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1.A.3.b vi - Road Transport: Automobile Tyre and Brake Wear
Short description
In sub-categories 1.A.3.b vi - Road transport: Automobile tyre and brake wear emissions from automobile tyre and brake wear in RT are reported. Therefore, these sub-category is an important source for a) particle emissions and b) emissions of heavy metals, POPs etc. included in these particles.
Category Code | Method | AD | EF |
---|---|---|---|
1.A.3.b vi | T1, T3 | NS, M | CS |
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NOx | NMVOC | SO2 | NH3 | PM2.5 | PM10 | TSP | BC | CO | Pb | Cd | Hg | As | Cr | Cu | Ni | Se | Zn | PCDD/F | B(a)P | B(b)F | B(k)F | I(x)P | PAH1-4 | HCB | PCBs |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
NA | NA | NA | NA | L/- | L/- | L/- | L/- | NA | L/- | -/- | NA | L/- | L/- | L/T | -/- | L/- | L/T | NA | -/- | -/- | NE | -/- | -/- | NA | NA |
|
Methodology
Activity data
Abrasive emissions from tyre and brake wear are estimated based on vehicle-type specific mileage data.
For detailed mileage data, please see superordinate chapter on abrasive emissions from road vehicles.
Emission factors
Table 1: Emission factors applied
Tyre Wear | Brake Wear | ||||||||||||
PCs | LDVs | HDVs | Buses | Mopeds | Motorcycles | PCs | LDVs | HDVs | Buses | Mopeds | Motorcycles | ||
BC | [mg/km] | 1.07 | 1.69 | 4.50 | 4.50 | 0.55 | 0.55 | 0.75 | 1.17 | 3.27 | 3.27 | 0.44 | 0.44 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
PM2.5 | 4.49 | 7.10 | 18.9 | 18.9 | 1.93 | 1.93 | 2.93 | 4.56 | 12.7 | 12.7 | 1.44 | 1.44 | |
PM10 | 6.40 | 10.1 | 27.0 | 24.3 | 2.80 | 2.80 | 7.35 | 11.5 | 32.0 | 28.8 | 3.63 | 3.63 | |
TSP | 10.7 | 16.9 | 45.0 | 45.0 | 4.60 | 4.60 | 7.50 | 11.7 | 32.7 | 32.7 | 3.70 | 3.7 | |
Pb | [µg/km] | 1.88 | 2.97 | 4.26 | 3.10 | 0.81 | 0.81 | 45.5 | 71.0 | 199 | 199 | 22.5 | 22.5 |
Hg | NA | ||||||||||||
Cd | 0.05 | 0.08 | 0.11 | 0.08 | 0.02 | 0.02 | 0.17 | 0.26 | 0.73 | 0.73 | 0.08 | 0.08 | |
As | 0.04 | 0.06 | 0.09 | 0.07 | 0.02 | 0.02 | 0.51 | 0.79 | 2.21 | 2.21 | 0.25 | 0.25 | |
Cr | 0.26 | 0.40 | 0.58 | 0.42 | 0.11 | 0.11 | 17.3 | 27.0 | 75.7 | 75.7 | 8.55 | 8.55 | |
Cu | 1.86 | 2.94 | 4.21 | 3.06 | 0.80 | 0.80 | 383 | 598 | 1674 | 1674 | 189 | 189 | |
Ni | 0.32 | 0.51 | 0.72 | 0.53 | 0.14 | 0.14 | 2.45 | 3.83 | 10.71 | 10.71 | 1.21 | 1.21 | |
Se | 0.21 | 0.34 | 0.48 | 0.35 | 0.09 | 0.09 | 0.15 | 0.23 | 0.66 | 0.66 | 0.07 | 0.07 | |
Zn | 79.5 | 126 | 180 | 131 | 34.2 | 34.2 | 65.1 | 102 | 284 | 284 | 32.1 | 32.1 | |
B[a]P | 0.032 | 0.049 | 0.134 | 0.120 | 0.013 | 0.013 | NA | ||||||
B[b]F | 0.038 | 0.063 | 0.161 | 0.144 | 0.019 | 0.019 | |||||||
B[k]F | 0 | 0 | 0 | 0 | 0 | 0 | |||||||
I[..]P | 0.019 | 0.028 | 0.082 | 0.072 | 0.006 | 0.006 | |||||||
∑ PAHs 1-4 | 0.090 | 0.140 | 0.379 | 0.336 | 0.038 | 0.038 |
Discussion of emission trends
(emissions from wear/abrasion only; no fuel combustion included)
Table 2: Outcome of Key Category Analysis
for: | BC | PM2.5 | PM10 | TSP |
---|---|---|---|---|
by: | L/- | L/- | L/- | L/- |
All reported emissions from tyre and brake wear are linked directly to the mileage driven by the road vehicles covered.
Here, after a moderate decrease during the Covid-19 pandemic, mileage related abrasive emissions show a slow recovery not yet reaching pre-pandemic levels again.
Whereas annual copper emissions result almost entirely from the wear of (disc) brakes…
…zinc emissions result from both tyre and brake wear with high amounts of zinc used in tyre rubber and drum brakes applied in trucks (heayv loads) and buses (stop-and-go).
Recalculations
With all input data remaining unrevised, no recalculations were made compared to the previous submission.
Planned improvements
Besides a routine revision of the underlying model, no specific improvements are planned.