Article Sidebar

PDF
Published: 2024-06-03
Abstract Views: 76
Views PDF: 159
DOI: https://doi.org/10.53747/nst.v13i4.450
Issue
Vol. 13 No. 4 (2023)
Section
Articles
How to Cite
Vuong, T. B., Ha , L. A., Mai , D. K., & Nguyen , H. T. . (2024). Characteristics of fine dust pollution PM₂.₅ in Hanoi in 2021. Nuclear Science and Technology, 13(4), 1-10. https://doi.org/10.53747/nst.v13i4.450

Characteristics of fine dust pollution PM₂.₅ in Hanoi in 2021

Thu Bac Vuong1, Ha Lan Anh2, Mai Dinh Kien2, Nguyen Huyen Trang 2
1 INST_VINATOM
2 Institute for Nuclear Science & Technique (INST)

Main Article Content

Abstract

Fine particulate matter (PM2.5) is one of the most dangerous pollutions in the atmosphere in the Hanoi capital. PM2.5 fine dust pollution characteristics in Hanoi in the duration from 5/2021 to 3/2022 have been studied. The concentration of main chemical elements (such as As, Br, Ca, Cd, Ce, Cl, Cu, Fe, K, Mn, Pb, S, Sr, Ti, Zn, Zr…), main water-soluble ions (such as Na+, NH4+, K+, Mg2+, Ca2+, SO42-, Cl-, NO3-, F-, NO2-) and black carbon (BC) in the PM2.5 sample have been analyzed. The average PM2.5 fine dust concentration was (78.09 ± 51.71) µg/m3 and ranged from 17.55 to 271.39 µg/m3. PM2.5 tends to increase and is about 3.12 times larger than Who Air Quality Guidelines 2005 (25 µg/m3 for PM2.5 24h). The average PM2.5 concentration in the rainy season from 5/2021 to 9/2021 was (51.97 ± 16.40) µg/m3. This value for the dry season from 10/2021 to 3/2022 was (104.70 ± 61.19) µg/m3. It is much higher than that in the rainy season about 2.01 times. The major contributors were the secondary components such as NH4+, SO42-, NO3- and BC... The main pollution contribution sources and the potential pollution areas map have been identified. This research shows a worrying picture of fine dust PM2.5 in Hanoi in the studying duration.

Article Details

Author Biographies

Ha Lan Anh, Institute for Nuclear Science & Technique (INST)

179 Hoang Quoc Viet, Nghia Do, Cau Giay, Ha Noi

Mai Dinh Kien, Institute for Nuclear Science & Technique (INST)

179 Hoang Quoc Viet, Nghia Do, Cau Giay, Ha Noi

Nguyen Huyen Trang , Institute for Nuclear Science & Technique (INST)

179 Hoang Quoc Viet, Nghia Do, Cau Giay, Ha Noi

Keywords

PM2.5 fine dust in Hanoi 2021, major chemical elements and ions concentrations, main pollution sources, PSCF maps

References

[1]. Anderson JO, Thundiyil JG, Stolbach A (2012) Clearing the air: a review of the effects of particulate matter air pollution on human health. J Med Toxicol 8(2):166–175. https://doi.org/10.1007/s13181-011-0203-1.
[2]. BP (Bristish Petroleum 2019). BP Statistical Report on World Energy. 68th edition. https://www.bp.com/content/dam/bp/businesssites/en/global/corporate/pdfs/energy-economics/statisticalreview/bp-statsreview-2019-full-report.pdf
[3]. Cohen. David D., Jagoda Crawford, Eduard Stelcer, Vuong Thu Bac. Characterization and source apportionment of fine particulate sources at Hanoi from 2001 to 2008. Atmospheric Environment 44 (2010) 320-328.
[4]. Eleftheriadis K, Klaus MO, Theopisti L, Angeliki K, Panayiotis R, Maria OP (2014) Influence of local and regional sources on the observed spatial and temporal variability of size resolved atmospheric aerosol mass concentrations and water-soluble species in the Athens metropolitan area. Atmos Environ 97:252–261. https://doi.org/10.1016/j.atmosenv.2014.08.013.
[5]. Fuller R, Landrigan PJ, Balakrishnan K. Pollution and health: A progress update. The Lancet Planetary Health. 2022: 6, (6), E535-E547. doi: 10.1016/S2542-5196(22)00090-0. BP Statistical Review of World Energy 2019, 68th edition.
[6]. Gary Norris, Rachelle Duval. EPA Positive Matrix Factorization (PMF) 5.0 Fundamentals and User Guide. EPA/600/R-14/108 April 2014. www.epa.gov
[7]. Hien, P.D., Bac, V.T., Lam, D.T., Thinh, N.T.H. (2004). PMF receptor modeling of fine and coarse PM10 in air masses governing monsoon conditions in Hanoi, northern Vietnam. Atmos. Environ. 38, 189–201. https://doi.org/10.1016/j.atmosenv.2003.09.064
[8]. Hopke, P.K., Cohen, D.D., Begum, B.A., Biswas, S.K., Ni, B., Pandit, G.G., Santoso, M., Chung, Y.S., Davy, P., Markwitz, A., Waheed, S., Siddique, N., Santos, F.L., Pabroa, P.C.B., Seneviratne, M.C.S., Wimolwattanapun, W., Bunprapob, S., Vuong, T.B., Duy Hien, P., Markowicz, A. (2008). Urban air quality in the Asian region. Sci. Total Environ. 404, 103–112. https://doi.org/10.1016/j.scitotenv.2008.05.039
[9]. Hopke, P.K., Gao, N., Cheng, M.-D., 1993. Combining chemical and meteorological data to infer source areas of airborne pollutants. Chemom. Intell. Lab. Syst. 19, 187-199.
[10]. https://www.ready.noaa.gov/HYSPLIT.php
[11]. IQAir (2020). World air quality report 2019. Solutions for the environment (GPMT) compiled 2020.
[12]. Tran Thanh Long (2020), How harmful is air pollution and fine dust PM 2.5 to health? Reference link: https://youmed.vn/tin-tuc/o-nhiem-khong-khi-bui-min-pm2-5-gay-hai-the-nao-toi-suc-khoe/
[13]. Lin C, Ying L, Alexis KHL, Xuejiao D, Tim KTT, Jimmy CHF, Chengcai L, Zhiyuan L, Xingcheng L, Xuguo Z, Qiwei Y (2016) Estimation of long-term population exposure to PM2.5 for dense urban areas using 1-km MODIS data. Remote Sens Environ 179:13–22. https://doi.org/10.1016/j.rse.2016.03.023.
[14]. Norris, G., Ram, V., Katie, W., Patrick, Z., Steve, B., Paatero, P., Eberly, S., Foley, C. (2009). Guidance document for PMF applications with the multilinear engine EPA 600/R-09/032 April 2009.
[15]. P.D.Hien, Vuong Thu Bac et al. (2021). A Comparison Study of Chemical Compositions and Sources of PM1.0 and PM2.5 in Hanoi. Aerosol and Air Quality Research. https://aaqr.org 1 of 16 Volume 21. Issue 10. 210056. https://doi.org/10.4209/aaqr.210056.
[16]. Paatero, P., Tapper, U. (1994). Positive matrix factorization: A non-negative factor model with optimal utilization of error estimates of data values. Environmetrics 5, 111–126. https://doi.org/ 10.1002/ENV.3170050203
[17]. State of global air 2019. s.l. : Health Effects Institue, 2019.
[18]. Seiko Instruments, Inc. SEA2100 series Desktop Fluorescent X-ray Analyzer.
[19]. Sun Z, Yujing M, Yanju L, Longyi S (2013) A comparison study on airborne particles during haze days and non-haze days in Beijing. Sci Total Environ 456–457:1–8. https://doi.org/10.1016/j.scitotenv.2013.03.006.
[20]. TTXVN (15/1/2020). https://en.vietnamplus.vn/air-pollution-costs-vietnamat-least-108-billion-usd-eachyear/167359.vnp
[21]. Institute of Occupational and Environmental Health (2019), Air pollution and what you need to know. Reference links: http://nioeh.org.vn/suc-khoe-moi-truong/o-nhiem-khong-khi-nhung-dieu-nen-biet.
[22]. Quang T.V., Vuong Thu Bac, P.Q. Thang et al. (2023). Trace element characterization and source identification of particulate matter of different sizes in Hanoi, Vietnam. Urban Climate 48 (2023) 101408. https://doi.org/10.1016/j.uclim.2023.101408.
[23]. WHO, 2006. World Health Organization. Regional Office for Europe. Air quality guidelines: Global update 2005: Particulate matter, ozone, nitrogen dioxide and sulfur dioxide. https://apps.who.int/iris/handle/10665/107823 (Accessed on April 26, 2022).
[24]. WHO, 2021. World Health Organization. WHO global air quality guidelines: Particulate matter (PM2.5 and PM10), ozone, nitrogen dioxide, sulfur dioxide and carbon monoxide. https://apps.who.int/iris/handle/10665/345329 (Accessed on April 26, 2022).