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sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2021/03/24 09:19] – [Table] kotzulla | sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2022/02/08 07:48] – kotzulla | ||
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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: ' | + | Subsector-specific consumption data is included in the primary fuel-delivery data are available from NEB line 67: ' |
__Table 1: Sources for primary fuel-delivery data__ | __Table 1: Sources for primary fuel-delivery data__ | ||
Line 20: | Line 20: | ||
|| as of 1995 || **AGEB** - National Energy Balance, line 67: ' | || as of 1995 || **AGEB** - National Energy Balance, line 67: ' | ||
- | Following the deduction of energy inputs for military vehicles as provided in (BAFA, | + | Following the deduction of energy inputs for military vehicles as provided in (BAFA, |
__Table 2: Annual contribution of agricultural vehicles and mobile machinery to the primary diesel< | __Table 2: Annual contribution of agricultural vehicles and mobile machinery to the primary diesel< | ||
- | | **1990** | + | | **1990** |
- | | 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% |
- | < | + | < |
__Table 3: Annual mobile fuel consumption in agriculture, | __Table 3: Annual mobile fuel consumption in agriculture, | ||
- | | | + | | |
- | ^ Diesel Oil | 53.263 | 44.622 | 41.696 | 37.942 | 42.024 | 42.864 | 42.137 | 44.531 | 46.259 | 48.905 | 51.027 | 52.561 | 49.009 | 49.591 | | + | ^ Diesel Oil | 53,263 | 44,622 | 41,696 | 37,942 | 42,024 | 42,864 | 42,137 | 44,531 | 46,259 | 48,905 | 51,027 | 52,561 | 49,006 | 49,679 | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | | **Ʃ 1.A.4.c ii (i)** ^ 53.263 ^ 44.622 ^ 41.696 ^ 40.366 ^ 45.246 ^ 45.855 ^ 45.111 ^ 47.172 ^ 49.102 ^ 51.580 ^ 53.732 ^ 55.367 ^ 51.858 ^ 52.415 ^ | + | | **Ʃ 1.A.4.c ii (i)** ^ 53,263 ^ 44,622 ^ 41,696 ^ 40,366 ^ 45,246 ^ 45,855 ^ 45,111 ^ 47,172 ^ 49,102 ^ 51,580 ^ 53,732 ^ 55,367 ^ 51,855 ^ 52,509 ^ |
==== Emission factors ==== | ==== Emission factors ==== | ||
The emission factors applied here are of rather different quality: | The emission factors applied here are of rather different quality: | ||
- | For all **main pollutants**, | + | For all **main pollutants**, |
__Table 3: Annual country-specific emission factors< | __Table 3: Annual country-specific emission factors< | ||
- | | | + | | |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC<sup>3</ | + | ^ PM<sup>2</ |
- | ^ PM<sup>2</ | + | ^ BC<sup>3</ |
- | ^ CO | 882 | 834 | 779 | 674 | 555 | 536 | 518 | 502 | 484 | 468 | 453 | 441 | 428 | 416 | | + | ^ CO | 882 | 834 | 779 | 674 | 555 | 536 | 518 | 502 | 484 | 468 | 453 | 441 | 428 | |
< | < | ||
< | < | ||
- | < | + | < |
- | > **NOTE:** With respect to the country-specific emission factors applied for particulate matter, given the circumstances during test-bench measurements, | + | > **NOTE:** With respect to the country-specific emission factors applied for particulate matter, given the circumstances during test-bench measurements, |
- | > For information on the **emission factors for heavy-metal and POP exhaust emissions**, | + | > For information on the **emission factors for heavy-metal and POP exhaust emissions**, |
===== Recalculations ===== | ===== Recalculations ===== | ||
- | Revisions in **activity data** result from slightly adapted EBZ67 shares as well as the implementation of primary activity data from the now finalised | + | With **emissions factors** unrevised, recalculated emission estimates |
- | __Table | + | __Table |
- | | | **1990** | + | | |
- | ^ Submission 2021 | 0,476 | 0,456 | 0,439 | 0,462 | 0,475 | 0,472 | 0,473 | 0,480 | 0,478 | 0,483 | 0,485 | 0,485 | 0,484 | | + | ^ current submission |
- | ^ Submission 2020 | 0,484 | 0,467 | 0,468 | 0,501 | 0,509 | 0,506 | 0,506 | 0,505 | 0,503 | 0,507 | 0,510 | 0,511 | 0,512 | | + | ^ previous submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | __Table 6: Resulting revised activity data, in terajoules__ | + | <WRAP center round info 60%> |
- | | | **1990** | + | For more information on recalculated emission estimates reported for Base Year and 2019, please see the pollutant-specific recalculation tables following chapter [[general: |
- | ^ Submission 2021 | | + | </ |
- | ^ Submission 2020 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | In addition, all **emission factors** remain unrevised compared to last year's susbmission, | + | ===== Planned improvements ===== |
- | | | **1990** | + | Besides a routine revision of the underlying model, no specific |
- | | | + | |
- | ^ Submission 2021 | 0,153 | 0,156 | 0,159 | 0,162 | 0,163 | 0,164 | 0,164 | 0,164 | 0,164 | 0,164 | 0,164 | 0,164 | 0,165 | | + | |
- | ^ Submission 2020 | 0,152 | 0,155 | 0,158 | 0,160 | 0,163 | 0,163 | 0,163 | 0,163 | 0,164 | 0,164 | 0,164 | 0,164 | 0,164 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | 258 | 232 | 205 | 165 | 124 | 118 | 112 | 106 | 100 | 94 | 89 | 84 | 79 | | + | |
- | ^ Submission 2020 | 261 | 237 | 216 | 182 | 139 | 132 | 126 | 119 | 112 | 105 | 99 | 93 | 88 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | 874 | 886 | 916 | 832 | 682 | 655 | 629 | 605 | 581 | 560 | 541 | 523 | 506 | | + | |
- | ^ Submission 2020 | 869 | 887 | 917 | 846 | 713 | 686 | 660 | 632 | 604 | 575 | 544 | 514 | 487 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ 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 | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ 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 2020 | 129,7 | 114,9 | 100,5 | 84,6 | 63,9 | 61,3 | 58,6 | 55,6 | 52,4 | 49,3 | 46,3 | 43,8 | 41,2 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | 229 | 201 | 171 | 134 | 97,1 | 91,5 | 86,2 | 81,5 | 76,3 | 71,4 | 66,9 | 62,7 | 58,6 | | + | |
- | ^ Submission 2020 | 238 | 211 | 184 | 152 | 110 | 105,0 | 99,4 | 93,4 | 87,5 | 81,8 | 76,5 | 72,0 | 67,5 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | 882 | 834 | 779 | 674 | 555 | 536 | 518 | 502 | 484 | 468 | 453 | 441 | 428 | | + | |
- | ^ Submission 2020 | 896 | 853 | 813 | 723 | 603 | 584 | 564 | 543 | 522 | 504 | 486 | 471 | 457 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | | + | |
- | ^ Submission 2020 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | | + | |
- | ^ Submission 2021 | | + | |
- | ^ Submission 2020 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | > For **information on the impacts on emission estimates for Base Year and 2017**, please see the pollutant | + | |
- | ------ | + | [(AGEB2020> |
- | + | [(BAFA2020> | |
- | [[bibliography]] | + | URL: https:// |
- | : 1 : AGEB, 2019: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; | + | [(KNOERR2020b> |
- | : 2 : BAFA, 2019: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, | + | [(EMEPEEA2019> |
- | URL: https:// | + | [(RENTZ2008> |
- | : 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, | + | [(KNOERR2009> |
- | : 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, | + | |
- | [[/bibliography]] | + |