DOI QR코드

DOI QR Code

Major factors determining the size distributions of atmospheric water-soluble aerosol particles at an urban site during winter

겨울철 도시지역 대기 수용성 에어로졸 입자의 크기 분포를 결정하는 주요 인자

  • Park, Seungshik (Department of Environment and Energy Engineering, Chonnam National University)
  • 박승식 (전남대학교 환경에너지공학과)
  • Received : 2021.08.03
  • Accepted : 2021.09.01
  • Published : 2021.09.30

Abstract

Size distributions of atmospheric particulate matter (PM) and its water-soluble organic and inorganic components were measured between January and February 2021 at an urban site in Gwangju in order to identify the major factors that determine their size distributions. Their size distributions during the study period were mainly divided into two groups. In the first group, PM, NO3-, SO42-, NH4+ and water-soluble organic carbon (WSOC) exhibited bi-modal size distributions with a dominant condensation mode at a particle size of 0.32 ㎛. This group was dominated by local production of secondary water-soluble components under atmospheric stagnation and low relative humidity (RH) conditions, rather than long-range transportation of aerosol particles from China. On the other hand, in the second group, they showed tri-modal size distributions with a very pronounced droplet mode at a diameter of 1.0 ㎛. These size distributions were attributable to the local generation and accumulation of secondary aerosol particles under atmospheric conditions such as atmospheric stagnation and high RH, and an increase in the influx of atmospheric aerosol particles by long-distance transportation abroad. Contributions of droplet mode NO3-, SO42-, NH4+ and WSOC to fine particles in the second group were significantly higher than those in the first group period. However, their condensation mode contributions were about two-fold higher in the first group than in the second group. The significant difference in the size distribution of the accumulation mode of the WSOC and secondary ionic components between the two groups was due to the influx of aerosol particles with a long residence time by long-distance transport from China and local weather conditions (e.g., RH).

Keywords

Acknowledgement

이 논문은 2020년도 정부(교육부)의 재원으로 한국연구재단 기초연구사업의 지원(NRF-2020R1I1A3A04036617)과 2020년 정부(과학기술정보통신부)의 재원으로 한국연구재단 기후변화대응 기술개발사업의 지원을 받아 수행된 연구입니다(No. 2019M1A2A2103953). 또한 대기측정 및 성분 분석에 도움을 준 전남대학교 환경에너지공학과의 성병철, 최지율, 최연정 학생에게 감사를 표합니다.

References

  1. Brook, R.D., Rajagopalan, S., Pope, A., Brook, J.R., Bhatnagar, A., Diez-Roux, A.V., Holguin, F., Hong, Y., Luepker, R.V., Mittleman, M.A., Peters, A., Siscovick, D., Smith, S.C., Whitxel, L., and Kaufman, J.D. (2010). Particulate matter air pollution and cardiovascular disease: An up-date to the scientific statement from the American Heart Association, Circulation, 121, 2331-2378. https://doi.org/10.1161/CIR.0b013e3181dbece1
  2. Donaldson, K., Tran, C.L., and ManNee, W. (2002). Deposition and effects of fine and ultrafine particles in the respiratory tract, European Respiratory Monograph, 21, 77-92.
  3. Dockery, D.W. (2001). Epidemiological evidence of cardiovascular effects of particulate air pollution, Environmental Health Perspectives, 109, 483-486. https://doi.org/10.2307/3454657
  4. Dominici, F., Peng, R.D., Bell, M.L., Pham, L., McDermott, A., Zeger, S.L., and Samet, J.M. (2006). Fine particulate air pollution and hospital admission for cardiovascular and respiratory diseases, Journal of American Medical Association, 295, 1127-1134. https://doi.org/10.1001/jama.295.10.1127
  5. Hinds, W.C. (1999). Aerosol technology: Properties, behavior, and measurement of airborne particles, John Wiley & Sons: New York, NY.
  6. Heyder, J., Gebhart, J., Rudolf, G., Schiller, C.F., and Stahlhofen, W. (1986). Deposition of particles in the human respiratory tract in the size range 0.005-15 ㎛, Journal of Aerosol Science, 17, 811-825. https://doi.org/10.1016/0021-8502(86)90035-2
  7. Lippmann, M., Yeates, D.B., and Albert, R.E. (1980). Deposition, retention and clearance of inhaled particles, British Journal of Industrial Medicine, 37, 337-362.
  8. Oberdorster, G., Oberdorster, E., and Obertorster, J. (2005). Nanotoxicology: an emerging discipline evolving from studies of ultrafine particles, Environmental Health Perspectives, 113, 823-839. https://doi.org/10.1289/ehp.7339
  9. Ostro, B., Hu, J., Goldberg, D., Reynolds, P., Hertz, A., Bernstein, L., and Kleeman, M.J. (2015). Associations of mortality with long-term exposures to fine and ultrafine particles, species and sources: Results from the California teachers study cohort, Environmental Health Perspectives, 123, 549-556. https://doi.org/10.1289/ehp.1408565
  10. Park, S.S., Sim, S.Y., Bae, M.S., and Schauer, J.J. (2013). Size distribution of water-soluble components in particulate matter emitted from biomass burning, Atmospheric Environment, 73, 62-72. https://doi.org/10.1016/j.atmosenv.2013.03.025
  11. Park, S. and Yu, G. (2018). Effect of air stagnation conditions on mass size distributions of water-soluble aerosol particles, Journal of Korean Society for Atmospheric Environment, 34(3), 418-429. https://doi.org/10.5572/KOSAE.2018.34.3.418
  12. Park, S. (2019). Change in mass size distributions of ambient aerosol particles during asian dust storm event in late fall at an urban site of Gwangju, Journal of Korean Society for Atmospheric Environment, 35(4), 502-515. https://doi.org/10.5572/kosae.2019.35.4.502
  13. Park, S. and Yu, G.-H. (2019). Absorption properties and size distribution of aerosol particles during the fall season at an urban site of Gwangju, Korea, Environmental Engineering Research, 24(1), 159-172. https://doi.org/10.4491/eer.2018.166
  14. Raaschou-Nielsen, O., et al. (2016). Particulate matter air pollution components and risk for lung cancer, Environmental International, 87, 66-73. https://doi.org/10.1016/j.envint.2015.11.007
  15. Seinfeld, J.H. and Pandis, S.N. (2006). Atmospheric chemistry and physics: From air pollution to climate change, 2nd Ed., John Wiley & Sons, Inc., pp. 440-444.
  16. Son, S.-C. and Park, S.-S. (2019). Mass size distributions of water-soluble aerosol particles during high fine particulate matter episode over Gwangju in November 2018, Journal of Korean Society for Atmospheric Environment 35(4), 423-437. https://doi.org/10.5572/kosae.2019.35.4.423
  17. Stafoggia, M., Samoli, E., Alessandrini, E., Cadum, E., Ostro, B., Berti, G., Faustini, A., Jacquemin, B., Linares, C., Pascal, M., Randi, G., Ranzi, A., Stivanello, E., and Forastiere, F. (2013). Short-term associations between fine and coarse particulate matter and hospitalizations in Southern Europe: results from the MED-PARTICLES Project, Environmental Health Perspectives, 121, 1026-1033. https://doi.org/10.1289/ehp.1206151
  18. WHO (2006). Air quality guidelines: Global update 2005. particulate matter, ozone, nitrogen dioxide and sulfur Dioxide, World Health Organization.
  19. Yu, G.-H., Park, S.-S., Jung, S. A., Jo, M.R., Lim, Y.J., Shin, H.J., Lee, S.B., and Ghim, Y.S. (2018). Investigation on characteristics of high PM2.5 pollution occurred during October 2015 in Gwangju, Journal of Korean Society for Atmospheric Environment, 34(4), 567-587. https://doi.org/10.5572/KOSAE.2018.34.4.567
  20. Yu, G.-H., Lee, B.-J., Pakr, S.S, Jung, S.A., Jo, M.R., Lim, Y.J., and Kim, S. (2019). A case study of severe PM2.5 event in the Gwangju urban area during February 2014, Journal of Korean Society for Atmospheric Environment, 35(2), 195-213. https://doi.org/10.5572/kosae.2019.35.2.195