| Literature DB >> 34322805 |
Muhammad Khalid Anser1, Danish Iqbal Godil2, Muhammad Azhar Khan3, Abdelmohsen A Nassani4, Khalid Zaman5, Muhammad Moinuddin Qazi Abro4.
Abstract
The severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2) spread to more than 200 countries with a current case fatality ratio (CFR) of more than 2% globally. The concentration of air pollutants is considered a critical factor responsible for transmitting coronavirus disease among the masses. The photochemical process and coal combustions create respiratory disorders that lead to coronavirus disease. Based on the crucial fact, the study evaluated the impact of nitrous oxide (N2O) emissions, coal combustion, and traffic emissions on COVID-19 cases in a panel of 39 most affected countries of the world. These three air pollution factors are considered to form a lethal smog that negatively affects the patient's respiratory system, leading to increased susceptibility to coronavirus worldwide. The study used the Markov two-step switching regime regression model for obtaining parameter estimates. In contrast, an innovation accounting matrix is used to assess smog factors' intensity on possibly increasing coronavirus cases over time. The results show that N2O emissions, coal combustion, and traffic emissions increase COVID-19 cases in regime-1. On the other hand, N2O emissions significantly increase coronavirus cases in regime-2. The innovation accounting matrix shows that N2O emissions would likely have a more significant share of increasing coronavirus cases with a variance of 33.902%, followed by coal combustion (i.e., 6.643%) and traffic emissions (i.e., 2.008%) over the time horizon. The study concludes that air quality levels should be maintained through stringent environmental policies, such as carbon pricing, sustainable urban planning, green technology advancement, renewable fuels, and pollution less accessible vehicles. All these measures would likely decrease coronavirus cases worldwide.Entities:
Keywords: COVID-19 cases; Coal combustion; Nitrous oxide emissions; Smog; Switching regression; Traffic emissions
Mesh:
Substances:
Year: 2021 PMID: 34322805 PMCID: PMC8318325 DOI: 10.1007/s11356-021-15494-x
Source DB: PubMed Journal: Environ Sci Pollut Res Int ISSN: 0944-1344 Impact factor: 4.223
Literature on emissions and COVID-19 nexus worldwide
| Persico & Johson (2021) | Level of PM2.5, PM10, and O3 | The ease of environmental regulations increasing environmental pollution, causing the susceptibility of COVID-19 cases. |
| Vasquez-Apestegui et al. ( | Level of PM2.5 | The particulate matter found a transmission channel that increases COVID-19 cases in Lima, Peru. |
| De Angelis et al. ( | Level of PM2.5, PM10, and NO2 | Humidity, the annual concentration of PM2.5, and PM10 causing COVID-19 cases and mortality in Lombardy, Italy. |
| Zhang et al. ( | Ambient air pollution and COVID-19 cases | The increased concentration of PM2.5, PM10, and NO2 found detrimental factors that exacerbated COVID-19 cases in China. |
| Aabed and Lashin ( | CO2 emissions | The concentration of carbon emissions in the air causing the spread of COVID-19 cases in a large panel of countries. |
| Konstantinoudis et al. ( | NO2 and PM2.5 emissions | NO2 and PM2.5 emissions are causing an increase in the COVID-19 mortality risk in the UK. |
| Marquès et al. ( | PM10, NO2 and O3 level | The stated environmental pollutants causing a transmission channel of COVID-19 cases in most of the cases in Catalonia, Spain |
| Tung et al. ( | Particulate matter | The particulate matters negatively affected the health of the residents, causing an increase in COVID-19 cases. |
| Travaglio et al. ( | NO2, NO and O3 | The concentration of stated pollutants correlated with the COVID-19 deaths in the UK. |
| Isphording and Pestel ( | The concentration of PM10 level and O3 | The particulate matter and ozone concentration are causing an increase in the severity of the COVID-19 pandemic. |
Fig. 1Smog concentration and COVID-19 cases across countries. Source: Worldometer (2021) and World Bank (2021)
Fig. 2Theoretical framework of the study. Source: Self-extract
Descriptive statistics
| Mean | 2,462,785 | 27.47 | 39,319.36 | 27.76 |
| Maximum | 27,897,214 | 92.71 | 288,878 | 53.28 |
| Minimum | 236,333 | 0.14 | 1,408 | 11.41 |
| Std. Dev. | 4,747,195 | 24.60 | 64,409.08 | 10.12 |
| Skewness | 4.305 | 0.93 | 2.84 | 0.22 |
| Kurtosis | 22.680 | 3.10 | 10.14 | 2.52 |
COVID19_CASES show COVID-19 registered cases, SMOG_CF shows smog formation by coal fires, SMOG_N2O shows smog formation by nitrous oxide, and SMOG_TE shows smog formation by transport emissions
Correlation matrix
| COVID19_CASES | 1 | |||
| – | ||||
| SMOG_CF | 0.08 | 1 | ||
| (0.63) | – | |||
| SMOG_N2O | 0.89 | 0.13 | 1 | |
| (0.00) | (0.41) | – | ||
| SMOG_TE | 0.07 | − 0.57 | 0.01 | 1 |
| (0.64) | (0.00) | (0.95) | – |
Small bracket shows probability values, COVID19_CASES show COVID-19 registered cases, SMOG_CF shows smog formation by coal fires, SMOG_N2O shows smog formation by nitrous oxide emissions, and SMOG_TE shows smog formation by transport emissions
Markov switching regression (BFGS/Marquardt steps)
| Variable | Coefficient | Std. error | z-Statistic | Prob. |
|---|---|---|---|---|
| Regime 1 | ||||
| SMOG_CF | 137900.3 | 59246.99 | 2.33 | 0.01 |
| SMOG_N2O | 84.46 | 5.59 | 15.11 | 0.00 |
| SMOG_TE | 130514.40 | 51285.33 | 2.54 | 0.01 |
| C | − 5589576 | 1925383 | − 2.90 | 0.00 |
| Regime 2 | ||||
| SMOG_CF | 444.57 | 6692.43 | 0.06 | 0.94 |
| SMOG_N2O | 41.71 | 2.58 | 16.11 | 0.00 |
| SMOG_TE | 1200.10 | 16837.96 | 0.07 | 0.94 |
| C | 148592.60 | 612952.20 | 0.24 | 0.80 |
| Common | ||||
| LOG(SIGMA) | 13.39 | 0.13 | 95.95 | 0.00 |
| Transition matrix parameters | ||||
| P11-C | 1.04 | 1.21 | 0.86 | 0.38 |
| P21-C | − 2.74 | 0.89 | − 3.07 | 0.00 |
| Mean dependent var | 2462785 | S.D. dependent var | 4747195 | |
| S.E. of regression | 3281051 | Sum squared resid | 3.23E+14 | |
| Durbin-Watson stat | 2.38 | Log-likelihood | − 586.60 | |
| Akaike info criterion | 30.64 | Schwarz criterion | 31.11 | |
| Hannan-Quinn criteria. | 30.81 | |||
COVID19_CASES shows COVID-19 registered cases, SMOG_CF shows smog formation by coal fires, SMOG_N2O shows smog formation by nitrous oxide emissions, and SMOG_TE shows smog formation by transport emissions
Variance decomposition analysis of COVID-19 cases
|
| |||||
|---|---|---|---|---|---|
| March | 437079.0 | 76.50 | 0.15 | 20.02 | 3.30 |
| April | 528964.9 | 64.34 | 2.90 | 30.49 | 2.25 |
| May | 559674.7 | 61.70 | 3.74 | 32.32 | 2.21 |
| June | 578686.7 | 59.18 | 5.89 | 32.81 | 2.10 |
| July | 588463.3 | 58.15 | 6.31 | 33.48 | 2.04 |
| August | 592896.8 | 57.80 | 6.43 | 33.73 | 2.01 |
| September | 595061.9 | 57.63 | 6.51 | 33.83 | 2.02 |
| October | 596213.8 | 57.50 | 6.61 | 33.86 | 2.01 |
| November | 596849.4 | 57.44 | 6.64 | 33.90 | 2.00 |
COVID19_CASES shows COVID-19 registered cases, SMOG_CF shows smog formation by coal fires, SMOG_N2O shows smog formation by nitrous oxide emissions, and SMOG_TE shows smog formation by transport emissions