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sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2021/03/24 09:24] – kotzullasector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2021/12/15 20:00] (current) – external edit 127.0.0.1
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 ====Activity data==== ====Activity data====
  
-Subsector-specific consumption data is included in the primary fuel-delivery data are available from NEB line 67: 'Commercial, trade, services and other consumers' (AGEB, 2019) [((bibcite 1))].+Subsector-specific consumption data is included in the primary fuel-delivery data are available from NEB line 67: 'Commercial, trade, services and other consumers' (AGEB, 2020) [(AGEB2020)].
  
 __Table 1: Sources for primary fuel-delivery data__ __Table 1: Sources for primary fuel-delivery data__
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 || as of 1995 || **AGEB** - National Energy Balance, line 67: 'Gewerbe, Handel, Dienstleistungen u. übrige Verbraucher'  || || as of 1995 || **AGEB** - National Energy Balance, line 67: 'Gewerbe, Handel, Dienstleistungen u. übrige Verbraucher'  ||
  
-Following the deduction of energy inputs for military vehicles as provided in (BAFA, 2019) [((bibcite 2))], the remaining amounts of gasoline and diesel oil are apportioned onto off-road construction vehicles (NFR 1.A.2.g vii) and off-road vehicles in commercial/institutional use (1.A.4. ii) as well as agriculture and forestry (NFR 1.A.4.c ii) based upon annual shares derived from TREMOD-MM (Knörr et al. (2019b)) (cf. [[[ 1-a-4-mobile-combustion | NFR 1.A.4 - mobile ]]]).+Following the deduction of energy inputs for military vehicles as provided in (BAFA, 2020) [(BAFA2020)], the remaining amounts of gasoline and diesel oil are apportioned onto off-road construction vehicles (NFR 1.A.2.g vii) and off-road vehicles in commercial/institutional use (1.A.4. ii) as well as agriculture and forestry (NFR 1.A.4.c ii) based upon annual shares derived from TREMOD-MM (Knörr et al. (2020b) [(KNOERR2020b)] (cf. NFR 1.A.4 - mobile).
  
 __Table 2: Annual contribution of agricultural vehicles and mobile machinery to the primary diesel<sup>1</sup> fuels delivery data provided in NEB line 67__ __Table 2: Annual contribution of agricultural vehicles and mobile machinery to the primary diesel<sup>1</sup> fuels delivery data provided in NEB line 67__
 |  **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**  |
 |      47,6% |      45,6% |      43,9% |      46,2% |      47,5% |      47,2% |      47,3% |      48,0% |      47,8% |      48,3% |      48,5% |      48,5% |      48,4% |      48,4% | |      47,6% |      45,6% |      43,9% |      46,2% |      47,5% |      47,2% |      47,3% |      48,0% |      47,8% |      48,3% |      48,5% |      48,5% |      48,4% |      48,4% |
-<sup>1</sup>no gasoline used in agricultural vehicles and mobile machinery+<sup>1</sup> no gasoline used in agricultural vehicles and mobile machinery
  
 __Table 3: Annual mobile fuel consumption in agriculture, in terajoules__ __Table 3: Annual mobile fuel consumption in agriculture, in terajoules__
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 The emission factors applied here are of rather different quality: The emission factors applied here are of rather different quality:
-For all **main pollutants**, **carbon monoxide** and **particulate matter**, annual IEF modelled within TREMOD MM [((bibcite 3))] are used, representing the sector's vehicle-fleet composition, the development of mitigation technologies and the effect of fuel-quality legislation.  +For all **main pollutants**, **carbon monoxide** and **particulate matter**, annual IEF modelled within TREMOD MM [(KNOERR2020b)] are used, representing the sector's vehicle-fleet composition, the development of mitigation technologies and the effect of fuel-quality legislation.  
  
 __Table 3: Annual country-specific emission factors<sup>1</sup>, in kg/TJ__ __Table 3: Annual country-specific emission factors<sup>1</sup>, in kg/TJ__
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 <sup>1</sup> due to lack of better information: similar EF are applied for fossil and biofuels \\ <sup>1</sup> due to lack of better information: similar EF are applied for fossil and biofuels \\
 <sup>2</sup> EF(PM<sub>2.5</sub>) also applied for PM<sub>10</sub> and TSP (assumption: > 99% of TSP consists of PM<sub>2.5</sub>)\\ <sup>2</sup> EF(PM<sub>2.5</sub>) also applied for PM<sub>10</sub> and TSP (assumption: > 99% of TSP consists of PM<sub>2.5</sub>)\\
-<sup>3</sup> estimated via a f-BCs as provided in [((bibcite 3))], Chapter 1.A.2.g vii, 1.A.4.a ii, b ii, c ii, 1.A.5.b i - Non-road, note to Table 3-1: Tier 1 emission factors for off-road machinery \\+<sup>3</sup> estimated via a f-BCs as provided in [(EMEPEEA2019)], Chapter 1.A.2.g vii, 1.A.4.a ii, b ii, c ii, 1.A.5.b i - Non-road, note to Table 3-1: Tier 1 emission factors for off-road machinery \\
  
-> **NOTE:** With respect to the country-specific emission factors applied for particulate matter, given the circumstances during test-bench measurements, condensables are most likely included at least partly.[[footnote]] During test-bench measurements, temperatures are likely to be significantly higher than under real-world conditions, thus reducing condensation. On the contrary, smaller dillution (higher number of primary particles acting as condensation germs) together with higher pressures increase the likeliness of condensation. So over-all condensables are very likely to occur but different to real-world conditions. [[/footnote]]+> **NOTE:** With respect to the country-specific emission factors applied for particulate matter, given the circumstances during test-bench measurements, condensables are most likely included at least partly. During test-bench measurements, temperatures are likely to be significantly higher than under real-world conditions, thus reducing condensation. On the contrary, smaller dillution (higher number of primary particles acting as condensation germs) together with higher pressures increase the likeliness of condensation. So over-all condensables are very likely to occur but different to real-world conditions.
  
-> For information on the **emission factors for heavy-metal and POP exhaust emissions**, please refer to [[[ appendix2.3-HM-from-mobile-sources | Appendix 2.3 - Heavy Metal (HM) exhaust emissions from mobile sources]]] and [[[ appendix2.4-POPs-from-mobile-sources | Appendix 2.4 - Persistent Organic Pollutant (POP) exhaust emissions from mobile sources ]]].+> For information on the **emission factors for heavy-metal and POP exhaust emissions**, please refer to Appendix 2.3 - Heavy Metal (HM) exhaust emissions from mobile sources and Appendix 2.4 - Persistent Organic Pollutant (POP) exhaust emissions from mobile sources.
  
 ===== Recalculations ===== ===== Recalculations =====
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 ^ relative change  |     -1,62% |     -2,30% |     -6,33% |    -3,67% |    -5,70% |    -6,28% |     -6,00% |     -4,67% |    -4,91% |    -4,82% |     -4,95% |     -4,94% |     -4,94% | ^ relative change  |     -1,62% |     -2,30% |     -6,33% |    -3,67% |    -5,70% |    -6,28% |     -6,00% |     -4,67% |    -4,91% |    -4,82% |     -4,95% |     -4,94% |     -4,94% |
  
-In addition, all **emission factors** remain unrevised compared to last year's susbmission, emission estimates for the years as of 2015 change in accordance with the underlying activity data.+In addition, several **emission factors** have been revised within TREMOD MM.
  
 +__Table 7: Revised annual implied emission factors (IEF), in [kg/TJ__
 |                  |  **1990**  |  **1995**  |  **2000**  | **2005**  | **2010**  | **2011**  |  **2012**  |  **2013**  | **2014**  | **2015**  |  **2016**  |  **2017**  |  **2018**  | |                  |  **1990**  |  **1995**  |  **2000**  | **2005**  | **2010**  | **2011**  |  **2012**  |  **2013**  | **2014**  | **2015**  |  **2016**  |  **2017**  |  **2018**  |
 |   **Ammonia**                                                                                                                                                ||||||||||||||             |   **Ammonia**                                                                                                                                                ||||||||||||||            
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 ^ absolute change  |       4,90 |      -1,57 |      -1,06 |    -14,27 |    -31,05 |    -31,00 |     -30,70 |     -26,64 |    -22,57 |    -14,33 |      -2,54 |       8,58 |      18,80 | ^ absolute change  |       4,90 |      -1,57 |      -1,06 |    -14,27 |    -31,05 |    -31,00 |     -30,70 |     -26,64 |    -22,57 |    -14,33 |      -2,54 |       8,58 |      18,80 |
 ^ relative change  |      0,56% |     -0,18% |     -0,12% |    -1,69% |    -4,35% |    -4,52% |     -4,65% |     -4,21% |    -3,74% |    -2,49% |     -0,47% |      1,67% |      3,86% | ^ relative change  |      0,56% |     -0,18% |     -0,12% |    -1,69% |    -4,35% |    -4,52% |     -4,65% |     -4,21% |    -3,74% |    -2,49% |     -0,47% |      1,67% |      3,86% |
-|                                                                                                                                                             |||||||||||||| 
-^ Submission 2021  |       79,6 |       60,5 |       14,0 |       0,4 |       0,4 |       0,4 |        0,4 |        0,4 |       0,4 |       0,4 |        0,4 |        0,4 |        0,4 | 
-^ Submission 2020  |       79,6 |       60,5 |       14,0 |       0,4 |       0,4 |       0,4 |        0,4 |        0,4 |       0,4 |       0,4 |        0,4 |        0,4 |        0,4 | 
-^ absolute change  |       0,00 |       0,00 |       0,00 |      0,00 |      0,00 |      0,00 |       0,00 |       0,00 |      0,00 |      0,00 |       0,00 |       0,00 |       0,00 | 
-^ relative change  |      0,00% |      0,00% |      0,00% |     0,00% |     0,00% |     0,00% |      0,00% |      0,00% |     0,00% |     0,00% |      0,00% |      0,00% |      0,00% | 
 | **Black Carbon**                                                                                                                                               |||||||||||||| | **Black Carbon**                                                                                                                                               ||||||||||||||
 ^ Submission 2021  |      125,1 |      109,4 |       93,1 |      74,7 |      57,4 |      54,8 |       52,4 |       50,1 |      47,4 |      44,8 |       42,2 |       39,8 |       37,5 | ^ Submission 2021  |      125,1 |      109,4 |       93,1 |      74,7 |      57,4 |      54,8 |       52,4 |       50,1 |      47,4 |      44,8 |       42,2 |       39,8 |       37,5 |
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 ^ absolute change  |     -14,42 |     -19,03 |     -33,83 |    -48,66 |    -48,03 |    -47,51 |     -46,06 |     -40,75 |    -38,52 |    -36,09 |     -32,91 |     -30,70 |     -28,62 | ^ absolute change  |     -14,42 |     -19,03 |     -33,83 |    -48,66 |    -48,03 |    -47,51 |     -46,06 |     -40,75 |    -38,52 |    -36,09 |     -32,91 |     -30,70 |     -28,62 |
 ^ relative change  |     -1,61% |     -2,23% |     -4,16% |    -6,73% |    -7,96% |    -8,14% |     -8,16% |     -7,51% |    -7,37% |    -7,17% |     -6,77% |     -6,51% |     -6,27% | ^ relative change  |     -1,61% |     -2,23% |     -4,16% |    -6,73% |    -7,96% |    -8,14% |     -8,16% |     -7,51% |    -7,37% |    -7,17% |     -6,77% |     -6,51% |     -6,27% |
- 
  
 <WRAP center round info 60%> <WRAP center round info 60%>
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 Besides a routine revision of the underlying model, no specific improvements are planned.  Besides a routine revision of the underlying model, no specific improvements are planned. 
  
------- +[(AGEB2020>AGEB, 2020: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; URL: http://www.ag-energiebilanzen.de/7-0-Bilanzen-1990-2018.html, (Aufruf: 29.11.2020), Köln & Berlin, 2020.)] 
- +[(BAFA2020>BAFA, 2020: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland; 
-[[bibliography]] +URL: https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2018_dezember.html, Eschborn, 2020.)]    
-: 1 : AGEB, 2019: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; URL: https://ag-energiebilanzen.de/7-0-Bilanzen-1990-2017.html, (Aufruf: 29.11.2019), Köln & Berlin, 2019. +[(KNOERR2020b> Knörr et al. (2020b): Knörr, W., Heidt, C., Gores, S., & Bergk, F.: ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Aktualisierung des Modells TREMOD-Mobile Machinery (TREMOD MM) 2020, Heidelberg, 2020.)] 
-: 2 : BAFA, 2019: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland;  +[(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook – 2019, Copenhagen, 2019.)] 
-URL: https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2017_dezember.html, Eschborn, 2019.    +[(RENTZ2008> Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, FKZ 205 67 444, UBA Texte | 01/2008, January 2008 - URL: http://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer )] 
-: 3 : Knörr et al. (2018b): Knörr, W., Heidt, C., Gores, S., & Bergk, F. (2019b): ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Aktualisierung des Modells TREMOD-Mobile Machinery (TREMOD MM) 2018, Heidelberg, 2019. +[(KNOERR2009> Knörr et al. (2009): Knörr, W., Heldstab, J., & Kasser, F.: Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland; final report; URL: https://www.umweltbundesamt.de/sites/default/files/medien/461/publikationen/3937.pdf, FKZ 360 16 023, Heidelberg & Zürich, 2009.)]
-: 4 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook – 2019, Copenhagen, 2019. +
-: 5 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, FKZ 205 67 444, UBA Texte | 01/2008, January 2008 - URL: http://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer +
-[[/bibliography]]+