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sector:agriculture:agricultural_soils:start [2021/02/26 13:42] – [Table] gniffkesector:agriculture:agricultural_soils:start [2024/11/06 15:10] (current) – external edit 127.0.0.1
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 The application of residues from the digestion of energy crops (3.D.a.2.c) leads to 54.6 kt NH<sub>3</sub> or 17.5 %. N excretions on pastures (3.D.a.3) have a share of 12.8 kt NH<sub>3</sub> or 4.1 %. The application of residues from the digestion of energy crops (3.D.a.2.c) leads to 54.6 kt NH<sub>3</sub> or 17.5 %. N excretions on pastures (3.D.a.3) have a share of 12.8 kt NH<sub>3</sub> or 4.1 %.
  
-NH<sub>3</sub> emissions from application of residues from the digestion of energy crops are excluded from emission accounting by adjustment as they are not considered in the NEC and Gothenburg commitments (see Chapter 11 - Adjustments and Emissions Reduction Commitments).+NH<sub>3</sub> emissions from application of residues from the digestion of energy crops are excluded from emission accounting by adjustment as they are not considered in the NEC and Gothenburg commitments (see Chapter 11 - Adjustments and Emissions Reduction Commitments [[general:adjustments:adjustment_de-d|Adjustment DE - D - Nitrogen oxides (3.D.a.2.c Other organic fertilisers applied to soils (including compost)') &amp; Ammonia from Energy Crops]]).
  
 In 2019, agricultural soils were the source of 98.6 % (110.7 kt) of the total of NO<sub>x</sub> emissions in the agricultural category (112.2 kt). The NO<sub>x</sub> emissions from agricultural soils are mostly due to application of inorganic fertilizer (3.D.a.1) (50.6 %) and manure (3.D.a.2.a) (33.9 %). Application of residues from digested energy crops (3.D.a.2.c) contributes 10.4 % to agricultural soil emissions, 4.6 % are due to excretions on pastures (3.D.a.3). Emissions from application of sewage sludge (3.D.a.2.b) contribute 0.5 %. In 2019, agricultural soils were the source of 98.6 % (110.7 kt) of the total of NO<sub>x</sub> emissions in the agricultural category (112.2 kt). The NO<sub>x</sub> emissions from agricultural soils are mostly due to application of inorganic fertilizer (3.D.a.1) (50.6 %) and manure (3.D.a.2.a) (33.9 %). Application of residues from digested energy crops (3.D.a.2.c) contributes 10.4 % to agricultural soil emissions, 4.6 % are due to excretions on pastures (3.D.a.3). Emissions from application of sewage sludge (3.D.a.2.b) contribute 0.5 %.
  
-All NO<sub>x</sub> emissions from the agricultural category are excluded from emission accounting by adjustment as they are not considered in the NEC commitments (see Chapter 11 - Adjustments and Emissions Reduction Commitments).+All NO<sub>x</sub> emissions from the agricultural category are excluded from emission accounting by adjustment as they are not considered in the NEC commitments (see Chapter 11 - Adjustments and Emissions Reduction Commitments [[general:adjustments:adjustment_de-c|]] and [[general:adjustments:adjustment_de-d|Adjustment DE - D - Nitrogen oxides (3.D.a.2.c Other organic fertilisers applied to soils (including compost)') &amp; Ammonia from Energy Crops]]).
  
 ==== NMVOC ==== ==== NMVOC ====
-In 2019, the category of agricultural soils contributed 8.6 kt NMVOC or 2.8 % to the total agricultural NMVOC emissions in Germany. The only emission source was cultivated crops (3.D.e). All NMVOC emissions from the agricultural category are excluded from emission accounting by adjustment as they are not considered in the NEC commitments.+In 2019, the category of agricultural soils contributed 8.6 kt NMVOC or 2.8 % to the total agricultural NMVOC emissions in Germany. The only emission source was cultivated crops (3.D.e). All NMVOC emissions from the agricultural category are excluded from emission accounting by adjustment as they are not considered in the NEC commitments (see [[general:adjustments:adjustment_de-c|]]).
  
 ====  TSP, PM₁₀ & PM₂.₅ ==== ====  TSP, PM₁₀ & PM₂.₅ ====
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 =====3.D.a.1 - Inorganic N-fertilizers ===== =====3.D.a.1 - Inorganic N-fertilizers =====
-The calculation of NH<sub>3</sub> and NOx (NO) emissions from the application of inorganic fertilizers is described in Rösemann et al. (2021), Chapter 11.1 ((Rösemann et al. (2021): Rösemann C., Haenel H-D., Vos C., Dämmgen U., Döring U., Wulf S., Eurich-Menden B., Freibauer A., Döhler H., Schreiner C., Osterburg B. & Fuß, R. (2021): Calculations of gaseous and particulate emissions from German Agriculture 1990 –2019. Report on methods and data (RMD), Submission 2021. Thünen Report (in preparation). https://www.thuenen.de/de/ak/arbeitsbereiche/emissionsinventare/)).+The calculation of NH<sub>3</sub> and NOx (NO) emissions from the application of inorganic fertilizers is described in Rösemann et al. (2021), Chapter 11.1 ((Rösemann et al. (2021): Rösemann C., Haenel H-D., Vos C., Dämmgen U., Döring U., Wulf S., Eurich-Menden B., Freibauer A., Döhler H., Schreiner C., Osterburg B. & Fuß, R. (2021): Calculations of gaseous and particulate emissions from German Agriculture 1990 –2019. Report on methods and data (RMD), Submission 2021. Thünen Report (in preparation). https://www.thuenen.de/de/fachinstitute/agrarklimaschutz/arbeitsbereiche/emissionsinventare)).
  
 ==== Activity Data ==== ==== Activity Data ====