Table 1.
Product emission factors for coal- and lignite-fired power plants in 2017 and after adjustment to the BAT conclusions
| Fuel type | 2017 | After 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] | |
| Coal | 0.186 | 0.254 | 0.0113 | 0.119 | 0.135 | 0.0075 |
| Lignite1) | 0.282 | 0.231 | 0.0120 | 0.146 | 0.187 | 0.0086 |

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
Table 2.
Avoided emissions from combustion of the examined fuels in different types of boilers due to compliance with the BAT LCP conclusions
Table 3.
Average operating hours of facilities based on data from the Ministry of Environment [Podręcznik dotyczący zasad udzielania odstępstw… 2017]
| Technology | Operating hours [h/year] |
|---|---|
| KP-WK | 4000 |
| KF-WK | 5500 |
| KP-WB | 5800 |
| KF-WB | 6500 |
Table 4.
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 fuel | Power rate [MWt] | CAPEX and OPEX 2021 [EURO/Mg] | ||
|---|---|---|---|---|
| SO2 | NOx | TSP | ||
| KP-WK | 300–1000 | 565.53 | 720.11 | 6.60 |
| KP-WK | ≥1000 | 630.49 | 605.88 | 4.50 |
| KF-WK | 300–1000 | 379.61 | 968.25 | 4.731) |
| KF-WK | ≥1000 | 363.681) | 764.28 | 3.201) |
| KP-WB | 300–1000 | 388.39 | 576.90 | 10.04 |
| KP-WB | ≥1000 | 330.79 | 479.67 | 6.81 |
| KF-WB | 300–1000 | 350.07 | 694.67 | 4.05 |
| KF-WB | ≥1000 | 291.20 | 549.011) | 2.75 |
Table 5.
Total costs of reducing emissions of the examined pollutants from coal and lignite combustion, related to compliance with BAT LCP Conclusions
| Type of fuel | Costs of reducing emissions [EURO/year] | ||
|---|---|---|---|
| SO2 | NOx | TSP | |
| Coal | 9 608 019 | 17 897 638 | 4 996 |
| Lignite | 8 274 080 | 3 950 497 | 2 715 |
| Total | 17 882 099 | 21 848 135 | 7 710 |
Table 6.
Unit external costs of air pollution and total benefits of reductions due to compliance with BAT LCP conclusions.
| Pollutants | SO2 | NOx | PM10 | PM2.5 |
|---|---|---|---|---|
| Avoided emission [Mg/year] | 41 123 | 36 710 | 1 092 | 468 |
| Unit external costs of emissions [EURO/Mg] | 14 289 | 8 457 | 27 684 | 42 634 |
| Total benefits [EURO/year] | 587 613 339 | 310 458 410 | 30 230 085 | 19 952 156 |
| 50 182 2411) | ||||