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Human health and food quality are greatly affected by the state of the ambient air. In the European Union, Poland is considered as a country that has the most polluted air. The level of PM10 concentration exceeds the EU limit value in almost all the areas of Poland, but higher concentrations are registered in the southern regions, which are considered as the coal heartlands. Katowice, Kraków, and Rzeszów are three big cities in the southern part of Poland and are surrounded by coal mining industries. High PM10 concentrations are usually registered in these three cities, especially in the winter period. In 2018, the peak PM10 daily concentration occurred in the three cities at the same period (04/03/2018 in Rzeszów, 05/03/2018 in Kraków, and 05/03/2018 in Katowice). The aim was to identify the effect of each of the 8 coal mines that exist in Poland on the level PM10 concentration for the first week and March where the highest daily PM10 concentration for the year 2018 was registered. Using HYSPLIT Frequency analysis, the results showed that 100% of the particles coming from Bełchatów, Bolesław Śmiały, Halemba, Jas-Mos, Pniówek and Marcel Coal Mines hit Katowice region, and 10% from Bogdanka. While for Kraków, it was affected by 100% of the particles that are originated from Bolesław Śmiały, Pniówek, Halemba, and Jas-Mos Coal Mines and 10% Bogdanka, Bełchatów, and Marcel Coal Mines. Moreover, Rzeszów was the least affected city by the coal mines, 10% of the particles coming from Bogdanka, Bełchatów, Jas-Mos and Marcel, Halemba, and Pniówek Coal Mines attributed to high PM10 concentration during the first week of March 2018. Katowice and Kraków are more affected by the coal mines industry, Particulate Matter particles originating from the coal mines sites contribute to the high level of PM10 concentration.
Czasopismo
Rocznik
Tom
Strony
27--34
Opis fizyczny
Bibliogr. 27 poz., rys., wykr.
Twórcy
autor
- Mechanical Engineering Doctoral School, Hungarian University of Agriculture and Life Sciences, Gödöllő 2100, Hungary
autor
- Institute of Environmental Science, Hungarian University of Agriculture and Life Sciences, Gödöllő 2100, Hungary
autor
- Institute of Environmental Science, Hungarian University of Agriculture and Life Sciences, Gödöllő 2100, Hungary
Bibliografia
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- [2] Jasiński R, Galant-Gołębiewska M, Nowak M, Kardach M, Kurzawska P, Kurtyka K, et al. Case study of pollution with particulate matter in selected locations of Polish cities. Energies. 2021;14(9):2529. https://doi.org/10.3390/en14092529.
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- [4] Foszcz D, Niedoba T, Siewior J. Models of air pollution propagation in the selected region of Katowice. Atmosphere. 2021;12(6):695. https://doi.org/10.3390/atmos12060695.
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- [6] Traczyk P, Gruszecka-Kosowska A. The condition of air pollution in Kraków, Poland, in 2005–2020, with health risk assessment. International Journal of Environmental Research and Public Health. 2020;17(17):6063. https://doi.org/10.3390/ijerph17176063.
- [7] European Environment Agency. Air quality in Europe: 2020 report. LU: Publications Office; 2020. Available from: https://data.europa.eu/doi/10.2800/786656.
- [8] Kurek S, Goc Z, Greń A, Kapusta E, Formicki G. Influence of air pollution with PM10 and PM2.5 particles on spatial differentiation of death rates in the Małopolska province. In 2021. p. 60.
- [9] Aga E, Samoli E, Touloumi G, Anderson HR, Cadum E, Forsberg B, et al. Short-term effects of ambient particles on mortality in the elderly: Results from 28 cities in the APHEA2 project. European Respiratory Journal. 2003;21(40 suppl):28s–33s. https://doi.org/10.1183/09031936.03.00402803.
- [10] Khomenko S, Cirach M, Pereira-Barboza E, Mueller N, Barrera-Gómez J, Rojas-Rueda D, et al. Premature mortality due to air pollution in European cities: A health impact assessment. The Lancet Planetary Health. 2021;5(3):e121– 134. https://doi.org/10.1016/S2542-5196(20)30272-2.
- [11] Kobza J, Geremek M, Dul L. Characteristics of air quality and sources affecting high levels of PM10 and PM2.5 in Poland, Upper Silesia urban area. Environmental Monitoring and Assessment. 2018;190(9):515. https://doi.org/10.1007/s10661-018-6797-x.
- [12] Juda-Rezler K, Reizer M, Maciejewska K, Błaszczak B, Klejnowski K. Characterization of atmospheric PM2.5 sources at a Central European urban background site. Science of the Total Environment. 2020;713:136729. https://doi.org/10.1016/j.scitotenv.2020.136729.
- [13] Reizer M, Juda-Rezler K. Explaining the high PM10 concentrations observed in Polish urban areas. Air Qual Atmosphere and Health. 2016;9(5):517–31. https://doi.org/10.1007/s11869-015-0358-z.
- [14] Poland – Country Commercial Guide. Energy Sector. In: International Trade Administration. Washington: U.S. Department of Commerce; 2021. [Internet]. Available from: http://www.trade.gov/country-commercial-guides/ poland-energy-sector.
- [15] Bodnar I, Matusz-Kalasz D, Farago D, Palotas AB, Simenfalvi ZK. Electricity production and its environmental effects. Journal of Agricultural and Environmental Law. 2020;15(28):86. https://doi.org/10.21029/JAEL.2020.28.86.
- [16] Breeze P. Electricity Generation and the Environment. London; San Diego, CA: Academic Press, an imprint of Elsevier; 2017.
- [17] Qor-El-Aine A, Benécs J, Béres A, Géczi G. Evaluation of particulate matter low-cost sensors: Laboratory case study. Mechanical Engineering Letters. 2020;20:67–72. https://www.gek.szie.hu/english/sites/default/files/MEL_2020_20.pdf.
- [18] Báthory C, Kiss ML, Trohák A, Dobó Z, Palotás ÁB. Preliminary research for low-cost particulate matter sensor network. E3S Web of Conferences; 2019;100:00004. https://doi.org/10.1051/e3sconf/201910000004.
- [19] Danek T, Zaręba M. The Use of public data from low-cost sensors for the geospatial analysis of air pollution from solid fuel heating during the COVID-19 pandemic spring period in Krakow, Poland. Sensors. 2021;21(15):5208. https://doi.org/10.3390/s21155208.
- [20] Rogulski M. Using low-cost PM monitors to detect local changes of air quality. Polish Journal of Environmental Studies. 2018;27(4);1699–1705. https://doi.org/10.15244/pjoes/77075.
- [21] Benécs J, Hermanucz P, Dodog Z. Examination of Intelligent Measurement System (IMRE) applications. International Conference on Science, Technology, Engineering and Economy. 2018;39.
- [22] Draxler R, Hess G. An overview of the HYSPLIT_4 modeling system for trajectories, dispersion, and deposition. Australian Meteorological Magazine. 1998;47:295–308. https://www.arl.noaa.gov/documents/reports/MetMag.pdf.
- [23] Su L, Yuan Z, Fung JCH, Lau AKH. A comparison of HYSPLIT backward trajectories generated from two GDAS datasets. Science of the Total Environment. 2015;506–507:527–537. https://doi.org/ 10.1016/j. scitotenv.2014.11.072.
- [24] Rolph G, Stein A, Stunder B. Real-time environmental applications and display sYstem: READY. Environmental Modelling and Software. 2017;95:210–228. https://doi. org/10.1016/j.envsoft.2017.06.025.
- [25] Oleniacz R, Gorzelnik T, Szulecka A. A comparative analysis of air pollutant concentrations and inflow trajectories: A case study of selected cities in South-Eastern Poland. E3S Web of Conferences. 2018;45:00060. https:// doi.org/10.1051/e3sconf/20184500060.
- [26] Woźniak J, Pactwa K. Responsible mining – the impact of the mining industry in Poland on the quality of atmospheric air. Sustainability. 2018;10(4):1184. https://doi.org/10.3390/su10041184.
- [27] Helios-Rybicka E, Rybicki S. Impact of coal mining on the environment in Poland. In: 88 Applied Environmental Geology (AEG’03) – BE 228 (2003); 2003.
Typ dokumentu
Bibliografia
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