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sector:energy:fuel_combustion:other_including_military:military_transport:military_aviation [2022/01/10 10:11] – [Table] kotzulla | sector:energy:fuel_combustion:other_including_military:military_transport:military_aviation [2022/03/22 12:12] (current) – [Discussion of emission trends] kotzulla | ||
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For source category 1.A.5.b, consumption data for **kerosene**, | For source category 1.A.5.b, consumption data for **kerosene**, | ||
- | For the years as of 1995, the official mineral-oil data of the Federal Republic of Germany (Amtliche Mineralöldaten der Bundesrepublik Deutschland 2012), prepared by the Federal Office of Economics and Export Control (BAFA), are used (BAFA, | + | For the years as of 1995, the official mineral-oil data of the Federal Republic of Germany (Amtliche Mineralöldaten der Bundesrepublik Deutschland 2012), prepared by the Federal Office of Economics and Export Control (BAFA), are used (BAFA, |
- | As there is no consistent AGEB data availabe for **aviation gasoline**, delivery data from BAFA [(BAFA2020)] | + | As there is no consistent AGEB data availabe for **aviation gasoline**, delivery data from BAFA is used. |
__Table 1: Sources for consumption data in 1.A.5.b__ | __Table 1: Sources for consumption data in 1.A.5.b__ | ||
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__Table 2: Annual fuel consumption in military aviation, in terajoules__ | __Table 2: Annual fuel consumption in military aviation, in terajoules__ | ||
| ^ 1990 | | ^ 1990 | ||
- | ^ Jet Kerosene | + | ^ Jet Kerosene |
- | ^ Aviation Gasoline | + | ^ Aviation Gasoline |
- | | **Ʃ 1.A.5.b ii** | + | | **Ʃ 1.A.5.b ii** |
< | < | ||
- | {{ : | + | {{: |
- | {{ : | + | {{: |
==== Emission factors ==== | ==== Emission factors ==== | ||
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__Table 3: Country-specific emission factors, in kg/TJ__ | __Table 3: Country-specific emission factors, in kg/TJ__ | ||
- | | | + | | |
- | | **JET KEROSENE** | + | | **JET KEROSENE** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | | + | ^ NMVOC | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | 98.0 | |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ CO | + | ^ CO |
- | | **AVIATION GASOLINE** | + | | **AVIATION GASOLINE** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | 300 | | + | ^ NMVOC | |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ TSP< | + | ^ TSP< |
- | ^ CO | + | ^ CO |
< | < | ||
< | < | ||
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Therefore, the fuel-consumption dependend trends in emission estimates are only influenced by the annual fuel mix. | Therefore, the fuel-consumption dependend trends in emission estimates are only influenced by the annual fuel mix. | ||
- | {{ : | + | {{: |
- | {{ : | + | {{: |
- | Here, as the EF(BC) are estimated via fractions provided in [((bibcite 3))], black carbon emissions follow the corresponding emissions of PM< | + | Here, as the EF(BC) are estimated via fractions provided in [(EMEPEEA2019)], black carbon emissions follow the corresponding emissions of PM< |
Nonetheless, | Nonetheless, | ||
- | {{ : | + | {{: |
Until 1997, lead emissions were dominated by the combustion of leaded gasoline in military ground-based vehicles. Therefore, the over-all trend for lead emissions from military vehicles and aircraft is driven mostly by the abolition of leaded gasoline in 1997. Towards this date, the amount of leaded gasoline decreased significantly. After 1997, the only source for lead from mobile fuel combustion is avgas used in military aircraft. | Until 1997, lead emissions were dominated by the combustion of leaded gasoline in military ground-based vehicles. Therefore, the over-all trend for lead emissions from military vehicles and aircraft is driven mostly by the abolition of leaded gasoline in 1997. Towards this date, the amount of leaded gasoline decreased significantly. After 1997, the only source for lead from mobile fuel combustion is avgas used in military aircraft. | ||
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With both **activity data** and **emission factors** remaining unrevised, no recalculations took place with this submission. | With both **activity data** and **emission factors** remaining unrevised, no recalculations took place with this submission. | ||
- | <WRAP center round info 60%> | + | <WRAP center round info 65%> |
- | For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2019**, please see the recalculation tables following [[general: |
</ | </ | ||
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**//Why are similar EF applied for estimating exhaust heavy metal emissions from both fossil and biofuels?// | **//Why are similar EF applied for estimating exhaust heavy metal emissions from both fossil and biofuels?// | ||
- | The EF provided in [((bibcite 3))] represent summatory values for (i) the fuel's and (ii) the lubricant' | + | The EF provided in [(EMEPEEA2019)] represent summatory values for (i) the fuel's and (ii) the lubricant' |
- | [(AGEB2020> | + | [(AGEB2021> |
- | [(BAFA2020> | + | [(BAFA2021> |
- | URL: https:// | + | URL: https:// |
- | [(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, | + | [(KNOERR2021b> Knörr et al. (2021b): 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) 2021, Heidelberg, |
[(EMEPEEA2019> | [(EMEPEEA2019> | ||
[(RENTZ2008> | [(RENTZ2008> | ||
[(KNOERR2009> | [(KNOERR2009> | ||
[(IZT2007> | [(IZT2007> |