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sector:agriculture:agricultural_soils:start [2025/02/28 15:46] – [Table] niebuhrsector:agriculture:agricultural_soils:start [2025/03/10 10:53] (current) – [Table] mielke
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 | 3.D.c      |  NA              |  NA     |  NA              |  NA              |  **L/-**           ^  L/-              ^  L/-  |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | | 3.D.c      |  NA              |  NA     |  NA              |  NA              |  **L/-**           ^  L/-              ^  L/-  |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    |
 | 3.D.e      |  NA              |  -/-    |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | | 3.D.e      |  NA              |  -/-    |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    |
-| 3.D.f      |  NA              |  NA     |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    ^  L/-  |  NA    |+| 3.D.f      |  NA              |  NA     |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    ^  -/-  |  NA    |
  {{page>general:Misc:LegendEIT:start}}  {{page>general:Misc:LegendEIT:start}}
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-__Table 4: REC-1: Revised NH<sub>3</sub> and NO<sub>x</sub> emissions, in kilotonnes__+__Table 4: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions [kt] with previous submission__
 ^  NH3 and NOx emissions from fertilizer application, in Gg                                                                                                                                                                   ^^^^^^^^^^^^^^^^ ^  NH3 and NOx emissions from fertilizer application, in Gg                                                                                                                                                                   ^^^^^^^^^^^^^^^^
 |                                                            ^ Submission           ^  1990    ^  1995    ^  2000    ^  2005    ^  2010    ^  2015    ^  2016    ^  2017    ^  2018    ^  2019    ^  2020    ^  2021    ^  2022    ^  2023   ^ |                                                            ^ Submission           ^  1990    ^  1995    ^  2000    ^  2005    ^  2010    ^  2015    ^  2016    ^  2017    ^  2018    ^  2019    ^  2020    ^  2021    ^  2022    ^  2023   ^
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 Further details on recalculations are described in Rösemann et al. (2025) ((Rösemann, C., Vos, C., Haenel, H.-D., Dämmgen, U., Döring, U., Wulf, S., Eurich-Menden, B., Freibauer, A., Döhler, H., Schreiner, C., Osterburg, B., Fuß,R. (2025) Calculations of gaseous and particulate emissions from German agriculture 1990 – 2023 : Report on methods and data (RMD) Submission 2024. www.eminv-agriculture.de)), Chapter 1.3.  Further details on recalculations are described in Rösemann et al. (2025) ((Rösemann, C., Vos, C., Haenel, H.-D., Dämmgen, U., Döring, U., Wulf, S., Eurich-Menden, B., Freibauer, A., Döhler, H., Schreiner, C., Osterburg, B., Fuß,R. (2025) Calculations of gaseous and particulate emissions from German agriculture 1990 – 2023 : Report on methods and data (RMD) Submission 2024. www.eminv-agriculture.de)), Chapter 1.3. 
  
-__Table 7: REC-2: Revised  NH<sub>3</sub> and NO<sub>x</sub> emissions, in kilotonnes__+__Table 7: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions [kt] with previous submission__
 |                       ^ Submission           ^  1990   ^  1995   ^  2000   ^  2005   ^  2010   ^  2015   ^  2016   ^  2017   ^  2018   ^  2019   ^  2020   ^  2021   ^  2022   ^ 2023    ^ |                       ^ Submission           ^  1990   ^  1995   ^  2000   ^  2005   ^  2010   ^  2015   ^  2016   ^  2017   ^  2018   ^  2019   ^  2020   ^  2021   ^  2022   ^ 2023    ^
 |                       |                      |         |         |         |         |         |         |         |         |         |         |         |         |         |         | |                       |                      |         |         |         |         |         |         |         |         |         |         |         |         |         |         |
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 There were no recalculations concerning sewage sludge except the replacement of extrapolated activity data in 2022 with data from the Federal Statistical Office. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.  There were no recalculations concerning sewage sludge except the replacement of extrapolated activity data in 2022 with data from the Federal Statistical Office. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3. 
  
-__Table 9: Revised NH<sub>3</sub> and NO<sub>x</sub> emissions, in kilotonnes__+__Table 9: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions [kt] with previous submission__
 |                        ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023  ^ |                        ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023  ^
 |                        |                      |        |        |        |        |        |        |        |        |        |        |        |        |        |       | |                        |                      |        |        |        |        |        |        |        |        |        |        |        |        |        |       |
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 Recalculations after 2013 are mainly due to the update of activity data. Concerning NH<sub>3</sub> emissions, small differences occur in all years. This is because the underlying spatial distribution of imported manure is different, which results in different IEFs compared to last year’s submission. Another reason is the interpolation of RAUMIS distribution data before 1999 (see [[sector:agriculture:start|main page of the agricultural sector]], list of recalculation **reasons, 19, 20 and 21**, and Rösemann et al. (2025), Chapter 1.3).  Recalculations after 2013 are mainly due to the update of activity data. Concerning NH<sub>3</sub> emissions, small differences occur in all years. This is because the underlying spatial distribution of imported manure is different, which results in different IEFs compared to last year’s submission. Another reason is the interpolation of RAUMIS distribution data before 1999 (see [[sector:agriculture:start|main page of the agricultural sector]], list of recalculation **reasons, 19, 20 and 21**, and Rösemann et al. (2025), Chapter 1.3). 
  
-__Table 12:REC-4: Revised NH<sub>3</sub> and NO<sub>x</sub> emissions from application of other organic fertilizers, in kilotonnes__+__Table 12: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions from application of other organic fertilizers [kt] with previous submission__
 |                       ^ Submission           ^  1990  ^  1995  ^  2000  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^ |                       ^ Submission           ^  1990  ^  1995  ^  2000  ^  2013  ^  2014  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^
 |                       |                      |        |        |        |        |        |        |        |        |        |        |        |        |        |        | |                       |                      |        |        |        |        |        |        |        |        |        |        |        |        |        |        |
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 The main reason for that is the correction of the horse animal numbers by a factor of 2.75 (see main page of the agricultural sector, list of recalculations, **No. 4)**. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.   The main reason for that is the correction of the horse animal numbers by a factor of 2.75 (see main page of the agricultural sector, list of recalculations, **No. 4)**. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.  
  
-__Table 15: REC-5: Revised NH<sub>3</sub> and NO<sub>x</sub> emissions, in kilotonnes__+__Table 15: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions [kt] with previous submission__
 |                      ^  NH3 and NOx emissions from grazing, in Gg                                                                                                                  ||||||||||||||| |                      ^  NH3 and NOx emissions from grazing, in Gg                                                                                                                  |||||||||||||||
 |                      ^ Submission                                  ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^ |                      ^ Submission                                  ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^
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 ==== Emission factors ==== ==== Emission factors ====
-According to the methodology given in EMEP (2023) the emission factor for the NH<sub>3</sub> emissions from crop residues applied to the soil is zero if the N content of the above ground crop residues is below or equal to the threshold of 0.0132 kg N per kg dry matter. In all other cases the NH<sub>3</sub> emission factor is determined using the following linear regression,  +According to the methodology given in EMEP (2023) the emission factor for the NH<sub>3</sub> emissions from crop residues applied to the soil is zero if the N content of the above ground crop residues is below or equal to the threshold of 0.0132 kg N per kg dry matter. In all other cases the NH<sub>3</sub> emission factor is determined using the following linear regression, see EMEP (2023): 
-**Formel** see EMEP (2023):EF_〖NH〗_(3_x )=(410×N_(〖above dm〗_x )-5.42)÷100 **Formel**+ 
 +EF_//NH//<sub>3</sub><sub>x</sub>=(410×N<sub>above dm</sub><sub>x</sub> -5.42)÷100  
 + 
 Where x is the according crop and N<sub>above</sub> dm is the N content of the above ground dry matter. Where x is the according crop and N<sub>above</sub> dm is the N content of the above ground dry matter.
 The implied emission factors provided in the following table are defined as ratio of the total NH<sub>3</sub>-N emissions from crop residues to the total N in aboveground crop residues. The implied emission factors provided in the following table are defined as ratio of the total NH<sub>3</sub>-N emissions from crop residues to the total N in aboveground crop residues.
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 There are no recalculations because this source is reported the first time. There are no recalculations because this source is reported the first time.
  
-__Table 18: REC-6: Revised NH<sub>3</sub> emissions, in kilotonnes__+__Table 18: Comparison of NH<sub>3</sub> emissions [kt] with previous submission__
 |       |             ^  NH3 emissions from crop residues, in Gg                                                                                             |||||||||||||| |       |             ^  NH3 emissions from crop residues, in Gg                                                                                             ||||||||||||||
 |       ^ Submission  ^ 1990                                      ^ 1995  ^ 2000  ^ 2005  ^ 2010  ^ 2015  ^ 2016  ^ 2017  ^ 2018  ^ 2019  ^ 2020  ^ 2021  ^ 2022  ^ 2023  ^ |       ^ Submission  ^ 1990                                      ^ 1995  ^ 2000  ^ 2005  ^ 2010  ^ 2015  ^ 2016  ^ 2017  ^ 2018  ^ 2019  ^ 2020  ^ 2021  ^ 2022  ^ 2023  ^
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 For all years, totals of TSP, PM<sub>10</sub> and PM<sub>2.5</sub> emissions are higher than those of last year’s submission. This is mostly due to the introduction of cover crops to the calculation method (see main page of the agricultural sector, list of recalculations, No. 2). Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.   For all years, totals of TSP, PM<sub>10</sub> and PM<sub>2.5</sub> emissions are higher than those of last year’s submission. This is mostly due to the introduction of cover crops to the calculation method (see main page of the agricultural sector, list of recalculations, No. 2). Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.  
  
-__Table 21: REC-6: Revised particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>), in kilotonnes__+__Table 21: Comparison of particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>) [kt] with previous submission__
 ^  TSP, PM10, PM2.5 emissions from crop production, in Gg                                                                                                                                        |||||||||||||||| ^  TSP, PM10, PM2.5 emissions from crop production, in Gg                                                                                                                                        ||||||||||||||||
 |                                                          ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^ |                                                          ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023   ^
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 There were no recalculations. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.  There were no recalculations. Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3. 
  
-__Table 24: REC-8: Revised NMVOC emissions, in kilotonnes__+__Table 24: Comparison of NMVOC emissions [kt] with previous submission__
 |         | Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023  ^ |         | Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^ 2023  ^
 |  NMVOC  ^ current submission   |   7.69 |   8.19 |   8.79 |   9.17 |   9.53 |   9.91 |   9.69 |   9.74 |   7.82 |   8.56 |   9.16 |   9.44 |   8.91 | 9.23  | |  NMVOC  ^ current submission   |   7.69 |   8.19 |   8.79 |   9.17 |   9.53 |   9.91 |   9.69 |   9.74 |   7.82 |   8.56 |   9.16 |   9.44 |   8.91 | 9.23  |