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sector:energy:fuel_combustion:industry:mobile_combustion_in_manufacturing_industries_construction [2021/02/12 10:24] – [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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Under NFR //1.A.2.g vii - Mobile Combustion in Manufacturing Industries and Construction//, | Under NFR //1.A.2.g vii - Mobile Combustion in Manufacturing Industries and Construction//, | ||
- | ^ | + | ^ Category Code ^ Method |
- | | T1, T2 | NS, M | CS, D, M | | + | | 1.A.2.g vii |
+ | ^ Key Category | ||
+ | | 1.A.2.g vii | ||
===== Methodology ===== | ===== Methodology ===== | ||
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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__ | ||
- | | | + | | |
- | ^ Diesel Fuels | 43,0% | 46,4% | 47,0% | | + | ^ Diesel Fuels | 43,0% | 46,4% | 47,0% | 43,7% | 43,1% | 43,4% | 43,7% | 43,2% | 43,5% | 43,1% | 43,0% | 42,9% | 42,6% | 42,4% | |
- | ^ Gasoline Fuels | 31,5% | 59,7% | 55,1% | | + | ^ Gasoline Fuels | 31,5% | 59,7% | 55,1% | 58,6% | 64,5% | 64,4% | 66,9% | 67,1% | 66,9% | 66,7% | 68,4% | 68,1% | 64,2% | 63,2% | |
- | + | ||
__Table 3: Annual fuel consumption in construction vehicles and mobile machinery, in terajoules__ | __Table 3: Annual fuel consumption in construction vehicles and mobile machinery, in terajoules__ | ||
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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*, in kg/TJ__ | + | __Table 4: Annual country-specific emission factors< |
- | | | **1990** | + | | |
- | | **Gasoline fuels** | + | | **Gasoline fuels** |
- | ^ NH< | + | ^ NH< |
- | ^ NMVOC<sub>exhaust</sub> | 77.8 | 74.8 | 82.3 | 101 | 106 | 106 | 106 | 106 | 106 | 106 | 106 | 106 | 106 | | + | ^ NMVOC<sup>2</sup> |
- | ^ NMVOC<sub>evapor.</sub> | 678 | 623 | 571 | 563 | 561 | 561 | 561 | 561 | 561 | 561 | 561 | 561 | 561 | | + | ^ NMVOC<sup>3</sup> |
- | ^ NO< | + | ^ NO< |
- | ^ SO< | + | ^ SO< |
- | ^ BC | 0.302 | 0.271 | 0.241 | 0.236 | 0.236 | 0.236 | 0.236 | 0.236 | 0.235 | 0.235 | 0.235 | 0.235 | 0.235 | | | + | ^ BC< |
- | ^ PM | + | ^ PM< |
- | ^ TSP | 2.35 | 0.82 | | + | ^ 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 | |
- | + | <sup>1</ | |
- | - 1 due to lack of better information: | + | <sup>2</ |
- | | + | <sup>3</ |
- | | + | <sup>4</ |
- | | + | <sup>5</ |
- | | + | <sup>6</ |
- | | + | |
<WRAP center round info 100%> | <WRAP center round info 100%> | ||
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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**, | ||
===== Discussion of emission trends ===== | ===== Discussion of emission trends ===== | ||
- | + | __Table: Outcome of Key Category Analysis__ | |
- | > **NFR 1.A.2.g vii** is key source | + | | for: ^ CO |
+ | | by: | Level | L | ||
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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Revisions in **activity data** result from slightly adapted EBZ67 shares as well as the implementation of primary activity data from the now finalised NEB 2019. | Revisions in **activity data** result from slightly adapted EBZ67 shares as well as the implementation of primary activity data from the now finalised NEB 2019. | ||
- | __Table | + | __Table |
| | | | ||
- | | **diesel fuels** | + | | **diesel fuels** |
^ Submission 2021 | ^ Submission 2021 | ||
^ Submission 2020 | ^ Submission 2020 | ||
^ absolute change | ^ absolute change | ||
^ relative change | ^ relative change | ||
- | | **gasoline fuels** | + | | **gasoline fuels** |
^ Submission 2021 | ^ Submission 2021 | ||
^ Submission 2020 | ^ Submission 2020 | ||
^ absolute change | ^ absolute change | ||
^ relative change | ^ relative change | ||
- | |||
__Table 6: Revised activity data, in terajoules__ | __Table 6: Revised activity data, in terajoules__ | ||
| | **1990** | | | **1990** | ||
- | | **diesel fuels** | + | | **diesel fuels** |
^ Submission 2021 | | ^ Submission 2021 | | ||
^ Submission 2020 | | ^ Submission 2020 | | ||
^ absolute change | ^ absolute change | ||
^ relative change | ^ relative change | ||
- | | **gasoline fuels** | + | | **gasoline fuels** |
^ Submission 2021 | 1.420 | 4.453 | 4.079 | 4.302 | 2.907 | 2.641 | 826 | 815 | 870 | 3.471 | 3.554 | 3.536 | 3.263 | | ^ Submission 2021 | 1.420 | 4.453 | 4.079 | 4.302 | 2.907 | 2.641 | 826 | 815 | 870 | 3.471 | 3.554 | 3.536 | 3.263 | | ||
^ Submission 2020 | 1.420 | 4.453 | 4.079 | 4.288 | 2.886 | 2.619 | 819 | 808 | 861 | 3.431 | 3.512 | 3.491 | 3.419 | | ^ Submission 2020 | 1.420 | 4.453 | 4.079 | 4.288 | 2.886 | 2.619 | 819 | 808 | 861 | 3.431 | 3.512 | 3.491 | 3.419 | | ||
^ absolute change | ^ absolute change | ||
^ relative change | ^ relative change | ||
- | | **over-all fuel consumption** | + | | **over-all fuel consumption** |
^ Submission 2021 | | ^ Submission 2021 | | ||
^ Submission 2020 | | ^ Submission 2020 | | ||
^ absolute change | ^ absolute change | ||
^ relative change | ^ relative change | ||
- | |||
- | |||
- | |||
- | source: own estimates based on [((bibcite 1))] and [((bibcite 3))] | ||
As in contrast, all **emission factors** remain unrevised compared to last year's susbmission, | As in contrast, all **emission factors** remain unrevised compared to last year's susbmission, | ||
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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> |