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1.A3.b ii - Transport: Road Transport: Light Duty Vehicles
Short description
In sub-category 1.A.3.b ii - Road Transport: Light Duty Vehicles emissions from fuel combustion in Light Duty Vehicles (LDVs) are reported.
Method | AD | EF | Key Category |
---|---|---|---|
T1, T3 | NS, M | CS, M, D | L& : NO,,x,,, PM,,2.5,,, PM,,10,,, BC |
Method
Activity data
Specific consumption data for light-duty vehicles (LDV) are generated within TREMOD 1). - The following table provides an overview of annual amounts of fuels consumed by LDV in Germany.
Table 1: Annual fuel consumption of light duty vehicles, in terajoules
= 1990 | = 1995 | = 2000 | = 2005 | = 2006 | = 2007 | = 2008 | = 2009 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | = 2018 | |||||||||||||||||||
~ Diesel oil | > 41,153 | > 89,124 | > 116,634 | > 121,822 | > 105,582 | > 105,122 | > 108,097 | > 109,289 | > 108,711 | > 111,764 | > 110,034 | > 115,424 | > 118,957 | > 126,159 | > 134,558 | > 143,170 | > 143,928 | ||||||||||||||||||
~ Gasoline | > 31,432 | > 19,932 | > 16,561 | > 10,726 | > 9,665 | > 8,888 | > 7,792 | > 7,367 | > 6,899 | > 6,646 | > 6,117 | > 6,022 | > 5,989 | > 6,042 | > 6,145 | > 6,354 | > 6,442 | ||||||||||||||||||
~ CNG | > 0 | > 0 | > 0 | > 341 | > 485 | > 707 | > 928 | > 1,128 | > 1,218 | > 1,267 | > 1,179 | > 953 | > 981 | > 1,073 | > 858 | > 771 | > 900 | ||||||||||||||||||
~ Biodiesel | > 0 | > 139 | > 1,292 | > 8,112 | > 12,701 | > 14,020 | > 10,724 | > 8,761 | > 8,273 | > 7,730 | > 7,704 | > 6,789 | > 7,248 | > 6,839 | > 7,082 | > 7,593 | > 8,307 | ||||||||||||||||||
~ Biogasoline | > 0 | > 0 | > 0 | > 74 | > 139 | > 120 | > 149 | > 210 | > 267 | > 272 | > 271 | > 258 | > 260 | > 262 | > 267 | > 268 | > 290 | ||||||||||||||||||
~ Biogas | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 0 | > 168 | > 189 | > 247 | > 181 | > 202 | > 240 | > 210 | ||||||||||||||||||
~ Ʃ 1.A.3.b ii | ~ 72,585 | ~ 109,194 | ~ 134,487 | ~ 141,075 | ~ 128,572 | ~ 128,857 | ~ 127,690 | ~ 126,756 | ~ 125,368 | ~ 127,680 | ~ 125,473 | ~ 129,636 | ~ 133,683 | ~ 140,556 | ~ 149,111 | ~ 158,395 | ~ 160,078 |
gallery size="medium" : 1A3bii_AD.png : 1A3bii_AD_diesel.png : 1A3bii_AD_gasoline.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 here in a comprehendible way .
[!– , the following table provides a set of fuel-specific implied emission factors (ratio of total emissions per pollutant and total annual consumption.)
Table 2: Annual country-specific implied tier3 emission factors for light-duty vehicles, in kg/TJ
= 1990 | = 1995 | = 2000 | = 2005 | = 2006 | = 2007 | = 2008 | = 2009 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | ||||||||||||||||||||||
< Diesel fuels | 1 | ||||||||||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
~ NH,,3,, | > 0.31 | > 0.31 | > 0.32 | > 0.32 | > 0.32 | > 0.32 | > 0.32 | > 0.33 | > 0.33 | > 0.34 | > 0.34 | > 0.35 | > 0.35 | > 0.35 | > 0.36 | > 0.36 | |||||||||||||||||||||
~ NMVOC | > 74.6 | > 72.3 | > 50.3 | > 28.4 | > 25.1 | > 22.0 | > 17.9 | > 15.7 | > 14.1 | > 12.5 | > 11.1 | > 9.79 | > 8.71 | > 7.86 | > 7.16 | > 6.61 | |||||||||||||||||||||
~ NO,,x,, | > 610 | > 528 | > 477 | > 438 | > 428 | > 412 | > 394 | > 384 | > 376 | > 369 | > 361 | > 355 | > 351 | > 345 | > 338 | > 316 | |||||||||||||||||||||
~ SO,,2,, | > 80.9 | > 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 | > 330 | > 337 | > 249 | > 149 | > 135 | > 119 | > 97.9 | > 86.3 | > 77.5 | > 69.1 | > 62.1 | > 56.0 | > 50.8 | > 46.8 | > 43.4 | > 40.8 | |||||||||||||||||||||
~ BC | 5 | > 57.8 | > 53.0 | > 39.6 | > 26.7 | > 25.2 | > 23.6 | > 21.6 | > 20.6 | > 19.6 | > 18.2 | > 16.3 | > 14.0 | > 11.8 | > 9.87 | > 8.28 | > 6.94 | ||||||||||||||||||||
~ PM | 3 | > 105 | > 93.5 | > 60.9 | > 37.3 | > 34.7 | > 31.9 | > 28.2 | > 26.4 | > 24.7 | > 22.7 | > 20.2 | > 17.4 | > 14.7 | > 12.3 | > 10.4 | > 8.82 | ||||||||||||||||||||
< Gasoline fuels | 1 | ||||||||||||||||||||||||||||||||||||
~ NH,,3,, | > 0.64 | > 2.43 | > 19.55 | > 21.94 | > 21.16 | > 21.10 | > 22.23 | > 21.46 | > 20.55 | > 19.44 | > 18.36 | > 17.23 | > 16.09 | > 14.92 | > 14.07 | > 13.19 | |||||||||||||||||||||
~ NMVOC | 2 | > 1,112 | > 599 | > 388 | > 295 | > 289 | > 269 | > 230 | > 208 | > 191 | > 176 | > 166 | > 158 | > 151 | > 148 | > 145 | > 141 | ||||||||||||||||||||
~ NO,,x,, | > 665 | > 584 | > 438 | > 338 | > 334 | > 308 | > 259 | > 229 | > 204 | > 182 | > 167 | > 154 | > 144 | > 138 | > 134 | > 127 | |||||||||||||||||||||
~ SO,,2,, | > 12.8 | > 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 | > 7,982 | > 7,242 | > 5,709 | > 4,636 | > 4,547 | > 4,248 | > 3,710 | > 3,384 | > 3,093 | > 2,853 | > 2,670 | > 2,524 | > 2,405 | > 2,320 | > 2,277 | > 2,198 | |||||||||||||||||||||
~ BC | 5 | > 0.10 | > 0.13 | > 0.58 | > 0.62 | > 0.60 | > 0.59 | > 0.61 | > 0.59 | > 0.55 | > 0.52 | > 0.48 | > 0.44 | > 0.41 | > 0.37 | > 0.35 | > 0.32 | ||||||||||||||||||||
~ PM | 3 | > 5.02 | > 4.15 | > 4.49 | > 4.11 | > 3.99 | > 3.83 | > 3.65 | > 3.48 | > 3.27 | > 3.09 | > 2.90 | > 2.74 | > 2.60 | > 2.46 | > 2.39 | > 2.28 | ||||||||||||||||||||
~ TSP | 4 | > 7.67 | > 4.92 | > 4.49 | > 4.11 | > 3.99 | > 3.83 | > 3.65 | > 3.48 | > 3.27 | > 3.09 | > 2.90 | > 2.74 | > 2.60 | > 2.46 | > 2.39 | > 2.28 | ||||||||||||||||||||
< Liquefied Petroleum Gas - LPG | |||||||||||||||||||||||||||||||||||||
~ NH,,3,, | > | > | > | > | > 7.06 | > 7.13 | > 7.48 | > 7.87 | > 7.94 | > 8.05 | > 8.00 | > 8.01 | > 8.07 | > 7.93 | > 8.13 | > 8.19 | |||||||||||||||||||||
~ NMVOC | > | > | > | > | > 3.51 | > 3.55 | > 3.69 | > 3.84 | > 3.87 | > 3.90 | > 3.89 | > 3.90 | > 3.90 | > 3.88 | > 3.92 | > 3.95 | |||||||||||||||||||||
~ NO,,x,, | > | > | > | > | > 28.1 | > 28.4 | > 29.3 | > 30.1 | > 30.2 | > 30.3 | > 30.4 | > 29.7 | > 28.0 | > 26.3 | > 24.7 | > 23.2 | |||||||||||||||||||||
~ 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 | |||||||||||||||||||||
~ CO | > | > | > | > | > 304 | > 307 | > 321 | > 337 | > 340 | > 344 | > 342 | > 341 | > 338 | > 329 | > 329 | > 326 | |||||||||||||||||||||
~ BC | 5 | > | > | > | > | > 0.07 | > 0.07 | > 0.07 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | > 0.08 | ||||||||||||||||||||
~ PM | 3 | > | > | > | > | > 0.47 | > 0.48 | > 0.50 | > 0.52 | > 0.53 | > 0.53 | > 0.53 | > 0.53 | > 0.54 | > 0.54 | > 0.56 | > 0.57 | ||||||||||||||||||||
< Compressed Natural Gas (CNG) & Biogas | 6 | ||||||||||||||||||||||||||||||||||||
~ NH,,3,, | > | > | > | > 7.7 | > 7.7 | > 7.9 | > 8.1 | > 8.4 | > 8.4 | > 8.6 | > 8.5 | > 8.7 | > 8.5 | > 8.1 | > 8.4 | > 8.4 | |||||||||||||||||||||
~ NMVOC | > | > | > | > 0.32 | > 0.32 | > 0.32 | > 0.33 | > 0.34 | > 0.34 | > 0.35 | > 0.35 | > 0.35 | > 0.36 | > 0.37 | > 0.37 | > 0.38 | |||||||||||||||||||||
~ NO,,x,, | > | > | > | > 15.5 | > 15.5 | > 15.6 | > 15.6 | > 15.7 | > 15.5 | > 15.1 | > 14.6 | > 13.9 | > 12.9 | > 12.2 | > 11.6 | > 11.2 | |||||||||||||||||||||
~ 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 | > | > | > | > 508 | > 508 | > 506 | > 516 | > 534 | > 543 | > 554 | > 552 | > 555 | > 573 | > 579 | > 590 | > 594 | |||||||||||||||||||||
~ BC | 5 | > | > | > | > 0.17 | > 0.17 | > 0.17 | > 0.17 | > 0.18 | > 0.18 | > 0.18 | > 0.18 | > 0.18 | > 0.19 | > 0.19 | > 0.19 | > 0.19 | ||||||||||||||||||||
~ PM | 3 | > | > | > | > 1.12 | > 1.12 | > 1.12 | > 1.14 | > 1.17 | > 1.19 | > 1.21 | > 1.21 | > 1.21 | > 1.25 | > 1.26 | > 1.28 | > 1.29 | ||||||||||||||||||||
1 | |||||||||||||||||||||||||||||||||||||
2 | |||||||||||||||||||||||||||||||||||||
3 | |||||||||||||||||||||||||||||||||||||
4 | |||||||||||||||||||||||||||||||||||||
5 | |||||||||||||||||||||||||||||||||||||
6 |
–]
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 the 2019 EMEP Guidebook (EMEP/EEA, 2019) 4) have been applied. Regarding PCDD/F, a tier1 EF from (Rentz et al., 2008) 5) is used instead.
Table 3: tier1 emission factors
= | = Pb | = Cd | = Hg | = As | = Cr | = Cu | = Ni | = Se | = Zn | = B[a]P | = B[b]F | = B[k]F | = I[1,2,3-c,d]p | = PAH 1-4 | = PCDD/F | ||||||||||||||||||||||||
= | = [g/TJ] | = [mg/TJ] | = [µg/km] | ||||||||||||||||||||||||||||||||||||
~ Diesel oil | > 0.012 | > 0.001 | > 0.123 | > 0.002 | > 0.198 | > 0.133 | > 0.005 | > 0.002 | > 0.419 | > 498 | > 521 | > 275 | > 493 | > 1.788 | > | ||||||||||||||||||||||||
~ Biodiesel | 1 | > 0.013 | > 0.001 | > 0.142 | > 0.003 | > 0.228 | > 0.153 | > 0.005 | > 0.003 | > 0.483 | > 575 | > 601 | > 317 | > 569 | > 2.062 | > | |||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
~ Gasoline fuels | > 0.037 | > 0.005 | > 0.200 | > 0.007 | > 0.145 | > 0.103 | > 0.053 | > 0.005 | > 0.758 | > 96 | > 140 | > 69 | > 158 | > 464 | > | ||||||||||||||||||||||||
~ 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 | > 13.0 | > | |||||||||||||||||||||||
~ all fuels | > 0.000006 | ||||||||||||||||||||||||||||||||||||||
1 | |||||||||||||||||||||||||||||||||||||||
2 | |||||||||||||||||||||||||||||||||||||||
3 | |||||||||||||||||||||||||||||||||||||||
4 |
+ Discussion of emission trends
NFR 1.A.3.b ii is key category for NO,,x,,, PM,,2.5,,, PM,,10,, and BC.
++ Nitrogen oxides (NO,,x,,)
NO,,x,, emissions increased steadily until 2002 following the shift to diesel engines. During the last ten years, emissions decline steadily due to catalytic-converter use and engine improvements resulting from ongoing tightening of emissions laws and improved fuel quality.
gallery size="medium" : 1A3bii_EM_NOx.PNG gallery
++ Particulate matter (BC, PM,,2.5,,, PM,,10,,, and TSP)
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.
gallery size="medium" : 1A3bii_EM_PM.png gallery
+ Recalculations
Compared to submission 2019, 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 2017.
Furthermore, several re-allocations of consumption shares between the different vehicle types and classes were conducted, with the 1.A.3.b fuel totals remaining unaltered.
Table 3: Revised consumption data, in terajoules
= 1990 | = 1995 | = 2000 | = 2005 | = 2010 | = 2011 | = 2012 | = 2013 | = 2014 | = 2015 | = 2016 | = 2017 | ||||||||||||||
< Diesel oil | |||||||||||||||||||||||||
~ Submission 2020 | > 41,153 | > 89,124 | > 116,634 | > 121,822 | > 108,711 | > 111,764 | > 110,034 | > 115,424 | > 118,957 | > 126,159 | > 134,558 | > 143,170 | |||||||||||||
~ Submission 2019 | > 22,864 | > 54,127 | > 78,326 | > 88,164 | > 88,105 | > 90,229 | > 88,430 | > 91,446 | > 93,592 | > 94,263 | > 94,945 | > 96,467 | |||||||||||||
~ absolute change | > 18,289 | > 34,996 | > 38,308 | > 33,659 | > 20,606 | > 21,535 | > 21,604 | > 23,978 | > 25,365 | > 31,896 | > 39,613 | > 46,702 | |||||||||||||
~ relative change | > 80.0% | > 64.7% | > 48.9% | > 38.2% | > 23.4% | > 23.9% | > 24.4% | > 26.2% | > 27.1% | > 33.8% | > 41.7% | > 48.4% | |||||||||||||
< Biodiesel | |||||||||||||||||||||||||
~ Submission 2020 | > 0.00 | > 139 | > 1,292 | > 8,112 | > 8,273 | > 7,730 | > 7,704 | > 6,789 | > 7,248 | > 6,839 | > 7,082 | > 7,593 | |||||||||||||
~ Submission 2019 | > 0.00 | > 84 | > 868 | > 5,871 | > 6,705 | > 6,241 | > 6,192 | > 5,379 | > 5,702 | > 5,110 | > 4,997 | > 5,116 | |||||||||||||
~ absolute change | > 0.00 | > 55 | > 424 | > 2,241 | > 1,568 | > 1,490 | > 1,513 | > 1,410 | > 1,545 | > 1,729 | > 2,085 | > 2,477 | |||||||||||||
~ relative change | > 0.00 | > 64.7% | > 48.9% | > 38.2% | > 23.4% | > 23.9% | > 24.4% | > 26.2% | > 27.1% | > 33.8% | > 41.7% | > 48.4% | |||||||||||||
< Gasoline | |||||||||||||||||||||||||
~ Submission 2020 | > 31,432 | > 19,932 | > 16,561 | > 10,726 | > 6,899 | > 6,646 | > 6,117 | > 6,022 | > 5,989 | > 6,042 | > 6,145 | > 6,354 | |||||||||||||
~ Submission 2019 | > 23,875 | > 14,538 | > 13,392 | > 9,052 | > 5,510 | > 5,262 | > 4,797 | > 4,643 | > 4,571 | > 4,416 | > 4,260 | > 4,264 | |||||||||||||
~ absolute change | > 7,557 | > 5,394 | > 3,168 | > 1,674 | > 1,389 | > 1,384 | > 1,320 | > 1,379 | > 1,418 | > 1,626 | > 1,885 | > 2,090 | |||||||||||||
~ relative change | > 31.7% | > 37.1% | > 23.7% | > 18.5% | > 25.2% | > 26.3% | > 27.5% | > 29.7% | > 31.0% | > 36.8% | > 44.2% | > 49.0% | |||||||||||||
< Biogasoline | |||||||||||||||||||||||||
~ Submission 2020 | > 0.00 | > 0.00 | > 0.00 | > 74 | > 267 | > 272 | > 271 | > 258 | > 260 | > 262 | > 267 | > 268 | |||||||||||||
~ Submission 2019 | > 0.00 | > 0.00 | > 0.00 | > 62 | > 213 | > 216 | > 213 | > 199 | > 199 | > 192 | > 185 | > 182 | |||||||||||||
~ absolute change | > 0.00 | > 0.00 | > 0.00 | > 11.5 | > 53.7 | > 56.7 | > 58.5 | > 59.1 | > 61.7 | > 70.5 | > 81.9 | > 86.4 | |||||||||||||
~ relative change | > 0.00 | > 0.00 | > 0.00 | > 18.5% | > 25.2% | > 26.3% | > 27.5% | > 29.7% | > 31.0% | > 36.8% | > 44.2% | > 47.6% | |||||||||||||
< LPG | |||||||||||||||||||||||||
~ Submission 2020 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | |||||||||||||
~ Submission 2019 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 505 | > 543 | > 558 | > 577 | > 575 | > 569 | > 536 | > 469 | |||||||||||||
~ absolute change | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > -505 | > -543 | > -558 | > -577 | > -575 | > -569 | > -536 | > -469 | |||||||||||||
~ relative change | > | > | > | > | > -100% | > -100% | > -100% | > -100% | > -100% | > -100% | > -100% | > -100% | |||||||||||||
< CNG | |||||||||||||||||||||||||
~ Submission 2020 | > 0.00 | > 0.00 | > 0.00 | > 341 | > 1,218 | > 1,267 | > 1,179 | > 953 | > 981 | > 1,073 | > 858 | > 771 | |||||||||||||
~ Submission 2019 | > 0.00 | > 0.00 | > 0.00 | > 407 | > 1,314 | > 1,350 | > 1,366 | > 1,087 | > 1,101 | > 1,151 | > 883 | > 770 | |||||||||||||
~ absolute change | > 0.00 | > 0.00 | > 0.00 | > -65.7 | > -95.8 | > -82.4 | > -188 | > -133 | > -120 | > -78.2 | > -25.2 | > 0.72 | |||||||||||||
~ relative change | > 0.00 | > 0.00 | > 0.00 | > -16.1% | > -7.29% | > -6.11% | > -13.7% | > -12.3% | > -10.9% | > -6.79% | > -2.85% | > 0.09% | |||||||||||||
< Biogas | |||||||||||||||||||||||||
~ Submission 2020 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 168 | > 189 | > 247 | > 181 | > 202 | > 240 | |||||||||||||
~ Submission 2019 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 195 | > 215 | > 277 | > 194 | > 208 | > 183 | |||||||||||||
~ absolute change | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > -26.8 | > -26.4 | > -30.2 | > -13.2 | > -5.92 | > 56.7 | |||||||||||||
~ relative change | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > 0.00 | > -13.7% | > -12.3% | > -10.9% | > -6.79% | > -2.85% | > 31.0% |
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.
> For more information on recalculated emission estimates reported for Base Year and 2017, 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, im Auftrag des Umweltbundesamtes, Heidelberg & Berlin, 2019. : 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://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