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| sector:agriculture:agricultural_soils:start [2026/04/01 12:05] – kotzulla | sector:agriculture:agricultural_soils:start [2026/04/01 12:08] (current) – kotzulla | ||
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| - | For NO< | + | For NO< |
| The German inventory uses the emission factor 0.012 kg NO-N per kg N derived from Stehfest and Bouwman (2006) directly[(STEHFESTBOUWMAN2006)]. This is equivalent to an emission factor of 0.03943 kg NO< | The German inventory uses the emission factor 0.012 kg NO-N per kg N derived from Stehfest and Bouwman (2006) directly[(STEHFESTBOUWMAN2006)]. This is equivalent to an emission factor of 0.03943 kg NO< | ||
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| 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 Vos et al. (2026), Chapter 2.5. The frequencies are provided. in the NID 2026((NID (2026): | + | The frequencies of application techniques and incorporation times as well as the underlying data sources are described in Vos et al. (2026), Chapter 2.5. The frequencies are provided in the National Inventory Report 2026 for the German Greenhouse Gas Inventory 1990-2024 |
| __Table 5: AD for the estimation of NH< | __Table 5: AD for the estimation of NH< | ||