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| sector:agriculture:agricultural_soils:start [2022/12/16 11:07] – [3.D.c - Farm-level agricultural operations including storage, handling and transport of agricultural products] doering | sector:agriculture:agricultural_soils:start [2023/05/05 10:48] (current) – [3.D.a.1 - Inorganic N-fertilizers] doering | ||
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| Line 23: | Line 23: | ||
| | 3.D.c | - | | 3.D.c | - | ||
| | 3.D.e | - | | 3.D.e | - | ||
| - | | 3.D.f | - | + | | 3.D.f | - |
| | | ||
| \\ | \\ | ||
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| =====3.D.a.1 - Inorganic N-fertilizers ===== | =====3.D.a.1 - Inorganic N-fertilizers ===== | ||
| - | The calculation of NH< | + | The calculation of NH< |
| ==== Activity Data ==== | ==== Activity Data ==== | ||
| Line 53: | Line 53: | ||
| //Table 1: AD for the estimation of NH< | //Table 1: AD for the estimation of NH< | ||
| - | ^ Application of inorganic | + | ^ Application of synthetic |
| - | ^ ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 ^ | + | ^ ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | Application of fertilizers (total) | + | | Application of fertilizers (total) |
| - | | Calcium ammonium nitrate | + | | Calcium ammonium nitrate |
| - | | Nitrogen solutions (urea AN) | + | | Nitrogen solutions (urea AN) |
| - | | Urea | + | | Urea |
| - | | Ammonium phosphates | + | | Ammonium phosphates |
| - | | Other NK and NPK | + | | Other NK and NPK |
| - | | Other straight fertilizers | + | | Other straight fertilizers |
| Line 73: | Line 73: | ||
| //Table 2: NH< | //Table 2: NH< | ||
| - | ^ Synthetic fertilizers, | + | ^ Synthetic fertilizers, |
| - | ^ Fertilizer type ^ EF ^ | + | ^ Fertilizer type ^ EF ^ |
| - | | Calcium ammonium nitrate | + | | Calcium ammonium nitrate |
| - | | Nitrogen solutions (UREA AN) | + | | Nitrogen solutions (UREA AN) |
| | Urea | | Urea | ||
| - | | Ammonium phosphates | + | | Ammonium phosphates |
| - | | Other NK and NPK | + | | Other NK and NPK |
| - | | Other straight fertilizers | + | | Other straight fertilizers |
| For NO< | For NO< | ||
| Line 100: | Line 100: | ||
| Table REC-1: Comparison of NH< | Table REC-1: Comparison of NH< | ||
| - | ^ NH< | + | ^ NH< |
| - | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 ^ | + | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | **NH< | + | | **NH< |
| - | | **NH< | + | | **NH< |
| - | | **NO< | + | | **NO< |
| - | | **NO< | + | | **NO< |
| ==== Planned improvements ==== | ==== Planned improvements ==== | ||
| Line 111: | Line 111: | ||
| ===== 3.D.a.2.a - Animal manure applied to soils ===== | ===== 3.D.a.2.a - Animal manure applied to soils ===== | ||
| - | In this sub category Germany reports the NH< | + | In this sub category Germany reports the NH< |
| Germany uses the Tier 2 methodology for estimating NMVOC emissions for cattle in sector 3.B (manure management). The use of this methodology yields NMVOC emissions which formally could be reported in the sectors 3.D.a.2.a and 3.D.a.3 (grazing emissions). However, to be congruent with the NMVOC emissions for other animal categories, Germany reports these emissions in the NMVOC emissions reported from manure management (3.B). For the NFR codes 3.D.a.2.a and 3.D.a.3 the notation key IE is used for NMVOC emissions. | Germany uses the Tier 2 methodology for estimating NMVOC emissions for cattle in sector 3.B (manure management). The use of this methodology yields NMVOC emissions which formally could be reported in the sectors 3.D.a.2.a and 3.D.a.3 (grazing emissions). However, to be congruent with the NMVOC emissions for other animal categories, Germany reports these emissions in the NMVOC emissions reported from manure management (3.B). For the NFR codes 3.D.a.2.a and 3.D.a.3 the notation key IE is used for NMVOC emissions. | ||
| Line 122: | Line 122: | ||
| //Table 4: AD for the estimation of NH< | //Table 4: AD for the estimation of NH< | ||
| - | ^ Application of manure in Gg N ||||||||||||||| | + | ^ Application of manure in Gg N |||||||||||||||| |
| - | ^ 1990 | + | ^ 1990 |
| - | | 1' | + | | 1,129 | |
| Line 135: | Line 135: | ||
| //Table 5: IEF for NH< | //Table 5: IEF for NH< | ||
| - | ^ IEF in kg NH< | + | ^ IEF in kg NH< |
| - | ^ 1990 | + | ^ 1990 |
| - | | 0.202 | 0.187 | 0.180 | 0.168 | 0.162 | 0.162 | 0.157 | 0.155 | 0.152 | 0.150 | 0.148 | 0.147 | 0.145 | 0.143 | 0.140 | | + | | 0.208 | 0.194 | 0.187 | 0.174 | 0.168 | 0.169 | 0.165 | 0.164 | 0.162 | 0.160 | 0.158 | 0.156 | 0.154 | 0.152 | 0.149 | 0.150 |
| For NO< | For NO< | ||
| Line 154: | Line 154: | ||
| //Table REC-2: Comparison of the NH< | //Table REC-2: Comparison of the NH< | ||
| - | ^ NH< | + | ^ NH< |
| - | ^ | + | ^ |
| - | | **NH< | + | | **NH< |
| - | | **NH< | + | | **NH< |
| - | | **NO< | + | | **NO< |
| - | | **NO< | + | | **NO< |
| Line 172: | Line 172: | ||
| //Table 6: AD for the estimation of NH< | //Table 6: AD for the estimation of NH< | ||
| - | ^ Application of sewage sludge in Gg N ||||||||||||||| | + | ^ Application of sewage sludge in Gg N |||||||||||||||| |
| - | ^ 1990 | + | ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | 27 | 35 | 33 | 27 | 26 | 25 | 25 | 22 | 21 | 19 | 19 | 14 | 12 | 14 | 14 | | + | | |
| ==== Methodology ==== | ==== Methodology ==== | ||
| - | A tier 1 methodology is used (EMEP, 2019, 3D, Chapter 3.3.1). NH< | + | A Tier 1 methodology is used (EMEP, 2019, 3D, Chapter 3.3.1). NH< |
| ==== Emission factors ==== | ==== Emission factors ==== | ||
| Line 193: | Line 193: | ||
| //Table REC-3: Comparison of the NH< | //Table REC-3: Comparison of the NH< | ||
| - | ^ NH< | + | ^ NH< |
| - | ^ | + | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | **NH< | + | | **NH< |
| - | | **NH< | + | | **NH< |
| - | | **NO< | + | | **NO< |
| - | | **NO< | + | | **NO< |
| ==== Planned improvements ==== | ==== Planned improvements ==== | ||
| Line 221: | Line 221: | ||
| //Table 7: AD for the estimation of NH< | //Table 7: AD for the estimation of NH< | ||
| - | ^ Application of residues from digested energy plants | + | ^ Application of other organic fertilizers |
| - | ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 | + | ^ |
| - | | | + | ^ Residues, digested energy crops |
| + | ^ Residues, digested waste | ||
| + | ^ Compost, biowaste | ||
| + | ^ Compost, greenwaste | ||
| + | ^ Total | 5.68 | 25.07 | 46.49 | 89.01 | 211.78 | 255.44 | 277.91 | 323.53 | 343.18 | 355.13 | 353.77 | 347.74 | 346.91 | 347.03 | 354.98 | 354.74 | | ||
| ==== Methodology ==== | ==== Methodology ==== | ||
| Line 239: | Line 242: | ||
| //Table 8: IEF for NH< | //Table 8: IEF for NH< | ||
| - | + | ^ IEF in kg NH3-N per kg N of other organic fertilizers | |
| - | ^ IEF in kg NH< | + | ^ ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | ^ 1990 | + | ^ Residues, digested energy crops | 0.182 | 0.182 | 0.183 | 0.183 | 0.183 | 0.184 | 0.174 | 0.166 | 0.159 | 0.153 | 0.150 | 0.147 | 0.144 | 0.141 | 0.139 | 0.139 | |
| - | | | + | ^ Residues, digested waste | 0.000 | 0.000 | 0.192 | 0.193 | 0.193 | 0.189 | 0.195 | 0.196 | 0.183 | 0.171 | 0.164 | 0.156 | 0.163 | 0.162 | 0.163 | 0.162 | |
| + | ^ Compost, biowaste | ||
| + | ^ Compost, greenwaste | ||
| + | ^ Total | ||
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| Line 254: | Line 259: | ||
| //Table REC-4: Comparison of the NH3 and NOx emissions from application of other organic fertilizers of the submissions (SUB) 2022 and 2023// | //Table REC-4: Comparison of the NH3 and NOx emissions from application of other organic fertilizers of the submissions (SUB) 2022 and 2023// | ||
| - | ^ NH< | + | ^ NH< |
| - | ^ | + | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | **NH< | + | | **NH< |
| - | | **NH< | + | | **NH< |
| - | | **NO< | + | | **NO< |
| - | | **NO< | + | | **NO< |
| Line 274: | Line 279: | ||
| // Table 9: Share of N excretions on pasture // | // Table 9: Share of N excretions on pasture // | ||
| - | ^ N excretions on pasture in % of total N excreted | + | ^ N excretions on pasture in % of total N excreted |
| - | ^ | + | ^ ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | Dairy cows | 20.3 | 15.6 | 12.7 | 11.3 | 10.3 | | + | ^ Dairy cows |
| - | | Other cattle | + | ^ Other cattle |
| - | | Sheep | + | ^ Sheep | 55.1 | 55.5 | 55.1 | 55.4 | 54.8 | 55.1 | 55.1 | 55.2 | 55.3 | 55.4 | 55.4 | 55.4 | 55.6 | 55.5 | 55.4 | 55.5 | |
| - | | Goats | + | ^ Goats | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | 34.2 | |
| - | | Horses | + | ^ Horses |
| + | ^ Laying hens | 0.1 | 0.1 | 0.5 | 1.1 | 1.7 | 1.9 | 2.0 | 2.1 | 2.3 | 2.3 | 2.4 | 2.3 | 2.5 | 2.6 | 2.8 | 2.8 | | ||
| ==== Methodology ==== | ==== Methodology ==== | ||
| Line 290: | Line 296: | ||
| //Table 10: Emission factors for emissions of NH< | //Table 10: Emission factors for emissions of NH< | ||
| - | ^ Emission factors | + | ^ Emission factors |
| - | | Dairy cows | 0.14 kg NH3-N per kg TAN excreted | + | | Dairy cows |
| - | | Other cattle | + | | Other cattle |
| - | | Horses | + | | Horses |
| - | | Sheep, goats | 0.09 kg NH3-N per kg TAN excreted | + | | Sheep, goats |
| - | | All animals | + | | Laying hens | 0.35 kg NH3-N per kg TAN excreted |
| + | | All animals | ||
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| Line 309: | Line 316: | ||
| //Table REC-5: Comparison of the NH< | //Table REC-5: Comparison of the NH< | ||
| - | ^ NH< | + | ^ NH< |
| - | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 ^ | + | ^ |
| - | | **NH< | + | | **NH< |
| - | | **NH< | + | | **NH< |
| - | | **NO< | + | | **NO< |
| - | | **NO< | + | | **NO< |
| ==== Planned improvements ==== | ==== Planned improvements ==== | ||
| Line 323: | Line 330: | ||
| ==== Activity data ==== | ==== Activity data ==== | ||
| - | The activity data is the total area of arable and horticultural land. This data is provided by official statistics. | + | The activity data is the total area of agricultural land (arable |
| //Table 11: AD for the estimation of TSP, PM< | //Table 11: AD for the estimation of TSP, PM< | ||
| - | ^ Arable and horticultural land in 1000*ha | + | ^ Arable and horticultural land in 1000*ha |
| - | ^ 1990 | + | ^ 1990 ^ 1995 |
| - | | | + | | 16,597 | 15, |
| ==== Methodology ==== | ==== Methodology ==== | ||
| - | As the Tier 2 methodology described in EMEP (2019)-3D-17 | + | The Tier 2 methodology |
| ==== Emission factors ==== | ==== Emission factors ==== | ||
| - | Emission factors given in EMEP (2019)-3D-12 are used. The Guidebook does not indicate whether EFs have considered the condensable component (with or without). | + | Emission factors given in EMEP (2019)-3D-18, Tables 3.5 and 3.7 are used with the exception of „Harvesting“ PM< |
| //Table 12: Emission factors for PM emissions from agricultural soils// | //Table 12: Emission factors for PM emissions from agricultural soils// | ||
| - | ^ | + | ^ |
| - | | EF< | + | ^ |
| - | | EF<sub>PM10</ | + | | TSP |
| - | | EF<sub>PM2.5</ | + | | PM<sub>10</ |
| + | | PM<sub>2.5</ | ||
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| - | TSP and PM< | + | |
| + | TSP and PM< | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-6 shows the effects of recalculations on particulate matter emissions. There are minor changes with respect to last year’s submission in several years because of updates of cultivation areas (see [[sector: | ||
| - | //Table REC-6: Comparison of particle emissions (TSP, PM< | + | Table REC-6 shows the effects of recalculations on particulate matter emissions. The emissions are considerably higher than those of submission 2022. In particular the PM< |
| + | |||
| + | //Table REC-6: Comparison of particle emissions (TSP, PM< | ||
| - | ^ TSP, PM< | + | ^ TSP, PM< |
| - | ^ | + | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | **TSP** | + | | **TSP** |
| - | | **TSP** | + | | **TSP** |
| - | | **PM< | + | | **PM< |
| - | | **PM< | + | | **PM< |
| - | | **PM< | + | | **PM< |
| - | | **PM< | + | | **PM< |
| Line 368: | Line 377: | ||
| ===== 3.D.e - Cultivated crops ===== | ===== 3.D.e - Cultivated crops ===== | ||
| - | In this category Germany reports NMVOC emissions from crop production according to EMEP (2019)-3D-16. For details see Vos et al. (2022), Chapter | + | In this category Germany reports NMVOC emissions from crop production according to EMEP (2019)-3D-16. For details see Rösemann |
| ==== Activity data ==== | ==== Activity data ==== | ||
| Line 374: | Line 383: | ||
| // Table 13: AD for the estimation of NMVOC emissions from crop production// | // Table 13: AD for the estimation of NMVOC emissions from crop production// | ||
| - | ^ Arable land and grassland in 1000*ha | + | ^ Arable land and grassland in 1000*ha |
| - | ^ 1990 | + | ^ 1990 ^ 1995 |
| - | | 16'506 | 15'312 | 15'498 | 15'561 | 15'734 | 15'752 | 15'729 | 15'769 | 15'802 | 15'719 | 15'662 | 15'647 | 15'570 | 15'563 | 15'447 | | + | | |
| Line 386: | Line 395: | ||
| // Table 14: IEF for NMVOC emissions from crop production// | // Table 14: IEF for NMVOC emissions from crop production// | ||
| - | ^ IEF for NMVOC emissions from crop production in kg ha<sub>-1</sub> ||||||||||||||| | + | ^ IEF for NMVOC emissions from crop production in kg ha<sup>-1</sup> |||||||||||||||| |
| - | ^ 1990 | + | ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | 0.47 | 0.53 | 0.57 | 0.59 | 0.61 | 0.57 | 0.64 | 0.66 | 0.72 | 0.63 | 0.62 | 0.62 | 0.50 | 0.55 | 0.59 | | + | | |
| Line 395: | Line 404: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-7 shows the effects of recalculations on NMVOC emissions. There are minor changes with respect to last year’s submission | + | Table REC-7 shows the effects of recalculations on NMVOC emissions. There are no changes with respect to last year’s submission. Further details on recalculations are described in Rösemann |
| - | //Table REC-7: Comparison of NMVOC emissions of the submissions (SUB) 2021 and 2022// | + | //Table REC-7: Comparison of NMVOC emissions of the submissions (SUB) 2022 and 2023// |
| - | ^ NMVOC emissions from crop production, in Gg |||||||||||||||| | + | ^ NMVOC emissions from crop production, in Gg ||||||||||||||||| |
| - | ^ SUB | + | ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 |
| - | | **2022** | + | | **2023** | 7.69 | 8.19 | 8.79 | 9.17 | 9.53 | 9.03 | 10.05 | 10.36 | 11.40 | 9.91 | 9.69 | 9.74 | 7.82 | 8.56 | |
| - | | **2021** | + | | **2022** | 7.69 | 8.19 | 8.79 | 9.17 | 9.53 | 9.03 | 10.05 | 10.36 | 11.40 | 9.91 | 9.69 | 9.74 | 7.82 | |
| <WRAP center round info 60%> | <WRAP center round info 60%> | ||
| - | For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the pollutant specific recalculation tables following [[general: | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2020**, please see the pollutant specific recalculation tables following [[general: |
| </ | </ | ||
| ==== Planned improvements ==== | ==== Planned improvements ==== | ||