1.A.3.b i-iv - Emissions from Fuel Combustion in Road Vehicles

Last updated on 30 Aug 2017 16:54 (cf. Authors)

Short description

In sub-categories 1.A.3.b i - iv the emissions from fuel combustion activities in road transport are reported.

NFR-Code Name of Category
1.A.3.b i Passenger Cars
1.A.3.b ii Light Duty Vehicles
1.A.3.b iii Heavy Duty Vehicles
1.A.3.b iv Mopeds & Motorcycles

Method

Activity data

Basically, total inland fuel deliveries are available from the National Energy Balances (NEBs) (AGEB, 2016) [1], line 62: Straßenverkehr (Road Transport) as compiled by the Association of the German Petroleum Industry (MWV) [2].

Based upon these primary activity data, specific consumption data for the different types of road vehicles are generated within TREMOD [3].

For further details see main chapter 1.A.3.b - Road Transport as wells as the sub-category chapters linked above.

Emission factors

The majority of emissions factors for exhaust emissions from road transport are taken from the 'Handbook Emission Factors for Road Transport' (HBEFA, version 3.2) [4] where they are provided on a tier3 level mostly and processed within the TREMOD software used by the party [3].

As it is not possible to present these tier3 values in a comprehendible way, the NFR sub-chapters linked above provide sets of fuel-specific implied emission factors instead.

For heavy-metal (other then lead from leaded gasoline) and PAH exhaust-emissions, default emission factors from (EMEP/EEA, 2016) [5] have been applied.
Regarding PCDD/F, tier1 EF from (Rentz et al., 2008) [6] are used instead.

Trends of exhaust emissions from road transport vehicles

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.

The observed trends for NOx, NMVOC and CO emissions represent the changes in legislatory emission limits and the regarding implementation of mitigation technologies.

Trends for sulphur dioxide (SO2) and ammonia (NH3) exhaust emissions show charcteristics very different from those shown above.
Here, the strong dependence on increasing fuel qualities leads to an cascaded downward trend of SO2 emissions, influenced only slightly by increases in fuel consumption and mileage.

The following table provides the development of sulphur contents over the years for Old (OGL) and New German Länder (NGL) and Germany (GER).

Table 1: Development of fuel sulphur contents in Germany
Covered Area Covered Year(s) gasoline diesel oil
NGL
until 1988 500 ppm 6,000 ppm
1989-1990 500 ppm 6,000 ppm
OGL
until 1984 250 ppm 2,700 ppm
1985 250 ppm 2,500 ppm
1986 250 ppm 2,100 ppm
1987 250 ppm 2,100 ppm
1988 250 ppm 1,700 ppm
1989 250 ppm 1,700 ppm
1990 220 ppm 1,700 ppm
GER
1991 220 ppm 1,300 ppm
1992 220 ppm 1,300 ppm
1993 220 ppm 1,300 ppm
1994 220 ppm 1,300 ppm
1995 180 ppm 1,300 ppm
1996 180 ppm 600 ppm
1997 180 ppm 400 ppm
1998-2000 70 ppm 300 ppm
2001 55 ppm 250 ppm
2002 25 ppm 40 ppm
since 2003 8 ppm 8 ppm

For exhaust particulate matter emissions from diesel road vehicles, the party assumes that nearly all particles emitted are within the PM2.5 range, resulting in similar emission values for PM2.5, PM10, and TSP.
Excumptions from this assumption can be observed for gasoline road vehicles for the years until 1997 when additional TSP emissions resulted from the use of leaded gasoline that was banned in 1997.
Furthermore, black carbon emissions are estimated via implied emission factors derived from fractions of PM as provided in [5].

For Heavy Metals and PAHs, emissions are calculated with tier1 default EF from [5] resulting in trends that simply reflect the annual fuel consumption.
Here, the only excumption are lead emissions from leaded gasoline that was in use until 1996 with lead contents provided in the table below:

Table 2: Development of gasoline's lead content in Germany
Area Year Pb content
NGL 1989-1990 126 mg/l
OGL 1990 42 mg/l
GER 1991 29 mg/l
1992 20 mg/l
1993 16 mg/l
1994 11 mg/l
1995 8 mg/l
1996 4 mg/l
since 1997 0 mg/l (banned)

For further details and information on recalculations, uncertainty assessment etc. see superordinate chapter 1.A.3.b - Road Transport as well as the different sub-chapters linked above.

Uncertainties

Uncertainty estimates for activity data of mobile sources derive from research project FKZ 360 16 023: "Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland" by (ifeu & INFRAS, 2009) [7]. - For detailled information, please refer to the project's final report here (German version only!)

Uncertainty estimates for emission factors for all 1.A.3.b sub-categories were compiled during the PAREST research project. Here, the final report has not yet been published.

Planned improvements

Besides the routine revision of the TREMOD model used, no further sector-specific improvements are planned.


Bibliography
1. AGEB, 2016: Arbeitsgemeinschaft Energiebilanzen (Hrsg.): Energiebilanz für die Bundesrepublik Deutschland; URL: http://www.ag-energiebilanzen.de/7-0-Bilanzen-1990-2014.html, Köln & Berlin, 2016.
2. MWV, 2016: Mineralölwirtschaftsverband (MWV, Association of the German Petroleum Industry): MWV Jahresberichte: URL: https://www.mwv.de/publikationen/jahresberichte/, Berlin, 2016.
3. ifeu, 2016a: Knörr, W. et al., IFEU - Institut für Energie- und Umweltforschung Heidelberg gGmbH: Fortschreibung des Daten- und Rechenmodells: Energieverbrauch und Schadstoffemissionen des motorisierten Verkehrs in Deutschland 1960-2030, sowie TREMOD, im Auftrag des Umweltbundesamtes, Heidelberg & Berlin, 2016.
4. INFRAS, 2014: Handbook Emission Factors for Road Transport, version 3.2 (Handbuch Emissionsfaktoren des Straßenverkehrs 3.1) URL: http://www.hbefa.net/e/index.html - Dokumentation, Bern, January 2011
5. EMEP/EEA, 2016: EMEP/EEA air pollutant emission inventory guidebook 2016; Copenhagen, 2016.
6. Rentz et al., 2008: Nationaler Durchführungsplan unter dem Stockholmer Abkommen zu persistenten organischen Schadstoffen (POPs), im Auftrag des Umweltbundesamtes, FKZ 205 67 444, UBA Texte | 01/2008, January 2008 - URL: http://www.umweltbundesamt.de/en/publikationen/nationaler-durchfuehrungsplan-unter-stockholmer
7. ifeu & INFRAS, 2009: IFEU – Institut für Energie- und Umweltforschung Heidelberg gGmbH und INFRAS Zürich: Ermittlung der Unsicherheiten der mit den Modellen TREMOD und TREMOD-MM berechneten Luftschadstoffemissionen des landgebundenen Verkehrs in Deutschland, FKZ 360 16 023, Heidelberg & Zürich.
Unless otherwise stated, the content of this page is licensed under Creative Commons Attribution-NonCommercial-NoDerivs 3.0 License