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sector:agriculture:manure_management:start [2021/12/25 11:40] – [TSP, PM10 and PM2.5] doeringsector:agriculture:manure_management:start [2022/09/15 13:44] (current) – [Country specifics] Fix link hausmann
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 | 3.B.4.h                                          | Other animals                                                                                                            |                                                                                                     | NE                                                              | | 3.B.4.h                                          | Other animals                                                                                                            |                                                                                                     | NE                                                              |
  
-^  Key Category  ^  SO₂     ^  NOₓ  ^  NH₃  ^  NMVOC  ^  CO   ^  BC   ^  Pb   ^  Hg   ^  Cd   ^  Diox  ^  PAH  ^  HCB  ^  TSP  ^  PM₁₀  ^  PM₂ ₅  ^ +^  Key Category  ^  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.B.1.a         |  -          |  -/-  |  L/T  |  L/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.1.a        |  -/-             |  L/-     -               |  L/-             |  L/-               |  L/             |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.1.b         |  -          |  -/-  |  L/T  |  L/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.1.b        |  -/-             |  L/-     -               |  L/T             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.2           |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.2          |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.3           |  -          |  -/-  |  L/T  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  L/ |  -/-   |  -/-    | +| 3.B.3          |  -/-             |  -/-     -               |  L/T             |  -/-               |  -/-              |  L/-  |  -   |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.d         |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.4.d        |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.e         |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.4.e        |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.g.i       |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  L/ |  -/-   |  -/-    | +| 3.B.4.g.i      |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  L/-  |  -   |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.g.ii      |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.4.g.ii     |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.g.iii     |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    | +| 3.B.4.g.iii    |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    | 
-| 3.B.4.g.iv      |  -          |  -/-  |  -/-  |  -/-    |  -    |  -     -    |  -    |  -    |  -     |  -    |  -    |  -/-  |  -/-   |  -/-    |+| 3.B.4.g.iv     |  -/-             |  -/-     -               |  -/-             |  -/-               |  -/-              |  -/-    |  -   |  -   |  -   |  -   |  -     |  -    |  -    |
  
  {{page>general:Misc:LegendEIT:start}}  {{page>general:Misc:LegendEIT:start}}
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-NO<sub>x</sub> emissions from category 3.B (manure management) contribute only 1.3 % (~ 1.4 kt) to the total agricultural NO<sub>x</sub> emissions. They are calculated proportionally to N<sub>2</sub>O emissions, see Vos et al. (2022) ((VosC., Rösemann C., Haenel H-D., Dämmgen U., Döring U., Wulf S., Eurich-Menden B., Freibauer A., Döhler H., Schreiner C., Osterburg B. & FußR(2022)Calculations of gaseous and particulate emissions from German Agriculture 1990 –2020Report on methods and data (RMD)Submission 2022. Thünen Report (in preparation). https://www.thuenen.de/de/ak/arbeitsbereiche/emissionsinventare)).+NO<sub>x</sub> emissions from category 3.B (manure management) contribute only 1.3 % (~ 1.4 kt) to the total agricultural NO<sub>x</sub> emissions. They are calculated proportionally to N<sub>2</sub>O emissions, see 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 BFuß 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)).
  
 NMVOC emissions from category 3.B (manure management) contributed 96.9 % (289.8 kt) from total agricultural NMVOC emissions (298.9 kt). NMVOC emissions from category 3.B (manure management) contributed 96.9 % (289.8 kt) from total agricultural NMVOC emissions (298.9 kt).
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 ==== Method ==== ==== Method ====
-EMEP (2013)-3B-26 [9] provided a Tier 2 methodology. In the current Guidebook (EMEP, 2019), this methodology has been replaced by a Tier 1 methodology. However, EF for cattle derived with the EMEP 2013 Tier 2 methodology remained unchanged. So the EMEP 2013((EMEP (2013): EMEP/EEA air pollutant emission inventory guidebook – 2013)) methodology was kept for cattle. For swine the EMEP 2013 methodology was formally kept but the EMEP 2019 Tier 1 EF was used both for slurry and solid based manure management systems. The same was done with the EMEP 2016 EFs for laying hens (used for cages and perchery). In case the EMEP 2019 EFs are just the rounded EMEP 2013 EFs, the unrounded EMEP 2013 EFs were kept. +EMEP (2013-3B-26provided a Tier 2 methodology. In the current Guidebook (EMEP, 2019), this methodology has been replaced by a Tier 1 methodology. However, EF for cattle derived with the EMEP 2013 Tier 2 methodology remained unchanged. Therfore, the EMEP 2013((EMEP (2013): EMEP/EEA air pollutant emission inventory guidebook – 2013)) methodology was kept for cattle. For swine the EMEP 2013 methodology was formally kept but the EMEP 2019 Tier 1 EF was used both for slurry and solid based manure management systems. The same was done with the EMEP 2016 EFs for laying hens (used for cages and perchery). In case the EMEP 2019 EFs are simply rounded EMEP 2013 EFs, the unrounded EMEP 2013 EFs were kept. 
-The inventory considers air scrubber systems in swine and poultry husbandry. For animal places equipped with air scrubbing the emission factors are reduced according to the removal efficiency of the air scrubber systems (90 % for TSP and PM<sub>10</sub>, 70 % for PM<sub>2.5</sub>). For details see Rösemann et al. (2021), Chapter 3.3.4.3.3.+The inventory considers air scrubber systems in swine and poultry husbandry. For animal places equipped with air scrubbing the emission factors are reduced according to the removal efficiency of the air scrubber systems (90 % for TSP and PM<sub>10</sub>, 70 % for PM<sub>2.5</sub>). For details see Vos et al. (2022), Chapter 3.3.4.3.3.
  
 === Activity data === === Activity data ===
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 === Emission factors === === Emission factors ===
-Tier 1 emission factors for TSP, PM<sub>10</sub> and PM<sub>2.5</sub> from livestock husbandry are provided in EMEP (2019)-3B-19, Table 3.5 and 55, Table A1.7. For cattle the Tier 2 emission factors provided in EMEP (2013)-3B-29, Table 3-11 were used, because they differentiate between slurry and solid manure systems and were also used to develop the EMEP 2019 Tier 1 emissions factors.+Tier 1 emission factors for TSP, PM<sub>10</sub> and PM<sub>2.5</sub> from livestock husbandry are provided in EMEP (2019-3B-19), Table 3.5 and 55, Table A1.7. For cattle the Tier 2 emission factors provided in EMEP (2013-3B-29), Table 3-11 were used, because they differentiate between slurry and solid manure systems and were also used to develop the EMEP 2019 Tier 1 emissions factors.
  
 The implied emission factors given in Table 5 relate the overall TSP and PM emissions to the number of animals in each animal category. The Guidebook does not indicate whether EFs have considered the condensable component (with or without). The implied emission factors given in Table 5 relate the overall TSP and PM emissions to the number of animals in each animal category. The Guidebook does not indicate whether EFs have considered the condensable component (with or without).
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 ==== Trend discussion for Key Sources ==== ==== Trend discussion for Key Sources ====
-Swine and laying hens are key sources of TSP emissions from manure management. The total TSP emissions from swine mainly follow the animal numbers given in Table 1. However, due to air scrubbing and different emission factors of the different housing systems of the four swine subcategories (sows with piglets, weaners, fattening pigs, boars) and the varying population shares in those housing systems the R<sup>2</sup> of the linear regression is lower than 1 (0.79). For laying hens and broilers, due to the low prevalence of air scrubbing systems. TSP emissions almost perfectly correlate with the animal numbers provided in Table 1 (R<sup>2</sup> = 1).+Swine and laying hens are key sources of TSP emissions from manure management. The total TSP emissions from swine mainly follow the animal numbers given in Table 1. However, due to air scrubbing and different emission factors of the different housing systems of the four swine subcategories (sows with piglets, weaners, fattening pigs, boars) and the varying population shares in those housing systems the R<sup>2</sup> of the linear regression is lower than 1 (0.78). For laying hens and broilers, due to the low prevalence of air scrubbing systems. TSP emissions almost perfectly correlate with the animal numbers provided in Table 1 (R<sup>2</sup> = 1).
  
 ==== Recalculations ==== ==== Recalculations ====
-Table REC-4 shows the effects of recalculations on emissions of particulate matter. Changes in the years 1990 through 1999 are a consequence of the update of the dairy cow model (**recalculation reason 1**, see [[sector:agriculture:start|main page of the agricultural sector]]). This update includes a modified calculation of the share of year spent on pasture, resulting in longer grazing periods and therefore lower emissions of particulate matter from manure management in the years 1990 through 1999. Differences of TSP and PM emissions in the years as of 2005 are due to updated activity data of air scrubbing systems for sows, weaners, fattening pigs and broilers, see **recalculation reasons 8 and 10** on [[sector:agriculture:start|the main page of the agricultural sector]]. Further details on recalculations are described in Rösemann et al. (2021), Chapter 3.5.2.+Table REC-4 shows the effects of recalculations on emissions of particulate matter. Changes in the years 2000 through 2019 are a consequence of the use of the data of the official agricultural census 2020 as well as new animal population figures for the years 2017-2019 (**recalculation reason 1**, see [[sector:agriculture:start|main page of the agricultural sector]]). Further details on recalculations are described in Vos et al. (2022), Chapter 3.5.2.
  
-//Table REC-4: Comparison of particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>) of the submissions (SUB) 2020 and 2021//+//Table REC-4: Comparison of particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>) of the submissions (SUB) 2021 and 2022//
  
 ^  TSP, PM10, PM2.5 emissions from manure management, in Gg                                                                                                                                  ||||||||||||||||| ^  TSP, PM10, PM2.5 emissions from manure management, in Gg                                                                                                                                  |||||||||||||||||
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 ^ PM<sub>2.5</sub>                                            2021  |   5.01 |   4.47 |   4.18 |   3.89 |   3.86 |   3.86 |   3.91 |   4.01 |   4.01 |   3.97 |   3.91 |   3.88 |   3.80 |   3.72 |        | ^ PM<sub>2.5</sub>                                            2021  |   5.01 |   4.47 |   4.18 |   3.89 |   3.86 |   3.86 |   3.91 |   4.01 |   4.01 |   3.97 |   3.91 |   3.88 |   3.80 |   3.72 |        |
  
 +
 +<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]].
 +</WRAP>
 ===== Planned improvements ===== ===== Planned improvements =====
 No improvements are planned at present. No improvements are planned at present.