meta data for this page
Differences
This shows you the differences between two versions of the page.
Both sides previous revisionPrevious revisionNext revision | Previous revision | ||
sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:commercial_and_institutional [2021/04/12 13:19] – kotzulla | sector:energy:fuel_combustion:small_combustion:mobile_small_combustion:commercial_and_institutional [2023/04/11 12:25] (current) – [Regulated pollutants] kotzulla | ||
---|---|---|---|
Line 12: | Line 12: | ||
==== Activity data ==== | ==== Activity data ==== | ||
- | Sector-specific **diesel** consumption data are included in the primary fuel-delivery data available from NEB line 67: ' | + | Sector-specific **diesel** consumption data are included in the primary fuel-delivery data available from NEB line 67: ' |
__Table 1: Sources for primary fuel-deliveries data__ | __Table 1: Sources for primary fuel-deliveries data__ | ||
Line 18: | Line 18: | ||
|| as of 1995 || NEB line 67: ' | || as of 1995 || NEB line 67: ' | ||
- | Following the deduction of diesel oil inputs for military vehicles as provided in (BAFA, | + | Following the deduction of diesel oil inputs for military vehicles as provided in (BAFA, |
__Table 2: Annual contribution of NFR 1.A.4.a ii to the over-all amounts of diesel oil provided in NEB line 67__ | __Table 2: Annual contribution of NFR 1.A.4.a ii to the over-all amounts of diesel oil provided in NEB line 67__ | ||
- | | **1990** | **1995** | **2000** | **2005** | **2010** | **2011** | **2012** | **2013** | **2014** | **2015** | **2016** | **2017** | **2018** | **2019** | | + | ^ |
- | | 7,01% | 6,65% | 6,99% | 7,18% | 6,52% | 6,36% | 6,21% | 5,96% | 5,82% | 5,73% | 5,83% | 5,78% | 5,68% | | + | | 7.01% | 6.65% | 6.98% | 7.17% | 6.51% | 6.35% | 6.20% | 5.95% | 5.81% | 5.73% | 5.83% | 5.77% | 5.67% | 5.59% | 5.45% | 5.59% | |
- | source: | + | source: |
As the NEB does not distinguish into specific biofuels, consumption data for biodiesel are calculated by applying Germany' | As the NEB does not distinguish into specific biofuels, consumption data for biodiesel are calculated by applying Germany' | ||
Line 30: | Line 30: | ||
__Table 3: Annual fuel consumption, | __Table 3: Annual fuel consumption, | ||
- | | | **1990** | **1995** | **2000** | **2005** | **2010** | **2011** | **2012** | **2013** | **2014** | **2015** | **2016** | **2017** | **2018** | **2019** | | + | | ^ |
- | ^ Diesel Oil | 7.847 | 6.508 | 6.646 | 5.894 | 5.773 | 5.770 | 5.533 | 5.524 | 5.629 | 5.810 | 6.145 | 6.257 | 5.749 | 5.726 | | + | ^ Diesel Oil | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | ^ LPG | + | ^ LPG |
- | | **Ʃ 1.A.4.a ii** ^ | + | | **Ʃ 1.A.4.a ii** ^ 10,627 ^ 9,951 ^ 10,899 ^ 10,796 ^ 10,836 ^ 10,722 ^ 10,400 ^ 10,254 ^ 10,300 ^ 10,376 ^ 10,799 ^ 10,884 ^ 10,339 ^ |
{{ : | {{ : | ||
Line 41: | Line 41: | ||
The emission factors used here are of rather different quality: | The emission factors used here are of rather different quality: | ||
- | Basically, for all **main pollutants**, | + | Basically, for all **main pollutants**, |
As no such specific EF are available for biofuels, the values used for diesel oil are applied to biodiesel, too. | As no such specific EF are available for biofuels, the values used for diesel oil are applied to biodiesel, too. | ||
__Table 4: Annual country-specific emission factors from TREMOD MM, in kg/TJ__ | __Table 4: Annual country-specific emission factors from TREMOD MM, in kg/TJ__ | ||
- | | | **1990** | **1995** | **2000** | **2005** | **2010** | **2011** | **2012** | **2013** | **2014** | **2015** | **2016** | **2017** | **2018** | **2019** | | + | | ^ |
- | | **Diesel fuels**< | + | | **Diesel fuels**< |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ CO | 856 | | + | ^ CO | 856 | |
- | | **LPG** | + | | **LPG** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ CO | 114 | 114 | 112 | 112 | 112 | 112 | 112 | 112 | 112 | 112 | 112 | 112 | 112 | | + | ^ CO | 114 | 114 | 112 | 112 | |
< | < | ||
< | < | ||
Line 71: | Line 71: | ||
</ | </ | ||
- | For lead (Pb) from leaded gasoline and corresponding TSP emissions, additional emissions are are calculated from 1990 to 1997 based upon contry-specific emission factors from [(KNOERR2020b)]. | + | <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 ===== | ||
Line 81: | Line 81: | ||
==== Unregulated pollutants ==== | ==== Unregulated pollutants ==== | ||
- | {{ : | ||
For all unregulated pollutants, emission trends directly follow the trend in fuel consumption. | For all unregulated pollutants, emission trends directly follow the trend in fuel consumption. | ||
Line 87: | Line 86: | ||
==== Regulated pollutants ==== | ==== Regulated pollutants ==== | ||
- | ===Nitrogen oxides and Sulphur dioxide== | + | ===Nitrogen oxides and Sulphur dioxide=== |
For all regulated pollutants, emission trends follow not only the trend in fuel consumption but also reflect the impact of fuel-quality and exhaust-emission legislation. | For all regulated pollutants, emission trends follow not only the trend in fuel consumption but also reflect the impact of fuel-quality and exhaust-emission legislation. | ||
+ | Here, emissions of sulphur oxides follow the step-by-step reduction of sulphur contents in liquid fuels, resulting in a reduction of over 99% since 1990. | ||
{{ : | {{ : | ||
+ | ===Ammonia=== | ||
+ | |||
+ | Ammonia emissions are driven by the consumption of LPG with its comparably high emission factor. | ||
+ | |||
+ | {{ : | ||
+ | |||
+ | ===NMVOC=== | ||
+ | |||
+ | Emissions oif NMVOC are again driven by the consumption of LPG with its comparably high emission factor. Here, the ongoing downward trend results from the decrease in the emission factor applied for diesel fuels. | ||
+ | {{ : | ||
====Particulate matter & Black carbon==== | ====Particulate matter & Black carbon==== | ||
Line 100: | Line 110: | ||
Additional contributors such as the impact of TSP emissions from the use of leaded gasoline (until 1997) have no significant effect onto over-all emission estimates. | Additional contributors such as the impact of TSP emissions from the use of leaded gasoline (until 1997) have no significant effect onto over-all emission estimates. | ||
- | Here, as the EF(BC) are estimated via fractions provided in [(EMEPEEA2019)], | + | Here, as the EF(BC) are estimated via fractions provided in the 2019 EMEP Guidebook |
{{ : | {{ : | ||
Line 106: | Line 116: | ||
===== Recalculations ===== | ===== Recalculations ===== | ||
- | **Activity data** | + | **Activity data** |
- | + | ||
- | __Table 5: Revised annual contribution of 1.A.4.a ii to over-all diesel oil deliveries provided in NEB line 67__ | + | |
- | | | + | |
- | ^ Submission 2021 | + | |
- | ^ Submission 2020 | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | __Table | + | __Table |
- | | | **1990** | **1995** | **2000** | **2005** | + | | | **DIESEL OIL** | **BIODIESEL** | **LPG** | **OVER-ALL FUEL CONSUMPTION** | |
- | | **Diesel Oil** |||||||||||||| | + | ^ current submission |
- | ^ Submission 2021 | + | ^ previous submission |
- | ^ Submission 2020 | 7.774 | 6.413 | 6.316 | 5.851 | 6.213 | 6.314 | 6.158 | 6.348 | 6.562 | 6.885 | 7.153 | 7.343 | 6.816 | | + | ^ absolute change |
- | ^ absolute change | + | ^ relative change |
- | ^ relative change | + | |
- | | **Biodiesel** | + | |
- | ^ Submission 2021 | 0.00 | 0.00 | 0.00 | 377 | 443 | 403 | 390 | 328 | 346 | 318 | | + | |
- | ^ Submission 2020 | 0.00 | 0.00 | 0.00 | 128 | 403 | 414 | 402 | 368 | 398 | 372 | 376 | 389 | 372 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **LPG** | + | |
- | ^ Submission 2021 | 2.787 | 3.450 | 4.261 | 4.533 | 4.629 | 4.557 | 4.484 | 4.409 | 4.333 | 4.256 | 4.336 | 4.301 | 4.264 | | + | |
- | ^ Submission 2020 | 2.787 | 3.450 | 4.261 | 4.894 | 5.431 | 5.441 | 5.449 | 5.456 | 5.462 | 5.467 | 5.471 | 5.474 | 5.477 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | | **over-all fuel consumption** | + | |
- | ^ Submission 2021 | | + | |
- | ^ Submission 2020 | | + | |
- | ^ absolute change | + | |
- | ^ relative change | + | |
- | <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 2020**, please see the recalculation tables following [[general: |
</ | </ | ||
Line 158: | Line 145: | ||
The EF provided in [(EMEPEEA2019)] 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> | + | [(AGEB2022> |
- | [(BAFA2020> | + | [(BAFA2022> |
- | URL: https:// | + | 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, | + | [(KNOERR2022b>Knörr et al. (2022b): 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) 2022, Heidelberg, |
[(EMEPEEA2019> | [(EMEPEEA2019> | ||
- | [(RENTZ2008> | ||
[(KNOERR2009> | [(KNOERR2009> |