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sector:agriculture:manure_management:start [2021/02/12 12:52] – [Methodology] renamed to Method gniffkesector:agriculture:manure_management:start [2021/12/15 20:00] – external edit 127.0.0.1
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 ===== Short description ===== ===== Short description =====
  
-^ NFR-Code                                         ^ Name of Category        ^ Method                                                                                           ^ AD      ^ EF                                                                                          ^ Key Category <sup>1</sup>                    ^ State of reporting                                              ^ +^ NFR-Code                                         ^ Name of Category        ^ Method                                                                                           ^ AD      ^ EF                                                                                          ^ State of reporting                                              ^ 
-| **3.B    **                                      | ** Manure Management**  | **see sub-category details**                                                                                                                                                                         |                                              |                                                                 | +| **3.B    **                                      | ** Manure Management**  | **see sub-category details**                                                                                                                                                                           |||                                                                 | 
-| **consisting of / including source categories**                                                                                                                                                                                                                                                                                                                                                  ||||||| +| **consisting of / including source categories**                                                                                                                                                                                                                                                                                                    |||||| 
-| 3.B.1.a & 3.B.1.b                                | Cattle                  | T3 (NH<sub>3</sub> ), T2 (NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>, NMVOC)       | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  | L & T: NH<sub>3</sub>  (for 3.B.1.b), NMVOC  | L: NH<sub>3</sub>  (for 3.B.1.a)                                | +| 3.B.1.a & 3.B.1.b                                | Cattle                  | T3 (NH<sub>3</sub> ), T2 (NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>, NMVOC)       | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  | L: NH<sub>3</sub>  (for 3.B.1.a)                                | 
-| 3.B.2, 3.B.4.d, 3.B.4.e                          | Sheep, Goats, Horses    | T2 (NH<sub>3</sub> , NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)       | NS, RS  | CS (NH<sub>3</sub> ,NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)   | no key category                              |                                                                 | +| 3.B.2, 3.B.4.d, 3.B.4.e                          | Sheep, Goats, Horses    | T2 (NH<sub>3</sub> , NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)       | NS, RS  | CS (NH<sub>3</sub> ,NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)                                                                   | 
-| 3.B.3                                            | Swine                   | T3 (NH<sub>3</sub> ), T2 (NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)  | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  | L & T: NH<sub>3</sub> , TSP                  |                                                                 | +| 3.B.3                                            | Swine                   | T3 (NH<sub>3</sub> ), T2 (NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)  | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  |                                                                 | 
-| 3.B.4.a                                          | Buffalo                                                                                                                  |                                                                                                     |                                              | NO, from 1990 until 1995, since 1996 IE, considered in 3.B.1.b +| 3.B.4.a                                          | Buffalo                                                                                                                  |                                                                                                     | NO, from 1990 until 1995, since 1996 IE, considered in 3.B.1.b 
-| 3.B.4.f                                          | Mules and asses                                                                                                          |                                                                                                     |                                              | IE, considered in 3.B.4.e                                       | +| 3.B.4.f                                          | Mules and asses                                                                                                          |                                                                                                     | IE, considered in 3.B.4.e                                       | 
-| 3.B.4.g i-iv                                     | Poultry                 | T2 (NH<sub>3</sub> , NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)       | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  | L: TSP (for 3.B.4.g i)                       | T: NH<sub>3</sub>  (for 3.B.4.g iii)                            | +| 3.B.4.g i-iv                                     | Poultry                 | T2 (NH<sub>3</sub> , NO<sub>x</sub> , TSP, PM<sub>10</sub> , PM<sub>2.5</sub>), T1 (NMVOC)       | NS, RS  | CS (NH<sub>3</sub> , NO<sub>x</sub> ), D (TSP, PM<sub>10</sub> , PM<sub>2.5</sub> , NMVOC)  | T: NH<sub>3</sub>  (for 3.B.4.g iii)                            | 
-| 3.B.4.h                                          | Other animals                                                                                                            |                                                                                                     |                                              | NE                                                              |+| 3.B.4.h                                          | Other animals                                                                                                            |                                                                                                     | NE                                                              |
  
-<hidden> +^  Key Category  ^  SO₂      NOₓ  ^  NH₃  ^  NMVOC  ^  CO    BC    Pb    Hg    Cd    Diox  ^  PAH  ^  HCB  ^  TSP  ^  PM₁₀  ^  PM₂ ₅  ^ 
- +| 3.B.1.a          -          |  -/-  |  L/T  |  L/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
----- +| 3.B.1.b         |           |  -/  L/T  |  L/    -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
-Legend +| 3.B.2            -          |  -/-  |  -/-  |  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
-= key source by Trend / L = key source by Level +| 3.B.3            -          |  -/-  |  L/  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  L/ |  -/  |  -/-    | 
- +| 3.B.4.d          -          |  -/-  |  -/-  |  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
----- +3.B.4.e          -          |  -/-  |  -/-   -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
- +| 3.B.4.g.i        -          |  -/-  |  -/-  |  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  L/-  |  -/-    -/-    | 
-//Methods//  +| 3.B.4.g.ii      |           |  -/ |  -/-  |  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
-D: Default +| 3.B.4.g.iii      -          |  -/-  |  -/-   -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/-    | 
-RA: Reference Approach +| 3.B.4.g.iv      |           |  -/  -/-  |  -/-    |  -    |  -    |  -    |  -    |  -    |  -      -    |  -    |  -/-  |  -/-    -/   |
-T1: Tier 1 Simple Methodology * +
-T2: Tier 2* +
-T3: Tier 3 / Detailed Methodology * +
-C: CORINAIR +
-CS: Country Specific +
-M: Model +
-as described in the EMEP/CORINAIR Emission Inventory Guidebook 2019, in the group specific chapters.  +
- +
----- +
- +
-//AD:Data Source for Activity Data // +
-NS: National Statistics +
-RS: Regional Statistics +
-IS: International Statistics +
-PS: Plant Specific data +
-AS: Associations, business organisations +
-Q: specific questionnaires, surveys +
- +
-----+
  
-//EF - Emission Factors//  + {{page>general:Misc:LegendEIT:start}} 
-D: Default (EMEP Guidebook) +\\
-C: Confidential +
-CS: Country Specific +
-PS: Plant Specific data</hidden>+
  
  
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-NO<sub>x</sub> emissions from category 3.B (manure management) contribute only 1.2 % (~ 1.4 kt) to the total agricultural NO<sub>x</sub> emissions. They are calculated proportionally to N<sub>2</sub>O emissions, see 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)).+NO<sub>x</sub> emissions from category 3.B (manure management) contribute only 1.2 % (~ 1.4 kt) to the total agricultural NO<sub>x</sub> emissions. They are calculated proportionally to N<sub>2</sub>O emissions, see 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 84. https://www.thuenen.de/de/ak/arbeitsbereiche/emissionsinventare)).
  
 NMVOC emissions from category 3.B (manure management) contributed 97.2 % (295.8 kt) from total agricultural NMVOC emissions (304.4 kt). NMVOC emissions from category 3.B (manure management) contributed 97.2 % (295.8 kt) from total agricultural NMVOC emissions (304.4 kt).
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 == N mass flow and emission assessment == == N mass flow and emission assessment ==
-The calculation of the emissions of NH<sub>3</sub>, N<sub>2</sub>O, NO<sub>x</sub> and N2 from German animal husbandry is based on the so-called N mass flow approach (e. g. Dämmgen and Hutchings, 2008 ((Dämmgen U., Hutchings N.J. (2008): Emissions of gaseous nitrogen species from manure management - a new approach. Environmental Pollution 154, 488-497.))).+The calculation of the emissions of NH<sub>3</sub>, N<sub>2</sub>O, NO<sub>x</sub> and N<sub>2</sub> from German animal husbandry is based on the so-called N mass flow approach (e. g. Dämmgen and Hutchings, 2008 ((Dämmgen U., Hutchings N.J. (2008): Emissions of gaseous nitrogen species from manure management - a new approach. Environmental Pollution 154, 488-497.))).
 This approach differentiates between N excreted with faeces (organic nitrogen Norg, i. e. undigested feed N) and urine (total ammoniacal nitrogen TAN, i. e. fraction of feed N metabolized). The N flow within the manure management system is treated as depicted in the figure below. This method reconciles the requirements of both the Atmospheric Emission Inventory Guidebook for NH<sub>3</sub> emissions (EMEP, 2019), and the IPCC guidelines for greenhouse gas emissions (IPCC (2006)((IPCC – Intergovernmental Panel on Climate Change (2006): IPCC Guidelines for National Greenhouse Gas Inventories, Volume 4 Agriculture, Forestry and Other Land Use.)). Reidy et al. (2008),((Reidy B. et al. (2008): Reidy B., Dämmgen U., Döhler H., Eurich-Menden B., Hutchings N.J., Luesink H.H., Menzi H., Misselbrook T.H., Monteny G.-J., Webb J. (2008): Comparison of models used for the calculation of national NH3 emission inventories from agriculture: liquid manure systems. Atmospheric Environment 42, 3452-3467.)), showed for several European countries (Germany, the Netherlands, Switzerland, United Kingdom) that their N-flow based inventory models yielded, in spite of national peculiarities, comparable results as long as standardised data sets for the input variables were used. This approach differentiates between N excreted with faeces (organic nitrogen Norg, i. e. undigested feed N) and urine (total ammoniacal nitrogen TAN, i. e. fraction of feed N metabolized). The N flow within the manure management system is treated as depicted in the figure below. This method reconciles the requirements of both the Atmospheric Emission Inventory Guidebook for NH<sub>3</sub> emissions (EMEP, 2019), and the IPCC guidelines for greenhouse gas emissions (IPCC (2006)((IPCC – Intergovernmental Panel on Climate Change (2006): IPCC Guidelines for National Greenhouse Gas Inventories, Volume 4 Agriculture, Forestry and Other Land Use.)). Reidy et al. (2008),((Reidy B. et al. (2008): Reidy B., Dämmgen U., Döhler H., Eurich-Menden B., Hutchings N.J., Luesink H.H., Menzi H., Misselbrook T.H., Monteny G.-J., Webb J. (2008): Comparison of models used for the calculation of national NH3 emission inventories from agriculture: liquid manure systems. Atmospheric Environment 42, 3452-3467.)), showed for several European countries (Germany, the Netherlands, Switzerland, United Kingdom) that their N-flow based inventory models yielded, in spite of national peculiarities, comparable results as long as standardised data sets for the input variables were used.
  
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 For the Tier 2 methodology applied to dairy cattle and other cattle the following data was used: For the Tier 2 methodology applied to dairy cattle and other cattle the following data was used:
    * gross feed intake in MJ per year, country specific data from the annual reporting of greenhouse gas emissions, see NIR 2021, Chapter 5.1.3.3,    * gross feed intake in MJ per year, country specific data from the annual reporting of greenhouse gas emissions, see NIR 2021, Chapter 5.1.3.3,
-   * proportion x house of the year the animals spend in the livestock building: country specific data, being equal to 1 – xgraz with xgraz the proportion of the year spent on pasture, see NIR 2021, Chapter 19.3.2, +   * proportion x<sub>house</sub> of the year the animals spend in the livestock building: country specific data, being equal to 1 – x<sub>graz</sub> with x<sub>graz</sub> the proportion of the year spent on pasture, see NIR 2021, Chapter 19.3.2, 
-   FRACsilage 1 as proposed by EMEP (2019)-3B-29, since silage feeding for cattle is considered dominant in Germany +   FRAC<sub>silage</sub>: 1 as proposed by EMEP (2019)-3B-29, since silage feeding for cattle is considered dominant in Germany 
-   FRACsilage store: 0.25 as proposed by EMEP (2019)-3B-30 for European conditions +   FRAC<sub>silage store</sub>: 0.25 as proposed by EMEP (2019)-3B-30 for European conditions 
-   EFNMVOC silage_feeding, EFNMVOC, house, EFNMVOC, graz are taken from EMEP (2019)-3B-32, table 3.11 as 0.0002002, 0.0000353 and 0.0000069 kg NMVOC/MJ feed intake, respectively, +   EF<sub>NMVOC, silage_feeding</sub>EF<sub>NMVOC, house</sub>EF<sub>NMVOC, graz</sub> are taken from EMEP (2019)-3B-32, table 3.11 as 0.0002002, 0.0000353 and 0.0000069 kg NMVOC/MJ feed intake, respectively, 
-   EFNH3,storage, EFNH3,buildingand EFNH3,application are taken from the NH3 reporting (see above and 3.D).+   EF<sub>NH₃,storage</sub>EF<sub>NH₃,building</sub> and EF<sub>NH₃,application<sub> are taken from the NH<sub>3</sub> reporting (see above and 3.D).
  
 For all other animal categories the Tier 1 emission factors for NMVOC as provided in EMEP (2019)-3B-18, Table 3.4 [10] were used: For horses the emission factors for feeding with silage was chosen, for all other animals the emission factors for feeding without silage. Due to missing country-specific emission factors or emission factors that do not correspond to the inventory’s animal categories, the emission factors provided in EMEP (2019)-3B-18, Table 3.4, were used to define specific emission factors for weaners, boars, lambs, ponies/light horses and pullets, see Rösemann et al. (2021), Chapter 3.3.4.2. For all other animal categories the Tier 1 emission factors for NMVOC as provided in EMEP (2019)-3B-18, Table 3.4 [10] were used: For horses the emission factors for feeding with silage was chosen, for all other animals the emission factors for feeding without silage. Due to missing country-specific emission factors or emission factors that do not correspond to the inventory’s animal categories, the emission factors provided in EMEP (2019)-3B-18, Table 3.4, were used to define specific emission factors for weaners, boars, lambs, ponies/light horses and pullets, see Rösemann et al. (2021), Chapter 3.3.4.2.
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 =====  TSP, PM10 and PM2.5 ===== =====  TSP, PM10 and PM2.5 =====
-In 2019, TSP emissions from manure management amount to 71.1 % of total emissions from the agricultural sector. Within the emissions from manure management 22.4 % originate from cattle, 39.3 % from pigs, and 37.7 % from poultry. 42.7 % of the PM<ub>10</sub> emissions from the agricultural sector are caused by manure management, where 34.0 % originate from cattle, 18.9 % from pigs, and 46.2 % from poultry. PM<sub>2.5</sub> emissions from the agricultural sector mostly originate from manure management (84.8 %), of which are 77.5 % from cattle, 3.0 % from pigs, and 18.0 % from poultry.+In 2019, TSP emissions from manure management amount to 71.1 % of total emissions from the agricultural sector. Within the emissions from manure management 22.4 % originate from cattle, 39.3 % from pigs, and 37.7 % from poultry. 42.7 % of the PM<sub>10</sub> emissions from the agricultural sector are caused by manure management, where 34.0 % originate from cattle, 18.9 % from pigs, and 46.2 % from poultry. PM<sub>2.5</sub> emissions from the agricultural sector mostly originate from manure management (84.8 %), of which are 77.5 % from cattle, 3.0 % from pigs, and 18.0 % from poultry.
  
 ==== Method ==== ==== Method ====