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sector:energy:fuel_combustion:transport:road_transport:emissions_from_fuel_combustion_in_road_vehicles:heavy_duty_vehicles [2021/04/08 15:14] – [Table] kotzulla | sector:energy:fuel_combustion:transport:road_transport:emissions_from_fuel_combustion_in_road_vehicles:heavy_duty_vehicles [2021/04/15 08:13] – [Table] kotzulla | ||
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^ 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 ||||| NS, M ||||| CS, M, D ||||| | ||
- | ^ Key Category | + | ^ Key Category |
| 1.A.3.b iii | | 1.A.3.b iii | ||
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==== 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 [(KNOERR2020a)]. - The following tables provide an overview of annual amounts of fuels consumed by these vehicles in Germany. |
{{ : | {{ : | ||
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^ Petroleum | ^ Petroleum | ||
| **Ʃ 1.A.3.b iii** | | **Ʃ 1.A.3.b iii** | ||
- | source: TREMOD 6.02 [((bibcite 1))] | + | source: TREMOD 6.02 [(KNOERR2020a)] |
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- | : 1A3biii_AD_Bus.png | + | |
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- | --] | + | |
<WRAP center round info 60%> | <WRAP center round info 60%> | ||
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==== 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. | ||
- | |||
<WRAP center round info 100%> | <WRAP center round info 100%> | ||
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</ | </ | ||
- | 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__ | ||
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===== Discussion of emission trends ===== | ===== Discussion of emission trends ===== | ||
- | ^ Key Category | + | __Outcome of Key Category |
- | | ::: | -/ | + | | for: ^ NO< |
+ | | by: | L/T | ||
==== Nitrogen oxides==== | ==== Nitrogen oxides==== | ||
- | Until 2005, NO,,x,, emissions followed mileage and fuel consumption. Since 2006, in contrast to nearly unchanged fuel consumption, | + | Until 2005, NO<sub>x</ |
{{ : | {{ : | ||
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==== 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</ |
{{ : | {{ : | ||
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====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</ |
{{ : | {{ : | ||
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===== FAQs ===== | ===== FAQs ===== | ||
- | ------ | + | [(KNOERR2020a> |
- | + | [(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, | + | |
- | [[/ | + |