UV-C radiation [21,22] at ground level. Even when the virus is exposed to UV-A (the terrestrial UV radiation) over 15 min, the virus inactivation happens [23], even in aerosols [24]. UV radiation damages genetic material, achieving the virus inactivation. The temperature has been correlated to SARS-CoV-2 cases; based on findings, the temperature is a key parameter [25,26]. Researchers found a negative association between daily SARS-CoV-2 cases and temperature. Solar radiation as a physical phenomenon includes UV radiation in its spectra and infrared radiation, mainly responsible for rising temperature [27]. Therefore, it could be expected that solar radiation, temperature, and UV Index (UVI) are correlated with SARS-CoV-2 simultaneously. A negative and positive correlation of temperature and relative humidity, respectively, with SARS-CoV-2 cases, has been reported in the Indian city of Mumbai [28], and relative humidity has been found to spread different kinds of viruses, including SARS-CoV-2 [29]. Water vapor is a precursor of droplets (> 100 μm), aerosols (< 100 μm), and airborne (< 5 μm), and on the other hand, these particles can also be produced from infected people respiration and be spread due to relative humidity. High relative humidity values indicate the presence of water vapor over-dry air. It is hypothesized that at low temperatures, aerosols, and small particles (airborne) could linger in the air and potentially transport viruses [4,30,31]. Wind speed is inversely correlated with infection cases [32,33]. Thus, meteorological conditions such as high relative humidity, low temperatures, low solar radiation, and low wind speed values may propitiate the virus to be spread or persist for a long time in the air.

SARS-CoV-2 cases and pollution parameters effect

Almost all air pollutants are significantly correlated with SARS-CoV-2 cases, except for PM10, but ozone was found to be inversely correlated with SARS-CoV-2 cases [10,34]. This correlation could be explained by the oxidative effect of ozone over virus and bacteria [35,36] due to the damage provoked in nucleic acids. Some previous studies have confirmed ozone inactivate SARS-CoV-2 [36,37], this could indicate ozone technologies are adequate to degrade the virus indoors and prevent infection cases. Because CO could be taken as a marker of people's mobility (because of the use of cars), this pollutant could indicate that people kept interacting and getting infected regardless of the lockdown politics of the Government. NO, NO2 and NOx show also positive correlations [12,38]. Since NO and NO2 are emitted from the exhaust and oxidized to other nitrogen oxides (NOx) by solar radiation and free radicals, these contaminants are expected to be associated with the infectivity of SARS-CoV-2 (due to people mobility). In one Study, SO2 was positively correlated with SARS-CoV-2 cases [12] but this contradicts the results reported in another study, however, they studied COVID deaths instead of SARS-CoV-2 cases [12,38]. NO2, SO2, and CO are common products of burned fuels, and as they rise together and are correlated positively to infection cases, they could be used to predict SARS-CoV-2 spread [11,39]. One of the most reported pollutants correlated with this virus in papers is PM [5,40]. It has been found that PM2.5 was negatively correlated with SARS-CoV-2 cases while PM10 demonstrated not to be significant with infection cases [41,42]. This could indicate that PM does not act as a carrier of virions, but airborne derived from water vapor does.

Recommendations to decrease or avoid SARS-CoV-2 infections

To prevent or reduce infections that come with a new wave of infections, the following considerations are helpful that authorities can send to people in cities as a warning or advice. Cold dry seasons, which include low solar radiation and UVI and consequently low temperatures, as well as rainy seasons can be dangerous for many people in outdoor activities. Months with less wind speed are more likely to provoke more infections with the virus. Due to air pollution parameters, they have less correlation with SARS-CoV-2 than meteorology. In general, the more polluted the air, the more infections there are, which means that strategies must be developed to prevent short-term exposure to pollutants. Although ozone is produced from SOx and NOx, its presence, on the contrary, due to its oxidative capacity, reduces viral infections and aggravates health problems, so people with cardiovascular disease should be exposed to avoid it. Pollutants should be used as markers to regulate mobility and interaction. Finally, even if no one is around, it is recommended to use an outdoor face mask to prevent new infections due to the spread of the virus through the air.

In conclusion, geographical location can alleviate various specific meteorological conditions that can have multifactorial effects on virus behavior. Therefore, contagion reduction policies must take into account the specific requirements of the geographical area. Regardless of government efforts to shut down, the presence of CO, SO2, and NO2 produced from the exhaust indicates mobility as an indicator of mobility and thus explains the increase in SARS-CoV-2 cases, so it can be concluded that there was no real isolation or trade disruption. All meteorological parameters were significantly associated with SARS-CoV-2 cases, mainly temperature, solar radiation, UVI and wind speed, with relationships ranging from weak to strong. High relative humidity, low solar radiation, low temperature and low wind speed values ​​can cause the virus to persist in the air for a long time. Air pollution parameters (except PM10) are significantly associated with SARS-CoV-2 cases. Therefore, it can be inferred that meteorological phenomena mainly affect both the spread and inactivation of the virus. Cold and rainy dry seasons can be dangerous for people who work outdoors. In terms of contamination parameters, CO, SO2, and O3, are better associated with SARS-CoV-2 cases. Therefore, CO, SO2 and NO2 can be used to predict and prevent the release of a new type of SARSCoV-2. Ozone can have an inactive effect on the virus, but it can predispose or worsen people's health. The more polluted the air, the more infections there are, so the use of adequate masks, even outdoors, should be considered to prevent inhalation of air pollutants and SARS-CoV-2.

  1. Jung C. Omicron: What makes the latest SARS-CoV-2 variant of concern so concerning? Journal of Virology. 2022;96(6). https://tinyurl.com/2raneuzd
  2. Hoffmann M. The Omicron variant is highly resistant against antibody-mediated neutralization: Implications for control of the COVID-19 pandemic. Cell. 2022;185(3):447-456. https://tinyurl.com/bdfkvej4
  3. Mohapatra RK, Tiwari R, Sarangi AK, Sharma SK, Khandia R, Saikumar G, Dhama K. Twin combination of Omicron and Delta variants triggering a tsunami wave of ever high surges in COVID-19 cases: A challenging global threat with a special focus on the Indian subcontinent. J Med Virol. 2022 May;94(5):1761-1765. doi: 10.1002/jmv.27585. Epub 2022 Feb 12. PMID: 35014038; PMCID: PMC9015634.
  4. Ehsanifar M. Airborne aerosols particles and COVID-19 transition. Environ Res. 2021 Sep;200:111752. doi: 10.1016/j.envres.2021.111752. Epub 2021 Jul 22. PMID: 34302822; PMCID: PMC8295061.
  5. Marquès M, Domingo JL. Positive association between outdoor air pollution and the incidence and severity of COVID-19. A review of the recent scientific evidences. Environ Res. 2022 Jan;203:111930. doi: 10.1016/j.envres.2021.111930. Epub 2021 Aug 21. PMID: 34425111; PMCID: PMC8378989.
  6. Ehsanifar M. Does exposure to air pollution fine particles and covid-19 contribute to the risk of ischemic stroke? Health. 2021;2(2):1020.
  7. Ehsanifar M, Yavari Z, Motaghedifar MR, Rezaei M. Risk of activation of human viruses lurking in ambient following COVID-19 prevention supplies excessive use. J Community Med Health Solut. 2022;3:11-15. https://tinyurl.com/yy9bjpw2
  8. Ehsanifar M, Rafati, Wang. Neurological complications related to COVID-19 infections following exposure to airborne aerosol particles. Clinical Research and Clinical Trials. 2022;5(3). https://tinyurl.com/msnpxe2w
  9. Piscitelli P. The role of outdoor and indoor air quality in the spread of SARS-CoV-2: Overview and recommendations by the research group on COVID-19 and particulate matter (RESCOP commission). Environmental Research. 2022;113038. https://tinyurl.com/3fkhf6xy
  10. Huang H, Lin C, Liu X, Zhu L, Avellán-Llaguno RD, Lazo MML, Ai X, Huang Q. The impact of air pollution on COVID-19 pandemic varied within different cities in South America using different models. Environ Sci Pollut Res Int. 2022 Jan;29(1):543-552. doi: 10.1007/s11356-021-15508-8. Epub 2021 Jul 31. PMID: 34331646; PMCID: PMC8325399.
  11. Zang ST, Luan J, Li L, Yu HX, Wu QJ, Chang Q, Zhao YH. Ambient air pollution and COVID-19 risk: Evidence from 35 observational studies. Environ Res. 2022 Mar;204(Pt B):112065. doi: 10.1016/j.envres.2021.112065. Epub 2021 Sep 15. PMID: 34534520; PMCID: PMC8440008.
  12. Fang ZG, Yang SQ, Lv CX, An SY, Guan P, Huang DS, Zhou BS, Wu W. The correlation between temperature and the incidence of COVID-19 in four first-tier cities of China: a time series study. Environ Sci Pollut Res Int. 2022 Jan 30:1–10. doi: 10.1007/s11356-021-18382-6. Epub ahead of print. PMID: 35094276; PMCID: PMC8800824.
  13. Ali Q, Raza A, Saghir S, Khan MTI. Impact of wind speed and air pollution on COVID-19 transmission in Pakistan. Int J Environ Sci Technol (Tehran). 2021 Mar 13:1-12. doi: 10.1007/s13762-021-03219-z. Epub ahead of print. PMID: 33747099; PMCID: PMC7955222.
  14. Coccia M. Effects of the spread of COVID-19 on public health of polluted cities: results of the first wave for explaining the dejà vu in the second wave of COVID-19 pandemic and epidemics of future vital agents. Environ Sci Pollut Res Int. 2021 Apr;28(15):19147-19154. doi: 10.1007/s11356-020-11662-7. Epub 2021 Jan 4. PMID: 33398753; PMCID: PMC7781409.
  15. Ben Maatoug A, Triki MB, Fazel H. How do air pollution and meteorological parameters contribute to the spread of COVID-19 in Saudi Arabia? Environ Sci Pollut Res Int. 2021 Aug;28(32):44132-44139. doi: 10.1007/s11356-021-13582-6. Epub 2021 Apr 12. PMID: 33844142; PMCID: PMC8039502.
  16. An open letter by a group of public health experts; clinicians; scientists. Covid-19: An urgent call for global "vaccines-plus" action. BMJ. 2022 Jan 2;376:01. doi: 10.1136/bmj.o1. PMID: 34980603.
  17. Mojtaba Ehsanifar. Exposure to ambient nanoparticles and COVID-19 infection. Novel Practices in Med Study. 2022;1(1).
  18. Bera B. Variation and dispersal of PM10 and PM2. 5 during COVID-19 lockdown over Kolkata metropolitan city, India investigated through HYSPLIT model. Geoscience Frontiers. 2022;13(1):101291. https://tinyurl.com/3khbvemt
  19. Peng W, Kan H, Zhou L, Wang W. Residential greenness is associated with disease severity among COVID-19 patients aged over 45 years in Wuhan, China. Ecotoxicol Environ Saf. 2022 Mar 1;232:113245. doi: 10.1016/j.ecoenv.2022.113245. Epub 2022 Jan 25. PMID: 35093816; PMCID: PMC8786605.
  20. Wondrak GT, Jandova J, Williams SJ, Schenten D. Solar simulated ultraviolet radiation inactivates HCoV-NL63 and SARS-CoV-2 coronaviruses at environmentally relevant doses. bioRxiv [Preprint]. 2021 Jul 13:2021.06.25.449831. doi: 10.1101/2021.06.25.449831. Update in: J Photochem Photobiol B. 2021 Sep 21;224:112319. PMID: 34282415; PMCID: PMC8288145.
  21. Biasin M, Pareschi G, Cavalleri A, Cavatorta C, Fenizia C. UV-C irradiation is highly effective in inactivating SARS-CoV-2 replication. Scientific Reports. 2021. https://tinyurl.com/2hrfbdwc
  22. Storm N, McKay LGA, Downs SN, Johnson RI, Birru D, de Samber M, Willaert W, Cennini G, Griffiths A. rapid and complete inactivation of SARS-CoV-2 by ultraviolet-C irradiation. Sci Rep. 2020 Dec 30;10(1):22421. doi: 10.1038/s41598-020-79600-8. PMID: 33380727; PMCID: PMC7773738.
  23. Huang Y, Xiao S, Song D, Yuan Z. Evaluating the virucidal activity of four disinfectants against SARS-CoV-2. Am J Infect Control. 2022 Mar;50(3):319-324. doi: 10.1016/j.ajic.2021.10.035. Epub 2021 Nov 12. PMID: 34774899; PMCID: PMC8585555.
  24. Richter WR, Sunderman MM, Mera TO, O'Brien KA, Morgan K, Streams S. Evaluation of environmental conditions as a decontamination approach for SARS-CoV-2 when applied to common library, archive and museum-related materials. J Appl Microbiol. 2022 Apr;132(4):3405-3415. doi: 10.1111/jam.15468. Epub 2022 Feb 15. PMID: 35094472.
  25. Habib G, Shah Zeb Khan M, Gul H, Hayat A, Ur Rehman M. A persistent high ambient temperature waned the community spread of severe acute respiratory syndrome coronavirus-2 in Pakistan. New Microbes New Infect. 2022 Jan;45:100961. doi: 10.1016/j.nmni.2022.100961. Epub 2022 Jan 24. PMID: 35096398; PMCID: PMC8784618.
  26. Wang D, Wu X, Li C, Han J, Yin J. The impact of geo-environmental factors on global COVID-19 transmission: A review of evidence and methodology. Sci Total Environ. 2022 Jun 20;826:154182. doi: 10.1016/j.scitotenv.2022.154182. Epub 2022 Feb 26. PMID: 35231530; PMCID: PMC8882033.
  27. Lai T, Wang W. Attribution of community emergency volunteer behaviour during the covid-19 pandemic: A study of community residents in shanghai, china. Voluntas. 2022 Jan 10:1-13. doi: 10.1007/s11266-021-00448-1. Epub ahead of print. PMID: 35035120; PMCID: PMC8747455.
  28. Shetty S. Impact of key meteorological parameters on the spread of COVID-19 in Mumbai. Correlation and Regression Analysis. 2022. https://tinyurl.com/2p8dftud
  29. García-Arroyo L, Prim N, Del Cuerpo M, Marín P, Roig MC, Esteban M, Labeaga R, Martí N, Berengua C, Gich I, Navarro F, Rabella N. Prevalence and seasonality of viral respiratory infections in a temperate climate region: A 24-year study (1997-2020). Influenza Other Respir Viruses. 2022 Feb 16. doi: 10.1111/irv.12972. Epub ahead of print. PMID: 35170253.
  30. Karaböce B. Prevention of viral transmission by infrared techniques. 2022. https://tinyurl.com/27b6m9hs
  31. Wilson AM, Sleeth DK, Schaefer C, Jones RM. Transmission of respiratory viral diseases to health care workers: Covid-19 as an example. Annu Rev Public Health. 2022 Apr 5;43:311-330. doi: 10.1146/annurev-publhealth-052120-110009. Epub 2022 Jan 7. PMID: 34995130.
  32. Zhou N, Dai H, Zha W, Lv Y. The impact of meteorological factors and PM2.5 on COVID-19 transmission. Epidemiol Infect. 2022 Jan 21;150:e38. doi: 10.1017/S0950268821002570. PMID: 35057873; PMCID: PMC8886088.
  33. Coccia M. The spread of the novel coronavirus disease-2019 in polluted cities: Environmental and demographic factors to control for the prevention of future pandemic diseases, in socioeconomic dynamics of the covid-19 crisis. 2022;351-369. https://tinyurl.com/3f84sj87
  34. Yan Y. Can tourism sustain itself through the pandemic: Nexus between tourism, COVID-19 cases and air quality spread in the ‘Pineapple State’ Hawaii. Current Issues in Tourism. 2022;25(3):421-440. https://tinyurl.com/rzupnrvc
  35. Premjit Y, Sruthi NU, Pandiselvam R, Kothakota A. Aqueous ozone: Chemistry, physiochemical properties, microbial inactivation, factors influencing antimicrobial effectiveness, and application in food. Compr Rev Food Sci Food Saf. 2022 Mar;21(2):1054-1085. doi: 10.1111/1541-4337.12886. Epub 2022 Jan 24. PMID: 35068040.
  36. Costa LRC, Féris LA. Use of ozonation technology to combat viruses and bacteria in aquatic environments: Problems and application perspectives for SARS-CoV-2. Environ Technol. 2022 Feb 13;1-13. doi: 10.1080/09593330.2022.2034981. Epub ahead of print. PMID: 35078388.
  37. Tizaoui C. Ozone for SARS-CoV-2 inactivation on surfaces and in liquid cell culture media. Journal of hazardous materials. 2022;128251. https://tinyurl.com/mwb492h3
  38. Choi W, Kim KY. Correlation between COVID-19 infection rate and atmospheric environmental factors in seoul metropolitan city, South Korea. 2022. https://tinyurl.com/2c8szwnn
  39. Bauleo L, Giannini S, Ranzi A, Nobile F, Stafoggia M, Ancona C, Iavarone I, The EpiCovAir Study Group. A methodological approach to use contextual factors for epidemiological studies on chronic exposure to air pollution and covid-19 in italy. Int J Environ Res Public Health. 2022 Mar 1;19(5):2859. doi: 10.3390/ijerph19052859. PMID: 35270551; PMCID: PMC8910469.
  40. Veronesi G. Long-term exposure to air pollution and COVID-19 incidence: a prospective study of residents in the city of Varese, Northern Italy. Occupational and environmental medicine. 2022;79(3). https://tinyurl.com/3s88n2vn
  41. Jasim IA, Fileeh MK, Ebrahhem MA, Al-Maliki LA, Mamoori SK, Al-Ansari N. Geographically weighted regression model for physical, social, and economic factors affecting the COVID-19 pandemic spreading. Environ Sci Pollut Res Int. 2022 Mar 4:1–14. doi: 10.1007/s11356-022-18564-w. Epub ahead of print. PMID: 35246792; PMCID: PMC8896849.
  42. Ibarra-Espinosa S, Dias de Freitas E, Ropkins K, Dominici F, Rehbein A. Negative-binomial and quasi-Poisson regressions between COVID-19, mobility and environment in São Paulo, Brazil. Environ Res. 2022 Mar;204(Pt D):112369. doi: 10.1016/j.envres.2021.112369. Epub 2021 Nov 9. PMID: 34767818; PMCID: PMC8577054.

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