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sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2021/04/09 09:50] kotzullasector:energy:fuel_combustion:small_combustion:mobile_small_combustion:agriculture_and_forestry:agriculture [2024/02/27 12:14] (current) – [Table] 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: 'Commercial, trade, services and other consumers' (AGEB, 2020) [(AGEB2020)].+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, 2022) [(AGEB2022)].
  
 __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, 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. [[[ 1-a-4-mobile-combustion | NFR 1.A.4 - mobile ]]]).+Following the deduction of energy inputs for military vehicles as provided in (BAFA, 2022) [(BAFA2022)], 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. (2022b) [(KNOERR2022b)] (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  ^  2020  ^  2021  ^ 
-     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% | + 47.5% |  45.6% |  43.8% |  46.2% |  47.4% |  47.2% |  47.2% |  48.0% |  47.8% |  48.2% |  48.4% |  48.5% |  48.4% |  48.4% |  48.2% |  48.6% | 
-<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__
-|                        **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    2021   ^ 
-^ 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            |  53,188  44,553  41,633  37,893  41,973  42,813  42,087  44,479  46,205  48,848  50,968  52,500  48,950  49,622 |  50,901 |  51,619 
-^ Biodiesel                      0 |          0 |          0 |      2.424      3.222      2.991      2.974      2.641      2.843      2.675      2.705      2.806      2.849      2.824 +^ Biodiesel                   0 |       0 |       0 |   2,421   3,218   2,987   2,970   2,638   2,839   2,672   2,702   2,803   2,846   2,826 |   4,228 |   3,586 
-| **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)**   53,188  44,553  41,633  40,315  45,191  45,800  45,057  47,117  49,045  51,520  53,670  55,302  51,795  52,448 ^  55,129 ^  55,205 ^
    
 ==== 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**, **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.  +For all **main pollutants**, **carbon monoxide** and **particulate matter**, annual IEF modelled within TREMOD MM 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 4: Annual country-specific emission factors<sup>1</sup>, in kg/TJ__ 
-|                  **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  ^  2021  ^ 
-^ NH<sub>3</sub>      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     0,165 +^ NH<sub>3</sub>   0.15   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16   0.16 |   0.16 |   0.16 
-^ NMVOC                  258 |        232        205 |        165 |        124 |        118 |        112 |        106 |        100       93,8 |       88,6 |       83,8 |       79,1 |      74,8 | +^ NMVOC              258 |    231    205 |    165 |    124 |    118 |    112 |    106 |   99.7   93.8 |   88.6 |   83.8 |   79.1 |   74.|   70.6 |   66.4 
-^ NO<sub>x</sub>        874        886 |        916 |        832 |        682 |        655 |        629 |        605 |        581 |        560 |        541 |        523        506       490 +^ NO<sub>x</sub>    873    886 |    916 |    832 |    682 |    655 |    629 |    605 |    581 |    560 |    541 |    522    505    489 |    471 |    451 
-^ SO<sub>x</sub>       79,6 |       60,5 |       14,0 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |       0,37 |      0,37 | +^ SO<sub>x</sub>   79.6 |   60.5 |   14.0 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 |   0.37 | 
-BC<sup>3</sup>      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 |      35,3 +PM<sup>2</sup>    125 |    109 |   93.1 |   74.7 |   57.4 |   54.8 |   52.4 |   50.1 |   47.5   44.8 |   42.3   39.8 |   37.5 |   35.4 |   33.2 |   30.9 
-PM<sup>2</sup>        229 |        201 |        171 |        134 |       97,1 |       91,5 |       86,2       81,5 |       76,3       71,4       66,9 |       62,7 |       58,6 |      54,9 | +BC<sup>3</sup>    229 |    201 |    171 |    134 |   97.1 |   91.5 |   86.3   81.5 |   76.4   71.5   66.9 |   62.7 |   58.6 |   54.|   51.3 |   47.6 
-^ CO              |        882 |        834 |        779 |        674 |        555 |        536 |        518 |        502        484        468        453 |        441 |        428       416 |+^ CO              |    882 |    834 |    779 |    674 |    555 |    536 |    518 |    500    479    459    441 |    424 |    407 |    391 |    375    359 |
 <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 [(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 \\ <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 =====
  
-Revisions in **activity data** result from slightly adapted EBZ67 shares as well as the implementation of primary activity data from the now finalised NEB 2019.+Revisions in **activity data** result from slightly revised annual shares adapted EBZ 67 shares as well as the implementation of primary activity data from the now finalised NEB 2020.
  
-__Table 5: Revised annual contribution of 1.A.2.g vii to fuel-specific over-all fuel deliveries provided in NEB line 67__ +__Table 5: Revised annual shares of NEB line 67, in %__ 
-                  |  **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   ^  2019    2020   ^ 
-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   |   0,475   0,456 |   0,438   0,462 |   0,474   0,472 |   0,472   0,480 |   0,478 |   0,482   0,484   0,485 |   0,484 |   0,484 |   0,482 | 
-^ 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  |   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   0,484   0,483 | 
-^ absolute change   |     -0,008     -0,011     -0,030    -0,038    -0,034    -0,034     -0,033     -0,024    -0,025    -0,025     -0,025     -0,025     -0,028 | +^ absolute change      |  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001  -0,001 |  -0,001 |  -0,001 |  -0,001 
-^ relative change       -1,62%     -2,30%     -6,33% |    -7,66% |    -6,75% |    -6,65% |     -6,47% |     -4,80% |    -4,98% |    -4,87% |     -5,00% |     -4,97% |     -5,52% | +^ relative change      |  -0,14% |  -0,15% |  -0,15% |  -0,13% |  -0,12|  -0,12% |  -0,12% |  -0,12% |  -0,12% |  -0,12% |  -0,12% |  -0,12% |   -0,1% |  -0,12% |   -0,1% |
- +
-__Table 6: Resulting revised activity data, in terajoules__ +
-|                  |  **1990**  |  **1995**  |  **2000**  | **2005**  | **2010**  | **2011**  |  **2012**  |  **2013**  | **2014**  | **2015**  |  **2016**  |  **2017**  |  **2018** +
-^ Submission 2021  |     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 | +
-^ Submission 2020  |     54.142 |     45.674 |     44.513 |    41.905 |    47.980 |    48.928 |     47.989 |     49.482 |    51.634 |    54.190 |     56.531 |     58.245 |     54.553 | +
-^ absolute change  |       -878 |     -1.053 |     -2.817 |    -1.538 |    -2.734 |    -3.073 |     -2.878 |     -2.311 |    -2.533 |    -2.610 |     -2.799 |     -2.878 |     -2.695 | +
-^ 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, 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** +
-|   **Ammonia**                                                                                                                                                ||||||||||||||             +
-^ 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  |       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       0,35%      0,62% |      0,88% |     1,05% |     0,56% |     0,50% |      0,43% |      0,34% |     0,29% |     0,24% |      0,19% |      0,17% |      0,13% | +
-|    **NMVOC**                                                                                                                                                         |||||||||||||| +
-^ 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  |      -3,31 |      -5,53 |     -10,80 |    -16,58 |    -14,89 |    -14,78 |     -14,31 |     -12,68    -11,94 |    -11,11 |     -10,10 |      -9,52 |      -8,94 | +
-^ relative change  |     -1,27% |     -2,33% |     -5,01% |    -9,13% |   -10,72% |   -11,16% |    -11,37% |    -10,69% |   -10,70% |   -10,58% |    -10,23% |    -10,20% |    -10,15% | +
-|   **Nitrogen oxides**                                                                                                                                          |||||||||||||| +
-^ 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  |       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% | +
-| **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 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  |      -4,68 |      -5,54 |      -7,40 |     -9,84 |     -6,50 |     -6,57 |      -6,28 |      -5,50 |     -5,01 |     -4,52 |      -4,10 |      -3,93 |      -3,73 | +
-^ relative change  |     -3,61% |     -4,82% |     -7,36% |   -11,63% |   -10,17% |   -10,71% |    -10,71% |     -9,89% |    -9,55% |    -9,17% |     -8,86% |     -8,99% |     -9,06% | +
-|  **Particulate Matter (PM) **                                                                                                                                 |||||||||||||| +
-^ 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,|       99,4 |       93,4 |      87,5 |      81,8 |       76,5 |       72,0 |       67,5 | +
-^ absolute change  |      -8,46 |      -9,99 |     -13,49 |    -18,45 |    -13,39 |    -13,58 |     -13,21 |     -11,92 |    -11,17 |    -10,40 |      -9,64 |      -9,31 |      -8,90 | +
-^ relative change  |     -3,56% |     -4,74% |     -7,32% |   -12,14% |   -12,12% |   -12,93% |    -13,29% |    -12,76% |   -12,77% |   -12,70% |    -12,59% |    -12,94% |    -13,18% | +
-|  **Carbon monoxide**                                                                                                                                         |||||||||||||| +
-^ 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  |     -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% |+
  
 +__Table 6: Revised activity data, in terajoules__
 +|                      ^  1990    1995    2000    2005    2010    2011    2012    2013    2014    2015    2016    2017    2018    2019    2020   ^
 +^ current submission    53,188 |  44,553 |  41,633 |  40,315 |  45,191 |  45,800 |  45,057 |  47,117 |  49,045 |  51,520 |  53,670 |  55,302 |  51,795 |  52,448 |  55,129 |
 +^ previous submission  |  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 |  54,641 |
 +^ absolute change      |   -75.7 |   -68.7 |   -63.4 |   -51.4 |   -54.6 |   -54.8 |   -53.6 |   -54.7 |   -56.7 |   -59.9 |   -62.4 |   -64.3 |   -59.9 |   -60.6 |     488 |
 +^ relative change      |  -0.14% |  -0.15% |  -0.15% |   -0.1% |   -0.1% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |  -0.12% |   0.89% |
 <WRAP center round info 60%> <WRAP center round info 60%>
-For more information on recalculated emission estimates reported for Base Year and 2018, please see the pollutant-specific recalculation tables following chapter [[general:recalculations:start| 8.1 - Recalculations]].+For **pollutant-specific information on recalculated emission estimates reported for Base Year and 2020**, please see the recalculation tables following chapter [[general:recalculations:start| 8.1 - Recalculations]].
 </WRAP> </WRAP>
  
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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.)] +[(AGEB2022>AGEB, 2022: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; https://ag-energiebilanzen.de/daten-und-fakten/bilanzen-1990-bis-2020/?wpv-jahresbereich-bilanz=2011-2020, (Aufruf: 23.11.2021), Köln & Berlin, 2022)] 
-[(BAFA2020>BAFA, 2020: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland; +[(BAFA2022>BAFA, 2022: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, BAFA): Amtliche Mineralöldaten für die Bundesrepublik Deutschland; 
-URL: https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2018_dezember.html, Eschborn, 2020.)]    +https://www.bafa.de/SharedDocs/Downloads/DE/Energie/Mineraloel/moel_amtliche_daten_2021_12.xlsx;jsessionid=80E1FD32B36918F682608C03FDE79257.1_cid381?__blob=publicationFile&v=5, Eschborn, 2022.)] 
-[(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.)]+[(KNOERR2022b>Knörr et al. (2022b): 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) 2022, Heidelberg, 2022.)]
 [(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook – 2019, Copenhagen, 2019.)] [(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook – 2019, Copenhagen, 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 )] 
 [(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.)] [(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.)]