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sector:energy:fuel_combustion:transport:civil_aviation:domestic_civil_aviation_-_lto [2021/04/07 20:31] – kotzulla | sector:energy:fuel_combustion:transport:civil_aviation:domestic_civil_aviation_-_lto [2021/12/15 20:00] (current) – external edit 127.0.0.1 | ||
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==== Actitvity Data ==== | ==== Actitvity Data ==== | ||
- | Specific jet kerosene consumption during LTO-stage is calculated within TREMOD AV as described in the [[sector: | + | Specific jet kerosene consumption during LTO-stage is calculated within TREMOD AV as described in the superordinate chapter. |
__Table 1: Percentual annual fuel consumption during LTO-stage of domestic flights__ | __Table 1: Percentual annual fuel consumption during LTO-stage of domestic flights__ | ||
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Furthermore, | Furthermore, | ||
- | For more details, please see [[sector: | + | For more details, please see the superordinate chapter on civil aviation. |
__Table 3: Country-specific emission factors, in kg/TJ__ | __Table 3: Country-specific emission factors, in kg/TJ__ | ||
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^ CO | ^ CO | ||
| **AVIATION GASOLINE** | | **AVIATION GASOLINE** | ||
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | | | | | | | | | | | | | | | + | ^ NMVOC | |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ TSP< | + | ^ TSP< |
- | ^ CO | + | ^ CO |
- | < | + | < |
- | < | + | < |
< | < | ||
Line 72: | Line 72: | ||
</ | </ | ||
- | + | <WRAP center round info 100%> | |
- | __Table 4: Tier1 emission factors for heavy-metal and POP exhaust | + | For information on the **emission factors for heavy-metal and POP exhaust |
- | | | + | </WRAP> |
- | | | + | |
- | ^ Kerosene | + | |
- | ^ Aviation gasoline | + | |
- | < | + | |
===== Trend discussion for Key Sources ===== | ===== Trend discussion for Key Sources ===== | ||
- | > NFR 1.A.3.a ii (i) - Domestic Civil Aviation - LTO is **no key source**. | + | <WRAP center round info 60%> |
+ | NFR sub-category | ||
+ | </ | ||
Where **sulphur oxides** emissions are dominated by jet kerosene due to the amount of fuel used, the majority of **carbon monoxide** stems from the consumption of avgas given the much higher emission factor applied to this fuel. | Where **sulphur oxides** emissions are dominated by jet kerosene due to the amount of fuel used, the majority of **carbon monoxide** stems from the consumption of avgas given the much higher emission factor applied to this fuel. | ||
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__Table 6: Revised country-specific emission factors for jet kerosene, in [kg/TJ]__ | __Table 6: Revised country-specific emission factors for jet kerosene, in [kg/TJ]__ | ||
- | | | + | | | **1990** |
+ | | **AMMONIA** | ||
+ | ^ Submission 2021 | 3,98 | 3,95 | 3,95 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | 3,97 | | ||
+ | ^ Submission 2020 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | 4,00 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
| **NON-METHANE VOLATILE ORGANIC COMPUNDS - NMVOC** | | **NON-METHANE VOLATILE ORGANIC COMPUNDS - NMVOC** | ||
- | ^ Submission 2021 | + | ^ Submission 2021 | 28,4 | 28,9 | 30,5 | 32,4 | 33,9 | 34,4 | 34,7 | 33,2 | 32,3 | 31,9 | 32,0 | 34,9 | 37,0 | 36,9 | 36,5 | 38,3 | |
- | ^ Submission 2020 | + | ^ Submission 2020 | 29,1 | 30,2 | 30,5 | 32,4 | 33,9 | 34,7 | 35,1 | 33,9 | 33,4 | 33,2 | 33,5 | 36,8 | 37,7 | 38,8 | 39,0 | 40,9 | |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **NITROGEN OXIDES** | + | | **NITROGEN OXIDES** |
- | ^ Submission 2021 | + | ^ Submission 2021 | |
- | ^ Submission 2020 | + | ^ Submission 2020 | |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **SULPHUR OXIDES** |||||||||||||||||| | + | | **BLACK CARBON - BC** | | | | | | | | | | | | | | | | | | |
- | ^ Submission 2021 | | | | | | | | | | | | | | | | | | | + | ^ Submission |
- | ^ Submission | + | ^ Submission 2020 |
- | ^ absolute change | + | ^ absolute |
- | ^ relative | + | ^ relative change |
- | | **BLACK CARBON - BC** | + | | **PARTICULATE MATTER - PM** |
- | ^ Submission 2021 | | | | | | | | | | | | | | | | | | + | ^ Submission 2021 |
- | ^ Submission 2020 | | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative |
- | | **PARTICULATE MATTER - PM** | + | | **CARBON MONOXIDE - CO** | | | | | | | | | | | | | | | | | | |
- | ^ Submission | + | ^ Submission 2021 | |
- | ^ Submission 2020 | | | | | | | | | | | | | | | | | | + | ^ Submission 2020 | |
- | ^ absolute | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **CARBON MONOXIDE - CO** | + | |
- | ^ Submission 2021 | + | |
- | ^ Submission 2020 | + | <WRAP center round info 60%> |
- | ^ absolute change | + | For more information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following chapter [[general: |
- | ^ relative change | + | </ |
+ | |||
+ | ===== Uncertainties ===== | ||
+ | |||
+ | For uncertainties information, | ||
+ | |||
+ | ===== Planned improvements ===== | ||
+ | |||
+ | For information on planned improvements, | ||
- | The TSP emissions calculated depend directly on the reported lead emissions: The emission factor for TSP is 1.6 times the emission factor used for lead: EF(TSP) = 1.6 x EF(Pb). | ||
- | The applied procedure is similar to the one used for calculating TSP emissions from leaded gasoline used in road transport. | ||
[(KNOERR2012> | [(KNOERR2012> | ||
[(KNOERR2020c> | [(KNOERR2020c> | ||
[(GORES2020> | [(GORES2020> | ||
- | [(EMEPEEA2012> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, https:// | + | [(EMEPEEA2019> EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, https:// |
- | [(EUROCONTROL2020> | + | [(EUROCONTROL2020> |