EGU25-4876, updated on 14 Mar 2025
https://doi.org/10.5194/egusphere-egu25-4876
EGU General Assembly 2025
© Author(s) 2025. This work is distributed under
the Creative Commons Attribution 4.0 License.
Poster | Wednesday, 30 Apr, 16:15–18:00 (CEST), Display time Wednesday, 30 Apr, 14:00–18:00
 
Hall X5, X5.60
Seasonal Trends, Sources, and Health Impacts of PAH-Bound PM10 in Krakow Amidst the COVID-19 Pandemic
Rakshit Jakhar1, Przemysław Furman2, Alicja Skiba2, Dariusz Widel3, Mirosław Zimnoch1, Lucyna Samek2, and Katarzyna Styszko1
Rakshit Jakhar et al.
  • 1AGH University of Krakow, Faculty of Energy and Fuels, Krakow, Poland (jakhar@agh.edu.pl)
  • 2AGH University of Krakow, Faculty of Physics and Applied Computer Science, Krakow, Poland
  • 3UJK Jan Kochanowski University, Institute of Chemistry, Kielce, Poland

The main objective of this research was to evaluate the seasonal variability of PM10-bonded polycyclic aromatic hydrocarbons (PAH) and their sources and analyse their health impacts during the COVID-19 pandemic period.  PM10samples were collected in Krakow in 2020-2021. The chemical composition of PM10 in terms of the content of polycyclic aromatic hydrocarbons (PAHs) was carried out using the gas chromatography-mass spectrometry (GC-MS) technique. A total of 92 samples of particulate matter (PM10 fraction) were analysed. The analyses contained 16 basic PAHs identified by the US EPA as the most harmful. Acenaphtene (Acn), Acenaphthylene (Acy), Anthracene (Ant), Benzo[b]fluoranthene (B[b]F), Benzo[a]anthracene (B[a]A), Benzo[a]pyrene (B[a]P), Benzo[ghi]perylene (B[ghi]P), Benzo[k]fluoranthene (B[k]F), Chrysene (Chry), Dibenzo[ah]anthracene (D[ah]A), Fluoranthene (Flt), Fluorene (Flu), Indeno[1,2,3-cd]pyrene (IP), Naphthalene (Nap), and Phenanthrene (Phen) and Pyrene (Pyr). The information obtained on the concentrations of PAHs was used to determine the profiles of pollution sources, exposure profiles, and the values of toxic equivalency factors recommended by the EPA: mutagenic equivalent to B [a] P (ang. mutagenic equivalent, MEQ), toxic equivalent to B[a]P (ang. toxic equivalent, TEQ) and carcinogenic equivalent to 2,3,7,8-tetrachlorodienzo-p-dioxin (ang. carcinogenic equivalent, CEQ). In addition, the air trajectory frequency analysis were performed to obtain information on the possibility of transporting pollutants from selected areas in the vicinity of the studied site. The analyses were performed using the NOAA Air Resources Laboratory's HYSPLIT model (Hybrid Single-Particle Lagrangian Integrated Trajectory Model) developed by the NOAA Air Resources Laboratory (National Oceanic and Atmospheric Administration). Interpreting the trajectory results provided information on the nature of air pollution sources.

Acknowledgement: This research project was supported by the programme "Excellence Initiative – Research University" for the AGH University of Krakow, Poland [project no. 501.696.7996 L34,D.4,V ed.,wn. 10457

 

How to cite: Jakhar, R., Furman, P., Skiba, A., Widel, D., Zimnoch, M., Samek, L., and Styszko, K.: Seasonal Trends, Sources, and Health Impacts of PAH-Bound PM10 in Krakow Amidst the COVID-19 Pandemic, EGU General Assembly 2025, Vienna, Austria, 27 Apr–2 May 2025, EGU25-4876, https://doi.org/10.5194/egusphere-egu25-4876, 2025.