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FIELD TESTING AND EVALUATION OF DUST DEPOSITION AND ...

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four heights. The root mean sum of squares (RMS) was then computed from the relative<br />

difference between the calculated velocities and the measured velocities. The sum of the<br />

RMS over all 110 intervals was used as a weighting function. The final estimate for z 0<br />

was obtained by minimizing the weighting function. Note that this method is superior to<br />

performing a regression for each 15-minute interval, since it provides a single value for z 0<br />

that is applicable to all intervals.<br />

20<br />

15<br />

DustTrak Reading (mg/m3)<br />

10<br />

5<br />

Vehicle passes by DT_1<br />

0<br />

Baseline<br />

DT_1 DT_2<br />

DT_3<br />

-5<br />

18:02:10 18:02:27 18:02:44 18:03:01 18:03:19 18:03:36 18:03:53 18:04:11<br />

Time<br />

Figure 5-2. Example of time series of DustTrak PM 10 concentrations after the passage of a vehicle on<br />

the unpaved road at Ft. Bliss. The arrows in the figure illustrate the start and stop times estimated<br />

for a baseline reading and the dust plume passing through the downwind towers DT_1, DT_2, and<br />

DT_3.<br />

The final value of 0.005 m obtained for z 0 lies between those expected for “level<br />

desert” (0.001 m) and “lawn” (0.01 m) (Seinfeld and Pandis, 1999). Figure 5-3 shows the<br />

distribution of u * values over the 111 intervals. Ninety-five percent of the values of u *<br />

fell between 10 and 50 cm/s, with values between 30 and 40 cm/s occurring most<br />

frequently (35%). Examples of how the wind speed fitted to a logarithmic vertical profile<br />

compares with the measured wind speed are given in Figure 5-4 for conditions<br />

corresponding to the lightest, most frequent, and heaviest winds observed over the 110<br />

15-minute intervals. In general, the logarithmic fit is reasonable for all cases, though the<br />

wind speed at 12.2 meters is overestimated in the case of light winds. This may be caused<br />

by small differences in the resistance to motion among the four cup anemometers used.<br />

The fact that in Figure 5-4a the measured wind speed at 12.2 meters is slightly less than<br />

that at 5.7 meters supports this hypothesis.<br />

5.1.1.1 Emission Tests<br />

Road dust emissions were created by having a test vehicle travel back and forth<br />

along the roadway for a number of passes. This ranged from a minimum of 20 to a<br />

maximum of 102. The mean number of vehicle passes was 49. The test vehicles traveled<br />

at set speeds of 16, 24, 32, 40, 48, 56, 64, 72, and 81 km/hr. Not all vehicles attained the<br />

highest speeds for safety considerations. After two passes (one heading south and one<br />

returning north) at the same speed, the vehicle speed was increased incrementally to the<br />

5-4

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