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sector:agriculture:agricultural_soils:start [2026/02/12 08:45] – [Emission factors] roesemannsector:agriculture:agricultural_soils:start [2026/03/16 15:23] (current) – [Table] mielke
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 | [[start#de_-_cultivated_crops|3.D.e]]                                                                                      | Cultivated crops                                                                                       | T2 (NMVOC)                                    | NS, RS  | D                                        | | [[start#de_-_cultivated_crops|3.D.e]]                                                                                      | Cultivated crops                                                                                       | T2 (NMVOC)                                    | NS, RS  | D                                        |
 | [[use_of_pesticides|3.D.f]]                                                                                                | Use of pesticides                                                                                      | T2 (HCB)                                      | NS      | D                                        | | [[use_of_pesticides|3.D.f]]                                                                                                | Use of pesticides                                                                                      | T2 (HCB)                                      | NS      | D                                        |
 +| {{page>general:Misc:LegendEIT:start}}                                                                                                                                                                                                                                                                                                |||||
  
 ---- ----
  
-^            ^  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  |  Heavy Metals  |  PAHs  ^  HCB  |  PCBs  | +^                                         ^  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  |  As  |  Cr  |  Cu  |  Ni  |  Se  |  Zn  |  PCDD/F  |  B(a)P  |  B(b)F  |  B(k)F  |  I(x)P  |  PAH1-4  ^  HCB  |  PCBs  | 
-| 3.D.a.1    ^  L/T             |  NA     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.1                                 ^  L/T             |  NA     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.a.2.a  ^  L/-             |  IE     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.2.a                               ^  L/-             |  IE     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.a.2.b  |  -/-             |  NA     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.2.b                               |  -/-             |  NA     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.a.2.c  |  -/-             |  NA     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.2.c                               |  -/-             |  NA     |  NA              ^  L/T             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.a.3    |  -/-             |  IE     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.3                                 |  -/-             |  IE     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.a.4    |  NA              |  NA     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.a.4                                 |  NA              |  NA     |  NA              |  -/-             |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.c      |  NA              |  NA     |  NA              |  NA              |  **L/-**           ^  L/-              ^  L/-  |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.c                                   |  NA              |  NA     |  NA              |  NA              ^  L/-               ^  L/-              ^  L/-  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.e      |  NA              |  -/-    |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    |  NA   |  NA    | +| 3.D.e                                   |  NA              |  -/-    |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      |  NA   |  NA    | 
-| 3.D.f      |  NA              |  NA     |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA            |  NA    ^  -/-  |  NA    | +| 3.D.f                                   |  NA              |  NA     |  NA              |  NA              |  NA                |  NA               |  NA   |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA  |  NA      |  NA     |  NA     |  NA     |  NA     |  NA      ^  L/-  |  NA    | 
- {{page>general:Misc:LegendEIT:start}}+|  {{page>general:Misc:LegendKCA:start}}                                                                                                                                                                                                                                                        ||||||||||||||||||||||||||| 
 + 
 \\ \\
  
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 __Table 2: Synthetic fertilizers, emission factors in kg NH<sub>3</sub> per kg fertilizer N__ __Table 2: Synthetic fertilizers, emission factors in kg NH<sub>3</sub> per kg fertilizer N__
-^ Fertilizer type                         ^  EF     ^ +^ Fertilizer type                         ^  EF      ^ 
-| calcium ammonium nitrate                |   0.024 | +| calcium ammonium nitrate                |  0.024   | 
-| ammonia nitrate urea solutions (AHL)    |   0.087 | +| ammonia nitrate urea solutions (AHL)    |  0.087   | 
-| urea (up to 2019)                       |   0.195 | +| urea (up to 2019)                       |  0.195   | 
-| urea (from 2020 with urease inhibitor)  |   0.078 | +| urea (from 2020 with urease inhibitor)  |  0.078   | 
-| urea (from 2020 if incorporated)        |  0.0585 | +| urea (from 2020 if incorporated)        |  0.0585  | 
-| ammonium phosphates                     |   0.084 | +| ammonium phosphates                     |  0.084   | 
-| other NK and NPK                        |   0.084 | +| other NK and NPK                        |  0.084   | 
-| other straight fertilizers              |   0.024 |+| other straight fertilizers              |  0.024   |
  
 For NO<sub>x</sub>, the simpler methodology by EMEP (2023)-3D-13 was used. The emission factor 0.040 from EMEP, 2023-3D, Table 3.1 has the unit of [kg N<sub>2</sub>O per kg fertilizer N] and was derived from Stehfest and Bouwman (2006)((Stehfest E., Bouwman L. (2006): N2O and NO emission from agricultural fields and soils under natural vegetation: summarizing available measurement data and modelling of global emissions. Nutr. Cycl. Agroecosyst. 74, 207 – 228.)). For NO<sub>x</sub>, the simpler methodology by EMEP (2023)-3D-13 was used. The emission factor 0.040 from EMEP, 2023-3D, Table 3.1 has the unit of [kg N<sub>2</sub>O per kg fertilizer N] and was derived from Stehfest and Bouwman (2006)((Stehfest E., Bouwman L. (2006): N2O and NO emission from agricultural fields and soils under natural vegetation: summarizing available measurement data and modelling of global emissions. Nutr. Cycl. Agroecosyst. 74, 207 – 228.)).
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 __Table 3: Emission factor for NO<sub>x</sub> emissions from fertilizer application__ __Table 3: Emission factor for NO<sub>x</sub> emissions from fertilizer application__
-^  Emission factor   ^  kg NO-N  per kg fertilizer N  ^  kg NO<sub>x</sub> per kg fertilizer N  ^ +^  Emission factor    ^  kg NO-N  per kg fertilizer N  ^  kg NO<sub>x</sub> per kg fertilizer N  ^ 
-| EF<sub>fert</sub>  |                          0.012 |                                   0.039 |+|  EF<sub>fert</sub>  |  0.012                         |  0.039                                  |
  
 ==== Trend discussion for Key Sources ==== ==== Trend discussion for Key Sources ====
-Since 2016, fertilizer sales have fallen dramatically (by around a third). Emissions have fallen accordingly. This is even more pronounced for NH<sub>3</sub> than for NO<sub>x</sub>, as total NH<sub>3</sub> from the application of mineral fertilizers is, until the year 2019, very strongly correlated with the amount of urea applied (R<sup>2</sup> = 0.64), the sales of which have decreased more than for all other mineral fertilizers. Since 2020 the negative trend is reinforced as urea fertilizer have to be either used with urease inhibitors or have to be incorporated into the soil directly, which reduces emissions. +Since 2016, fertilizer sales have fallen dramatically (by around a third). Emissions have fallen accordingly. This is even more pronounced for NH<sub>3</sub> than for NO<sub>x</sub>, as total NH<sub>3</sub> from the application of mineral fertilizers is, until the year 2019, very strongly correlated with the amount of urea applied (R<sup>2</sup> = 0.64), the sales of which have decreased more than for all other mineral fertilizers. Since 2020 the negative trend is reinforced as urea fertilizer has to be either used with urease inhibitors or has to be incorporated into the soil directly, which reduces emissions. 
  
  
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 __Table 6: IEF for NH<sub>3</sub>–N from application of manure__ __Table 6: IEF for NH<sub>3</sub>–N from application of manure__
-^  IEF in kg NH<sub>3</sub>-N per kg N in applied manure                                                                                                                  ||||||||||||||| +^ IEF in kg NH<sub>3</sub>-N per kg N in applied manure                                                                                                                                ||||||||||||||| 
-^                                                    1990 ^   1995 ^   2000 ^   2005 ^   2010 ^   2015 ^   2016 ^   2017 ^   2018 ^   2019 ^   2020 ^   2021 ^   2022 ^   2023 ^   2024 ^ +^  1990                                                  ^  1995   ^  2000   ^  2005   ^  2010   ^  2015   ^  2016   ^  2017   ^  2018   ^  2019   ^  2020   ^  2021   ^  2022   ^  2023   ^  2024   ^ 
-|                                                   0.216 |  0.204 |  0.196 |  0.183 |  0.175 |  0.165 |  0.163 |  0.162 |  0.159 |  0.157 |  0.154 |  0.154 |  0.157 |  0.155 |  0.154 |+|  0.216                                                 |  0.204  |  0.196  |  0.183  |  0.175  |  0.165  |  0.163  |  0.162  |  0.159  |  0.157  |  0.154  |  0.154  |  0.157  |  0.155  |  0.154  |
 ==== Trend discussion for Key Sources ==== ==== Trend discussion for Key Sources ====
 Both NH<sub>3</sub> and NO<sub>x</sub> emissions from the application of animal manure are key sources. Total NO<sub>x</sub> is calculated proportionally to the total N applied with manure which decreased remarkably from 1990 to 1991 due to the decline in animal numbers following the German reunification (reduction of livestock numbers in Eastern Germany). In the 1990s and 2000s this was followed by a weakened decline in animal manure amounts. From 2010 to 2014 there was a slight increase and since then the amount of N in manure applied has been declining again, see Table 5. The NO<sub>x</sub> emissions follow these trends. For total NH<sub>3</sub> emissions there is a negative trend. This is due to the decreasing amounts of animal manure and the increasing use of application practices with lower NH<sub>3</sub> emission factors.  Both NH<sub>3</sub> and NO<sub>x</sub> emissions from the application of animal manure are key sources. Total NO<sub>x</sub> is calculated proportionally to the total N applied with manure which decreased remarkably from 1990 to 1991 due to the decline in animal numbers following the German reunification (reduction of livestock numbers in Eastern Germany). In the 1990s and 2000s this was followed by a weakened decline in animal manure amounts. From 2010 to 2014 there was a slight increase and since then the amount of N in manure applied has been declining again, see Table 5. The NO<sub>x</sub> emissions follow these trends. For total NH<sub>3</sub> emissions there is a negative trend. This is due to the decreasing amounts of animal manure and the increasing use of application practices with lower NH<sub>3</sub> emission factors. 
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 ^  Application of sewage sludge in kt N                                                                                                                  ||||||||||||||| ^  Application of sewage sludge in kt N                                                                                                                  |||||||||||||||
 ^  1990                                  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^ ^  1990                                  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^
-|                                     27 |     35 |     33 |     27 |     26 |     19 |     19 |     14 |     13 |     16 |     14 |     12 |     12 |     10 |     10 |+|  27                                    |  35    |  33    |  27    |  26    |  19    |  19    |  14    |  13    |  16    |  14    |  12    |  12    |  10    |  10    |
 ==== Methodology ==== ==== Methodology ====
 A Tier 1 methodology is used (EMEP, 2023, 3D, Chapter 3.3.1). NH<sub>3</sub> and NO<sub>x</sub> emissions are calculated by multiplying the amounts of N in sewage sludge applied with the respective emission factors. A Tier 1 methodology is used (EMEP, 2023, 3D, Chapter 3.3.1). NH<sub>3</sub> and NO<sub>x</sub> emissions are calculated by multiplying the amounts of N in sewage sludge applied with the respective emission factors.
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 ^  N in aboveground crop residues in kt N                                                                                                                  ||||||||||||||| ^  N in aboveground crop residues in kt N                                                                                                                  |||||||||||||||
 ^  1990                                    ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^ ^  1990                                    ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^
-|                                      370 |    377 |    418 |    429 |    411 |    417 |    416 |    443 |    348 |    391 |    403 |    425 |    413 |    424 |    424 |+|  370                                     |  377   |  418   |  429   |  411   |  417   |  416   |  443   |  348   |  391   |  403   |  425   |  413   |  424   |  424   |
 ==== Methodology ==== ==== Methodology ====
 According to EMEP (2023) the NH<sub>3</sub> emissions from crop residues can be neglected when the crop residues are on the field for less than three days. Thus the first step in the emission calculation is determining which share of the crop residues of each crop are incorporated into the soil or removed in the first three days after harvesting the crop. The remaining amounts are multiplied with their respective N contents and the resulting amounts of N are then multiplied with the NH<sub>3</sub>-emission factor. According to EMEP (2023) the NH<sub>3</sub> emissions from crop residues can be neglected when the crop residues are on the field for less than three days. Thus the first step in the emission calculation is determining which share of the crop residues of each crop are incorporated into the soil or removed in the first three days after harvesting the crop. The remaining amounts are multiplied with their respective N contents and the resulting amounts of N are then multiplied with the NH<sub>3</sub>-emission factor.
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 ==== Recalculations ==== ==== Recalculations ====
-There are no recalculations because this source is reported the first time.+For all years, NH<sub>3</sub> emissions from crop residues are slightly higher than those of last year's submission. The main reason for this is **recalculation No. 15** (update of number of grassland cuts). Further details on recalculations are described in Vos et al. (2026), Chapter 1.3.
  
 __Table 18: Comparison of NH<sub>3</sub> emissions [kt] with previous submission__ __Table 18: Comparison of NH<sub>3</sub> emissions [kt] with previous submission__
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 ===== 3.D.c - Farm-level agricultural operations including storage, handling and transport of agricultural products ===== ===== 3.D.c - Farm-level agricultural operations including storage, handling and transport of agricultural products =====
-In this category Germany reports TSP, PM<sub>10</sub> and PM<sub>2.5</sub> emissions from crop production according to EMEP (2023)-3D-22. For details see Rösemann et al. (2025), Chapter 5.2.4.  +In this category Germany reports TSP, PM<sub>10</sub> and PM<sub>2.5</sub> emissions from crop production according to EMEP (2023)-3D-22. For details see Vos et al. (2026), Chapter 5.2.4.  
  
 ==== Activity data ==== ==== Activity data ====
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 Emission factors given in EMEP (2023)-3D-18, Tables 3.6 and 3.8 are used with the exception of „Harvesting“ PM<sub>10</sub>-factors for Wheat, Rye, Barley and Oat which were taken from the Danish IIR. These Guidebook-EFs are obviously too high by a factor of 10 and were corrected in the Danish IIR.  Emission factors given in EMEP (2023)-3D-18, Tables 3.6 and 3.8 are used with the exception of „Harvesting“ PM<sub>10</sub>-factors for Wheat, Rye, Barley and Oat which were taken from the Danish IIR. These Guidebook-EFs are obviously too high by a factor of 10 and were corrected in the Danish IIR. 
  
-The missing default-EFs for „other arable“ in the 2023 EMEP/EEA Guidebook were replaced with the average of the EFs of wheat, rye, barley and oat, as it was done in the Danish IIR. The PM<sub>10</sub> EFs were also used as TSP EFs. The Guidebook does not indicate whether EFs have considered the condensable component (with or without). For details on country specific numbers of agricultural crop operations see Rösemann et al. (2025), Chapter 5.2.4. +The missing default-EFs for „other arable“ in the 2023 EMEP/EEA Guidebook were replaced with the average of the EFs of wheat, rye, barley and oat, as it was done in the Danish IIR. The PM<sub>10</sub> EFs were also used as TSP EFs. The Guidebook does not indicate whether EFs have considered the condensable component (with or without). For details on country specific numbers of agricultural crop operations see Vos et al. (2026), Chapter 5.2.4. 
  
 __Table 20: Implied emission factors for PM emissions from agricultural soils, in kg ha<sup>-1</sup>__ __Table 20: Implied emission factors for PM emissions from agricultural soils, in kg ha<sup>-1</sup>__
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 ==== Trend discussion for Key Sources ==== ==== Trend discussion for Key Sources ====
  
-TSP and PM<sub>10</sub> are key sources. Emissions depend on the areas covered, crop types and number of crop operations. With the exception of the numbers of soil cultivations, which is slightly decreasing, these data are relatively constant. Overall this is reflected in a slight decline of emissions in the last 12 years. +TSP and PM<sub>10</sub> are key sources. Emissions depend on the areas covered, crop types and number of crop operations. With the exception of the numbers of soil cultivations, which is slightly decreasing, these data are relatively constant. Overall this is reflected in a slight decline of emissions in the last years. 
  
 ==== Recalculations ==== ==== Recalculations ====
- +There were no recalculations. Further details on recalculations are described in Vos et al. (2026), Chapter 1.3. 
-For all years, totals of TSP, PM<sub>10</sub> and PM<sub>2.5</sub> emissions are higher than those of last year’s submission. This is mostly due to the introduction of cover crops to the calculation method (see main page of the agricultural sector, list of recalculations, No. 2). Further details on recalculations are described in Rösemann et al. (2025), Chapter 1.3.  +
  
 __Table 21: Comparison of particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>) [kt] with previous submission__ __Table 21: Comparison of particle emissions (TSP, PM<sub>10</sub> & PM<sub>2.5</sub>) [kt] with previous submission__
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 =====  3.D.e - Cultivated crops ===== =====  3.D.e - Cultivated crops =====
-In this category Germany reports NMVOC emissions from crop production according to EMEP (2023)-3D-21. For details see Rösemann et al. (2025), Chapter 5.2.3. +In this category Germany reports NMVOC emissions from crop production according to EMEP (2023)-3D-21. For details see Vos et al. (2026), Chapter 5.2.3. 
  
 ==== Activity data ==== ==== Activity data ====
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 __Table 24: Comparison of NMVOC emissions [kt] with previous submission__ __Table 24: Comparison of NMVOC emissions [kt] with previous submission__
 ^        ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^ ^        ^ Submission           ^  1990  ^  1995  ^  2000  ^  2005  ^  2010  ^  2015  ^  2016  ^  2017  ^  2018  ^  2019  ^  2020  ^  2021  ^  2022  ^  2023  ^  2024  ^
-^ NMVOC  ^ current              |   7.69 |   8.19 |   8.79 |   9.17 |   9.53 |   9.91 |   9.69 |   9.74 |   7.82 |   8.56 |   9.16 |   9.44 |   8.91 |   9.23 |   8.87 | +^ NMVOC  ^ current              |  7.69  |  8.19  |  8.79  |  9.17  |  9.53  |  9.91  |  9.69  |  9.74  |  7.82  |  8.56  |  9.16  |  9.44  |  8.91  |  9.23  |  8.87  | 
-| :::    ^ previous             |   7.69 |   8.19 |   8.79 |   9.17 |   9.53 |   9.91 |   9.69 |   9.74 |   7.82 |   8.56 |   9.16 |   9.44 |   8.91 |   9.23 |        |+| :::    ^ previous             |  7.69  |  8.19  |  8.79  |  9.17  |  9.53  |  9.91  |  9.69  |  9.74  |  7.82  |  8.56  |  9.16  |  9.44  |  8.91  |  9.23  |        |
 | :::    ^ 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  |  0.00  |        | | :::    ^ 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  |  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  |  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  |  0.00  |        |
  
 <WRAP center round info 65%> <WRAP center round info 65%>
-For **pollutant-specific information on recalculated emission estimates for Base Year and 2022**, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 9.1 - Recalculations]].+For **pollutant-specific information on recalculated emission estimates for Base Year and 2023**, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 9.1 - Recalculations]].
 </WRAP> </WRAP>
 ==== Planned improvements ==== ==== Planned improvements ====