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sector:energy:fuel_combustion:small_combustion:stationary_small_combustion:residential [2021/01/26 16:00] – [Table] juhrich | sector:energy:fuel_combustion:small_combustion:stationary_small_combustion:residential [2022/03/08 07:19] – [Table] kotzulla | ||
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===== Short description ===== | ===== Short description ===== | ||
- | {{ : | + | {{ : |
In source category // | In source category // | ||
- | ^ | + | ^ Category Code ^ Method |
- | | T2, T3 | NS | CS, D | | + | | 1.A.4.b.i |
+ | ^ ^ | ||
+ | | Key Category: | ||
{{page> | {{page> | ||
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^ Pollutant | ^ Pollutant | ||
^ Fuel | ^ Fuel | ||
- | ^ Hard Coal | 61.1 | 385.5 | 3,422 | 67.0 | | + | ^ Hard Coal | 61.1 | 385.5 | 3,422 | 67.0 | |
- | ^ Hard Coal Coke | + | ^ Hard Coal Coke |
- | ^ Hard Coal Briquettes | + | ^ Hard Coal Briquettes |
- | ^ Lignite Briquettes | + | ^ Lignite Briquettes |
- | ^ Natural Wood | + | ^ Natural Wood |
- | ^ Light Fuel Oil | + | ^ Light Fuel Oil |
- | ^ Natural Gas | 20.5 | 0.1 | | + | ^ Natural Gas | 20.5 | 0.1 | |
TSP and PM emission factors are to a large extend based on measurements without condensed compounds, according to CEN-TS 15883, annex I. | TSP and PM emission factors are to a large extend based on measurements without condensed compounds, according to CEN-TS 15883, annex I. | ||
- | PAH measurement data contain the following individual substances: Benzo(a)pyrene, | + | |
===== Trend Discussion for Key Sources ===== | ===== Trend Discussion for Key Sources ===== | ||
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{{: | {{: | ||
- | Annual fluctuations of all fuel types in source category // | + | Annual fluctuations of all fuel types in source category // |
==== Sulfur Oxides & Nitrogen Oxides | ==== Sulfur Oxides & Nitrogen Oxides | ||
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{{: | {{: | ||
- | The main driver of the POP emission trend are coal and fuelwood. PCDD/F emissions from coal fired furnaces are declining but the effect is retarded by increasing wood consumption. The same influencing variables apply accordingly to the PAH emission trends. The emission trend of HCB shows a high dominance of emissions from wood-burning. | + | The main driver of the POP emission trend are coal and fuelwood. PCDD/F emissions from coal fired furnaces are declining but the effect is retarded by increasing wood consumption. The same influencing variables apply accordingly to the PAH emission trends. The emission trend of HCB shows a high dominance of emissions from wood-burning. |
It's known that in spite of the existing legislation, | It's known that in spite of the existing legislation, | ||
===== Recalculations ===== | ===== Recalculations ===== | ||
- | Recalculations were necessary for the latest reference year (2018) due to the availability of the National Energy Balance. Germany has a federal structure which causes a time lack of the National Energy Balance. Therefore recalculations are always necessary. | + | Recalculations were necessary for the latest reference year (2019) due to the availability of the National Energy Balance. Germany has a federal structure which causes a time lack of the National Energy Balance. Therefore recalculations are always necessary. |
Further recalculations due to a comprehensive revision of PAH Emission factors. | Further recalculations due to a comprehensive revision of PAH Emission factors. | ||
<WRAP center round info 100%> | <WRAP center round info 100%> | ||
- | For specific **information on recalculated emission estimates for Base Year and 2018**, please see the pollutant specific recalculation tables following chapter [[General: | + | For specific **information on recalculated emission estimates for Base Year and 2019**, please see the pollutant specific recalculation tables following chapter [[General: |
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