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treasure valley road dust study: final report - ResearchGate

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400<br />

Ford Ranger on NS Road by DW1<br />

400<br />

TRAKER and HUMVEE on EW Road by DW1<br />

350<br />

EF = 20 s<br />

R 2 = 0.65<br />

350<br />

Emissions Factor (g/vkt)<br />

300<br />

250<br />

200<br />

150<br />

100<br />

Emissions Factor (g/vkt)<br />

300<br />

250<br />

200<br />

150<br />

100<br />

EF = 24 s<br />

R 2 = 0.68<br />

50<br />

50<br />

0<br />

0 2 4 6 8 10 12 14 16<br />

Vehicle Speed (mps)<br />

0<br />

0 2 4 6 8 10 12 14 16<br />

Vehicle Speed (mps)<br />

400<br />

350<br />

Ford Ranger on NS Road by DW2<br />

EF = 19 s<br />

R 2 = 0.67<br />

400<br />

350<br />

TRAKER and HUMVEE on EW Road by DW2<br />

EF = 29.0 s<br />

R 2 = 0.92<br />

300<br />

300<br />

Emissions Factor (g/vkt)<br />

250<br />

200<br />

150<br />

Emissions Factor (g/vkt)<br />

250<br />

200<br />

150<br />

100<br />

100<br />

50<br />

50<br />

0<br />

0 2 4 6 8 10 12 14 16<br />

Vehicle Speed (mps)<br />

0<br />

0 2 4 6 8 10 12 14 16<br />

Vehicle Speed (mps)<br />

Figure 3-20. Unpaved <strong>road</strong> <strong>dust</strong> emissions factors versus vehicle speed for two weight classes of vehicles. The<br />

Ford Ranger weighs ~1.5 Mg while the TRAKER and HUMVEE weigh ~3.5 to 4 Mg.<br />

The reasonable curve fits shown in Figure 3-20 indicate that the relationship between emissions<br />

factor and vehicle speed is approximately linear. This is consistent with the equation (See Eq 2-<br />

1) used to model unpaved <strong>road</strong> <strong>dust</strong> emissions in the U.S. E.P.A.’s AP-42 documentation<br />

(USEPA, 1995).<br />

3.5 Comparison of TRAKER Measurements with Flux<br />

By comparing the TRAKER signal (Eq. 1) with the emissions factors measured on the<br />

down wind towers, a calibration for the TRAKER vehicle has been developed. This calibration<br />

permits the inference of <strong>road</strong> <strong>dust</strong> emissions factors from valid TRAKER measurements.<br />

Table 3-4 shows the average TRAKER signal measurements from the unpaved <strong>road</strong> tests.<br />

The signal was calculated independently for both theright and left inlets. With the exception of<br />

the 1.4 m/s pass on the East-West test section, signals from the left and right inlets agree with<br />

each other within the limits of the measurement uncertainty. The TRAKER signal on the East -<br />

West test section was typically more than one order of magnitude higher than on the more<br />

heavily traveled North-South test section.<br />

In section 3.3.4, tests on paved <strong>road</strong>s in two separate locations indicated that the<br />

TRAKER signal increases approximately with the cube of the vehicle speed. In section 3.4, both<br />

our measurements and those used to develop the AP-42 emissions factors indicated that unpaved<br />

<strong>road</strong> emissions factors increase linearly with speed. Based on these two relationships, the<br />

emissions factor should be approximately proportional to the TRAKER signal raised to the 1/3<br />

power. That is:<br />

3-22

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