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Effect of ambient air pollutants and meteorological variables on COVID-19 incidence

Part of: SARS-CoV-2/COVID-19

Published online by Cambridge University Press:  11 May 2020

Ying Jiang ,
Xiao-Jun Wu  and
Yan-Jun Guan Open the ORCID record for Yan-Jun Guan [Opens in a new window]
Ying Jiang
Affiliation:
Department of Neurosurgery, Shanghai Chang Zheng Hospital affiliated with China Second Military Medical University, Shanghai, China
Xiao-Jun Wu
Affiliation:
Department of Neurosurgery, Shanghai Cancer Center, Shanghai Fu-Dan University School of Medicine, Shanghai, China
Yan-Jun Guan*
Affiliation:
Department of Otorhinolaryngology, Shanghai Rui-Jin Hospital, Shanghai Jiaotong University School of Medicine, Shanghai, China
*
Author for correspondence: Yan-Jun Guan, E-mail: [email protected]
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Abstract

Objective:

To determine whether ambient air pollutants and meteorological variables are associated with daily COVID-19 incidence.

Design:

A retrospective cohort from January 25 to February 29, 2020.

Setting:

Cities of Wuhan, Xiaogan, and Huanggang, China.

Patients:

The COVID-19 cases detected each day.

Methods:

We collected daily data of COVID-19 incidence, 8 ambient air pollutants (particulate matter of ≤2.5 µm [PM2.5], particulate matter ≤10 µm [PM10], sulfur dioxide [SO2], carbon monoxide [CO], nitrogen dioxide [NO2], and maximum 8-h moving average concentrations for ozone [O3-8h]) and 3 meteorological variables (temperature, relative humidity, and wind) in China’s 3 worst COVID-19–stricken cities during the study period. The multivariate Poisson regression was performed to understand their correlation.

Results:

Daily COVID-19 incidence was positively associated with PM2.5 and humidity in all cities. Specifically, the relative risk (RR) of PM2.5 for daily COVID-19 incidences were 1.036 (95% confidence interval [CI], 1.032–1.039) in Wuhan, 1.059 (95% CI, 1.046–1.072) in Xiaogan, and 1.144 (95% CI, 1.12–1.169) in Huanggang. The RR of humidity for daily COVID-19 incidence was consistently lower than that of PM2.5, and this difference ranged from 0.027 to 0.111. Moreover, PM10 and temperature also exhibited a notable correlation with daily COVID-19 incidence, but in a negative pattern The RR of PM10 for daily COVID-19 incidence ranged from 0.915 (95% CI, 0.896–0.934) to 0.961 (95% CI, 0.95–0.972, while that of temperature ranged from 0.738 (95% CI, 0.717–0.759) to 0.969 (95% CI, 0.966–0.973).

Conclusions:

Our data show that PM2.5 and humidity are substantially associated with an increased risk of COVID-19 and that PM10 and temperature are substantially associated with a decreased risk of COVID-19.

Type
Original Article
Information
Infection Control & Hospital Epidemiology , Volume 41 , Issue 9 , September 2020 , pp. 1011 - 1015
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Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited.
Copyright
© 2020 by The Society for Healthcare Epidemiology of America. All rights reserved.

Since it first appeared in Wuhan, China, in December 2019, coronavirus disease 2019 (COVID-19) has become a worldwide pandemic.Reference Zhu, Zhang and Wang1–Reference Li, Guan and Wu3 Severe acute respiratory syndrome coronavirus-2 (SARS-CoV-2) is the pathogen of the COVID-19, and it now poses a threat to global health. As of March 31, 2020, 785,979 confirmed cases and 37,810 deaths related to COVID-19 had been recorded among 204 countries.4

Ambient air pollution is a well-known threat to human health, and sufficient evidence is available to support the close correlation between pollutants and increased risks of numerous diseases.Reference Liu, Chen and Sera5–Reference Zhao, Johnston, Salimi, Kurabayashi and Negishi7 In particular, ambient air pollutants have raised concerns over their association with infectious diseases, some of which have caused local epidemics.Reference You, Tong, Neoh, Dai and Wang8–Reference Su, Wu, Geng, Zhao, Liu and Liu10 It has been speculated that airborne pollutants provide “condensation nuclei” to which virus particles can attach.Reference Lee, Saravia and You11 This hypothesis is supported by the influenza–PM2.5 correlation.Reference Su, Wu, Geng, Zhao, Liu and Liu10,Reference Liang, Fang and Pan12,Reference Feng, Li, Sun, Zhang and Wang13 Although SARS-CoV-2 is known to be transmitted human to human by infectious secretions,Reference Li, Guan and Wu3 these secretions can be transferred in many different ways. Thus, whether ambient air pollutants could affect the transmission of SARS-CoV-2 is an urgent question. Additionally, meteorological factors such as humidity and temperature have also been suggested to enhance air pollutionReference Moriyama, Hugentobler and Iwasaki14,Reference Xiang, Mertz and Arena15 and to promote transmission of infectious disease.Reference Moriyama, Hugentobler and Iwasaki14 Their role in SARS-CoV-2 transmission, however, remains largely unknown.

Wuhan is one of the most populated cities in China, and it has a subtropical humid monsoon climate. Due to rapid industrialization and urbanization, both the concentration and composition of air pollutants have become higher and more complicated,Reference Zeng, Lyu and Guo16,Reference Xing, Chen and Tian17 and pollution has already caused severe health problems for the local population.Reference Qian, He and Lin18 A previous study demonstrated that a tuberculosis surge in Wuhan was associated with worsening air pollution and weather.Reference Yang, Duan, Wang, Zhang and Jiang19 Nevertheless, no study has explored the association of Wuhan local air quality and/or meteorological data with COVID-19 incidence.

Due to the severe air pollution, high COVID-19, and the citywide lockdown, Wuhan is a good research setting in which to investigate this issue. We hypothesized the potential association of air pollutants and meteorological variables with daily COVID-19 incidence, and we sought to discover factors influencing the SARS-CoV-2 pandemic. We also enrolled Xiaogan and Huanggang in the current study because they were the second- and third-worst COVID-19–stricken cities in the province of Wuhan, respectively.

Methods

Data sources

Ambient air pollutants and meteorological variables

The daily air quality index (AQI) and average concentration data for 6 ambient air pollutants data were collected from the AQI platform website (https://www.aqistudy.cn). These pollutants included particulate matter of ≤2.5 µm (PM2.5), particulate matter ≤10 µm (PM10), sulfur dioxide (SO2]), carbon monoxide (CO), nitrogen dioxide (NO2), and maximum 8-h moving average concentrations for ozone (O3-8h). We calculated their daily concentrations by averaging the hourly concentrations from all stations in the city to represent citywide pollution exposure. The website uses the standard for particulate matter from the US Environmental Protection Agency (EPA).20 The daily temperature, relative humidity, and wind (in Beaufort number) were also obtained from the AQI platform, and we averaged the hourly data from all stations in the city to represent the citywide weather condition.

Population

The study population included a retrospective cohort of COVID-19 patients in Wuhan, Xiaogan and Huanggang, China, between January 25 and February 29, 2020. The population of each city was obtained from the China National Bureau of Statistics. Because all 3 cities were under a citywide lockdown during the entire study period, the population size was considered stable.

COVID-19 diagnosis and daily incidence

The daily COVID-19 incidence was obtained from the website of Health Commission of Hubei Province from January 25, 2020, onward.21 The COVID-19 diagnoses were made solely based on nucleic acid test from January 25 to February 11. Beginning February 12, clinical symptoms along with chest computed tomography (CT) scans were used for COVID-19 diagnoses.Reference Ravindranath22,Reference Wang23 When COVID-19 was diagnosed, the patient was immediately placed in a single isolation ward. These remained in quarantine until they fully recovered or died. A previous epidemiological study demonstrated that the median incubation period of SARS-CoV-2 is 4 days.Reference Guan, Ni and Hu24 Thus, we applied this correlation to analyze the relationship between COVID-19 incidence per day and the air pollution data 4 days prior.

Data analysis

We conducted a time-series analysis to examine the associations of the pollutants and meteorological variables with COVID-19 incidence per day. We first performed a descriptive analysis that provided the information for COVID-19 incidence, 6 air pollutants, and 3 meteorological variables in all 3 cities. We then used multivariate Poisson regression models to evaluate the association of pollutants and meteorological variables with COVID-19 incidence in 3 cities on a daily basis. All analyses were conducted using SPSS version 20.0 software (SPSS, Chicago, IL). Bonferroni correction was used for data correction, and a P value <.0056 was considered as statistically significant.

Results

Table 1 lists the descriptive statistics for daily COVID-19 incidence, air pollutant concentration, and meteorological variables in Wuhan, Xiaogan, and Huanggang. Starting January 26, Wuhan had 80 newly diagnosed COVID-19 cases, Xiaogan had 45, and Huanggang had 32. All cities reached their peak daily incidence between February 12 and 13. Thereafter, the daily incidences started to drop, and they reached their lowest by the end of the study.

Table 1. Descriptive statistics of coronavirus disease 2019 (COVID-19) incidences per day, three meteorological variables and six ambient air pollutants conditions from 25th Jan to 29th Feb 2020 in Wuhan, XiaoGan and HuangGang, China (total 36 days). Min., Max., and SEM stand for minimum, maximum and standard error of mean, respectively

Next, multiple linear relationships were used to evaluate the association of the daily COVID-19 incidence with air pollutants and meteorological variables in each city (Table 2). Due to the change in case definition on February 12, the COVID-19 incidence surged on February 12 and 13.Reference Ravindranath22,Reference Wang23 Additionally, Xiaogan and Huanggang showed negative COVID-19 incidences on February 17 and 19. Thus, we excluded data from these dates in our multiple linear regression analysis. First, in Wuhan (Table 2), all air pollutants (except SO2) were strongly associated with daily COVID-19 incidence (all P < .001). Among them, PM10 exhibited a negative association with COVID-19 incidence (relative risk [RR], 0.964; 95% confidence interval [CI], 0.961–0.967). Among the remaining pollutants, PM2.5 was a main effector on incidence increase (RR, 1.036; 95% CI, 1.032–1.039). Among the 3 meteorological variables, temperature (RR, 0.969; 95% CI, 0.966–0.973) and humidity (RR, 1.009; 95% CI, 1.007–1.011) were significantly associated with daily COVID-19 incidence (both P < .001).

Table 2. The association between the coronavirus disease 2019 (COVID-19) incidence per day and six ambient air pollutants/three meteorological variables from 25th Jan to 29th Feb 2020 in Wuhan, XiaoGan and HuangGang, China (total 35 days). RR and 95% CI stand for relative ratio and 95% confidence interval, respectively. The number marked with # indicated association between factors and COVID-19 incidence were NOT statistically significant (P>0.0056). Meanwhile, the p-value of those not marked data were <0.01 and considered statistically significant

In XiaoGan, all air pollutants were notably associated with daily COVID-19 incidence (all P < .001). Similar to that of Wuhan, both PM10 (RR, 0.961; 95% CI, 0.95–0.972) and temperature (RR, 0.89; 95% CI, 0.871–0.911) remained negatively correlated with daily COVID-19 incidence. Among the remaining air pollutants, COVID-19 incidence increase was also significantly associated with PM2.5 (RR, 1.059; 95% CI, 1.046–1.072). For 3 meteorological variables, humidity (RR, 1.013; 95% CI, 1.007–1.019) and temperature (RR, 0.89; 95% CI, 0.871–0.911) were the 2 main factors associated with COVID-19 incidence.

In Huanggang, all ambient air pollutants (expect NO2) were significantly associated with daily COVID-19 incidence (all P < .001). Similar to Wuhan and Xiaogan, PM10 remained negatively correlated with the daily COVID-19 incidence (RR, 0.915; 95% CI, 0.896–0.934). Among the remaining air pollutants, PM2.5 had the strongest correlation with COVID-19 incidence (RR, 1.144; 95% CI, 1.12–1.169). All meteorological variables were also significantly associated with daily COVID-19 incidence (both P < .001). Similar to the previous 2 cities, a negative association was detected between COVID-19 and temperature (RR, 0.738; 95% CI, 0.717–0.759) and between COVID-19 and wind level (RR, 0.79; 95% CI, 0.697–0.896).

Discussion

Ambient air pollution and meteorological variables can affect viral transmission; however, they have not yet been examined for the presence of SARS-CoV-2. In the current study, we have provided an initial assessment of the potential effects of ambient air pollutants and meteorological variables on the incidence of COVID-19 day by day from January 25 to February 29, 2020. Overall, based on data from China’s 3 worst COVID-19–stricken cities, COVID-19 incidence was negatively associated with PM10 and temperature. Meanwhile, a positive association was observed between COVID-19 and PM2.5 and relative humidity.

Particulate matter is a mixture of both solid particles and liquid droplets suspended in the air. Although it is not the sole cause of respiratory illness, previous studies have demonstrated that particulate matter is a strong environmental determinant of viral transmissions. For example, a close correlation was discovered between human influenza cases and PM2.5 concentrations in epidemiological studies based in big cities such as Beijing,Reference Liang, Fang and Pan12 Hong Kong,Reference Qiu, Yu and Tian25 and Brisbane.Reference Xu, Hu, Williams, Clements, Kan and Tong26 Its potential mechanisms are believed to damage bronchial immunityReference Ma, Song and Guo27 and epithelial cell integrity,Reference Jaspers, Ciencewicki and Zhang28 which enhances viral attachment to and replication in the bronchus.Reference Jaspers, Ciencewicki and Zhang28 In the current study, although our data could not reveal whether particulate matter promotes SARS-CoV-2 transmission, we observed that PM2.5 is the only air pollutant that is consistently associated with increased COVID-19 incidence in all cities. This finding agrees with the data from a previous influenza study. Contrary to PM2.5, increased PM10 concentration was associated with decreased COVID-19 incidence. We believe this phenomenon to be a diameter-related effect. As shown by previous study, the receptor for both SARS-CoV-2 and SARS-CoV binding is the angiotensin-converting enzyme 2, which concentrates on type II alveolar cells.Reference Zhou, Yang and Wang29 However, type II alveolar cells are located in the alveoli, which can only be reached by particles with a diameter <5 µm.Reference Brankston, Gitterman, Hirji, Lemieux and Gardam30 Thus, small airborne pollutants, such as PM2.5, are particularly harmful because they are more likely to penetrate the respiratory tract all the way to the alveolar region unfiltered.Reference Tellier31,Reference Hinds32 For larger particulate matter, penetration ability decreases dramatically when size increases; starting at 20 µm and beyond, particulate matter is not able to penetrate below the trachea.Reference Hinds32 Although all particulate matter might provide condensation nuclei for viral attachment,Reference Lee, Saravia and You11 PM2.5 deliver SARS-CoV-2 to their target cells in the alveoli, which is unreachable to PM10. This size factor might also explain our finding that PM2.5 correlates with COVID-19 incidence in a positive pattern while that of PM10 is negative. Future epidemiological studies in other countries and areas with similar population density but different PM2.5 and PM10 concentrations could be used to validate this result.

So far, a number of studies have indicated a negative effect of ambient temperature and humidity on the viral viability and transmission. For example, low humidity increases influenza viability in the aerosolReference Brankston, Gitterman, Hirji, Lemieux and Gardam30 and impairs the innate antiviral defense of the host,Reference Kudo, Song and Yockey33 which promotes influenza transmission. Meanwhile, temperature has the same effect as humidity on influenza.Reference Lowen, Mubareka, Steel and Palese34 Similar to influenza, epidemiological studies have also demonstrated that the transmission of SARS-CoV-2 is more efficient in low temperatures and at low humidity.Reference Qi, Xiao and Shi35,Reference Liu, Zhou and Yao36 This hypothesis was supported by the results from a laboratory study; SARS-CoV was more likely to be inactivated in higher temperature and humidity.Reference Casanova, Jeon, Rutala, Weber and Sobsey37,Reference Chan, Peiris, Lam, Poon, Yuen and Seto38 In the current study, our data agree with previous findings that temperature is negatively associated with COVID-19 incidence. However, our results regarding humidity do not agree with those from previous studies. Recently, an outbreak of COVID-19 was reported in a public bath center in China.Reference Luo, Yao and Zhang39 Since the bath center was extremely humid, SARS-CoV-2 should have been inactivated quickly; however, this was not the case. Thus, our results support this finding and suggest that the study of differences between SARS-CoV-2 and other viruses is warranted in future studies.

Whether SARS-CoV-2 can be transmitted via airborne droplets remains controversial.40 Recently, Luo et alReference Luo, Yao and Zhang39 reported a COVID-19 outbreak in a public bath center in China, which suggests the role of ambient droplet in SARS-CoV-2 transmission in conditions of high relative humidity. Later, van Doremalen et alReference van Doremalen, Bushmaker and Morris41 also demonstrated that, under laboratory conditions, SARS-CoV-2 is viable in aerosol droplets for at least 3 hours, which provides theoretical evidence for how SARS-CoV-2 transmission in that environment. However, some researchers dispute ambient droplet transmission because SARS-CoV-2 is not present in air samples obtained from the rooms of hospitalized COVID-19 patients.Reference van Doremalen, Bushmaker and Morris41 Most studies thus far have also reported that healthy people are infected by touching contaminated objects40 and that SARS-CoV-2 is stable on copper, cardboard, plastic, and stainless-steel surfaces for up to 72 hours.Reference van Doremalen, Bushmaker and Morris41 In the current study, we have shown that ambient air pollutants, especially PM2.5, are closely associated with COVID-19 incidence, which supports the hypothesis regarding airborne droplet transmission of SARS-CoV-2. However, the viability of SARS-CoV-2 attaching to PM2.5 remains largely unknown. Further studies are required to investigate the extent of SARS-CoV-2 transmission via airborne droplets.

Winter features overlap multiple viral seasons at various degrees. Previous studies have suggested that epidemics of cocirculating viral infections can interfere with each other.Reference van Asten, Bijkerk and Fanoy42,Reference Zheng, Song, Li, Zhang and Wang43 For example, influenza A could overlap coronavirus outbreaks.Reference van Asten, Bijkerk and Fanoy42 Thus, it is reasonable to hypothesize that COVID-19 incidence might also be significantly affected by other cocirculating viruses. Additionally, 1 study concluded that 2 SARS-CoV-2 strains are cocirculating in Italy.Reference Stefanelli, Faggioni and Lo Presti44 Whether these 2 strains affect the infectious ability of the other remains unknown. Further study is required to fully elucidate this issue.

The current study has several limitations. First, because the ambient PM2.5 is a mixture of solid particles and liquid droplets, the exact components of PM2.5 that may promote coronavirus transmission remain unknown. Second, due to the relatively short study period and imperfect daily reporting practices, our results are vulnerable to changes resulting from the emergence of more detailed data. Third, we studied only 9 variables in the current study. A number of other variables could potentially have affected COVID-19 transmission; thus, our study can only provide preliminary information on the association between COVID-19 and air pollutants or other meteorological variables. In a future study, we plan to gather data from more countries and regions to remedy these data gaps. Fourth, because detailed information from confirmed COVID-19 patients was not available, we were unable to determine how underlying health problems might promote COVID-19 infection. Thus, a longer study period might have affected our results. Moreover, winter overlapped the entire study period, which limited all meteorological variables (especially temperature) to a narrow band. Thus, further study is urgently needed further elucidate these issues.

In conclusion, our findings consistently suggest that increased temperature and airborne PM2.5 concentration are associated with increased daily COVID-19 incidence. Meanwhile, a negative association was observed between COVID-19 incidence and relative humidity and airborne PM10 concentration. In the context of the worldwide COVID-19 pandemic, our findings might provide some information for COVID-19 personal protection and transmission reduction.

Acknowledgments

We thank all medical staff and workers who risk their lives to save the general population from SARS-CoV-2.

Financial support

No financial support was obtained for the current study.

Conflicts of interest

All authors report no conflicts of interest relevant to this article.

Footnotes

a

Authors of equal contribution.

References

Zhu, N, Zhang, D, Wang, W, et al.A novel coronavirus from patients with pneumonia in China, 2019. N Engl J Med 2020;382:727–733.CrossRefGoogle Scholar
Rodríguez-Morales, AJ, MacGregor, K, Kanagarajah, S, Patel, D, Schlagenhauf, P. Going global—travel and the 2019 novel coronavirus. Trav Med Infect Dis 2020;33:101578.CrossRefGoogle ScholarPubMed
Li, Q, Guan, X, Wu, P, et al.Early transmission dynamics in Wuhan, China, of novel coronavirus-infected pneumonia. N Engl J Med 2020;382:1199–1207.CrossRefGoogle ScholarPubMed
Cases and latest updates. Coronavirus disease 2019 (COVID-19), 2020. Centers for Disease Control and Prevention website. https://www.cdc.gov/coronavirus/2019-ncov/cases-updates/world-map.html. Published 2020. Accessed May 11, 2020.Google Scholar
Liu, C, Chen, R, Sera, F, et al.Ambient particulate air pollution and daily mortality in 652 cities. N Engl J Med 2019;381:705–715.CrossRefGoogle ScholarPubMed
Rückerl, R, Schneider, A, Breitner, S, Cyrys, J, Peters, A. Health effects of particulate air pollution: a review of epidemiological evidence. Inhal Toxicol 2011;23:555–592.CrossRefGoogle ScholarPubMed
Zhao, B, Johnston, F, Salimi, F, Kurabayashi, M, Negishi, K. Short-term exposure to ambient fine particulate matter and out-of-hospital cardiac arrest: a nationwide case-crossover study in Japan. Lancet Planet Health 2020;4:e15–23.CrossRefGoogle ScholarPubMed
You, S, Tong, Y, Neoh, K, Dai, Y, Wang, C. On the association between outdoor PM(2.5) concentration and the seasonality of tuberculosis for Beijing and Hong Kong. Environ Pollut 2016;218:1170–1179.CrossRefGoogle ScholarPubMed
Horne, BA-O, Joy, EA, Hofmann, MG, et al.Short-term elevation of fine particulate matter air pollution and acute lower respiratory infection. Am J Respir Crit Care Med 2018;198:759–766.CrossRefGoogle ScholarPubMed
Su, W, Wu, X, Geng, X, Zhao, X, Liu, Q, Liu, T. The short-term effects of air pollutants on influenza-like illness in Jinan, China. BMC Public Health 2019;19:1319.CrossRefGoogle ScholarPubMed
Lee, G, Saravia, J, You, D, et al.Exposure to combustion generated environmentally persistent free radicals enhances severity of influenza virus infection. Part Fibre Toxicol 2014;11:57.CrossRefGoogle ScholarPubMed
Liang, Y, Fang, L, Pan, H, et al.PM2.5 in Beijing—temporal pattern and its association with influenza. Environ Health 2014;13:102.CrossRefGoogle ScholarPubMed
Feng, C, Li, J, Sun, W, Zhang, Y, Wang, Q. Impact of ambient fine particulate matter (PM2.5) exposure on the risk of influenza-like-illness: a time-series analysis in Beijing, China. Environ Health 2016;15:17.CrossRefGoogle ScholarPubMed
Moriyama, M, Hugentobler, W, Iwasaki, A. Seasonality of respiratory viral infections. Annu Rev Virol 2020 Mar 20 [Epub ahead of print]. doi: 10.1146/annurev-virology-012420-022445.CrossRefGoogle ScholarPubMed
Xiang, H, Mertz, K, Arena, V, et al.Estimation of short-term effects of air pollution on stroke hospital admissions in Wuhan, China. PLoS One 2013;8:e61168.CrossRefGoogle ScholarPubMed
Zeng, P, Lyu, XP, Guo, H, et al.Causes of ozone pollution in summer in Wuhan, central China. Environ Pollut 2018;241.Google Scholar
Xing, X, Chen, Z, Tian, Q, et al.Characterization and source identification of PM(2.5)-bound polycyclic aromatic hydrocarbons in urban, suburban, and rural ambient air, central China during summer harvest. Ecotoxicol Environ Saf 2020;191. doi: 10.1016/j.ecoenv.2020.110219.CrossRefGoogle ScholarPubMed
Qian, Z, He, Q, Lin, H, et al.Association of daily cause-specific mortality with ambient particle air pollution in Wuhan, China. Environ Res 2007;105:380–389.CrossRefGoogle ScholarPubMed
Yang, X, Duan, Q, Wang, J, Zhang, Z, Jiang, G. Seasonal variation of newly notified pulmonary tuberculosis cases from 2004 to 2013 in Wuhan, China. PLoS One 2014;9:e108369.CrossRefGoogle ScholarPubMed
What are the Air Quality Standards for PM? US Enviromental Protection Agency website. https://www3.epa.gov/region1/airquality/pm-aq-standards.html. Published 2019. Accessed May 11, 2020.Google Scholar
The realtime coronovirus epidemiological situationof Hubei province [in Chinese]. Health Commission of the Hubei Province website. http://wjw.hubei.gov.cn/bmdt/ztzl/fkxxgzbdgrfyyq/xxfb/index.shtml.Google Scholar
Ravindranath, P. COVID-19: China once again changes case definition in Hubei Province. 2020. Science Chronicle website. https://journosdiary.com/2020/02/20/covid-19-china-changes-case-definition-hubei/. Published February 20, 2020. Accessed May 11, 2020.Google Scholar
Wang, V. How many coronavirus cases in China? Officials tweak the answer. The New York Times website. https://www.nytimes.com/2020/02/12/world/asia/china-coronavirus-cases.html. Published February 12, 2020. Accessed May 11, 2020.Google Scholar
Guan, W-J, Ni, Z-Y, Hu, Y, et al.Clinical characteristics of coronavirus disease 2019 in China. N Engl J Med 2020;382:1708–1720.CrossRefGoogle ScholarPubMed
Qiu, H, Yu, I, Tian, L, et al.Effects of coarse particulate matter on emergency hospital admissions for respiratory diseases: a time-series analysis in Hong Kong. Environ Health Perspect 2012;120:572–576.CrossRefGoogle ScholarPubMed
Xu, Z, Hu, W, Williams, G, Clements, A, Kan, H, Tong, S. Air pollution, temperature, and pediatric influenza in Brisbane, Australia. Environ Int 2013;59:384–388.CrossRefGoogle ScholarPubMed
Ma, J, Song, S, Guo, M, et al.Long-term exposure to PM2.5 lowers influenza virus resistance via down-regulating pulmonary macrophage Kdm6a and mediates histone modification in IL-6 and IFN-β promoter regions. Biochem Biophys Res Commun 2017;493:1122–1128.CrossRefGoogle ScholarPubMed
Jaspers, I, Ciencewicki, J, Zhang, W, et al.Diesel exhaust enhances influenza virus infections in respiratory epithelial cells. Toxicol Sci 2005;85:990–1002.CrossRefGoogle ScholarPubMed
Zhou, P, Yang, X, Wang, X, et al.A pneumonia outbreak associated with a new coronavirus of probable bat origin. Nature 2020;579:270–273.CrossRefGoogle ScholarPubMed
Brankston, G, Gitterman, L, Hirji, Z, Lemieux, C, Gardam, M. Transmission of influenza A in human beings. Lancet Infect Dis 2007;7:257–265.CrossRefGoogle ScholarPubMed
Tellier, R. Aerosol transmission of influenza A virus: a review of new studies. J R Soc Interface 2009;6:S783–790.CrossRefGoogle ScholarPubMed
Hinds, W. Aerosol Technology, second ed.New York: John Wiley and Sons; 1999.Google Scholar
Kudo, E, Song, E, Yockey, L, et al.Low ambient humidity impairs barrier function and innate resistance against influenza infection. Proc Nat Acad Sci U S A 2019;116:10905–10910.CrossRefGoogle ScholarPubMed
Lowen, A, Mubareka, S, Steel, J, Palese, P. Influenza virus transmission is dependent on relative humidity and temperature. PLoS Path 2007;3:1470–1476.CrossRefGoogle ScholarPubMed
Qi, H, Xiao, S, Shi, R, et al.COVID-19 transmission in mainland China is associated with temperature and humidity: a time-series analysis. Sci Total Environ 2020;728:138778.CrossRefGoogle ScholarPubMed
Liu, J, Zhou, J, Yao, J, et al.Impact of meteorological factors on the COVID-19 transmission: a multicity study in China. Sci Total Environ 2020;726:138513.CrossRefGoogle Scholar
Casanova, L, Jeon, S, Rutala, W, Weber, D, Sobsey, M. Effects of air temperature and relative humidity on coronavirus survival on surfaces. Appl Environ Microbiol 2010;76:2712–2717.CrossRefGoogle ScholarPubMed
Chan, K, Peiris, J, Lam, S, Poon, L, Yuen, K, Seto, W. The effects of temperature and relative humidity on the viability of the SARS coronavirus. Adv Virol 2011;2011:734690.CrossRefGoogle ScholarPubMed
Luo, C, Yao, L, Zhang, L, et al.Possible transmission of severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2) in a public bath center in Huai’an, Jiangsu Province, China. JAMA Network Open 2020;3:e204583. doi: 10.1001/jamanetworkopen.2020.4583.CrossRefGoogle Scholar
66. Coronavirus disease (COVID-2019): situation report, 2020. World Health Organization website. https://www.who.int/docs/default-source/coronaviruse/situation-reports/20200326-sitrep-66-covid-19.pdf?sfvrsn=81b94e61_2. Published March 26, 2020. Accessed May 11, 2020.Google Scholar
van Doremalen, N, Bushmaker, T, Morris, DH, et al.Aerosol and surface stability of SARS-CoV-2 as compared with SARS-CoV-1. N Engl J Med 2020;382:1564–1567.CrossRefGoogle ScholarPubMed
van Asten, L, Bijkerk, P, Fanoy, E, et al.Early occurrence of influenza A epidemics coincided with changes in occurrence of other respiratory virus infections. Influenza Other Respir Viruses 2016;10:14–26.CrossRefGoogle ScholarPubMed
Zheng, X, Song, Z, Li, Y, Zhang, J, Wang, XL. Possible interference between seasonal epidemics of influenza and other respiratory viruses in Hong Kong, 2014–2017. BMC Infect Dis 2017;17:772.CrossRefGoogle Scholar
Stefanelli, P, Faggioni, G, Lo Presti, A, et al.Whole genome and phylogenetic analysis of two SARS-CoV-2 strains isolated in Italy in January and February 2020: additional clues on multiple introductions and further circulation in Europe. Euro Surveill 2020;25:2000305. doi: 10.2807/1560-7917.ES.2020.25.13.2000305.CrossRefGoogle ScholarPubMed
Figure 0

Table 1. Descriptive statistics of coronavirus disease 2019 (COVID-19) incidences per day, three meteorological variables and six ambient air pollutants conditions from 25th Jan to 29th Feb 2020 in Wuhan, XiaoGan and HuangGang, China (total 36 days). Min., Max., and SEM stand for minimum, maximum and standard error of mean, respectively

Figure 1

Table 2. The association between the coronavirus disease 2019 (COVID-19) incidence per day and six ambient air pollutants/three meteorological variables from 25th Jan to 29th Feb 2020 in Wuhan, XiaoGan and HuangGang, China (total 35 days). RR and 95% CI stand for relative ratio and 95% confidence interval, respectively. The number marked with # indicated association between factors and COVID-19 incidence were NOT statistically significant (P>0.0056). Meanwhile, the p-value of those not marked data were <0.01 and considered statistically significant