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1.A.3.b i - Transport: Road Transport: Passenger Cars
Short description
In sub-category 1.A.3.b i - Road transport: Passenger cars emissions from fuel combustion in passenger cars (PCs) are reported.
| Method | AD | EF | Key Category |
|---|---|---|---|
| T1, T3 | NS, M | CS, M, D | L&T: NO,,x,,, NMVOC, CO, PM,,2.5,, & PM,,10,,, BC, Pb; L PCDD/F |
Methodology
Detailed information on the methods applied is provided in the main chapter on road transportation.
Activity data
Specific consumption data for passenger cars is generated within TREMOD 1).
The following table gives an overview of annual amounts of the fuels consumed by passenger cars in Germany.
Table 1: Annual passenger car fuel consumption, in terajoule
| = 1990 | = 1995 | = 2000 | = 2005 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | = 2018 | |||||||||||||||
| ~ Diesel oil | > 253,892 | > 305,128 | > 324,929 | > 440,663 | > 492,791 | > 518,198 | > 518,957 | > 556,096 | > 589,674 | > 593,962 | > 621,938 | > 641,476 | > 610,293 | ||||||||||||||
| ~ Gasoline | > 1,275,916 | > 1,260,078 | > 1,196,370 | > 958,621 | > 765,478 | > 762,566 | > 718,328 | > 717,580 | > 720,676 | > 684,853 | > 684,954 | > 694,769 | > 668,337 | ||||||||||||||
| ~ LPG | > 138 | > 138 | > 94 | > 2,357 | > 21,823 | > 23,613 | > 23,532 | > 23,077 | > 21,464 | > 18,963 | > 16,799 | > 15,377 | > 13,570 | ||||||||||||||
| ~ CNG | > 0 | > 0 | > 0 | > 1,608 | > 5,361 | > 5,505 | > 5,151 | > 4,389 | > 4,519 | > 4,492 | > 3,603 | > 3,257 | > 3,980 | ||||||||||||||
| ~ Biodiesel | > 0 | > 476 | > 3,600 | > 29,343 | > 37,500 | > 35,842 | > 36,337 | > 32,710 | > 35,928 | > 32,198 | > 32,732 | > 34,022 | > 35,226 | ||||||||||||||
| ~ Biogasoline | > 0 | > 0 | > 0 | > 6,585 | > 29,575 | > 31,257 | > 31,833 | > 30,760 | > 31,340 | > 29,703 | > 29,752 | > 29,291 | > 30,051 | ||||||||||||||
| ~ Biogas | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 736 | > 868 | > 1,139 | > 757 | > 847 | > 1,013 | > 930 | ||||||||||||||
| ~ Ʃ 1.A.3.b i | ~ 1,529,946 | ~ 1,565,820 | ~ 1,524,993 | ~ 1,439,177 | ~ 1,352,529 | ~ 1,376,981 | ~ 1,334,873 | ~ 1,365,479 | ~ 1,404,740 | ~ 1,364,927 | ~ 1,390,625 | ~ 1,419,204 | ~ 1,362,386 |
Here, the following charts underline the ongoing shift from gasoline to diesel-powered passenger cars, that started around 1999/2000.
gallery size="medium" : 1A3bi_AD.png : 1A3bi_AD_Gasoline.png : 1A3bi_AD_Diesel.png : 1A3bi_AD_bio.png : 1A3bi_AD_Other.png gallery
For information on mileage, please refer to sub-chapters on emissions from tyre & brake wear and road abrasion].
Emission factors
The majority of emission factors for exhaust emissions from road transport are taken from the 'Handbook Emission Factors for Road Transport' (HBEFA, version 4.1) 2) where they are provided on a tier3 level mostly and processed within the TREMOD software used by the party 3).
However, it is not possible to present these highly specific tier3 values in a comprehendible way here.
[!– Table 2: selected annual fuel-specific IEF for passenger cars, in kg/TJ
| = 1990 | = 1995 | = 2000 | = 2005 | = 2006 | = 2007 | = 2008 | = 2009 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | ||||||||||||||||||||||
| < Gasoline fuels | 1 | ||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| ~ NH,,3,, | > 0.66 | > 12.6 | > 23.1 | > 21.3 | > 21.3 | > 20.8 | > 20.0 | > 18.9 | > 17.8 | > 17.1 | > 16.5 | > 15.8 | > 15.3 | > 15.0 | > 15.0 | > 14.9 | |||||||||||||||||||||
| ~ NMVOC | 2 | > 731 | > 281 | > 151 | > 106 | > 99.4 | > 94.8 | > 86.5 | > 82.1 | > 78.4 | > 76.0 | > 74.1 | > 72.4 | > 71.3 | > 70.5 | > 70.1 | > 69.5 | ||||||||||||||||||||
| ~ NO,,x,, | > 616 | > 342 | > 217 | > 142 | > 130 | > 119 | > 99.2 | > 87.8 | > 77.6 | > 70.7 | > 64.6 | > 59.3 | > 55.1 | > 51.8 | > 49.1 | > 46.5 | |||||||||||||||||||||
| ~ SO,,2,, | > 11.8 | > 8.36 | > 3.25 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | |||||||||||||||||||||
| ~ CO | > 4,698 | > 2,340 | > 1,397 | > 1,013 | > 948 | > 911 | > 844 | > 802 | > 763 | > 741 | > 720 | > 700 | > 687 | > 678 | > 677 | > 673 | |||||||||||||||||||||
| ~ BC | 5 | > 0.07 | > 0.30 | > 0.44 | > 0.36 | > 0.35 | > 0.34 | > 0.31 | > 0.28 | > 0.25 | > 0.24 | > 0.22 | > 0.20 | > 0.19 | > 0.18 | > 0.18 | > 0.17 | ||||||||||||||||||||
| ~ PM | 3 | > 3.67 | > 2.75 | > 2.48 | > 1.87 | > 1.82 | > 1.74 | > 1.60 | > 1.49 | > 1.37 | > 1.31 | > 1.24 | > 1.18 | > 1.14 | > 1.10 | > 1.09 | > 1.07 | ||||||||||||||||||||
| ~ TSP | 4 | > 5.58 | > 3.03 | > 2.48 | > 1.87 | > 1.82 | > 1.74 | > 1.60 | > 1.49 | > 1.37 | > 1.31 | > 1.24 | > 1.18 | > 1.14 | > 1.10 | > 1.09 | > 1.07 | ||||||||||||||||||||
| < Diesel fuels | 1 | ||||||||||||||||||||||||||||||||||||
| ~ NH,,3,, | > 0.36 | > 0.37 | > 0.39 | > 0.41 | > 0.40 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.42 | > 0.42 | > 0.42 | > 0.43 | > 0.44 | > 0.44 | |||||||||||||||||||||
| ~ NMVOC | > 45.5 | > 36.8 | > 29.1 | > 18.6 | > 16.5 | > 15.0 | > 13.5 | > 12.5 | > 11.7 | > 11.0 | > 10.4 | > 9.93 | > 9.64 | > 9.62 | > 9.85 | > 10.1 | |||||||||||||||||||||
| ~ NO,,x,, | > 273 | > 274 | > 304 | > 308 | > 302 | > 298 | > 294 | > 293 | > 298 | > 309 | > 320 | > 329 | > 334 | > 332 | > 324 | > 313 | |||||||||||||||||||||
| ~ SO,,2,, | > 80.8 | > 60.5 | > 14.0 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | > 0.37 | |||||||||||||||||||||
| ~ CO | > 250 | > 205 | > 152 | > 87.9 | > 78.8 | > 71.5 | > 64.3 | > 59.8 | > 56.3 | > 53.1 | > 50.4 | > 48.3 | > 46.7 | > 45.6 | > 44.6 | > 44.0 | |||||||||||||||||||||
| ~ BC | 5 | > 29.6 | > 30.4 | > 28.8 | > 18.3 | > 15.5 | > 13.3 | > 11.2 | > 9.53 | > 8.29 | > 7.19 | > 6.07 | > 5.13 | > 4.35 | > 3.72 | > 3.22 | > 2.80 | ||||||||||||||||||||
| ~ PM | 3 | > 48.8 | > 46.1 | > 39.5 | > 23.2 | > 19.6 | > 16.8 | > 14.1 | > 12.1 | > 10.5 | > 9.20 | > 7.86 | > 6.74 | > 5.82 | > 5.09 | > 4.49 | > 4.00 | ||||||||||||||||||||
| < Liquefied Petroleum Gas - LPG | |||||||||||||||||||||||||||||||||||||
| ~ NH,,3,, | > 0.84 | > 6.92 | > 37.3 | > 32.6 | > 28.6 | > 26.7 | > 23.5 | > 22.1 | > 21.6 | > 21.3 | > 20.9 | > 20.5 | > 20.2 | > 19.9 | > 19.8 | > 19.6 | |||||||||||||||||||||
| ~ NMVOC | > 329 | > 283 | > 49.6 | > 9.73 | > 8.63 | > 8.22 | > 7.50 | > 7.24 | > 7.17 | > 7.10 | > 6.97 | > 6.88 | > 6.82 | > 6.78 | > 6.77 | > 6.75 | |||||||||||||||||||||
| ~ NO,,x,, | > 1,047 | > 906 | > 200 | > 66.1 | > 58.7 | > 56.5 | > 52.6 | > 50.9 | > 49.9 | > 49.3 | > 48.1 | > 46.7 | > 45.6 | > 44.8 | > 44.0 | > 43.2 | |||||||||||||||||||||
| ~ SO,,2,, | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | > 0.41 | |||||||||||||||||||||
| ~ CO | > 2,043 | > 1,812 | > 662 | > 509 | > 452 | > 458 | > 456 | > 456 | > 453 | > 455 | > 452 | > 449 | > 448 | > 447 | > 452 | > 453 | |||||||||||||||||||||
| ~ BC | 5 | > 0.24 | > 0.33 | > 0.75 | > 0.56 | > 0.47 | > 0.43 | > 0.36 | > 0.33 | > 0.32 | > 0.31 | > 0.30 | > 0.29 | > 0.29 | > 0.28 | > 0.28 | > 0.28 | ||||||||||||||||||||
| ~ PM | 3 | > 0.97 | > 1.31 | > 3.01 | > 2.41 | > 2.05 | > 1.90 | > 1.64 | > 1.53 | > 1.48 | > 1.47 | > 1.43 | > 1.40 | > 1.38 | > 1.37 | > 1.37 | > 1.36 | ||||||||||||||||||||
| < Compressed Natural Gas (CNG) & Biogas | 6 | ||||||||||||||||||||||||||||||||||||
| ~ NH,,3,, | = | = | = | > 10.6 | > 10.6 | > 10.7 | > 10.7 | > 10.7 | > 10.7 | > 10.8 | > 10.8 | > 10.8 | > 11.0 | > 11.1 | > 11.4 | > 11.6 | |||||||||||||||||||||
| ~ NMVOC | = | = | = | > 0.48 | > 0.48 | > 0.48 | > 0.48 | > 0.48 | > 0.48 | > 0.49 | > 0.49 | > 0.49 | > 0.50 | > 0.51 | > 0.52 | > 0.52 | |||||||||||||||||||||
| ~ NO,,x,, | = | = | = | > 40.6 | > 40.6 | > 40.6 | > 40.4 | > 40.3 | > 39.6 | > 37.6 | > 35.1 | > 33.3 | > 31.7 | > 30.3 | > 29.3 | > 28.2 | |||||||||||||||||||||
| ~ SO,,2,, | = | = | = | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | > 0.15 | |||||||||||||||||||||
| ~ CO | = | = | = | > 258 | > 258 | > 262 | > 261 | > 261 | > 259 | > 258 | > 255 | > 252 | > 251 | > 252 | > 255 | > 257 | |||||||||||||||||||||
| ~ BC | 5 | = | = | = | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.10 | > 0.11 | > 0.11 | > 0.11 | > 0.11 | ||||||||||||||||||||
| ~ PM | 3 | = | = | = | > 0.67 | > 0.67 | > 0.67 | > 0.67 | > 0.67 | > 0.67 | > 0.68 | > 0.69 | > 0.70 | > 0.71 | > 0.72 | > 0.74 | > 0.75 | ||||||||||||||||||||
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–]
NOTE: With respect to the country-specific emission factors applied for particulate matter, given the circumstances during test-bench measurements, condensables are most likely included at least partly.footnote During test-bench measurements, temperatures are likely to be significantly higher than under real-world conditions, thus reducing condensation. On the contrary, smaller dillution (higher number of primary particles acting as condensation germs) together with higher pressures increase the likeliness of condensation. So over-all condensables are very likely to occur but different to real-world conditions. footnote
For heavy-metal (other then lead from leaded gasoline) and PAH exhaust-emissions, default emission factors from (EMEP/EEA, 2019) 4) have been applied. Regarding PCDD/F, a tier1 EF from (Rentz et al., 2008) 5) is used.
Table 3: Overview of tier1 emission factors for heavy-metal and POP exhaust emissions
| = | = Pb | = Cd | = Hg | = As | = Cr | = Cu | = Ni | = Se | = Zn | = B[a]P | = B[b]F | = B[k]F | = I[…]p | = PAH 1-4 | = PCDD/F | ||||||||||||||||||||||||
| = | = [g/TJ] | = [mg/TJ] | = [µg/km] | ||||||||||||||||||||||||||||||||||||
| ~ Diesel oil | > 0.012 | > 0.0012 | > 0.123 | > 0.0023 | > 0.198 | > 0.133 | > 0.005 | > 0.002 | > 0.419 | > 498 | > 521 | > 275 | > 493 | > 1,788 | > | ||||||||||||||||||||||||
| ~ Biodiesel | 1 | > 0.013 | > 0.0013 | > 0.142 | > 0.0027 | > 0.228 | > 0.153 | > 0.005 | > 0.003 | > 0.483 | > 575 | > 601 | > 317 | > 569 | > 2,062 | > | |||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| ~ Gasoline fuels | > 0.037 | > 0.0046 | > 0.200 | > 0.0069 | > 0.145 | > 0.103 | > 0.053 | > 0.005 | > 0.758 | > 126 | > 181 | > 90 | > 204 | > 602 | > | ||||||||||||||||||||||||
| ~ CNG | 2 | & biogas | 3 | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | > | |||||||||||||||||||||
| ~ LPG | 4 | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | = NE | > 4.35 | > 0.00 | > 4.35 | > 4.35 | > 13.04 | > | |||||||||||||||||||||||
| ~ all fuels | > | > 0.000002 | |||||||||||||||||||||||||||||||||||||
| 1 | |||||||||||||||||||||||||||||||||||||||
| 2 | |||||||||||||||||||||||||||||||||||||||
| 3 | |||||||||||||||||||||||||||||||||||||||
| 4 | |||||||||||||||||||||||||||||||||||||||
Discussion of emission trends
NFR 1.A.3.b i is key category for NH,,3,,, NO,,x,,, NMVOC, CO, PM,,2.5,, and PM,,10,,.
Non-methane volatile organic compounds (NMVOC), nitrogen oxides (NO,,x,,), and carbon monoxide (CO)
Since 1990, exhaust emissions of nitrogen oxides, NMVOC, and carbon monoxide have decreased sharply due to catalytic-converter use and engine improvements resulting from ongoing tightening of emissions laws and improved fuel quality.
gallery size="medium" : 1A3bi_EM_NOx.PNG : 1A3bi_EM_NMVOC.PNG : 1A3bi_EM_CO.PNG gallery
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 passenger cars show charcteristics very 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.
gallery size="medium" : 1A3bi_EM_SO2.png : 1A3bi_EM_NH3.png gallery
Particulate Matter
(from fuel combustion only; no wear/abrasion included)
Starting in the middle of the 1990s, a so-called “diesel boom” began, leading to a switch from gasoline to diesel powered passenger cars. As the newly registered diesel cars had to meet the EURO2 standard (in force since 1996/'97) with a PM limit value less than half the EURO1 value, the growing diesel consumption was overcompensated qickly by the mitigation technologies implemented due to the new EURO norm. During the following years, new EURO norms came into force. With the still ongoing “diesel boom” those norms led to a stabilisation (EURO3, 2000/'01) of emissions and to another strong decrease of PM emissions (EURO4, 2005/'06), respectively. Over-all, the increased consumption of diesel in passenger cars was overastimated by the implemented mitigation technologies. The table below shows the evolution of the limit value for particle emissions from passenger cars with diesel engines.
With this submission, Black Carbon (BC) emissions are reported for the first time. Here, EF are estimated based on as fractions of PM as provided in 6). Due to this fuel-specific fractions, the trend of BC emissions reflects the ongoing shift from gasoline to diesel (“dieselisation”).
gallery size="medium" : 1A3bi_EM_PM.PNG gallery
Table: EURO norms and their effect on limit values of PM emissions from diesel passenger cars
| ~ exhaust emission standard (EURO norm) | = Euro 1 | = Euro 2 | = Euro 3 | = Euro 4 | = Euro 5 | = Euro 6 | |||||||
| in force for type approval since: | = 1 Jul 1992 | = 1 Jan 1996 | = 1 Jan 2000 | = 1 Jan 2005 | = 1 Sep 2009 | = 1 Sep 2014 | |||||||
| in force for initial registration since | = 1 Jan 1993 | = 1 Jan 1997 | = 1 Jan 2001 | = 1 Jan 2006 | = 1 Jan 2011 | = 1 Jan 2015 | |||||||
| ~ resulting PM limit value in [mg/km] | = 180 | = 80/100^^1^^ | = 50 | = 25 | = 5 | = 5 | |||||||
| 1 | |||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Recalculations
Compared to submission 2020, specific activity data for passenger cars were revised within TREMOD for all years due to re-allocations of consumption shares between the different vehicle types and classes. In contrast, the over-all fuel consumption in road transport remains unaltered, with the only changes occuring for 2017 due to the implementation of the now finalised NEB 2017 (see superordinate chapter]).
Table 3: Revised fuel consumption data, in terajoule
| = 1990 | = 1995 | = 2000 | = 2005 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | ||||||||||||||||||||||
| < Diesel oil | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 253,892 | > 305,128 | > 324,929 | > 440,663 | > 492,791 | > 518,198 | > 518,957 | > 556,096 | > 589,674 | > 593,962 | > 621,938 | > 641,476 | |||||||||||||||||||||
| ~ Submission 2019 | > 237,993 | > 273,767 | > 290,816 | > 423,601 | > 494,934 | > 521,710 | > 523,848 | > 562,369 | > 596,544 | > 601,100 | > 627,995 | > 639,270 | |||||||||||||||||||||
| ~ absolute change | > 15,899 | > 31,361 | > 34,113 | > 17,062 | > -2,143 | > -3,512 | > -4,891 | > -6,273 | > -6,870 | > -7,138 | > -6,057 | > 2,206 | |||||||||||||||||||||
| ~ relative change | > 6.68% | > 11.5% | > 11.73% | > 4.03% | > -0.43% | > -0.67% | > -0.93% | > -1.12% | > -1.15% | > -1.19% | > -0.96% | > 0.35% | |||||||||||||||||||||
| < Biodiesel | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 0 | > 476 | > 3,600 | > 29,343 | > 37,500 | > 35,842 | > 36,337 | > 32,710 | > 35,928 | > 32,198 | > 32,732 | > 34,022 | |||||||||||||||||||||
| ~ Submission 2019 | > 0 | > 427 | > 3,222 | > 28,207 | > 37,663 | > 36,085 | > 36,679 | > 33,079 | > 36,347 | > 32,585 | > 33,050 | > 33,906 | |||||||||||||||||||||
| ~ absolute change | > 0 | > 49 | > 378 | > 1,136 | > -163 | > -243 | > -342 | > -369 | > -419 | > -387 | > -319 | > 116 | |||||||||||||||||||||
| ~ relative change | > | > 11.5% | > 11.7% | > 4.03% | > -0.43% | > -0.67% | > -0.93% | > -1.12% | > -1.15% | > -1.19% | > -0.96% | > 0.34% | |||||||||||||||||||||
| < Gasoline | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 1,275,916 | > 1,260,078 | > 1,196,370 | > 958,621 | > 765,478 | > 762,566 | > 718,328 | > 717,580 | > 720,676 | > 684,853 | > 684,954 | > 694,769 | |||||||||||||||||||||
| ~ Submission 2019 | > 1,284,554 | > 1,268,816 | > 1,204,479 | > 963,174 | > 768,521 | > 764,508 | > 719,363 | > 717,967 | > 720,801 | > 685,615 | > 686,310 | > 688,601 | |||||||||||||||||||||
| ~ absolute change | > -8,639 | > -8,738 | > -8,108 | > -4,552 | > -3,043 | > -1,942 | > -1,035 | > -388 | > -124 | > -763 | > -1,356 | > 6,169 | |||||||||||||||||||||
| ~ relative change | > -0.67% | > -0.69% | > -0.67% | > -0.47% | > -0.40% | > -0.25% | > -0.14% | > -0.05% | > -0.02% | > -0.11% | > -0.20% | > 0.90% | |||||||||||||||||||||
| < Biogasoline | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 0 | > 0 | > 0 | > 6,585 | > 29,575 | > 31,257 | > 31,833 | > 30,760 | > 31,340 | > 29,703 | > 29,752 | > 29,291 | |||||||||||||||||||||
| ~ Submission 2019 | > 0 | > 0 | > 0 | > 6,617 | > 29,693 | > 31,337 | > 31,878 | > 30,777 | > 31,346 | > 29,736 | > 29,811 | > 29,312 | |||||||||||||||||||||
| ~ absolute change | > 0 | > 0 | > 0 | > -31 | > -118 | > -80 | > -46 | > -17 | > -5 | > -33 | > -59 | > -21 | |||||||||||||||||||||
| ~ relative change | > | > | > | > -0,47% | > -0,40% | > -0,25% | > -0,14% | > -0,05% | > -0,02% | > -0,11% | > -0,20% | > -0,07% | |||||||||||||||||||||
| < LPG | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 138 | > 138 | > 94 | > 2,357 | > 21,823 | > 23,613 | > 23,532 | > 23,077 | > 21,464 | > 18,963 | > 16,799 | > 15,377 | |||||||||||||||||||||
| ~ Submission 2019 | > 138 | > 138 | > 94 | > 2,357 | > 21,318 | > 23,070 | > 22,974 | > 22,500 | > 20,889 | > 18,394 | > 16,263 | > 13,101 | |||||||||||||||||||||
| ~ absolute change | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 505 | > 543 | > 558 | > 577 | > 575 | > 569 | > 536 | > 2,276 | |||||||||||||||||||||
| ~ relative change | > 0.00% | > 0.00% | > 0.00% | > 0.00% | > 2.37% | > 2.35% | > 2.43% | > 2.56% | > 2.75% | > 3.09% | > 3.30% | > 17.4% | |||||||||||||||||||||
| < CNG | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 0 | > 0 | > 0 | > 1,608 | > 5,361 | > 5,505 | > 5,151 | > 4,389 | > 4,519 | > 4,492 | > 3,603 | > 3,257 | |||||||||||||||||||||
| ~ Submission 2019 | > 0 | > 0 | > 0 | > 1,939 | > 6,150 | > 6,220 | > 6,336 | > 5,277 | > 5,324 | > 5,313 | > 4,267 | > 3,836 | |||||||||||||||||||||
| ~ absolute change | > 0 | > 0 | > 0 | > -331 | > -789 | > -715 | > -1.184 | > -889 | > -805 | > -821 | > -664 | > -579 | |||||||||||||||||||||
| ~ relative change | > | > | > | > -17.1% | > -12.8% | > -11.5% | > -18.7% | > -16.8% | > -15.1% | > -15.5% | > -15.6% | > -15.1% | |||||||||||||||||||||
| < Biogas | |||||||||||||||||||||||||||||||||
| ~ Submission 2020 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 736 | > 868 | > 1,139 | > 757 | > 847 | > 1,013 | |||||||||||||||||||||
| ~ Submission 2019 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 905 | > 1,044 | > 1,342 | > 896 | > 1,003 | > 911 | |||||||||||||||||||||
| ~ absolute change | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > -169 | > -176 | > -203 | > -138 | > -156 | > 101 | |||||||||||||||||||||
| ~ relative change | > | > | > | > | > | > | > -18.7% | > -16.8% | > -15.1% | > -15.5% | > -15.6% | > 11.1% | |||||||||||||||||||||
source: own estimates based on TREMOD 7)
Due to the variety of tier3 emission factors applied, it is not possible to display any changes in these data sets in a comprehendible way.
Emission estimates
For more information on recalculated emission estimates for Base Year and 2018, please see the pollutant-specific recalculation tables following chapter 8.1 - Recalculations].
bibliography : 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: Energieverbrauch und Schadstoffemissionen des motorisierten Verkehrs in Deutschland 1960-2030, sowie TREMOD 6.02, im Auftrag des Umweltbundesamtes, Heidelberg & Berlin, 2019. : 2 : Keller et al., (2019): 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://www.hbefa.net/e/index.html - Dokumentation, Bern, 2019. : 3 : EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019; https://www.eea.europa.eu/publications/emep-eea-guidebook-2019/part-b-sectoral-guidance-chapters/1-energy/1-a-combustion/1-a-3-b-i/view; Copenhagen, 2019. : 4 : 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 bibliography