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sector:energy:fuel_combustion:industry:mobile_combustion_in_manufacturing_industries_construction [2021/04/10 09:38] – [Table] kotzulla | sector:energy:fuel_combustion:industry:mobile_combustion_in_manufacturing_industries_construction [2021/12/15 20:00] (current) – external edit 127.0.0.1 | ||
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==== Activity data ==== | ==== Activity data ==== | ||
- | Sector-specific consumption data is included in the primary fuel-delivery data are available from NEB line 67: ' | + | Sector-specific consumption data is included in the primary fuel-delivery data are available from NEB line 67: ' |
__Table 1: Sources for primary fuel-delivery data__ | __Table 1: Sources for primary fuel-delivery data__ | ||
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| as of 1995 | **AGEB** - National Energy Balance, line 67: ' | | as of 1995 | **AGEB** - National Energy Balance, line 67: ' | ||
- | Following the deduction of energy inputs for military vehicles as provided in (BAFA, | + | Following the deduction of energy inputs for military vehicles as provided in (BAFA, |
- | URL: http:// | + | |
__Table 2: Percental annual contribution of 1.A.2.g vii to fuel-specific over-all delivery data provided in NEB line 67__ | __Table 2: Percental annual contribution of 1.A.2.g vii to fuel-specific over-all delivery data provided in NEB line 67__ | ||
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{{ : | {{ : | ||
{{ : | {{ : | ||
- | |||
==== Emission factors ==== | ==== Emission factors ==== | ||
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**, |
__Table 4: Annual country-specific emission factors< | __Table 4: Annual country-specific emission factors< | ||
- | | | **1990** | + | | |
- | | **Gasoline fuels** | + | | **Gasoline fuels** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC< | + | ^ NMVOC< |
- | ^ NMVOC< | + | ^ NMVOC< |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ TSP< | + | ^ TSP< |
- | ^ CO | + | ^ CO | 38.459 | 35.290 | 32.423 | 32.108 | 34.681 | 35.250 | 35.791 | 36.289 | 36.661 | 36.840 | 36.918 | 36.973 | 37.010 | |
- | ^ Pb | + | ^ Pb | 1.471 | 0.516 | | | | | | | | | | | | | |
- | | **Diesel fuels** | + | | **Diesel fuels** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC | 185 | | + | ^ NMVOC |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC< | + | ^ BC< |
- | ^ PM< | + | ^ PM< |
- | ^ CO | + | ^ CO | |
< | < | ||
< | < | ||
< | < | ||
< | < | ||
- | < | + | < |
< | < | ||
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</ | </ | ||
+ | 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)]. | ||
- | For lead (Pb) from leaded gasoline | + | <WRAP center round info 100%> |
+ | For information on the **emission factors for heavy-metal | ||
+ | </ | ||
- | For information on the **emission factors for heavy-metal and POP exhaust emissions**, | ||
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__Table: Outcome of Key Category Analysis__ | __Table: Outcome of Key Category Analysis__ | ||
- | | for: ^ CO | + | | for: ^ CO |
- | | by: | | + | | by: | |
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. | ||
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{{ : | {{ : | ||
- | Here, as NMVOC emissions are dominated by gasoline fuels, the trend shows the same strong decline after 2011 as the underlying activity data (see above and [[ NFR 1.A.4 - mobile | + | Here, as NMVOC emissions are dominated by gasoline fuels, the trend shows the same strong decline after 2011 as the underlying activity data (see above and NFR 1.A.4 - mobile, Table 1.) |
The remarkable increase after 2014 relates to the strongly increased gasoline inland deliveries reported in NEB line 67. (see table 3 above). This noticeable increase will be checked by the compiler of the National Energy Balance. | The remarkable increase after 2014 relates to the strongly increased gasoline inland deliveries reported in NEB line 67. (see table 3 above). This noticeable increase will be checked by the compiler of the National Energy Balance. | ||
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- | Uncertainty estimates for **activity data** of mobile sources derive from research project FKZ 360 16 023: " | + | Uncertainty estimates for **activity data** of mobile sources derive from research project FKZ 360 16 023: " |
Uncertainty estimates for **emission factors** were compiled during the PAREST research project. Here, the final report has not yet been published. | Uncertainty estimates for **emission factors** were compiled during the PAREST research project. Here, the final report has not yet been published. | ||
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===== FAQs ===== | ===== FAQs ===== | ||
- | |||
**//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 4))] and [((bibcite 5))] 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' |
- | + | ||
- | ------ | + | |
- | + | ||
- | [[bibliography]] | + | |
- | : 1 : AGEB, 2019: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; | + | |
- | : 2 : BAFA, 2019: Federal Office of Economics and Export Control (Bundesamt für Wirtschaft und Ausfuhrkontrolle, | + | |
- | URL: http:// | + | |
- | : 3 : Knörr et al. (2019b): Knörr, W., Heidt, C., Gores, S., & Bergk, F. (2019b): 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, 2019. | + | |
- | : 4 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019; Copenhagen, 2019. | + | |
- | : 5 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, | + | |
- | : 6 : Knörr et al. (2009): Knörr, W., Heldstab, J., & Kasser, F.: Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland; | + | |
- | [[/ | + | |
+ | [(AGEB2020> | ||
+ | [(BAFA2020> | ||
+ | URL: https:// | ||
+ | [(KNOERR2020b> | ||
+ | [(EMEPEEA2019> | ||
+ | [(RENTZ2008> | ||
+ | [(KNOERR2009> |