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sector:energy:fuel_combustion:other_including_military:military_transport:ground-based [2021/02/12 12:02] – kotzulla | sector:energy:fuel_combustion:other_including_military:military_transport:ground-based [2021/05/27 07:50] – [Discussion of emission trends] kotzulla | ||
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| T1, T2 | NS | CS, D | see [[sector: | | T1, T2 | NS | CS, D | see [[sector: | ||
- | ===== Method | + | ===== Methodology |
==== Activity data ==== | ==== Activity data ==== | ||
- | Basically, all fuel consumption in military vehicles is included in the primary acitivity data provided by the National Energy Balances (NEB) (AGEB, | + | Basically, all fuel consumption in military vehicles is included in the primary acitivity data provided by the National Energy Balances (NEB) (AGEB, |
As the NEB does not provide specific data for military use, the following additional sources are used: | As the NEB does not provide specific data for military use, the following additional sources are used: | ||
- | For the years as of 1995, the official mineral-oil data of the Federal Republic of Germany (Amtliche Mineralöldaten der Bundesrepublik Deutschland), | + | For the years as of 1995, the official mineral-oil data of the Federal Republic of Germany (Amtliche Mineralöldaten der Bundesrepublik Deutschland), |
As the official mineral-oil data does not distinguish into fossil and biofuels but does provide amounts for inland deliveries of total diesel and gasoline fuels, no data on the consumption of biodiesel and bioethanol is available directly at the moment. Therefore, activity data for biofuels used in military vehicles are calculated by applying Germany' | As the official mineral-oil data does not distinguish into fossil and biofuels but does provide amounts for inland deliveries of total diesel and gasoline fuels, no data on the consumption of biodiesel and bioethanol is available directly at the moment. Therefore, activity data for biofuels used in military vehicles are calculated by applying Germany' | ||
__Table 1: Annual fuel deliveries to the military for ground-vehicles and machinery, in terajoules__ | __Table 1: Annual fuel deliveries to the military for ground-vehicles and machinery, in terajoules__ | ||
- | | | **1990** | + | | | **1990** |
- | | **Diesel Oil** | + | ^ **Diesel Oil** |
- | | **Biodiesel** | + | ^ **Biodiesel** |
- | | **Gasoline** | + | ^ **Gasoline** | NO |
- | | **Biogasoline** | 0 | 0 | 0 | | + | ^ **Biogasoline** |
- | ^ Ʃ 1.A.5.b i | + | | Ʃ 1.A.5.b i |
- | [[gallery size=" | + | {{ :sector: |
- | : 1A5bi_AD.png | + | |
- | : 1A5bi_AD_bio.png | + | |
- | [[/ | + | |
- | === Emission factors === | + | ==== Emission factors |
__Table 2: Annual country-specific emission factors< | __Table 2: Annual country-specific emission factors< | ||
| | | | ||
| **DIESEL FUELS** | | **DIESEL FUELS** | ||
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | 316 | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ PM< | + | ^ PM< |
- | ^ BC< | + | ^ BC< |
- | ^ CO | + | ^ CO | 515 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | |
| **GASOLINE FUELS** | | **GASOLINE FUELS** | ||
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | 594 | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ PM< | + | ^ PM< |
- | ^ BC< | + | ^ BC< |
- | ^ CO | + | ^ CO | 4.199 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | 4.010 | |
- | ^ TSP< | + | ^ TSP< |
- | ^ Pb< | + | ^ Pb< |
< | < | ||
< | < | ||
- | < | + | < |
- | < | + | < |
<WRAP center round info 100%> | <WRAP center round info 100%> | ||
- | With respect to the emission factors applied for particulate matter, given the circumstances during test-bench measurements, | + | With respect to the emission factors applied for particulate matter, given the circumstances during test-bench measurements, |
- | </ | + | |
<WRAP center round info 100%> | <WRAP center round info 100%> | ||
- | For information on the **emission factors for heavy-metal and POP exhaust emissions**, | + | For information on the **emission factors for heavy-metal and POP exhaust emissions**, |
</ | </ | ||
- | |||
===== Discussion of emission trends ===== | ===== Discussion of emission trends ===== | ||
- | > This sub-category | + | <WRAP center round info 60%> |
+ | As only NFR 1.A.5.b is as a whole is taken into account within the key catgegory analysis, this country-specific | ||
+ | </ | ||
Due to the application of very several tier1 emission factors, most emission trends reported for this sub-category only reflect the trend in fuel deliveries. | Due to the application of very several tier1 emission factors, most emission trends reported for this sub-category only reflect the trend in fuel deliveries. | ||
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. | ||
- | [[gallery size=" | + | {{ :sector: |
- | : 1A5bi_EM_NH3.png | + | |
- | : 1A5bi_EM_NOx.png | + | |
- | [[/ | + | |
Here, for **sulphur dioxide**, this consumption-based falling trend is intensified by the impact of fuel-sulphur legislation. | Here, for **sulphur dioxide**, this consumption-based falling trend is intensified by the impact of fuel-sulphur legislation. | ||
- | [[gallery size=" | + | {{ :sector: |
- | : 1A5bi_EM_SO2.png | + | |
- | [[/ | + | |
- | Over-all **particulate matter** emissions are by far dominated by emissions from diesel oil combustion with the falling trend basically following the decline in fuel consumption. | + | Over-all **particulate matter** emissions are dominated by emissions from diesel oil combustion with the falling trend basically following the decline in fuel consumption. |
- | Here, until 1997, the emission values reported for **total suspended particles (TSP)** are slightly higher than those reported for PM,,2.5,, and PM,,10,, due to the additional TSP emissions from leaded gasoline that was banned in 1997. | + | Here, until 1997, the emission values reported for **total suspended particles (TSP)** are slightly higher than those reported for PM<sub>2.5</ |
- | [[gallery size=" | + | {{ :sector: |
- | : 1A5bi_EM_PM.png | + | |
- | [[/ | + | |
===== Recalculations ===== | ===== Recalculations ===== | ||
- | **activity data** | + | Changes in specific |
- | __Table: Revised activity data, in terajoules__ | + | The annual amounts reported for fossil gasoline and bio-gasoline remain unaltered. |
- | | | **2009** | + | |
- | | **1.A.5.b i TOTAL** | + | |
- | ^ Submission 2021 | 6,119 | 6,103 | 5,551 | 5,395 | 4,988 | 4,580 | 4,099 | 3,748 | 3,046 | | | + | |
- | ^ Submission 2020 | 6,119 | 6,103 | 5,551 | 5,395 | 4,988 | 4,580 | 4,102 | 3,752 | 3,155 | | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **DIESEL OIL** ||||||||||| | + | |
- | ^ Submission 2021 | 1,003 | 990 | 622 | 972 | 681 | 683 | 580 | 578 | 415 | | | + | |
- | ^ Submission 2020 | 1,003 | 990 | 622 | 972 | 681 | 683 | 583 | 582 | 421 | | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **BIODIESEL** | + | |
- | ^ Submission 2021 | 69 | 64 | 41 | 63 | 39 | 41 | 31 | 30 | 22 | | | + | |
- | ^ Submission 2020 | 69 | 64 | 41 | 63 | 39 | 41 | 32 | 31 | 22 | | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **GASOLINE** | + | |
- | ^ Submission 2021 | 4,907 | 4,862 | 4,696 | 4,175 | 4,092 | 3,695 | 3,342 | 3,009 | 2,502 | | | + | |
- | ^ Submission 2020 | 4,907 | 4,862 | 4,695 | 4,175 | 4,092 | 3,695 | 3,342 | 3,009 | 2,605 | | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **BIOGASOLINE** | + | |
- | ^ Submission 2021 | 140 | 188 | 192 | 185 | 175 | 161 | 145 | 131 | 107 | | | + | |
- | ^ Submission 2020 | 140 | 188 | 192 | 185 | 175 | 161 | 145 | 131 | 106 | | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
+ | __Table: Revised activity data, in terajoules__ | ||
+ | | | **1990** | ||
+ | | **Diesel oil** | ||
+ | ^ Submission 2021 | | ||
+ | ^ Submission 2020 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **Biodiesel** | ||
+ | ^ Submission 2021 | 0 | 0 | 0 | 214 | 205 | 223 | 114 | 80 | 75 | 43 | 68 | 40 | 42 | 31,7 | 30,6 | 22,0 | 16,2 | | ||
+ | ^ Submission 2020 | 0 | 0 | 0 | 74 | 55 | 82 | 59 | 69 | 64 | 41 | 63 | 39 | 41 | 31,4 | 30,3 | 22,0 | 16,1 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
+ | | **Ʃ 1.A.5.b i** ||||||||||| | ||
+ | ^ Submission 2021 | | ||
+ | ^ Submission 2020 | | ||
+ | ^ absolute change | ||
+ | ^ relative change | ||
<WRAP center round info 60%> | <WRAP center round info 60%> | ||
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===== FAQs ====== | ===== FAQs ====== | ||
- | ------ | + | [(AGEB2020> |
- | + | [(BAFA2020> | |
- | [[bibliography]] | + | URL: https:// |
- | : 1 : BAFA, 2019: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, | + | [(KNOERR2020b> |
- | URL: https:// | + | [(EMEPEEA2019> |
- | : 2 : AGEB, 2019b: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Daten - Sondertabellen - Heizwerte der Energieträger und Faktoren für die Umrechnung von spezifischen Mengeneinheiten in Wärmeinheiten (2005-2017); | + | [(RENTZ2008> |
- | : 3 : Knörr et al. (2019b): Knörr, W., Heidt, C., Gores, S., & Bergk, F. (2018b): ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Aktualisierung des Modells TREMOD-Mobile Machinery (TREMOD MM) 2019, Heidelberg, | + | [(KNOERR2009> |
- | : 4 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019; Copenhagen, 2019. | + | [(IZT2007> |
- | : 5 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, | + | |
- | [[/bibliography]] | + |