Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2021 Jan 1;268(Pt A):115714.
doi: 10.1016/j.envpol.2020.115714. Epub 2020 Oct 15.

Assessing correlations between short-term exposure to atmospheric pollutants and COVID-19 spread in all Italian territorial areas

Affiliations

Assessing correlations between short-term exposure to atmospheric pollutants and COVID-19 spread in all Italian territorial areas

Gabriele Accarino et al. Environ Pollut. .

Abstract

The spread of SARS-CoV-2, the beta coronavirus responsible for the current pneumonia pandemic outbreak, has been speculated to be linked to short-term and long-term atmospheric pollutants exposure. The present work has been aimed at analyzing the atmospheric pollutants concentrations (PM10, PM2.5, NO2) and spatio-temporal distribution of cases and deaths (specifically incidence, mortality and lethality rates) across the whole Italian national territory, down to the level of each individual territorial area, with the goal of checking any potential short-term correlation between these two phenomena. The data analysis has been limited to the first quarter of 2020 to reduce the lockdown-dependent biased effects on the atmospheric pollutant levels as much as possible. The analysis looked at non-linear, monotonic correlations using the Spearman non-parametric correlation index. The statistical significance of the Spearman correlations has also been evaluated. The results of the statistical analysis suggest the hypothesis of a moderate-to-strong correlation between the number of days exceeding the annual regulatory limits of PM10, PM2.5 and NO2 atmospheric pollutants and COVID-19 incidence, mortality and lethality rates for all the 107 territorial areas in Italy. A weak-to-moderate correlation seems to exist when considering the 36 territorial areas in four of the most affected regions (Lombardy, Piedmont, Emilia-Romagna and Veneto). Overall, PM10 and PM2.5 showed a higher non-linear correlation than NO2 with incidence, mortality and lethality rates. As to particulate matters, PM10 profile has been compared with the incidence rate variation that occurred in three of the most affected territorial areas in Northern Italy (i.e., Milan, Brescia, and Bergamo). All areas showed a similar PM10 time trend but a different incidence rate variation, that was less severe in Milan compared with Brescia and Bergamo.

Keywords: COVID-19; Non-parametric correlation; PM(10); PM(2.5), and NO(2); Short-term exposure.

PubMed Disclaimer

Conflict of interest statement

Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Figures

Image 1
Graphical abstract
Fig. 1
Fig. 1
Air quality indicators, air quality index (AQI) and COVID-19 spread in the 107 Italian territorial areas: Panels A, B, and C, report the number of days (at least 45) that exceeded the annual regulatory limits in the period from January 1st to March 31st, 2020, in all 107 Italian territorial areas, with reference to PM2.5 (panel A), PM10 (panel B) and NO2 (panel C). Panel D reports the AQI for each territorial area (measured as in section 2.5), and the average index in the period from January 1st to March 31st, 2020. Panels E and F report the COVID-19 incidence rate (per 100,000 inhabitants) at territorial and regional level, respectively, in the period from February 20th to March 31st, 2020. Data references are available in Table 1.
Fig. 2
Fig. 2
Scatter plots for all 107 Italian territorial areas: number of days exceeding the annual regulatory limits (y-axis) for PM2.5, PM10, and NO2, from January 1st to March 31st, with respect to: COVID-19 incidence rates (panels A–C, x-axis), COVID-19 mortality rates (panels D–F, x-axis), and COVID-19 lethality rates (panels G–I, x-axis), in the period from February 20th to March 31st. Incidence and mortality rates are reported for 100,000 inhabitants. Data references are available in Table 1.
Fig. 3
Fig. 3
Scatter plots for the 36 territorial areas in four of the most affected Italian regions: number of days exceeding the annual regulatory limits (y-axis) for PM2.5, PM10, and NO2, from January 1st to March 31st, with respect to: COVID-19 incidence rates (panels A–C, x-axis), COVID-19 mortality rates (panels D–F, x-axis) and COVID-19 lethality rates (panels G–I, x-axis), in the period from February 20th to March 31st. Incidence and mortality rates are reported for 100,000 inhabitants. Data references are available in Table 1.
Fig. 4
Fig. 4
Profiles of PM2.5 (green line) and PM10 (red line) atmospheric pollutant levels in three of the most affected territorial areas in Lombardy, from January 1st to March 31st (x-axis). Panels A, B and C, report the concentrations for Milan, Brescia, and Bergamo, respectively. The y-axis reports the absolute levels of PMs in μg/m3. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 5
Fig. 5
Profile of the PM10 atmospheric pollutant levels (using a 7-day moving average) and COVID-19 incidence rate (per 100,000 inhabitants) variation in three of the most affected territorial areas in Lombardy, from March 1st to March 31st. Panels A, B and C, report the PM10 concentrations for Milan, Brescia, and Bergamo, respectively. PM10 profiles are represented by a red line with values on the y-axis, right side. Incidence rate variations are represented by blue bars with values on the y-axis, left side. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 6
Fig. 6
COVID-19 incidence rate (for 100,000 inhabitants) registered for each day in the period from February 24th to June 2nd (x-axis), in Milan (in green), Bergamo (in orange) and Brescia (in blue). The incidence rate values are reported on the y-axis. Data references are available in Table 1. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

References

    1. Ahn D.G., Shin H.J., Kim M.H., Lee S., Kim H.S., Myoung J., Kim B.T., Kim S.J. Current status of epidemiology, diagnosis, therapeutics, and vaccines for novel coronavirus disease 2019 (covid-19) J. Microbiol. Biotechnol. 2020;30:313–324. doi: 10.4014/jmb.2003.03011. - DOI - PMC - PubMed
    1. Bontempi E. First data analysis about possible COVID-19 virus airborne diffusion due to air particulate matter (PM): the case of Lombardy (Italy) Environ. Res. 2020;186:109639. doi: 10.1016/j.envres.2020.109639. - DOI - PMC - PubMed
    1. Bontempi E. Commercial exchanges instead of air pollution as possible origin of COVID-19 initial diffusion phase in Italy: more efforts are necessary to address interdisciplinary research. Environ. Res. 2020;188:109775. doi: 10.1016/j.envres.2020.109775. - DOI - PMC - PubMed
    1. Bontempi E., Vergalli S., Squazzoni F. Understanding COVID-19 diffusion requires an interdisciplinary, multi-dimensional approach. Environ. Res. 2020;188:109814. doi: 10.1016/j.envres.2020.109814. - DOI - PMC - PubMed
    1. CAMS . 2020. Copernicus Atmosphere Monitoring Service.https://atmosphere.copernicus.eu