RESEARCH ARTICLE


The Impact of COVID-19 Strict Lockdown on the Air Quality of Smart Cities of Rajasthan, India



Tansukh Barupal1, Praveen Kumar Tak2, Mukesh Meena3, *
iD
, Pradeep Kumar Vishwakarma4, Prashant Swapnil5
1 Sangidas Balkishan Kothari Government PG College, Jaisalmer – 345001, Rajasthan, India
2 M.L.V. Government College, Bhilwara – 311001, Rajasthan, India
3 Department of Botany, Laboratory of Phytopathology and Microbial Biotechnology, Mohanlal Sukhadia University, Udaipur – 313001, Rajasthan, India
4 Department of Mathematics and Statistics, Mohanlal Sukhadia University, Udaipur – 313001, Rajasthan, India
5 Department of Botany, School of Biological Science, Central University of Punjab, Bhatinda, Punjab – 151401, India


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Creative Commons License
© 2022 Barupal et al.

open-access license: This is an open access article distributed under the terms of the Creative Commons Attribution 4.0 International Public License (CC-BY 4.0), a copy of which is available at: https://creativecommons.org/licenses/by/4.0/legalcode. This license permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

* Address correspondence to this author at Department of Botany, Laboratory of Phytopathology and Microbial Biotechnology, Mohanlal Sukhadia University, Udaipur – 313001, Rajasthan, India; E-mails: mukeshmeenamlsu@gmail.com, mukeshmeenabhu@gmail.com


Abstract

Aim:

The main focus of this study is to evaluate the air quality by comparing the concentration of particulate matter PM2.5, PM10, NO2, CO, SO2, and ozone of smart cities of Rajasthan before the lockdown and during the period of lockdown.

Background:

In India, the first case of the COVID-19 was reported on January 30th, 2020. Indian government declared strict lockdown, i.e., public health emergency in India on March 24th, 2020, which is implemented from March 25th, 2020, to April 14th, 2020, for 21 days.

Objective:

The objective of this study is to evaluate the air quality by comparing the levels of all parameters of air pollution during the COVID-19 lockdown period with values registered in the pre-lockdown period.

Methods:

Data were obtained from four automatic monitoring stations under the control of the Central Pollution Control Board, New Delhi (https://www.cpcb.nic.in/). Data regarding all the parameters were recorded as 24 hours average period.

Results:

CO levels showed the highest significant reduction in Udaipur (50.76%) followed by Jaipur (19.96%), Ajmer (17.11%), and Kota (5.51%) due to the ban on transport and driving. The levels of PM2.5, PM10, NO2, and SO2 were also decreased substantially for each smart city. Ozone concentrations were recorded greater than before due to decreased nitrogen oxides levels.

Conclusion:

This study can be useful considering our present role in environmental restoration or environmental destruction. It will also be helpful in updating our present plan toward the assurance and conservation of nature.

Keywords: COVID-19, Sulfur dioxide, PM, Ozone, Public health, Lockdown.



1. INTRODUCTION

On December 8th, 2019, the novel SARS-CoV-2 corona-virus first reported in Wuhan, China. It causes COVID-19 disease, which spreads across the world. On January 9th, 2020, coronavirus was discovered as a novel infectious agent of COVID-19 [1, 2]. It is a communicable disease that spreads very quickly from one person to another. To date, all over the world, the total reported cases are estimated to be 4,628,821, and 308,654 people died because of this pandemic. All world governmental bodies are worried about this crisis because its cure has not been discovered yet. Currently, prevention is the only way to avoid infection. For this, many countries announced the complete lockdown to prevent the spread of infection and succeeded. The Indian government also imposed total fives lockdown with various rules and regulations. Out of five lockdowns, the first lockdown implemented from March 25th, 2020, to April 14th, 2020, for 21 days was very strict; there were strict restrictions on most of the activities, like the transportation, market, industries, etc.

Rajasthan also implemented all rules and regulations of this lockdown. We know that industries and transportation are major sources of pollutants, like particulate matter (PM2.5), nitrogen dioxide (NO2), sulfur dioxide (SO2), carbon monoxide (CO), and ozone (O3), which are directly impacting the air quality. It is a major concern of health risk and cause of large premature mortality [3, 4]. In research, it has been found that the air quality parameters of the most polluted cities (Delhi, Lucknow, Kolkata, Patna, and Bihar) and the least polluted cities (Amaravati, Panchkula, Shillong, and Chennai) of India have been changed during the lockdown period. The information regarding air quality parameters of the most and least polluted cities is provided in Table 1 [5]. In India, Rajasthan is also a very growing state with a lot of industrial development, power plants, and transportation. According to the WHO Global Air Pollution Database 2018, all four smart cities, i.e., Jaipur, Udaipur, Ajmer, and Kota, are listed in the polluted cities of the world. The major pollutants include CO, which is mainly introduced into the air by the burning of fossil fuels and vehicles exhaust, SO2 from petroleum refineries and thermal power plants, NO2 from thermal power plants and vehicle exhausts, ozone from industrial release and vehicle exhaust, and particulate matter consists of solid in the air in the form of dust, smoke, and vapour.

Recently, researchers have reported that the lockdown period dealt with social distancing and decreasing vehicle transport, significantly improving air quality. Tobias et al. [6] reported that NO2 and particulate matter (PM10) were reduced by 51% and 31%, respectively, in Barcelona (Spain) during the lockdown. Nakada and Urban [7] analyzed that concentrations of CO, NO, and NO2 decreased by 64.8%, 77.3%, and 54.3%, respectively, during the partial lockdown in the Sao Paulo state of Brazil. Dantas et al. [8] also reported a significant reduction in NO2, CO, and PM10 levels during the COVID-19 partial lockdown in Rio de Janeiro, Brazil. It has been estimated that long-term or wide exposure to air pollution is correlated with respiratory diseases, such as bronchitis, aggravated asthma, respiratory allergies, heart disease, stroke, and death [9-11]. Particulate matters (PM2.5 and PM10) are considered as one of the most health risk factors and cause millions (~ 9%) of deaths around the world annually [11]. A higher concentration of NO2 emitted from transportation and fuel combustion (outdoor anthropogenic sources) is another most important air pollutant that causes toxicity to human respiratory systems [12, 13]. A higher concentration of NO2 causes severe illnesses, like cytokine-mediated lungs inflammation, diabetes, hypertension, cardiovascular diseases, and even death [11, 14]. Polluted air is associated with more SARS fatality and influenza [15, 16]. In situ study declared that SARS-CoV-2 shows stability in ambient aerosols, which can be considered a source of COVID-19 transmission [17]. Atmospheric aerosol works as a cofactor that can alter immune defence response system pathways and causes severe pneumonia [16, 18-20].

Table 1. Comparison of average air quality parameters before and during lockdown phase among (A) Major polluted cities and (B) Least polluted cities of India [5].
(A)
Air quality Parameters Delhi, Delhi Lucknow, Uttar Pradesh Kolkata, West Bengal Patna, Bihar
Before Lockdown During Lockdown Before Lockdown During Lockdown Before Lockdown During Lockdown Before Lockdown During Lockdown
PM2.5 151.8 54.8 245 186.66 137.7 63.9 117.5 29.4
PM10 166.0 71.9 NA NA 109.5 72.0 226 NA
NO2 60.6 21.9 37 19.33 28.1 9.6 67.5 60
CO 91.4 61.3 61.66 46.66 23.5 16.8 45 29
SO2 13.4 12.0 5.66 5.66 10.7 8.2 9 7
Ozone 30.1 45.4 35 31.66 40.2 42.8 71 70
(B)
Air quality Parameters Amaravati, Andhra Pradesh Panchkula, Haryana Shillong, Meghalaya Chennai, Tamil Nadu
Before Lockdown During Lockdown Before Lockdown During Lockdown Before Lockdown During Lockdown Before Lockdown During Lockdown
PM2.5 40.5 29 32 23.33 59 74.5 38.5 25.33
PM10 42 36.66 NA NA 50 66 NA NA
NO2 11.5 5.3 21.5 22.66 3.5 3 4 2
CO 25.5 10.66 2 21.33 16 14.5 16 38.66
SO2 26 23 14 9.33 6 9 7.5 8.66
Ozone 29 20.66 56 35 52.5 11.5 52.5 24.33

In India, indoor air pollution is also causing serious public health issues because most households depend on the use of solid fuel. The long periods of lockdown to control COVID-19 in India causes adverse health effects through household air pollution [21]. In this study, we have selected four major cities of Rajasthan, i.e., Jaipur, Ajmer, Udaipur, and Kota. The details of the selected cities are provided in Table 2 [22]. The main goal of this study is to analyze the impact of strict lockdown amid COVID19 on the air quality of the smart cities of Rajasthan, India, by comparing the particulate matter, carbon monoxide, nitrogen dioxide, sulfur dioxide, and ozone concentrations determined during the strict lockdown with values obtained before and during the lockdown.

2. MATERIAL AND METHODS

2.1. Studied Area

Rajasthan is the largest state by area in India. It covers an area of 342,239 square kilometers (132,139 sq mi) or 10.4% of the total geographical area of India. It is located on the western side of the country, situated between 23 30’ and 30 11’ North latitude and 69 29’ and 78 17’ East longitude. In this study, we have selected four smart cities, i.e., Jaipur, Udaipur, Ajmer, and Kota, as shown in Fig. (1), and their geographical locations, coordinates, and monitoring station are shown in Table 2 [22].

Jaipur, a smart city, is situated in the East-central part of the state. It is the capital and largest city of Rajasthan. Udaipur, Ajmer, Kota are also important cities of Rajasthan. Udaipur is located in the southern region of Rajasthan. Ajmer is situated in the center or heart of Rajasthan, and the Kota is situated at the center of the southeastern region of Rajasthan. The main characteristics are briefly described in Table 2 [22].

2.2. Experimental Data and Analysis

In this study, we have selected a total of four parameters, i.e., PM2.5, NO2, SO2, CO, and ozone concentration, to assess the air quality of smart cities of Rajasthan. These data were obtained from four automatic monitoring stations, i.e., Adarsh Nagar, Jaipur – RSPCB, Ashok Nagar, Udaipur – RSPCB, Civil Lines, Ajmer – RSPCB and Shrinath Puram, Kota – RSPCB under the control of Central Pollution Control Board, New Delhi (https://www.cpcb.nic.in/). Data of all parameters were recorded as 24 hours average period, and the air quality of these cities was compared with the standard air quality index (AQI) before and during the lockdown (Table 3) [5]. Experimental data obtained by each monitoring station were analyzed using standard statistical techniques. Comparisons of each parameter, i.e., obtained during the lockdown and before the lockdown, were made by graphical representation. This study also included the data regarding total COVID-19 cases and death (mortality) registered in India in pre- and during the lockdown period (Table 4) [23].

Fig. (1). Geographical status of the studied smart cities of Rajasthan situated in India.

Table 2. Description of the studied smart cities of Rajasthan, India [22].
S. No. Smart city Coordinates Area (km2) City Population The Monitoring Station
1. Jaipur 26.9124°N, 75.7873° E 484.6 3,046,163 Adarsh Nagar, Jaipur - RSPCB
2. Udaipur 24.5854°N, 73.7125° E 37 451,100 Ashok Nagar, Udaipur - RSPCB
3. Ajmer 26.4499°N, 74.6399° E 55.76 542,321 Civil Lines, Ajmer - RSPCB
4. Kota 25.2138°N, 75.8648° E 527 1,001,694 Shrinath Puram, Kota - RSPCB
Table 3. (A) Standard AQI and (B) AQI registered in smart cities of Rajasthan in pre and during lockdown period [5].
(A)
AQI Remark
(Air Pollution Level)
Possible Health Impacts
0-50 Good Minimal impact
51-100 Satisfactory Minor breathing discomfort to sensitive people
101-200 Moderate Breathing discomfort to the people with lungs, asthma, and heart diseases
201-300 Poor Breathing discomfort to most people on prolonged exposure
301-400 Very Poor Respiratory illness on prolonged exposure
401-500 Severe Affects healthy people and seriously impacts those with existing diseases
(B)
S. No. Smart City Air Quality Index (AQI)
Pre-Lockdown Period During Lockdown Period
1. Jaipur 91.00 66.33
2. Udaipur 81.00 53.33
3. Ajmer 102.50 58.00
4. Kota 95.00 73.67
Table 4. COVID-19 cases and mortality registered in India in pre- and during lockdown period [23].
Duration Date Cases Mortality Percent (%) Average Percent (%)
Pre-Lockdown Period March 1 3 0 0 1.81
March 5 30 0 0
March 10 62 0 0
March 15 114 2 1.75
March 20 249 5 2.00
March 24 536 11
During Lockdown Period March 25 657 13 1.97 2.70
March 30 1251 33 2.63
April 1 4289 59 1.37
April 5 4778 119 2.49
April 10 7600 250 3.28
April 14 11887 349 2.94

3. RESULTS AND DISCUSSION

Changes in concentrations of major pollutants during the pre-lockdown and during-lockdown period are depicted in Fig. (2). Indian government declared a strict lockdown in India on March 24th, 2020, which was implemented from March 25th, 2020, to April 14th, 2020. During this period, i.e., 21 days, all four smart cities of Rajasthan observed substantial diminution of the pollutants. The present article assessed air quality during the strict lockdown (March 25th, 2020 to April 14th, 2020). Results showed the highest reduction in PM2.5 found in Ajmer (53.07%), followed by Jaipur (38.32%), Kota (28.39%), and Udaipur (15.37%), respectively. PM10 was also found to be reduced in Ajmer (45.56%), followed by Jaipur (36.18%), Udaipur (29.40%), and Kota (19.69%), respectively. Whereas, concerning NO2, the highest reduction was found in Udaipur (66.07%), followed by Jaipur (62.90%), Kota (56.83%), and Ajmer (54.36%), respectively. In the case of SO2, the highest reduction was found in Udaipur (28.70%), and the lowest was found in Jaipur (11.71%).

Fig. (2 A,B). Comparative analysis of different air quality parameters (PM2.5, PM10, NO2, CO, SO2, and ozone) of smart cities of Rajasthan, i.e., Jaipur, Udaipur, Ajmer, and Kota before and during the period of lockdown.

However, increasing O3 concentration was recorded at 12.82% in Kota and 6.08% in Ajmer, but Udaipur and Jaipur showed negative results -6.08 and -13.59%, respectively. Overall the result concluded that the air quality index of the cities was found more satisfactory during the lockdown period than the pre-lockdown period by comparing with standard AQI. In India, a high number of people were infected due to coronavirus. During the pre-lockdown (from March 1st to 24th, 2020), a total of 994 active cases and 18 deaths were registered. During the lockdown period (March 25th, 2020, to April 14th, 2020), a total of 30462 active cases and 823 deaths were registered. It was reported that active cases were increased during lockdown conditions (Table 4). The average death rate percentage was found to be 1.81% during the pre-lockdown and 2.70% during the lockdown phase. The relationship between active cases and deaths may specify the severity of any pandemic.

It has been investigated that meteorological conditions, such as air, temperature, wind direction, and wind speed, are known to greatly impact urban air pollutant’s level via some physical and chemical processes, like accumulation or dispersion and multiphase reactions of aerosol formation and growth [24]. Therefore, it is reasonable to suppose that changes in urban air pollutant concentrations during the COVID-19 lockdown may partially depend on meteorological conditions during that period [25]. Movements of air affect the fate of air pollutants. Concentrations of pollutants build up by non-dispersion of air pollutants due to calm air. However, when strong, turbulent winds blow, the concentration of air pollutants decreases. To estimate air quality, some important factors need to be measured, which can help in understanding the chemical reactions which occur in atmospheres, such as wind speed and direction, temperature, humidity, rainfall, and solar radiation [26].

In India, Rajasthan is also a growing state with the establishment of various kinds of industries and high pressure of transportation. Moreover, WHO also listed all four smart cities, i.e., Jaipur, Udaipur, Ajmer, and Kota, as the most polluted cities of the world based on the global air pollution database. The air quality of all these smart cities was measured by the data provided by the four automatic monitoring stations. The impact of lockdown on air quality in different parts of the world indicated how human beings drastically affect the environment. Therefore, the results of the present article will possibly help us in rethinking the kind of future we are establishing. The article may also help explain how industries and transportation negatively affect the environment and how we can restore the environment and provide a good quality ecosystem to future generations. Currently, on the one hand, the outrageous viruses have affected our lives, and on the other hand, the process of environmental restoration is also going on. Hence, global concern for air pollution has led to drawing significant attention towards analyzing air pollution during the pandemic. In the metropolitan area of São Paulo (2100 km2), the NO2 concentration reduction is visualized by satellite measurements [5, 27, 28]. However, Sharma et al. [29] reported an increase of 17% in O3 concentration in India. In China, about 25% carbon and 30% NO2 emission have been reduced during the period of lockdown [30-33]. Overall, pollutant concentrations decreased in all analyzed areas.

CONCLUSION

This study can be helpful in evaluating our present role in environmental restoration or environmental destruction. It will also be helpful in updating the present plan toward the assurance and conservation of nature. The main focus of this study is to evaluate the air quality by comparing the concentration of particulate matter PM2.5, PM10, NO2, CO, SO2, and ozone in smart cities of Rajasthan, i.e., Jaipur, Udaipur, Ajmer, and Kota before and during the period of lockdown. CO levels showed the highest significant reduction in Udaipur (50.76%), followed by Jaipur (19.96%), Ajmer (17.11%), and Kota (5.51%), due to the ban on transport and driving. The levels of PM2.5, PM10, NO2, and SO2, were also found to be substantially decreased for each smart city.

Ozone concentration was recorded greater than before lockdown due to decreased nitrogen oxides level. Although, more specific studies are required to explore the interactions between SARS-CoV-2 and air pollutants to understand their impacts on human health. Future studies should be investigated to examine the role of indoor air pollution (biomass and tobacco smoke) during COVID-19. Biology and atmospheric chemistry should be implicated in a more holistic way to the disease management and mitigation to address the current pandemic condition and future viral epidemics. We should not ignore our surrounding environment, which is causing not only chronic diseases but also severe infectious diseases. To establish a healthy future, we need to reduce air pollution from all sources, such as road traffic and heat generation, by strengthening public health policies.

LIST OF ABBREVIATIONS

PM = Particulate Matter
NO2 = Nitrogen Dioxide
SO2 = Sulfur Dioxide
CO = Carbon Monoxide
NO = Nitric Oxide
WHO = World Health Organization
AQI = Air Quality Index

AUTHORS’ CONTRIBUTION

TSB, MM, and PKT contributed to the study concept and design. PKT, TSB, and MM participated in data collection. Data analysis was performed by PKV and MM. TSB, PS, and MM contributed to the writing of the manuscript.

ETHICS APPROVAL AND CONSENT TO PARTICIPATE

Not applicable.

HUMAN AND ANIMAL RIGHTS

No animals/humans were used in the studies that are the basis of this research.

CONSENT FOR PUBLICATION

Not applicable.

AVAILABILITY OF DATA AND MATERIALS

Not applicable.

FUNDING

None.

CONFLICT OF INTEREST

The authors declare no conflict of interest, financial or otherwise.

ACKNOWLEDGEMENTS

The authors would like to thank the Central Pollution Control Board, Ministry of Environment, Forest and Climate Change (MoEFCC), and Ministry of Human Resources and Development, Government of India.

REFERENCES

[1] Cheng VCC, Wong SC, To KKW, Ho PL, Yuen KY. Preparedness and proactive infection control measures against the emerging novel coronavirus in China. J Hosp Infect 2020; 104(3): 254-5.
[2] Swapnil P, Meena M. SARS-CoV-2 (COVID-19) pandemic outbreak: A worldwide challenge and contemporary situation. Virol Mycol 2021; 10: 201.
[3] Sharma S, Zhang M, Anshika , Gao J, Zhang H, Kota SH. Effect of restricted emissions during COVID-19 on air quality in India. Sci Total Environ 2020; 728: 138878.
[4] Swapnil P, Meena M, Barupal T, Sompura Y, Hada D. Structure, transmission, diagnostic symptoms, host and entry mechanism of COVID-19: A review. Coronaviruses 2021; 2(5): 1-9.
[5] National Air Quality Index - CPCB. Available from: https://app.cpcbccr.com/AQI_India/
[6] Tobías A, Carnerero C, Reche C, et al. Changes in air quality during the lockdown in Barcelona (Spain) one month into the SARS-CoV-2 epidemic. Sci Total Environ 2020; 726: 138540.
[7] Nakada LYK, Urban RC. COVID-19 pandemic: Impacts on the air quality during the partial lockdown in São Paulo state, Brazil. Sci Total Environ 2020; 730: 139087.
[8] Dantas G, Siciliano B, França BB, da Silva CM, Arbilla G. The impact of COVID-19 partial lockdown on the air quality of the city of Rio de Janeiro, Brazil. Sci Total Environ 2020; 729: 139085.
[9] WHO. World Health Organization 2020. Available from: https://covid19.who.int/region/searo/country/in
[10] MHA (Ministry of Home Affairs). Govt of India Circulars for Covid-19 2020. Available from: https://www.mha.gov.in/notifications/circulars-covid-19
[11] Hu B, Guo H, Zhou P, Shi ZL. Characteristics of SARS-CoV-2 and COVID-19. Nat Rev Microbiol 2021; 19(3): 141-54.
[12] Chen LA, Chien LC, Li Y, Lin G. Nonuniform impacts of COVID-19 lockdown on air quality over the United States. Sci Total Environ 2020; 745: 141105.
[13] Berman JD, Ebisu K. Changes in U.S. air pollution during the COVID-19 pandemic. Sci Total Environ 2020; 739: 139864.
[14] Unnithan PSG. Kerala reports first Coronavirus case in India 2020. Available from: https://www.indiatoday.in/india/story/kerala-reports-first-confirmed-novel-coronavirus-case-in-india-1641593-2020-01-30
[15] He G, Pan Y, Tanaka T. COVID-19, city lockdowns, and air pollution: evidence from China. medRxiv 2020.
[16] Ndegwa S. An environmental silver lining amid COVID-19 cloud. China global television network, opinion. 2020. Available from: https://news.cgtn.com/news/2020-06-06/An-environmental-silver-lining-amid-COVID-19-cloud-R4TpEvr0ty/index.html
[17] Zambrano-Monserrate MA, Ruano MA, Sanchez-Alcalde L. Indirect effects of COVID-19 on the environment. Sci Total Environ 2020; 728: 138813.
[18] Meena M, Swapnil P. A review of contagious coronavirus (SARS-Cov-2) their clinical features, diagnosis, preventions and treatment. J Hum Virol Retrovirol 2020; 8(4): 99-105.
[19] European Environmental Agency. Air pollution goes down as Europe takes hard measures to combat 2020. Available from: https://www.eea.europa.eu/highlights/air-pollution-goes-down-as
[20] Garg A, Kumar A, Gupta NC. Impact of lockdown on ambient air quality in COVID-19 affected hotspot cities of India: Need to readdress air pollution mitigation policies. Environ Claims J 2021; 1(1): 65-76.
[21] Rani R, Arokiasamy P, Sikarwar A. Household air pollution during COVID-19 pandemic: A concern in India. J Public Aff 2021; 21(4): e2729.
[22] Census 2011 India. Available from: https://www.indiatoday.in/india/story/kerala-reports-first-confirmed-novel-coronavirus-case-in-india-1641593-2020-01-30
[23] Worldometers. Available from: https://www.worldometers.info/coronavirus/country/india/
[24] Cai WJ, Wang HW, Wu CL, Lu KF, Peng ZR, He HD. Characterizing the interruption-recovery patterns of urban air pollution under the COVID-19 lockdown in China. Build Environ 2021; 205: 108231.
[25] Díaz-Avalos C, Juan P, Chaudhuri S, Sáez M, Serra L. Association between the new COVID-19 cases and air pollution with meteorological elements in nine counties of New York state. Int J Environ Res Public Health 2020; 17(23): 9055.
[26] Queensland Governement. Available from: https://www.qld.gov.au
[27] Gorelick N, Hancher M, Dixson M, Ilyushchenko S, Thau D, Moore R. Google earth engine: planetary-scale geospatial analysis for everyone. Remote Sens Environ 2017; 202: 18-27.
[28] Yuen KY, Chan PK, Peiris M, et al. Clinical features and rapid viral diagnosis of human disease associated with avian influenza A H5N1 virus. Lancet 1998; 351: 467e71.
[29] Sharma S, Swapnil P, Meena M. A novel 2019 severe acute respiratory syndrome coronavirus 2 (COVID-19) as global pandemic. Cell Cellular Life Sci J 2020; 5(2): 000154.
[30] He G, Pan Y, Tanaka T. The short-term impacts of COVID-19 lockdown on urban air pollution in China. Nat Sustain 2020; 3(12): 1005-11. [https://doi.org/10.1038/s41893-020-0581-y].
[31] Liu F, Page A, Strode SA, et al. van der AR, Veefkind P, Levelt PF, Hauser OP, Joiner J. Abrupt declines in tropospheric nitrogen dioxide over China after the outbreak of COVID-19. Sci Adv 2020; 6(28): eabc2992.
[32] Barupal T, Tak PK, Meena M. COVID-19: Morphology, characteristics, symptoms, prevention, clinical diagnosis and current scenario. Coronaviruses 2020; 1(1): 82-9.
[33] Cheng VC, Lau SK, Woo PC, Yuen KY. Severe acute respiratory syndrome coronavirus as an agent of emerging and reemerging infection. Clin Microbiol Rev 2007; 20: 660e94.