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:transport:road_transport:emissions_from_fuel_combustion_in_road_vehicles:heavy_duty_vehicles [2021/04/08 15:17] – [Table] kotzulla | sector:energy:fuel_combustion:transport:road_transport:emissions_from_fuel_combustion_in_road_vehicles:heavy_duty_vehicles [2022/03/22 12:04] (current) – [Discussion of emission trends] kotzulla | ||
---|---|---|---|
Line 5: | Line 5: | ||
- | ^ Category Code ^ Method | + | ^ Category Code ^ Method |
- | | 1.A.3.b iii | T1, T3 ||||| NS, M ||||| CS, M, D ||||| | + | | 1.A.3.b iii | T1, T3 |
- | ^ | + | ^ |
- | | 1.A.3.b iii | + | | Key Category: |
{{page> | {{page> | ||
Line 16: | Line 16: | ||
==== Activity data ==== | ==== Activity data ==== | ||
- | Specific consumption data for heavy-duty vehicles (trucks and lorries) and buses are generated within TREMOD [((bibcite 1))]. - The following tables provide an overview of annual amounts of fuels consumed by these vehicles in Germany. | + | Specific consumption data for heavy-duty vehicles (trucks and lorries) and buses are generated within TREMOD [(KNOERR2021a)]. - The following tables provide an overview of annual amounts of fuels consumed by these vehicles in Germany. |
{{ : | {{ : | ||
Line 22: | Line 22: | ||
__Table 1: Annual fuel consumption of trucks and lorries, in terajoules__ | __Table 1: Annual fuel consumption of trucks and lorries, in terajoules__ | ||
- | | | **1990** | **1995** | **2000** | **2005** | **2006** | **2007** | **2008** | **2009** | **2010** | **2011** | **2012** | **2013** | **2014** | **2015** | **2016** | **2017** | **2018** | **2019** | | + | | ^ |
- | | **HDVs: Buses** | + | | **HDVs: Buses** |
- | ^ Diesel oil | | + | ^ Diesel oil | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | ^ CNG | + | ^ CNG |
- | ^ Biogas | + | ^ Biogas |
- | ^ Petroleum | + | ^ Petroleum |
- | | **Ʃ Buses** | + | | **Ʃ Buses** |
- | | **HDVs: Trucks & Lorries** | + | | **HDVs: Trucks & Lorries** |
- | ^ Diesel oil | 401.691 | 541.176 | | + | ^ Diesel oil | 401,801 | 541,198 | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | ^ CNG | + | ^ CNG |
- | ^ Biogas | + | ^ Biogas |
- | | **Ʃ Trucks & Lorries** | + | | **Ʃ Trucks & Lorries** |
- | | **HDVs over all** ||||||||||||||| | + | | **HDVs over all** |
- | ^ Diesel oil | 459.124 | 590.259 | 680.299 | 526.071 | 547.742 | 529.429 | 535.158 | 525.220 | 571.008 | 571.389 | 598.264 | 615.361 | 585.893 | | + | ^ Diesel oil | 459,124 | 590,259 | 680,299 | 526,071 | 547,742 | 529,429 | 535,158 | 525,222 | 571,016 | 571,405 | 598,290 | 615,392 | 585,865 | 608,497 | 615,976 | 619,134 | |
- | ^ Biodiesel | + | ^ Biodiesel |
- | ^ CNG | + | ^ CNG |
- | ^ Biogas | + | ^ Biogas |
- | ^ Petroleum | + | ^ Petroleum |
- | | **Ʃ 1.A.3.b iii** | + | | **Ʃ 1.A.3.b iii** |
- | source: TREMOD | + | source: TREMOD [(KNOERR2021a)] |
- | + | ||
- | + | ||
- | [[gallery size=" | + | |
- | : 1A3biii_AD.png | + | |
- | [[/ | + | |
- | + | ||
- | + | ||
- | [!-- | + | |
- | [[f< | + | |
- | + | ||
- | [[gallery size=" | + | |
- | : 1A3biii_AD_SNF.png | + | |
- | [[/ | + | |
- | + | ||
- | [[f< | + | |
- | + | ||
- | [[gallery size=" | + | |
- | : 1A3biii_AD_Bus.png | + | |
- | : 1A3biii_AD_CNG.png | + | |
- | [[/ | + | |
- | + | ||
- | --] | + | |
<WRAP center round info 60%> | <WRAP center round info 60%> | ||
Line 73: | Line 51: | ||
==== Emission factors ==== | ==== Emission factors ==== | ||
- | The majority of emission factors for exhaust emissions from road transport are taken from the ' | + | The majority of emission factors for exhaust emissions from road transport are taken from the ' |
However, it is not possible to present these tier3 values in a comprehendible way here. | However, it is not possible to present these tier3 values in a comprehendible way here. | ||
Line 81: | Line 59: | ||
</ | </ | ||
- | For heavy-metal (other then lead from leaded gasoline) and PAH exhaust-emissions, | + | For heavy-metal (other then lead from leaded gasoline) and PAH exhaust-emissions, |
- | Regarding PCDD/F, tier1 EF from (Rentz et al., 2008) [((bibcite 4))] are used instead. | + | Regarding PCDD/F, tier1 EF from (Rentz et al., 2008) [(RENTZ2008)] are used instead. |
__Table 2: tier1 EF derived from default values__ | __Table 2: tier1 EF derived from default values__ | ||
Line 96: | Line 74: | ||
===== Discussion of emission trends ===== | ===== Discussion of emission trends ===== | ||
- | ^ Key Category | + | __Table 3: Outcome of Key Category |
- | | ::: | + | | for: ^ NO< |
+ | | by: | L/T | ||
==== Nitrogen oxides==== | ==== Nitrogen oxides==== | ||
Line 103: | Line 82: | ||
Until 2005, NO< | Until 2005, NO< | ||
- | {{ : | + | {{ : |
====Non-methane volatile organic compounds (NMVOC) and carbon monoxide ==== | ====Non-methane volatile organic compounds (NMVOC) and carbon monoxide ==== | ||
Line 109: | Line 88: | ||
Since 1990, exhaust emissions of **NMVOC** | Since 1990, exhaust emissions of **NMVOC** | ||
- | {{ : | + | {{: |
- | {{ : | + | {{: |
==== Ammonia and sulphur dioxide ==== | ==== Ammonia and sulphur dioxide ==== | ||
- | As for the entire road transport sector, the trends for **sulphur dioxide** (SO,,2,,) and **ammonia** (NH,,3,,) exhaust emissions from heavy duty vehicles show charcteristics different from those shown above: Here, the strong dependence on increasing fuel qualities (sulphur content) leads to an cascaded downward trend of SO,,2,, emissions , influenced only slightly by increases in fuel consumption and mileage. For **ammonia** emissions the increasing use of catalytic converters in gasoline driven cars in the 1990s lead to a steep increase whereas both the technical development of the converters and the ongoing shift from gasoline to diesel cars resulted in decreasing emissions in the following years. | + | As for the entire road transport sector, the trends for **sulphur dioxide** (SO<sub>2</ |
- | {{ : | + | {{ : |
- | {{ : | + | |
====Particulate matter & Black carbon==== | ====Particulate matter & Black carbon==== | ||
- | As for all reported exhaust PM emissions from mobile diesel vehicles the Party assumes that nearly all particles emitted are within the PM,,2.5,, range, resulting in similar emission values for PM,,2.5,,, PM,,10,,, and TSP. | + | As for all reported exhaust PM emissions from mobile diesel vehicles the Party assumes that nearly all particles emitted are within the PM<sub>2.5</ |
{{ : | {{ : | ||
Line 129: | Line 107: | ||
Compared to submission 2020, recalculations were carried out due to a routine revision of the TREMOD software and the revision of several National Energy Balances (NEB). | Compared to submission 2020, recalculations were carried out due to a routine revision of the TREMOD software and the revision of several National Energy Balances (NEB). | ||
- | Here, **activity data** were revised within TREMOD due to the provision of the final NEB 2018. | + | Here, **activity data** were revised within TREMOD due to the provision of the final NEB 2019. |
Furthermore, | Furthermore, | ||
__Table 4: Revised fuel consumption data, in terajoules__ | __Table 4: Revised fuel consumption data, in terajoules__ | ||
- | | | **1990** | **1995** | **2000** | **2005** | **2006** | **2007** | **2008** | **2009** | **2010** | **2011** | **2012** | **2013** | **2014** | **2015** | **2016** | **2017** | **2018** | | + | | ^ |
- | | **DIESEL OIL** |||||||||||||||||| | + | | **DIESEL OIL** |||||||||||||||||| |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **BIODIESEL** | + | | **BIODIESEL** |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **CNG** | + | | **CNG** |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **BIOGAS** | + | | **BIOGAS** |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **PETROLEUM** | + | | **PETROLEUM** |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
- | | **TOTAL FUEL CONSUMPTION** | + | | **TOTAL FUEL CONSUMPTION** |
- | ^ Submission | + | ^ Submission |
- | ^ Submission | + | ^ Submission |
- | ^ absolute change | + | ^ absolute change |
- | ^ relative change | + | ^ relative change |
Due to the variety of highly specific tier3 **emission factors** applied, it is not possible to display any changes in these data sets in a comprehendible way. | Due to the variety of highly specific tier3 **emission factors** applied, it is not possible to display any changes in these data sets in a comprehendible way. | ||
- | <WRAP center round info 60%> | + | <WRAP center round info 65%> |
- | For more information on recalculated emission estimates | + | For **pollutant-specific |
</ | </ | ||
Line 178: | Line 156: | ||
===== FAQs ===== | ===== FAQs ===== | ||
- | ------ | + | [(KNOERR2021a> |
- | + | [(KELLER2017> | |
- | [[bibliography]] | + | [(EMEPEEA2019> |
- | : 1 : Knörr et al. (2019a): Knörr, W., Heidt, C., Gores, S., & Bergk, F.: ifeu Institute for Energy and Environmental Research (Institut für Energie- und Umweltforschung Heidelberg gGmbH, ifeu): Fortschreibung des Daten- und Rechenmodells: | + | [(RENTZ2008> |
- | : 2 : Keller et al. (2007): Keller, M., Hausberger, S., Matzer, C., Wüthrich, P., & Notter, B.: Handbook Emission Factors for Road Transport, version 4.1 (Handbuch Emissionsfaktoren des Straßenverkehrs 4.1) URL: http:// | + | |
- | : 3 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019; https:// | + | |
- | : 4 : Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, | + | |
- | [[/ | + |