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Costs and benefits of reducing air pollutant emissions as a result of bringing coal and lignite-fired power plants into compliance with BAT LCP conclusions Cover

Costs and benefits of reducing air pollutant emissions as a result of bringing coal and lignite-fired power plants into compliance with BAT LCP conclusions

Open Access
|Dec 2023

Figures & Tables

Figure 1.

Emission volumes for examined pollutants from the sector of main activity producer electricity plants fired by coal in 2017 and after adjustment to the BAT conclusions and percentage reduction rates

Figure 2.

Emission volumes for examined pollutants from the sector of main activity producer electricity plants fired by lignite in 2017 and after adjustment to the BAT conclusions and percentage reduction rates

Figure 3.

Total emissions of pollutants from the sector of main activity producer electricity plants, fired by coal and lignite in 2017 and after adaptation to BAT LCP conclusions and percentage reduction rates

Unit external costs of air pollution and total benefits of reductions due to compliance with BAT LCP conclusions_

PollutantsSO2NOxPM10PM2.5
Avoided emission [Mg/year]41 12336 7101 092468
Unit external costs of emissions [EURO/Mg]14 2898 45727 68442 634
Total benefits [EURO/year]587 613 339310 458 41030 230 08519 952 156
50 182 2411)

Total costs of reducing emissions of the examined pollutants from coal and lignite combustion, related to compliance with BAT LCP Conclusions

Type of fuelCosts of reducing emissions [EURO/year]
SO2NOxTSP
Coal9 608 01917 897 6384 996
Lignite8 274 0803 950 4972 715
Total17 882 09921 848 1357 710

Product emission factors for coal- and lignite-fired power plants in 2017 and after adjustment to the BAT conclusions

Fuel type2017After adjustment to the BAT conclusions
SO2 Pcee [kg/GJ]NOx Pcee [kg/GJ]TSP Pcee [kg/GJ]SO2 Pcee [kg/GJ]NOx Pcee [kg/GJ]TSP Pcee [kg/GJ]
Coal0.1860.2540.01130.1190.1350.0075
Lignite1)0.2820.2310.01200.1460.1870.0086

Avoided emissions from combustion of the examined fuels in different types of boilers due to compliance with the BAT LCP conclusions

Type of boiler and fuelPower rate [MWt]Avoided emissions [Mg/year]
SO2NOxTSP
KP-WK300–10007 4073 760389
KP-WK≥10008 40324 491540
KF-WK300–100031935001)
KF-WK≥100001)1601)
KP-WB300–10001 11170649
KP-WB≥100022 4237 387152
KF-WB≥10001 46001)430
Total41 12336 7101 560

Average operating hours of facilities based on data from the Ministry of Environment [Podręcznik dotyczący zasad udzielania odstępstw… 2017]

TechnologyOperating hours [h/year]
KP-WK4000
KF-WK5500
KP-WB5800
KF-WB6500

Unit costs of SO2, NOx, and TSP emission reductions for existing LCP facilities with no high-efficiency flue gas cleaning systems

Type of boiler and fuelPower rate [MWt]CAPEX and OPEX 2021 [EURO/Mg]
SO2NOxTSP
KP-WK300–1000565.53720.116.60
KP-WK≥1000630.49605.884.50
KF-WK300–1000379.61968.254.731)
KF-WK≥1000363.681)764.283.201)
KP-WB300–1000388.39576.9010.04
KP-WB≥1000330.79479.676.81
KF-WB300–1000350.07694.674.05
KF-WB≥1000291.20549.011)2.75
DOI: https://doi.org/10.2478/oszn-2023-0010 | Journal eISSN: 2353-8589 | Journal ISSN: 1230-7831
Language: English
Page range: 62 - 68
Published on: Dec 31, 2023
In partnership with: Paradigm Publishing Services
Publication frequency: 4 issues per year
Related subjects:

© 2023 Janusz Lewandowski, Krzysztof Melka, Anna Dubel, Maria Kłeczek, published by National Research Institute, Institute of Environmental Protection
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 License.