meta data for this page
  •  

Differences

This shows you the differences between two versions of the page.

Link to this comparison view

Both sides previous revisionPrevious revision
general:projections:wm-scenario [2025/04/30 09:13] – kotzullageneral:projections:wm-scenario [2025/04/30 09:14] (current) – kotzulla
Line 23: Line 23:
 The concrete procedure is illustrated using the example of NO<sub>X</sub> emissions from the use of raw lignite as fuel for heat generation in public district heating plants.  The concrete procedure is illustrated using the example of NO<sub>X</sub> emissions from the use of raw lignite as fuel for heat generation in public district heating plants. 
  
-The specific BAT-associated emission levels for lignite can be found in Commission Implementing Decision (EU) 2017/1442 BAT 20. With a reference oxygen of 6 %, the plants are differentiated according to size and specified with the emission levels in mg/Nm<sup>3</sup>. The upper end of the emission levels is interpreted as a maximum limit value and converted into kg/TJ using the specific conversion factor of 2.40 (see Table 4). The calculated maximum limit value is therefore averaged for each plant size, taking into account the number of plants, and thus, the estimated value for the necessary NO<sub>X</sub> emission factor for compliance with the maximum limit value is calculated in accordance with the BAT conclusions. The necessary data can be found in Table 6. This shows the plants subdivision according to their RTI with the assigned maximum limit values as annual averages in mg/Nm<sup>3</sup> and kg/TJ. +The specific BAT-associated emission levels for lignite can be found in Commission Implementing Decision (EU) 2017/1442 BAT 20. With a reference oxygen of 6%, the plants are differentiated according to size and specified with the emission levels in mg/Nm<sup>3</sup>. The upper end of the emission levels is interpreted as a maximum limit value and converted into kg/TJ using the specific conversion factor of 2.40 (see Table 4). The calculated maximum limit value is therefore averaged for each plant size, taking into account the number of plants, and thus, the estimated value for the necessary NO<sub>X</sub> emission factor for compliance with the maximum limit value is calculated in accordance with the BAT conclusions. The necessary data can be found in Table 6. This shows the plants subdivision according to their RTI with the assigned maximum limit values as annual averages in mg/Nm<sup>3</sup> and kg/TJ. 
  
 __Table 6: Emission limit values (annual averages) when using raw lignite in existing plants__  __Table 6: Emission limit values (annual averages) when using raw lignite in existing plants__ 
Line 50: Line 50:
  
 <m> EF_{heavy fuel oil} = (400mg/Nm³ ÷ 3.39) • 4.5% • 0.5 + (270 mg/Nm³ ÷ 3.39) • 4.5% • 0.5 + (270 mg/Nm³ ÷ 3.39) • 95.5% • 0.5 + (110 mg/Nm³ ÷ 3.39) • 95.5% • 0.5 = 58.0 kg/TJ </m>  <m> EF_{heavy fuel oil} = (400mg/Nm³ ÷ 3.39) • 4.5% • 0.5 + (270 mg/Nm³ ÷ 3.39) • 4.5% • 0.5 + (270 mg/Nm³ ÷ 3.39) • 95.5% • 0.5 + (110 mg/Nm³ ÷ 3.39) • 95.5% • 0.5 = 58.0 kg/TJ </m> 
- 
-    (2) EF (heavy fuel oil) = (400 mg/Nm³ ÷ 3.39) * 4.5 % * 0.5 + (270 mg/Nm³ ÷ 3.39) * 4.5 % * 0.5 + (270 mg/Nm³ ÷ 3.39) * 95.5 % * 0.5 + (110 mg/Nm³ ÷ 3.39) * 95.5 % * 0.5 = 58.0 kg/TJ. 
  
 Thus, the maximum emission quantity is applicable law and is below the inventory emission factor for the reference year 2022 under conservative assumptions and therefore assigned to the WM scenario for 2030 and beyond. The emission factor for 2025 was linearly interpolated between 2022 and 2030. Thus, the maximum emission quantity is applicable law and is below the inventory emission factor for the reference year 2022 under conservative assumptions and therefore assigned to the WM scenario for 2030 and beyond. The emission factor for 2025 was linearly interpolated between 2022 and 2030.