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Calibration of a Terrestrial Laser Scanner - Institute of Geodesy and ...

Calibration of a Terrestrial Laser Scanner - Institute of Geodesy and ...

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112 6. Applications <strong>of</strong> <strong>Terrestrial</strong> <strong>Laser</strong> ScanningFigure 6.4: Inlet gutter <strong>and</strong> vegetated road shoulder (left), watershed <strong>and</strong> initially assumed catchment area (right).Flow direction due to preferential flowbeneath the road is indicated.In the pilot plant, the road run<strong>of</strong>f was collected in a storage tank using a 0 5 m long gutter located directlybeneath the road. The volume was read periodically, cf. Figure 6.4, left.The rainfall height was measuredat a distance <strong>of</strong> 6m from the road. The first calculations for a catchment area <strong>of</strong> 15m2, 0 5m gutter lengthtimes 3 m road width, were not meaningful because too much water was collected in the sampling tankrelative to the road surface <strong>of</strong> 15 m2. The catchment area must be much largerthan assumed. This wouldbe the case if the road would have a slight slope in the longitudinal direction or other effects would occur,such as preferential flow.In order to assess the latter, simple tracer experimentswere conducted. Theserevealed significant water flow from the area adjacent to the road into the inlet gutter <strong>of</strong> the water storagetank. The length <strong>of</strong> this section is 2 5 m to 3 5 m <strong>and</strong> the watershed can be located within a range <strong>of</strong> 1 m,cf. Figure 6.4, right. Although this tracer experiment answered the question that there is some preferentialflow, the question<strong>of</strong> the size <strong>of</strong> the catchment area is still unsolved.Calculation <strong>of</strong> Catchment AreasThe catchment area was calculated by using the noise-reduced <strong>and</strong> geo-referenced laser scanning data.Based on these data, a grid with a sampling interval <strong>of</strong> 8 cm, the streams leaving the road, cf. Figure 6.5,as well as the different catchment areas for the inlet gutter, cf. Figure 6.6, were derived. These calculationsshowed that water flow is almost perpendicular to the road alignment. In addition, sensitivity analysesshowed the point density for deriving the grid is sufficient <strong>and</strong> a decreased point spacing <strong>of</strong> the grid doesnot significantlyaffect the size <strong>of</strong> the different catchment areas.As measured by the tracer experiments, the assumed location <strong>of</strong> the watershed lies within a range <strong>of</strong> about1 m. Based on the coloured tracer experiment it was not possible to estimate the watershed more accurately.For this reason, it was assumed that the watershed is located in the middle <strong>of</strong> the range at 0 5 m. Conse¬quently,in Figure 6.6.the two different catchment areas number 1<strong>and</strong> 2 lead to the catchment area <strong>of</strong> 14 1 m2, as shownBased on the catchment area <strong>of</strong> 14 1 m2, the maximal run<strong>of</strong>f was calculated <strong>and</strong> was compared with the col¬lected road run<strong>of</strong>f. As a result, 36 % <strong>of</strong> the maximal run<strong>of</strong>f drains directly into the storagetank <strong>and</strong> thereforewould infiltrate into the vegetated road shoulder. The other 64 % <strong>of</strong> the road run<strong>of</strong>f are dispersed mostlythrough diffusion within a distance <strong>of</strong> the road <strong>of</strong> 25 m [Steiner et al., 2005]. As the heavybe assumed to be nearly proportional to the water flow, about 36 % <strong>of</strong> the pollutantmetal load canload in the road run<strong>of</strong>finfiltrate the vegetated road shoulder directly below the road. During infiltration, many pollutantssuch asheavy metals <strong>and</strong> organic substances are accumulated. Thus, accumulation results in a high concentration

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