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FIELD TESTING AND EVALUATION OF DUST DEPOSITION AND ...

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situations. Some of these limitations are listed here with a detailed discussion given in a<br />

later section.<br />

1. If the flux through the ceiling above the road dm ceil /dt is not negligible. This<br />

implies that the thickness of the first layer of a regional air quality model is<br />

important to the transport of dust.<br />

2. If the flux upwind of the road dm ambin /dt is not negligible compared to the flux<br />

from the road. If the flux upwind from a source is not negligible, a regional<br />

model must accommodate carrying the dust from upwind to downwind.<br />

3. If the approximation of a well mixed dust concentration from the ground to the<br />

top of the control volume is not a good description of the natural situation.<br />

4. If the assignment of the flux through the ceiling of the control volume as KC(x) is<br />

different from the diffusion taking place in the natural situation.<br />

5. If the assignment of the deposition as V d C(x) is different from the deposition<br />

taking place in the natural situation.<br />

6. If steady state conditions not observed.<br />

7. If the downwind flux dm ambout /dt is not of the order of dm ambin /dt within a few<br />

hundred meters to a kilometer, the result of the model would not be applicable to<br />

most regional scale regional models. Since the grid-scale of regional models is of<br />

the order of a kilometer, dm ambout /dt should be of the order of dm ambin /dt within a<br />

few hundred meters. The downwind flux equilibration distance may vary<br />

depending on local surface variables. This may have some implications for the<br />

minimum spatial resolution of a regional dust transport model. Perhaps in<br />

modeling, the distance could be varied as a function of the soil and vegetative<br />

cover—which in turn implies the need of good geographic data bases of such<br />

information.<br />

8. The analysis above was done for the wind perpendicular to the road. For wind at<br />

an angle to but not parallel the road, the analysis would be almost the same, but<br />

with a wider “effective road width.” For an infinitely long road parallel to the<br />

wind, however, the assumptions of the analysis would be violated and the solution<br />

would not be useful<br />

4.1.3.2a<br />

Weaknesses of the Box Model<br />

1. The model continues to pass dust mass through the CV ceiling even though realworld<br />

situations exist where no vertical flux takes place or there is vertical flux<br />

from above the ceiling into the CV.<br />

2. The model assumes dust to be well mixed in the control volume even though there<br />

are situations where dust continues to lie close to the ground (possibly caused by<br />

atmospheric stratification.)<br />

4.2 Inter-comparison of the ADE, ISC3, and the Gillette Box Model<br />

Since the model Gillette has proposed is mechanistically different from the ADE<br />

and the ISC3, we begin with a discussion of the assumptions in the Box Model.<br />

Modeling results from the ADE and the ISC3 are then compared with those obtained<br />

from the Box Model. Note that except were noted, all simulations for deposition apply to<br />

particles with aerodynamic diameters of 8 µm. PM 10 is the mass of all particles with<br />

4-10

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