ISPRS, Vol.34, Part 2W2, “Dynamic and Multi-Dimensional GIS”, Bangkok, May 23-25, 2001
ISPRS, V
40
algorithms use different weights for the diagonal neighbors.
This study used a modified version of Sharpnack and Akin’s
method using unequal weights for the closer elevation values
(Horn, 1980) as follows,
e 5
e 2
e 6
ei
e
e 3
e 8
e 4
e 7
Fig. 2 Slope calculation from three by three window with
elevation values
Slope m =
(e 7 + 2e A + g 8 ) - (e 6 + 2e 2 + e 5 )
8 xcell size
the DEM, do not drain. These are rare in natural topography
and generally assumed to be artifacts arising due to the
discrete nature and data errors in the preparation of the DEM.
They were eliminated here using a ‘flooding’ approach. This
raised the elevation of each pit grid cell within the DEM to the
elevation of the lowest pour point on the perimeter of the pit
(Jenson and Domingue, 1988).
In most cases, the existence of pits in the DEM is explained by
numerical errors introduced in the process of interpolation of
observed values to estimate values for each grid cell. Filling the
DEM pits consists of increasing the value of the pit cells to the
level of the surrounding terrain, so that water is able to flow out
of the area. Once the pits have been filled and the flow
directions are known, the drainage area (in units of cells) is
calculated counting the number of cells located upstream of
each cell (the cell itself is not included) and, if multiplied by the
cell area, equals the drainage area.
• Contributing Area
Slope we
(g 8 +2e, +e 5 )~ (e 7 + 2e 3 + e 6 )
8 x cell size
• Flow direction
Topographic analysis required to define the hydrologic system
is based on the DEM. According to the process showed in Fig. 3,
a single downstream cell - in the direction of the steepest
descent -- was defined for each terrain cell, so that a unique
path from each cell to the basin outlet is determined. This
process produced a cell-network, with the shape of a spanning
tree, which represents the paths of the watershed flow system.
However, because a flow direction can not be determined for
cells that are lower than their surrounding neighbor cells, a
process of filling the spurious terrain pits is necessary before
the flow direction determination.
Fig. 3 Grid functions for terrain analysis for hydrologic
purposes (Francisco and David, 1999)
Pits in digital elevation data are defined as grid elements or sets
of grid elements surrounded by higher terrain that, in terms of
Upslope area (counted in terms of the number of grid cells) was
calculated for both single and multiple flow directions using a
recursive procedure that is an extension of the very efficient
recursive algorithm for single directions (Mark, 1988). The
upslope area of each grid cell is taken as its own area (one) plus
the area from upslope neighbors that have some fraction
draining to it. The flow from each cell either all drains to one
neighbor, if the angle falls along a cardinal (0, tt/2, tt, 3tt/2)
direction or diagonal (tt/4, 3tt/4, 5rr/4, 7tt/4) direction, or is on
an angle falling between the direct angle to two adjacent
neighbors. In the latter case the flow is proportioned between
these two neighbor pixels according to how close the flow
direction angle is to the direct angle to those pixels, as
illustrated in Fig. 4. Specific catchment area, is then upslope
area per unit contour length, taken here as the number of cells
times grid cell size (cell area divided by cell size). This assumes
that grid cell size is the effective contour length, in the definition
of specific catchment area (Fig. 4) and does not distinguish any
difference in contour length dependent upon the flow direction.
For shallow lateral subsurface flow follows topographic
gradients, this implies that the contributing area to flow at any
point is given by the specific catchment area defined from the
surface topography.
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