OMIT Manual for environmental calculation of international freight transport Enclosure AEnclosure A.1
|
Tons cargo |
EU 0 |
EU 1-4 |
1 |
9.4894 |
9.3491 |
2 |
9.6988 |
9.5554 |
3 |
9.9082 |
9.7617 |
4 |
10.1176 |
9.968 |
5 |
10.327 |
10.1743 |
6 |
10.5364 |
10.3806 |
7 |
10.7458 |
10.5869 |
8 |
10.9552 |
10.7932 |
9 |
11.1646 |
10.9995 |
10 |
11.374 |
11.2058 |
11 |
11.5834 |
11.4121 |
12 |
11.7928 |
11.6184 |
13 |
12.0022 |
11.8247 |
14 |
12.2116 |
12.031 |
15 |
12.421 |
12.2373 |
16 |
12.6304 |
12.4436 |
17 |
12.8398 |
12.6499 |
18 |
13.0492 |
12.8562 |
19 |
13.2586 |
13.0625 |
20 |
13.468 |
13.2688 |
21 |
13.6774 |
13.4751 |
22 |
13.8868 |
13.6814 |
23 |
14.0962 |
13.8877 |
24 |
14.3056 |
14.094 |
25 |
14.515 |
14.3003 |
26 |
14.7244 |
14.5066 |
27 |
14.9338 |
14.7129 |
28 |
15.1432 |
14.9192 |
The emissions depend on the cargo on the truck. They are load dependant and are thus
calculated on the basis of the consumption measured as MJ/km. Table 2 shows an example of
the basis of the formula for an EURO 2 engine.
Table 2.
Formula for EURO II truck.
EURO II |
|
|
|
MJ per km as a function of cargo weight in tons |
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Y = 9.1428 (MJ/km) + 0.2063 (MJ/tkm)*X (tons) |
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|
|
|
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g/km as a function of MJ/km Y = a*X + b*X^c |
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|
a (g/MJ) |
b (g/MJ) |
c |
CO2 |
73.3 |
0 |
1 |
SO2 |
0.0024 |
0 |
1 |
CO |
0 |
0.3411 |
0.4652 |
HC |
0 |
0.3398 |
0.1488 |
PM10 |
0 |
0.1186 |
0.2382 |
NOx |
0 |
0.8743 |
0.9489 |
Table 3.
Calculation requirements in TEMA2000.
Fuel |
Low-sulphur |
Travel speed, motorways outside urban areas |
80 |
Travel speed, other ways outside urban areas |
70 |
Share of trip, motorways outside urban areas |
90 |
Share of trip, other ways outside urban areas |
10 |
Travel speed in km/h - Share of trip in %.
In order to maintain OMIT as an operational tool, a number of the parameters in TEMA2000 have been set on default values. Table 3 shows the parameters used in OMIT for international transport.
There is an option for using different kinds of waste gas cleaning. These influence the emissions as showed in table 4.
Table 4.
Multiplication factor for waste gas technologies.
|
PM 10 |
NOx |
CO |
Oxid. kat |
0.81 |
0.95 |
0.1 |
Kat+filter |
0.06 |
0.95 |
0.1 |
Finally it may be useful to include a short pre- or end haulage in OMIT, rather than
calculating it separately. As the different engines have different emission profiles, it
will cause an error. The energy consumption, however, will be correct, if you take basis
in the realised km/l and distribute the emissions on the goods, which follow the model for
the 40 tons trucks.
Hence the energy consumption and emissions are distributed on the goods by its share of the average goods weight or when voluminous goods, by the share of the transported volume. The calculation includes all driven km, and if the method is used for transported goods, all emissions and the energy consumption from the actual truck will be distributed on the goods. (Nothing will be "forgotten").
You can get an idea of the error by using the mentioned method and look at table 5, where data for 40 tons is compared with distribution trucks from TEMA2000.
Table 5.
Deviation in % per ton goods for distribution trucks from TEMA2000 for
calculation in OMIT based on diesel consumption data and the used standard export truck
and driving pattern.
truck type |
capacity utilisation |
tons cargo |
Energy con- |
SO2 |
CO2 |
CO |
HC |
NOx |
PM10 |
25 t |
50 % |
8,5 |
0 |
0 |
0 |
19 |
27 |
0 |
29 |
10 t |
50 % |
2,6 |
0 |
0 |
0 |
48 |
64 |
3 |
62 |
As shown in table 5 there is no deviation for the direct diesel dependant components as
energy consumption, SO2, and CO2. For the other components the deviations vary between 0
and 64%, mostly for a 10 tons truck. Thus it also appears that this approximate method can
only be applied, when it is a matter of a limited part of the total transport.
Standard values for driving without load are 9%, EURO-norm is 1.5 and the average cargo weight of 16 tons is based on Danmarks Statistik, 2001:20.
Padborg, 2001.