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sector:agriculture:agricultural_other:start [2021/12/23 10:04] – [Table] doeringsector:agriculture:agricultural_other:start [2022/09/19 07:46] (current) – Fix link hausmann
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 | 3.I                                              | Storage of digestate from energy crops  | T2 (NH<sub>3</sub>, NO<sub>x</sub>)  | Q, PS  | CS (NH<sub>3</sub>, NO<sub>x</sub>)  |                     | | 3.I                                              | Storage of digestate from energy crops  | T2 (NH<sub>3</sub>, NO<sub>x</sub>)  | Q, PS  | CS (NH<sub>3</sub>, NO<sub>x</sub>)  |                     |
  
-^  Key Category  ^  SO₂     ^  NOₓ  ^  NH₃  ^  NMVOC  ^  CO   ^  BC   ^  Pb   ^  Hg   ^  Cd   ^  Diox  ^  PAH  ^  HCB  ^  TSP  ^  PM₁₀  ^  PM₂ ₅  ^ +^                ^  NO<sub>x</sub>  ^  NMVOC  ^  SO<sub>2</sub>  ^  NH<sub>3</sub>  ^  PM<sub>2.5</sub>  ^  PM<sub>10</sub>  ^  TSP  ^  BC  ^  CO  ^  Pb  ^  Cd  ^  Hg  ^  Diox  ^  PAH  ^  HCB  ^ 
-| 3.I             |  -          |  -/-  |  -/-  |  -      |  -    |  -    |  -    |  -    |  -    |  -     |  -    |  -    |  -    |  -     |  -      |+| Key Category:  |  -/-             |  -      |  -               |  -/-             |  -                 |  -                |  -    |  -   |  -   |  -   |  -   |  -   |  -     |  -    |  -    |
  {{page>general:Misc:LegendEIT:start}}  {{page>general:Misc:LegendEIT:start}}
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-In 2020, NH<sub>3</sub>  emissions from category 3.I (agriculture other) derived up to 0.6 % from total agricultural emissions, which is equal to ~ 3.1 kt NH<sub>3</sub> . NO<sub>x</sub>  emissions from category 3.I contribute 0.16 % (~ 0.17 kt) to the total agricultural emissions. All these emissions originate from the storage of digestate from energy crops (for details on anaerobic digestion of energy crops see Vos et al. 2022, Chapter 10 ((Vos et al. (2022): Vos C., Rösemann C., Haenel H-D., Dämmgen U., Döring U., Wulf S., Eurich-Menden B., Freibauer A., Döhler H., Schreiner C., Osterburg B. & Fuß, R. (2022): Calculations of gaseous and particulate emissions from German Agriculture 1990 –2020. Report on methods and data (RMD), Submission 2022. (in preparation). https://www.thuenen.de/de/ak/arbeitsbereiche/emissionsinventare/)). The emissions resulting from the application of energy crop digestates as organic fertilizer are dealt with under 3.D.a.2.c.+In 2020, NH<sub>3</sub>  emissions from category 3.I (agriculture other) derived up to 0.6 % from total agricultural emissions, which is equal to ~ 3.1 kt NH<sub>3</sub> . NO<sub>x</sub>  emissions from category 3.I contribute 0.16 % (~ 0.17 kt) to the total agricultural emissions. All these emissions originate from the storage of digestate from energy crops (for details on anaerobic digestion of energy crops see Vos et al. 2022, Chapter 10 ((Vos C, Rösemann C, Haenel H-D, Dämmgen U, Döring U, Wulf S, Eurich-Menden B, Freibauer A, Döhler H, Schreiner C, Osterburg B, Fuß R (2022) Calculations of gaseous and particulate emissions from German agriculture 1990 – 2020 : Report on methods and data (RMD) Submission 2022. Braunschweig: Johann Heinrich von Thünen-Institut, 452 p, Thünen Rep 91, DOI:10.3220/REP1646725833000. https://www.thuenen.de/de/fachinstitute/agrarklimaschutz/arbeitsbereiche/emissionsinventare)). The emissions resulting from the application of energy crop digestates as organic fertilizer are dealt with under 3.D.a.2.c.
  
 ==== Activity Data ==== ==== Activity Data ====
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 ==== Methodology ==== ==== Methodology ====
  
-The calculation of emissions from storage of digestate from energy crops considers two different types of storage, i. e. gastight storage and open tank. The frequencies of these storage types are also provided by KTBL (see Table 2). There are no emissions of NH<sub>3</sub>  and NO from gastight storage of digestate. Hence the total emissions from the storage of digestate are calculated by multiplying the amount of N in the digestate leaving the fermenter with the relative frequency of open tanks and the emission factor for open tank. The amount of N in the digestate leaving the fermenter is identical to the N amount in energy crops fed into anaerobic digestion (see Table 1) because N losses from pre-storage are negligible and there are no N losses from fermenter (see Rösemann et al. 2021, Chapter 10.2.1.)+The calculation of emissions from storage of digestate from energy crops considers two different types of storage, i.e. gastight storage and open tank. The frequencies of these storage types are also provided by KTBL (see Table 2). There are no emissions of NH<sub>3</sub>  and NO from gastight storage of digestate. Hence the total emissions from the storage of digestate are calculated by multiplying the amount of N in the digestate leaving the fermenter with the relative frequency of open tanks and the emission factor for open tank. The amount of N in the digestate leaving the fermenter is identical to the N amount in energy crops fed into anaerobic digestion (see Table 1) because N losses from pre-storage are negligible and there are no N losses from fermenter (see Vos et al. 2022, Chapter 10.2.1.).
  
 ==== Emission factors ==== ==== Emission factors ====
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 //Table 3: IEF for NH<sub>3</sub> -N and NO-N emissions from storage of digested energy crops// //Table 3: IEF for NH<sub>3</sub> -N and NO-N emissions from storage of digested energy crops//
  
-^  1990                                                             ^  1995    ^  2000    ^  2005    ^  2010    ^  2011    ^  2012    ^  2013    ^  2014    ^  2015    ^  2016    ^  2017    ^  2018    ^  2019    ^ +^  1990                                                             ^  1995    ^  2000    ^  2005    ^  2010    ^  2011    ^  2012    ^  2013    ^  2014    ^  2015    ^  2016    ^  2017    ^  2018    ^  2019    ^  2020    ^ 
-| **IEF in kg NH<sub>3</sub>-N per kg N in digested energy crops**                                                                                                                                    |||||||||||||| +| **IEF in kg NH<sub>3</sub>-N per kg N in digested energy crops**                                                                                                                                              ||||||||||||||| 
-| 0.0252                                                            | 0.0240   | 0.0228   | 0.0212   | 0.0146   | 0.0132   | 0.0102   | 0.0096   | 0.0091   | 0.0089   | 0.0089   | 0.0089   | 0.0089   | 0.0089   | +|                                                            0.0252 |   0.0240 |   0.0228 |   0.0212 |   0.0146 |   0.0132 |   0.0102 |   0.0096 |   0.0091 |   0.0089 |   0.0089 |   0.0089 |   0.0089 |   0.0087 |   0.0087 | 
-| **IEF in kg NO-N per kg N in digested energy crops **                                                                                                                                               |||||||||||||| +| **IEF in kg NO-N per kg N in digested energy crops **                                                                                                                                                         ||||||||||||||| 
-| 0.00050                                                           | 0.00048  | 0.00045  | 0.00042  | 0.00029  | 0.00026  | 0.00020  | 0.00019  | 0.00018  | 0.00018  | 0.00018  | 0.00018  | 0.00018  | 0.00018  |+|                                                           0.00050 |  0.00048 |  0.00045 |  0.00042 |  0.00029 |  0.00026 |  0.00020 |  0.00019 |  0.00018 |  0.00018 |  0.00018 |  0.00018 |  0.00018 |  0.00017 |  0.00017 |
  
  
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 ==== Recalculations ==== ==== Recalculations ====
  
-All time series of the emission inventory have completely been recalculated since 1990. Table REC-1 shows the effects of recalculations on NH<sub>3</sub> and NO<sub>x</sub> emissions from storage of anaerobically digested energy crops. Differences to last year’s submission occur only in 2018 and are due to the update of activity data (see main page of the agricultural sector, [[sector:agriculture:start|Chapter 5 - NFR 3 - Agriculture (OVERVIEW)]], **recalculation reason No 15**). For further details on recalculations see Rösemann et al. (2021), Chapter 3.5.2.+All time series of the emission inventory have completely been recalculated since 1990. Table REC-1 shows the effects of recalculations on NH<sub>3</sub> and NO<sub>x</sub> emissions from storage of anaerobically digested energy crops. Differences to last year’s submission occur only in 2019 and are due to the update of activity data (see main page of the agricultural sector, [[sector:agriculture:start|Chapter 5 - NFR 3 - Agriculture (OVERVIEW)]], **recalculation reason No 16**). For further details on recalculations see Vos et al. (2022), Chapter 3.5.2.
  
 +//Table REC-1: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions of the submissions (SUB) 2021 and 2022//
  
 +^ NH<sub>3</sub> / NO<sub>x</sub> emissions in Gg                                                                                                                                                |||||||||||||||||
 +^                                                  ^  SUB  ^  1990   ^  1995   ^  2000   ^  2005   ^  2010   ^  2011   ^  2012   ^  2013   ^  2014   ^  2015   ^  2016   ^  2017   ^  2018   ^  2019   ^  2020   ^
 +| NH<sub>3</sub>                                   | 2022  |  0.0015 |  0.0190 |  0.1563 |  1.2267 |  3.0426 |  3.4504 |  2.9206 |  3.3062 |  3.2814 |  3.3428 |  3.3004 |  3.2741 |  3.2013 |  3.1419 |  3.1419 |
 +| NH<sub>3</sub>                                   | 2021  |  0.0015 |  0.0190 |  0.1563 |  1.2267 |  3.0426 |  3.4504 |  2.9206 |  3.3062 |  3.2814 |  3.3428 |  3.3004 |  3.2741 |  3.2013 |  3.2013 |         |
 +| NO<sub>x</sub>                                   | 2022  |  0.0001 |  0.0010 |  0.0084 |  0.0659 |  0.1634 |  0.1852 |  0.1568 |  0.1775 |  0.1762 |  0.1795 |  0.1772 |  0.1758 |  0.1719 |  0.1687 |  0.1687 |
 +| NO<sub>x</sub>                                   | 2021  |  0.0001 |  0.0010 |  0.0084 |  0.0659 |  0.1634 |  0.1852 |  0.1568 |  0.1775 |  0.1762 |  0.1795 |  0.1772 |  0.1758 |  0.1719 |  0.1719 |         |
  
-//Table REC-1: Comparison of NH<sub>3</sub> and NO<sub>x</sub> emissions of the submissions (SUB) 2020 and 2021// +<WRAP center round info 60%> 
- +For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 8.1 - Recalculations]]. 
-^ NH<sub>3</sub> / NO<sub>x</sub> emissions in Gg                                                                                                                                       ||||||||||||^||| +</WRAP>
-^                                                  ^  SUB  ^  1990   ^  1995   ^  2000   ^  2005   ^  2010   ^  2011   ^  2012   ^  2013   ^  2014   ^  2015   ^  2016   ^  2017   ^  2018   ^  2019   ^ +
-| NH<sub>3</sub>                                   | 2021  | 0.0015  | 0.0190  | 0.1563  | 1.2267  | 3.0426  | 3.4504  | 2.9206  | 3.3062  | 3.2814  | 3.3428  | 3.3004  | 3.2741  | 3.2013  | 3.2013  | +
-| NH<sub>3</sub>                                   | 2020  | 0.0015  | 0.0190  | 0.1563  | 1.2267  | 3.0426  | 3.4504  | 2.9206  | 3.3062  | 3.2814  | 3.3428  | 3.3004  | 3.2741  | 3.2895  |         | +
-| NO<sub>x</sub>                                   | 2021  | 0.0001  | 0.0010  | 0.0084  | 0.0659  | 0.1634  | 0.1852  | 0.1568  | 0.1775  | 0.1762  | 0.1795  | 0.1772  | 0.1758  | 0.1719  | 0.1719  | +
-| NO<sub>x</sub>                                   | 2020  | 0.0001  | 0.0010  | 0.0084  | 0.0659  | 0.1634  | 0.1852  | 0.1568  | 0.1775  | 0.1762  | 0.1795  | 0.1772  | 0.1758  | 0.1766  |         |+
 ==== Uncertainty ==== ==== Uncertainty ====
  
-Details will be described in [[general:uncertainty_evaluation:start|chapter 1.7]].+Details are described in [[general:uncertainty_evaluation:start|chapter 1.7]].