Fig.1. Schematic of the Tokyo Vehicle NOx Emission Model. (From Murdock, 1996)
Table 1 Initial Conditions for the Tokyo Vehicle NOx Emission Model**
Parameter | Model Value for 1990* |
Calc'd Value for 1995 |
Model Value for 1995 |
Units |
Population | 11.86 | 11.97 | 11.77 | million people |
Vehicle Fleet | 4.529 | 4.965 | 4.617 | million vehicles |
Vehicle Ownership | 0.382 | 0.415 | 0.392 | veh/cap |
Annual Traffic | 50.51 | 53.12 | 51.55 | 109 v-km/yr |
Mean Vehicle Activity | 11,150 | 11,153 | 11,165 | km/v-yr |
Mean Gasoline E.F. | 0.602 | 0.500 | 0.254 | g NOx /km |
Mean Diesel E.F. | 3.990 | 3.168 | 2.099 | g NOx /km |
Total NOx Emission | 52.2 | 51.2 | 51.6 | kt/yr |
Vehicle Fraction | 71 | 71 | 67 | percent |
Mean Roadside Conc. | 0.041 | 0.041 | 0.042 | ppm |
* adapted from Kruger, et al., 1998. ** data from BEP-TMG, 1994,6,7 |
Table 2 Traffic Activity and Weighted Mean Emission Factors by Fuel Type*
Fuel | Traffic 1994 |
Mean 1995 EF |
Extrapolated Emission Factors |
Estimated EF |
|||
Type | (109 vkm/y) | (25km/h) | 2000 | 2005 | 2010 | 2020 | |
Gasoline | |||||||
small car | 1.69 | 0.161 | 0.161 | 0.161 | 0.161 | 0.161 | |
regular car | 25.59 | 0.183 | 0.183 | 0.183 | 0.183 | 0.183 | |
light truck | 3.48 | 0.482 | 0.419 | 0.419 | 0.419 | 0.419 | |
small truck | 0.63 | 1.417 | 1.093 | 0.850 | 0.850 | 0.850 | |
vans | 2.79 | 0.561 | 0.463 | 0.380 | 0.380 | 0.380 | |
special truck | 0.02 | 3.007 | 2.326 | 1.863 | 1.799 | 1.799 | |
LPG car | 4.96 | 0.161 | 0.161 | 0.161 | 0.161 | 0.161 | |
Total (%) | 39.16 (76%) | ||||||
Model Mean | 0.254 | 0.236 | 0.226 | 0.226 | 0.226 | ||
Diesel | |||||||
bus | 0.37 | 5.857 | 4.510 | 3.601 | 3.366 | 3.366 | |
regular car | 2.53 | 0.183 | 0.183 | 0.183 | 0.183 | 0.183 | |
small truck | 2.87 | 1.417 | 1.093 | 0.850 | 0.850 | 0.850 | |
vans | 2.20 | 0.561 | 0.463 | 0.380 | 0.380 | 0.380 | |
regular truck | 3.83 | 4.257 | 3.264 | 2.661 | 2.590 | 2.590 | |
special truck | 0.59 | 3.007 | 2.326 | 1.863 | 1.799 | 1.799 | |
Total (%) | 12.39 (24%) | ||||||
Model Mean | 2.099 | 1.627 | 1.321 | 1.228 | 1.228 | ||
*based data from BEP-TMG (1996) |
Fig. 2. Potential growth in the number of HZEVs in the Tokyo vehicle fleet.
Fig. 3. Potential reduction in NOx emission as a function of HZEV growth rate.
Fig. 4. Forecast of NOx concentration at roadside monitoring stations.