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| sector:agriculture:agricultural_soils:start [2021/12/25 14:23] – [Table] doering | sector:agriculture:agricultural_soils:start [2022/09/19 07:56] (current) – Fix link hausmann | ||
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| | [[3Df_Agriculture other|3.D.f]] | | [[3Df_Agriculture other|3.D.f]] | ||
| - | ^ Key Category | + | ^ Key Category |
| - | | 3.D.a.1 | + | | 3.D.a.1 |
| - | | 3.D.a.2.a | + | | 3.D.a.2.a |
| - | | 3.D.a.2.b | + | | 3.D.a.2.b |
| - | | 3.D.a.2.c | + | | 3.D.a.2.c |
| - | | 3.D.a.3 | + | | 3.D.a.3 |
| - | | 3.D.c | + | | 3.D.c | - |
| - | | 3.D.e | + | | 3.D.e | - |
| - | | 3.D.f | + | | 3.D.f | - |
| | | ||
| \\ | \\ | ||
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| ==== NH₃ and NOₓ ==== | ==== NH₃ and NOₓ ==== | ||
| - | In 2019, the category of agricultural soils emitted | + | In 2020, agricultural soils emitted |
| - | Application of sewage sludge (3.D.a.2.b) contributes 0.6 % or 1.7 kt NH< | + | Application of sewage sludge (3.D.a.2.b) contributes 0.7 % or 1.9 kt NH< |
| - | The application of residues from the digestion of energy crops (3.D.a.2.c) leads to 54.6 kt NH< | + | The application of residues from the digestion of energy crops (3.D.a.2.c) leads to 37.0 kt NH< |
| - | NH< | + | In 2020, agricultural soils were the source of 98.6 % (107.2 kt) of the total of NO< |
| - | + | ||
| - | In 2019, agricultural soils were the source of 98.6 % (110.7 kt) of the total of NO< | + | |
| - | + | ||
| - | All NO< | + | |
| ==== NMVOC ==== | ==== NMVOC ==== | ||
| - | In 2019, the category of agricultural soils contributed | + | In 2020, the category of agricultural soils contributed |
| ==== TSP, PM₁₀ & PM₂.₅ ==== | ==== TSP, PM₁₀ & PM₂.₅ ==== | ||
| - | In 2019, agricultural soils contributed, | + | In 2020, agricultural soils contributed, |
| =====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 ==== | ||
| - | German statistics report the amounts of fertilizers sold which are assumed to equal the amounts that are applied. Since the 2021 submission, storage effects are approximated by applying a moving average to the sales data (moving centered three-year average, for the last year a two-year average). | + | German statistics report the amounts of fertilizers sold which are assumed to equal the amounts that are applied. Since the 2021 submission, storage effects are approximated by applying a moving average to the sales data (moving centered three-year average, for the last year a weighted |
| //Table 1: AD for the estimation of NH< | //Table 1: AD for the estimation of NH< | ||
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| ==== Emission factors ==== | ==== Emission factors ==== | ||
| - | The emission factors for NH< | + | The emission factors for NH< |
| //Table 2: NH< | //Table 2: NH< | ||
| Line 88: | Line 84: | ||
| | Other straight fertilizers | | Other straight fertilizers | ||
| - | For NO< | + | For NO< |
| //Table 3: Emission factor for NO< | //Table 3: Emission factor for NO< | ||
| Line 96: | Line 92: | ||
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| - | In the last five years (and in the last three years in dramatic fashion) fertilizer sales have decreased. Emissions have fallen accordingly. This is even more the case with NH< | + | In the last years (and up to 2019 in dramatic fashion) fertilizer sales have decreased. |
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-1 shows the effects of recalculations on NH< | + | Table REC-1 shows the effects of recalculations on NH< |
| // | // | ||
| - | Table REC-1: Comparison of NH< | + | Table REC-1: Comparison of NH< |
| ^ NH< | ^ NH< | ||
| Line 117: | Line 113: | ||
| ===== 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< |
| ==== Activity data ==== | ==== Activity data ==== | ||
| The calculation of the amount of N in manure applied is based on the N mass flow approach (see 3.B). It is the total of N excreted by animals in the housing and the N imported with bedding material minus N losses by emissions of N species from housing and storage. Hence, the amount of total N includes the N contained in anaerobically digested manures to be applied to the field. | The calculation of the amount of N in manure applied is based on the N mass flow approach (see 3.B). It is the total of N excreted by animals in the housing and the N imported with bedding material minus N losses by emissions of N species from housing and storage. Hence, the amount of total N includes the N contained in anaerobically digested manures to be applied to the field. | ||
| - | The frequencies of application techniques and incorporation times as well as the underlying data sources are described in Rösemann | + | The frequencies of application techniques and incorporation times as well as the underlying data sources are described in Vos et al. (2022), Chapter 3.4.3. The frequencies are provided e. g. in the NIR 2022((NIR (2022): National Inventory Report |
| //Table 4: AD for the estimation of NH< | //Table 4: AD for the estimation of NH< | ||
| Line 132: | Line 128: | ||
| ==== Methodology ==== | ==== Methodology ==== | ||
| - | NH< | + | NH< |
| - | For NO< | + | For NO< |
| ==== Emission factors ==== | ==== Emission factors ==== | ||
| Line 146: | Line 142: | ||
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| - | Both NH< | + | Both NH< |
| - | For total NH< | + | For total NH< |
| - | For both gases, emissions are slightly decreasing since 2015. This is due to the fact that cattle and swine animal numbers are declining. | + | |
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-2 shows the effects of recalculations on NH< | + | Table REC-2 shows the effects of recalculations on NH< |
| + | These differences are predominantly caused by the update of data from the official agricultural census 2020 as well as the update of the suckler-cow model and the new raw protein contents in feed of fattening pigs and broilers, see [[sector: | ||
| - | //Table REC-2: Comparison of the NH< | + | Much smaller is the impact of the updates of activity data for male cattle > 2 years, pigs, poultry and sheep (see **recalculation reasons 5, 6 and 9 through 12**) Further details on recalculations are described in Vos et al. (2022), Chapter 3.5.2. |
| + | |||
| + | |||
| + | //Table REC-2: Comparison of the NH< | ||
| ^ NH< | ^ NH< | ||
| Line 168: | Line 167: | ||
| ===== 3.D.a.2.b – Sewage sludge applied to soils ===== | ===== 3.D.a.2.b – Sewage sludge applied to soils ===== | ||
| - | The calculation of NH< | + | The calculation of NH< |
| ==== Activity data ==== | ==== Activity data ==== | ||
| Line 190: | Line 189: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-3 shows the effects of recalculations on NH< | ||
| - | //Table REC-3: Comparison of the NH< | + | Table REC-3 shows the effects of recalculations on NH< |
| + | |||
| + | //Table REC-3: Comparison of the NH< | ||
| ^ NH< | ^ NH< | ||
| Line 205: | Line 205: | ||
| ===== 3.D.a.2.c - Other organic fertilizers applied to soils ===== | ===== 3.D.a.2.c - Other organic fertilizers applied to soils ===== | ||
| - | This sub category describes Germany’s NH< | + | This sub category describes Germany’s NH< |
| ==== Activity data ==== | ==== Activity data ==== | ||
| - | Activity data is the amount of N in residues from anaerobic digestion of energy crops when leaving storage. This amount of N is the N contained in the energy crops when being fed into the digestion process minus the N losses by emissions of N species from the storage of the residues (see 3.I). N losses from pre-storage are negligible and there are no N losses from fermenter (see Rösemann | + | Activity data is the amount of N in residues from anaerobic digestion of energy crops when leaving storage. This amount of N is the N contained in the energy crops when being fed into the digestion process minus the N losses by emissions of N species from the storage of the residues (see 3.I). N losses from pre-storage are negligible and there are no N losses from fermenter (see Vos et al. (2022), Chapter 10.2.1). |
| //Table 7: AD for the estimation of NH< | //Table 7: AD for the estimation of NH< | ||
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| ==== Methodology ==== | ==== Methodology ==== | ||
| - | The NH< | + | The NH< |
| For NO< | For NO< | ||
| ==== Emission factors ==== | ==== Emission factors ==== | ||
| - | For NH< | + | For NH< |
| Table 8 shows the implied emission factors for NH< | Table 8 shows the implied emission factors for NH< | ||
| Line 236: | Line 236: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-4 shows the effects of recalculations on NH< | ||
| - | //Table REC-4: Comparison of the NH< | + | Table REC-4 shows the effects of recalculations on NH< |
| + | |||
| + | //Table REC-4: Comparison of the NH< | ||
| ^ NH< | ^ NH< | ||
| ^ | ^ | ||
| Line 251: | Line 253: | ||
| ===== 3.D.a.3 - Urine and dung deposited by grazing animals ===== | ===== 3.D.a.3 - Urine and dung deposited by grazing animals ===== | ||
| - | The calculation of NH< | + | The calculation of NH< |
| ==== Activity data ==== | ==== Activity data ==== | ||
| Line 287: | Line 289: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-5 shows the effects of recalculations on NH< | + | Table REC-5 shows the effects of recalculations on NH< |
| + | |||
| + | Because overall N excretions on pasture are lower than in last year’s submission | ||
| + | |||
| + | //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 ^ | ^ ^ SUB ^ 1990 ^ 1995 ^ 2000 ^ 2005 ^ 2010 ^ 2011 ^ 2012 ^ 2013 ^ 2014 ^ 2015 ^ 2016 ^ 2017 ^ 2018 ^ 2019 ^ 2020 ^ | ||
| Line 301: | Line 306: | ||
| ===== 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< | + | In this category Germany reports TSP, PM< |
| ==== Activity data ==== | ==== Activity data ==== | ||
| Line 330: | Line 335: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-6 shows the effects of recalculations on particulate matter emissions. | + | Table REC-6 shows the effects of recalculations on particulate matter emissions. |
| - | //Table REC-6: Comparison of particle emissions (TSP, PM< | + | //Table REC-6: Comparison of particle emissions (TSP, PM< |
| ^ TSP, PM< | ^ TSP, PM< | ||
| Line 349: | Line 354: | ||
| ===== 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 Rösemann | + | In this category Germany reports NMVOC emissions from crop production according to EMEP (2019)-3D-16. For details see Vos et al. (2022), Chapter 11.12. |
| ==== Activity data ==== | ==== Activity data ==== | ||
| Line 355: | Line 360: | ||
| // 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 |
| - | | 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 | | + | | 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' |
| Line 367: | Line 372: | ||
| // 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< | + | ^ IEF for NMVOC emissions from crop production in kg ha< |
| - | ^ 1990 | + | ^ 1990 |
| - | | 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 | | + | | 0.47 | 0.53 | 0.57 | 0.59 | 0.61 | 0.57 | 0.64 | 0.66 | 0.72 | 0.63 | 0.62 | 0.62 | 0.50 | |
| ==== Trend discussion for Key Sources ==== | ==== Trend discussion for Key Sources ==== | ||
| - | Emissions | + | NMVOC emissions |
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | Table REC-7 shows the effects of recalculations on NMVOC emissions. | + | Table REC-7 shows the effects of recalculations on NMVOC emissions. |
| - | //Table REC-7: Comparison of NMVOC emissions of the submissions (SUB) 2020 and 2021// | ||
| - | ^ NMVOC emissions | + | //Table REC-7: Comparison of NMVOC emissions |
| - | ^ | + | |
| - | | **2021** | + | |
| - | | **2020** | + | |
| + | ^ NMVOC emissions from crop production, in Gg |||||||||||||||| | ||
| + | ^ SUB | ||
| + | | **2022** | ||
| + | | **2021** | ||
| + | <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: | ||
| + | </ | ||
| ==== Planned improvements ==== | ==== Planned improvements ==== | ||
| No improvements are planned at present. | No improvements are planned at present. | ||
| ==== Uncertainty ==== | ==== Uncertainty ==== | ||
| - | Details | + | Details |