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FIELD TESTING AND EVALUATION OF DUST DEPOSITION AND ...

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In the laboratory, the deposited material was weighed then separated into four size<br />

bins (d 30 µm, 10 d < 30 µm, 3 d < 10 µm and d < 3 µm) by gravity settling in<br />

water, based on the Stokes velocity difference between various size particles (see<br />

Equation 2-4). The dry and wet fractions collected in the field were analyzed separately<br />

and the results were added to get the total mass deposited. The size-separated fractions<br />

were dried and weighed and the amount of deposition on the AV in each size range was<br />

calculated by mass balance. The gravity separation method was validated in preliminary<br />

experiments using surrogate mixtures of particles with known size and the separations of<br />

the field samples were run in duplicate after splitting the sample using a riffler. The<br />

quality of the size separations obtained from the field samples was also verified using<br />

SEM.<br />

For the artificial vegetation (AV) experiments, the deposition velocity was<br />

determined using Equation 3-2 expressed on a mass basis. The GRIMM particle number<br />

data were converted to particle mass. The amount deposited was determined from<br />

weighing the 3 d < 10 µm and d < 3 µm wet separated fractions. The deposition<br />

velocity was calculated based on the horizontal projected area of the collector outline.<br />

3.1.3 Flat Substrate Method Testing<br />

This study of field measurement of vehicle-generated dust deposition required<br />

testing to evaluate alternative procedures, materials, sampling locations, sampling times,<br />

and data analysis methods. Twenty experiments measuring particle deposition on flat<br />

substrates were collected using various locations and numbers of vehicle trips. Samples<br />

were collected 1 or 2 m above grade at 5 and 10 m from the unpaved road. In addition, a<br />

blank sample was collected 100 m upwind from the road.<br />

Four substrates were tested to determine which surface gave the best data:<br />

1. Dry Polycarbonate filters (Isopore Membrane filter, 47 mm diameter,<br />

0.2 µm GTTP, Millipore)<br />

2. Oiled Polycarbonate filters, created by spraying DOW 316 (Slipicone®<br />

316 release agent, Dow Corning Corp., Midland, MI) on the filters and drying them<br />

3. Carbon tape (Catalog # 16073®, 8 mm, Ted Pella Inc, Redding, CA)<br />

4. Double sided clear tape (Scotch ®, 3M, St. Paul, MN)<br />

3.1.4 Vegetative Method Testing<br />

Six experiments were conducted to evaluate deposition velocities by the artificial<br />

vegetation method. A combination of different distances from the road (5 and 50 meters)<br />

and different artificial vegetation substrates (Fir Garland and artificial Ivy) were used.<br />

Deposition velocity was calculated using different areas in Equation 3-2:<br />

horizontal, total and projected. The horizontal projection area was used because it<br />

compares to what Slinn used in his calculations. It measures the enhancement of removal<br />

provided by vegetation. It is also easy to measure and is applicable to flux studies. The<br />

frontal projection area of the vegetation was used since it relates to the SEM flat substrate<br />

experiments. It represents the area of direct contact with the bulk of the dust cloud. The<br />

total area represents all surfaces available for deposition. Since not all exposed surfaces<br />

3-5

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