1.A.3.b - Transport: Road Transport

Short description

In category 1.A.3.b - Road Transport emissions from fuel combustion activities as well as abrasive and fugitive emissions are reported within the following categories:

Emissions from motorised road traffic in Germany are reported under this category. It includes traffic on public roads within Germany, except for agricultural and forestry transports and military transports. Calculations are made for the vehicle categories of passenger cars, motorcycles, light duty vehicles, heavy duty vehicles and buses. For calculation purposes, the vehicle categories are broken down into so-called vehicle layers with the same emissions behaviour. To this end, vehicle categories are also broken down by type of fuel used, vehicle size (trucks and buses by weight class; automobiles and motorcycles by engine displacement) and pollution control equipment used, as defined by EU directives for emissions control (“EURO norms”), and by regional traffic distribution (outside of cities, in cities and autobahn).

Since 1990, emissions of NOx, CO, NMVOC and SO2 from road transports have decreased sharply, due to catalytic-converter use and engine improvements resulting from continual tightening of emissions laws, and due to improved fuel quality.

For buses and heavy duty vehicles (over 3.5 t total permissible vehicle weight), maximum permissible levels of hydrocarbon (HC, incl. NMVOC) emissions were lowered especially sharply (-40%) via the introduction of the EURO3 standard in 2000. Since EURO3 vehicles were very quick to reach the market as of 2000, the emission factor for hydrocarbon emissions from diesel fuel - and the relevant emissions themselves – decreased considerably after 2000.

Methodology

Emissions are calculated with the aid of the TREMOD model (“Transport Emission Estimation Model”) from (Knörr, W. et al. (2022a)) 1).

This model adopts a “bottom-up” (tier3) approach whereby mileage of the individual vehicle layers is multiplied by region-specific emission factors. For passenger cars and light duty vehicles, a “cold start surplus” is also added. The total consumption calculated on the basis of fuel type is compared with the consumption according to the Energy Balance. The emissions are then corrected with the aid of factors obtained from this comparison process. For petrol-powered vehicles, the evaporation emissions of VOC are calculated in keeping with the pollution-control technology used. From the emissions and fuel consumption for the various vehicle layers, aggregated, fuelbased emission factors (kg of emissions per TJ of fuel consumption) are derived, and then the emission factors are forwarded to the CSE via a relevant interface. In keeping with the CORINAIR report structure, these factors are differentiated only by type of fuel, type of road (autobahn, rural road, city road) and, within the vehicle categories, by “without/with emissions-control equipment”. The following emissions-control categories are differentiated:

For calculation with TREMOD, extensive basic data from generally accessible statistics and special surveys were used, co-ordinated, and supplemented. An overview of the principal sources and key assumptions is given below. Detailed descriptions of the databases, including information on the sources used, and the calculation methods used in TREMOD, are provided in the aforementioned IFEU report.

Activity Data

The basis for CSE data collection for the road-transport sector consists of fuel consumption data provided by the Working Group on Energy Balances (AGEB) 2). For each year, the sum of the activity rates for the various individual structural elements must correspond to the Energy Balance data, in terajoule. The relevant basic Energy Balance data is shown in the table below.

Table 1: Fuel consumption in German road transport, in terajoules

Diesel oil Gasoline LPG CNG LNG Petroleum1 Biodiesel Biogasoline Biogas Lubricants2 TOTAL
1990 735,920 1,330,479 138 2,543 2,069,080
1991 785,174 1,332,285 137 1,702 2,119,298
1992 853,502 1,344,129 229 1,299 2,199,159
1993 907,787 1,350,617 184 473 872 2,259,933
1994 932,060 1,276,637 184 559 596 2,210,036
1995 964,013 1,299,982 138 610 1,504 455 2,266,702
1996 964,580 1,299,879 115 638 2,046 372 2,267,630
1997 979,586 1,297,487 106 357 3,652 266 2,281,454
1998 1,022,794 1,300,463 106 637 4,081 206 2,328,287
1999 1,097,036 1,300,602 100 637 5,370 116 2,403,861
2000 1,108,105 1,237,055 94 414 12,276 83 2,358,027
2001 1,097,416 1,199,318 98 471 16,740 74 2,314,117
2002 1,105,842 1,166,381 607 472 20,460 77 2,293,839
2003 1,078,352 1,108,989 694 0 29,948 73 2,218,056
2004 1,110,931 1,072,720 1,887 0 38,898 1,144 75 2,225,655
2005 1,078,620 992,377 2,357 3,127 0 72,080 6,817 78 2,155,457
2006 1,082,042 930,834 4,605 4,446 0 130,463 13,418 77 2,165,884
2007 1,073,987 892,982 8,942 5,845 0 143,691 12,061 80 2,137,589
2008 1,102,624 854,002 15,652 7,144 0 109,853 16,328 81 2,105,684
2009 1,114,939 829,227 23,842 8,443 0 90,074 23,691 87 2,090,304
2010 1,168,063 791,416 21,823 8,768 0 89,552 30,577 83 2,110,282
2011 1,197,252 787,803 23,613 8,771 0 83,536 32,292 81 2,133,348
2012 1,223,719 742,000 23,532 8,869 36 0 86,365 32,882 1,267 77 2,118,745
2013 1,283,637 741,150 23,077 7,389 41 0 76,126 31,770 1,462 78 2,164,730
2014 1,296,828 744,661 21,464 7,472 47 0 79,691 32,383 1,883 78 2,184,507
2015 1,348,789 708,672 18,963 7,407 52 0 73,779 30,736 1,249 78 2,189,725
2016 1,393,481 709,179 16,799 5,848 63 0 73,875 30,804 1,375 78 2,231,502
2017 1,425,424 719,580 15,377 5,848 104 0 76,096 30,337 1,616 77 2,274,459
2018 1,377,104 692,694 16,153 5,198 192 0 80,049 31,146 1,399 76 2,204,011
2019 1,390,837 699,835 14,602 5,848 830 0 79,219 30,184 2,378 77 2,223,810
2020 1,239,658 629,435 9,551 5,912 2,511 0 102,973 28,737 3,181 80 2,022,040
2021 1,254,201 634,080 9,500 6,657 5,045 0 87,131 30,165 3,181 73 2,030,033

1: applied only from 1993 to 2002 in a small number of buses (se chapter on NFR 1.A.3.b iii)

2: amounts of lubricants unintentionally co-incinerated in road vehicles (lubricants intentionally co-incinerated in 2-stroke road vehicles are taken into account in NFR 2.D.3.i Mobile Use of Lubricants

The following chart illustrates the (ongoing) trend to diesel vehicles operated in Germany, the so-called “Dieselization” with the amounts of fossil diesel oil exceeing those of fossil gasoline fuels from 2004 onwards.

 Vizualisation of so-called "Dieselization"

For more information on the derivation of activity data and the emission factors applied, please refer to the sub-ordinate chapters as well as Appendix 2.2.

Chart 2 illustrates the increase in annual mileage of electric road vehicles in 106 kilometers. Despite the exponential growth, only about 1 per cent of annual mileage was “electric” in 2021 (7,000,000,000 of 682,831,000,000 km).  Annual mileage of electric road vehicles

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 (Knörr et al. (2009)) 3).

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.

Recalculations

Basically, recalculations result from a) the revision of the National Energy Balance (for most recent years) and b) routine revsisions of the underlying TREMOD model (recent years or entire time series, depending on outline of revision).

For more details please refer to the related sub-chapters as linked above.

Planned improvements

Besides the routine revision of the TREMOD model, no specific improvements are planned.


1) Knörr et al. (2022a): Knörr, W., Heidt, C., Gores, S., & Bergk, F.: Fortschreibung des Daten- und Rechenmodells: Energieverbrauch und Schadstoffemissionen des motorisierten Verkehrs in Deutschland 1960-2035, sowie TREMOD, im Auftrag des Umweltbundesamtes, Heidelberg [u.a.]: Ifeu Institut für Energie- und Umweltforschung Heidelberg GmbH, Heidelberg & Berlin, 2022.
2) AGEB, 2022: Working Group on Energy Balances (Arbeitsgemeinschaft Energiebilanzen (Hrsg.), AGEB): Energiebilanz für die Bundesrepublik Deutschland; https://ag-energiebilanzen.de/daten-und-fakten/bilanzen-1990-bis-2020/?wpv-jahresbereich-bilanz=2011-2020, (Aufruf: 23.11.2022), Köln & Berlin, 2022
3) 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; final report; URL: https://www.umweltbundesamt.de/sites/default/files/medien/461/publikationen/3937.pdf, FKZ 360 16 023, Heidelberg & Zürich, 2009.