meta data for this page
Differences
This shows you the differences between two versions of the page.
Next revision | Previous revision | ||
sector:energy:fuel_combustion:other_including_military:military_transport:ground-based [2021/01/15 17:04] – created kotzulla | sector:energy:fuel_combustion:other_including_military:military_transport:ground-based [2021/12/15 20:00] (current) – external edit 127.0.0.1 | ||
---|---|---|---|
Line 1: | Line 1: | ||
===== 1.A.5.b i - Military Ground Vehicles and Vehicles ====== | ===== 1.A.5.b i - Military Ground Vehicles and Vehicles ====== | ||
+ | |||
+ | ===== Short description ===== | ||
+ | |||
+ | In sub-category //1.A.5.b i - Other, Mobile (including Military)// emissions from military ground-vehicles and mobile machinery are reported. | ||
+ | |||
+ | ^ Method | ||
+ | | T1, T2 | NS | CS, D | see [[sector: | ||
+ | |||
+ | ===== Methodology ===== | ||
+ | |||
+ | ==== Activity data ==== | ||
+ | |||
+ | Basically, all fuel consumption in military vehicles is included in the primary acitivity data provided by the National Energy Balances (NEB) (AGEB, 2020) [(AGEB2020)]. | ||
+ | |||
+ | 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), | ||
+ | |||
+ | 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__ | ||
+ | | | **1990** | ||
+ | ^ **Diesel Oil** | ||
+ | ^ **Biodiesel** | ||
+ | ^ **Gasoline** | ||
+ | ^ **Biogasoline** | ||
+ | | Ʃ 1.A.5.b i | ||
+ | |||
+ | {{ : | ||
+ | |||
+ | ==== Emission factors ==== | ||
+ | |||
+ | __Table 2: Annual country-specific emission factors< | ||
+ | | | ||
+ | | **DIESEL FUELS** | ||
+ | ^ NH< | ||
+ | ^ NMVOC | ||
+ | ^ NO< | ||
+ | ^ SO< | ||
+ | ^ PM< | ||
+ | ^ BC< | ||
+ | ^ CO | 515 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | 350 | | ||
+ | | **GASOLINE FUELS** | ||
+ | ^ NH< | ||
+ | ^ NMVOC | ||
+ | ^ NO< | ||
+ | ^ SO< | ||
+ | ^ PM< | ||
+ | ^ BC< | ||
+ | ^ 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 | 4.010 | | ||
+ | ^ TSP< | ||
+ | ^ Pb< | ||
+ | < | ||
+ | < | ||
+ | < | ||
+ | < | ||
+ | |||
+ | <WRAP center round info 100%> | ||
+ | With respect to the emission factors applied for particulate matter, given the circumstances during test-bench measurements, | ||
+ | </ | ||
+ | |||
+ | <WRAP center round info 100%> | ||
+ | For information on the **emission factors for heavy-metal and POP exhaust emissions**, | ||
+ | </ | ||
+ | |||
+ | ===== Discussion of emission trends ===== | ||
+ | |||
+ | <WRAP center round info 60%> | ||
+ | As only NFR 1.A.5.b as a whole is taken into account within the key category analysis, this country-specific sub-sector is not considered separately. | ||
+ | </ | ||
+ | |||
+ | 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. | ||
+ | |||
+ | {{ : | ||
+ | |||
+ | Here, for **sulphur dioxide**, this consumption-based falling trend is intensified by the impact of fuel-sulphur legislation. | ||
+ | |||
+ | {{ : | ||
+ | |||
+ | 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< | ||
+ | |||
+ | {{ : | ||
+ | |||
+ | ===== Recalculations ===== | ||
+ | |||
+ | Changes in specific **activity data** result from a correction of the shares of biodiesel and the NCV applied for fossil diesel oil. | ||
+ | |||
+ | The annual amounts reported for fossil gasoline and bio-gasoline remain unaltered. | ||
+ | |||
+ | __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%> | ||
+ | For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following chapter [[general: | ||
+ | </ | ||
+ | |||
+ | ===== Planned improvements ===== | ||
+ | |||
+ | Given the limited quality of the emission factors applied, the inventory compiler will check a possible revision at least for the main pollutants. | ||
+ | |||
+ | ===== FAQs ====== | ||
+ | |||
+ | [(AGEB2020> | ||
+ | [(BAFA2020> | ||
+ | URL: https:// | ||
+ | [(KNOERR2020b> | ||
+ | [(EMEPEEA2019> | ||
+ | [(RENTZ2008> | ||
+ | [(KNOERR2009> | ||
+ | [(IZT2007> |