Air Quality Variation in Daegu, Korea During the Outbreak of COVID-19 and its Health Risk Assessment

Asian Journal of Atmospheric Environment - Tập 14 - Trang 253-262 - 2020
Chang-Jin Ma1, Gong-Unn Kang2
1Department of Environmental Science, Fukuoka Women’s University, Fukuoka, Japan
2Department of Medical Administration, Wonkwang Health Science University, Iksan, Republic of Korea

Tóm tắt

Coronavirus disease 2019 (COVID-19), first reported in Wuhan, China, became pandemic in less than two months, and Korea was no exception. Daegu Metropolitan City, in particular, has become the center of the explosive outbreak in Korea. In this study, we evaluated how the air quality of Daegu Metropolitan City varied when people were fighting the spread of COVID-19. In concretely, we tried to estimate the air quality variation with the trend of COVID-19 in Daegu Metropolitan City based on the measured data at hourly intervals from two air quality monitoring stations (AQMSs) (see Fig. 2). In addition, we quantitatively assessed the positive health effects of improved air quality from fighting against COVID-19. Compared to the concentration in the same period of 2019, the PM2.5 measured at the ambient AQMS decreased by 36.7, 22.5, and 37.6% respectively in January, February, and March. Meanwhile, those at the road side AQMS were 39.9, 23.7, and 40.3% in January, February, and March, respectively. The decreasing trend was not shown in April. Along with the floating population, the concentration of NO2 at the road side AQMS decreased from 49.9 ppb to 32.7 ppb, indicating that the reduction rate was 34.5%. The summed concentration of seven hazardous metals decreased by 27.4% in February 2020 compared to 2019. Among them, lead showed the biggest drop to 43.4% in 2002 compared to 2019. The exposure of PM2.5, DosePM2.5 (µg), during 60 days of self-reflection for 10-year-old children has decreased by 29.6% compared to that in the same period of 2019. The results of adult females and males also show 27, 8% and 29.5% decrease, respectively.

Tài liệu tham khảo

Airborne nitrogen dioxide plummets over China, NASA (2020) https://earthobservatory.nasa.gov/images/146362/airborne-nitrogen-dioxide-plummets-over-china

Annual Report of Ambient Air Quality in Korea, Seoul (2009) NIER (National Institute of Environmental Research) (in Korean).

Almeida, S.M., Canha, N., Silva, A., Freitas, M.D.C., Pegas, P., Alves, C., Evtyugina, M., Pio, C.A. (2011) Children exposure to atmospheric particles in indoor of Lisbon Primary Schools. Atmospheric Environment, 45, 7594–7599. https://doi.org/10.1016/j.atmosenv.2010.11.052

Barnes, N.M., Ng, T.W., Ma, K.K., Lai, K.M. (2018) In-cabin air quality during driving and engine idling in air-conditioned private vehicles in Hong Kong. Journal of Environmental Research and Public Health, 15, 611–624. https://doi.org/10.3390/ijerph15040611

Cinema, Airport, Subway...There is nobody. JoongAng Ilbo 2020.02.27. https://news.joins.com/article/23716478 (in Korean).

Choi, D.H., Kang, D.H. (2018) Indoor/outdoor relationships of airborne particles under controlled pressure difference across the building envelope in Korean multifamily apartments. Sustainability, 10, 1–14. https://doi.org/10.3390/su10114074

COVID-19 pandemic could lead to fall in CO2 not seen since the end of WWII, Newsweek, Mon, May 04, 2020. https://www.newsweek.com/covid-19-pandemic-fall-co2-end-wwii-1495961

COVID-19 status, Korea Centers for Disease Control and Prevention (KCDC), https://www.cdc.go.kr/board/board.es?mid=a20501000000&bid=0015

Dai, Q.L., Bi, X.H., Wu, J.H., Zhang, Y.F., Wang, J., Xu, H., Yao, L., Jiao, L., Feng, Y.C. (2015) Characterization and source identification of heavy metals in ambient PM10 and PM2.5 in an integrated iron and steel industry zone compared with a background site. Aerosol and Air Quality Research, 15, 875–887. https://doi.org/10.4209/aaqr.2014.09.0226

Dye, J.A., Lehmann, J.R., McGee, J.K., Winsett, D.W., Ledbetter, A.D., Everitt, J.I., Ghio, A.J., Costa, D.L. (2001) Acute pulmonary toxicity of particulate matter filter extracts in rats: coherence with epidemiologic studies in Utah Valley residents. Environmental Health Perspectives, 109, 395–403.

Fifty-two days of struggle...Confirmed ‘0’ in Daegu, Korea Economic Daily, 2020.04.10. https://www.hankyung.com/society/article/2020041020261

He, M.Z., Kinney, P.L., Li, T., Chen, C., Sun, Q., Ban, J., Wang, J., Liu, S., Goldsmith, J., Kioumourtzoglou, M.A. (2020) Short- and intermediate-term exposure to NO2 and mortality: a multi-county analysis in China. Environmental Pollution, 261, 114165. https://doi.org/10.1016/j.envpol.2020.114165

Liberti, A. (1975) Modern methods for air pollution monitorin. Pure and Applied Chemistry 1, 44(3), 519–534.

Löndahl, J., Massling, A., Pagels, J., Swietlicki, E., Vaclavik, E., Loft, S. (2007) Size-resolved respiratory-tract deposition of fine and ultrafine hydrophobic and hygroscopic aerosol particles during rest and exercise. Inhalation Toxicology, 19, 109–116. https://doi.org/10.1080/08958370601051677

Ma, C.-J. (2015) Modeling study on dispersion and scavenging of traffic pollutants at a region of near busy road. Asian Journal of Atmospheric Environment 9, 272–279. https://doi.org/10.5572/ajae.2015.9.4.272

Nitrogen Dioxide (NO2) Pollution. 2019. U.S. Environmental Protection Agency. https://www.epa.gov/no2-pollution/basic-information-about-no2

Ostro, B. (2004) Outdoor air pollution: Assessing the environmental burden of disease at national and local levels; Environmental Burden of Disease Series, No 5; World Health Organization: Geneva, Switzerland, https://www.who.int/quantifying_ehimpacts/publications/ebd5.pdf

Pesch, B., Ranft, U., Jakubis, P., Nieuwenhuijsen, M.J., Hergemöller, A., Unfried, K., Jakubis, M., Miskovic, P., Keegan, T. (2002) Environmental arsenic exposure from a coal-burning power plant as a potential risk factor for nonmelanoma skin carcinoma: Results from a case-control study in the district of Prievidza, Slovakia. American Journal of Epidemiology, 155(9), 798–809. https://doi.org/10.1093/aje/155.9.798

Report on the results of air quality analysis in March. 2020. Institute of Health and Environment of Daegu Metropolitan City, pp. 2.

Rolph, G., Stein, A., Stunder, B. (2017) Real-time environmental applications and display system: READY. Environmental Modelling & Software, 95, 210–228. https://doi.org/10.1016/j.envsoft

Spiegel, H. (2002) Trace element accumulation in selected bioindicators exposed to emissions along the industrial facilities of Danube Lowland, Turkish. Journal of Chemistry, 26, 815–823.

Stein, A.F., Draxler, R.R., Rolph, G.D., Stunder, B.J.B., Cohen, M.D., Ngan, F. (2015) NOAA’s HYSPLIT atmospheric transport and dispersion modeling system. The Bulletin of the American Meteorological Society, 96, 2059–2077. https://doi.org/10.1175/BAMS-D-14-00110.1

Wieczorek-Dąbrowska, M., Tomza-Marciniak, A., Pilarczyk, B., Balicka-Ramisz, A. (2003) Roe and red deer as bioindicators of heavy metals contamination in north-western Poland. Chemistry and Ecology, 29, 100–110.

Yamada, Y., Fukutsu, K., Kurihara, O., Momose, T., Miyabe, K., Akashi, M. (2007) Influences of biometrical parameters on aerosol deposition in the ICRP 66 human respiratory tract model: Japanese and Caucasians. Aarozoru Kenkyu, 22, 236–243. https://doi.org/10.11203/jar.22.236

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Asian Journal of Atmospheric Environment

Tập 14

253-262

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