ISPRS Commission III, Vol.34, Part 3A „Photogrammetric Computer Vision“, Graz, 2002
Statistical analyses have shown that the laser-derived predicted
top heights describe 72 % of the variability of timber volume in
forest inventory data (R square = 0.72). The corresponding
standard error obtained amounts to 76 m? / ha. Typically, stand-
wise inventories of the most important forest parameters are
carried out with an error of about 15 % (in this case 55 m? / ha
for timber volume). This error affects the obtained R square and
standard error and thus the outcome of the previous analysis.
Assuming that these two errors (predicted timber volume and
timber volume derived from forest inventories) are independent
of each other, the corrected laser-based error can be estimated
by taking the root of the difference of the squared errors, de-
noted by s,
sz 767557
which is even slightly better than the error of the conventional
forest inventory (s = 52.5 m? / ha).
Conclusion
In summary this study demonstrates the feasibility of using laser
scanner data for the stand-wise assessment of timber volume for
forest inventories.
4.2 Method and Results of the Tree-wise approach
Different image processing steps are necessary in order to de-
rive the tree wise parameters listed in Chapter 2. The methods
described in the following section are suitable especially for
conical-shaped coniferous trees, as it was developed for the
Alpine Hohentauern test site.
4.2.1 Processing line for segmentation
In the following the whole processing chain is explained, start-
ing with the tree height image and ending with a segmented
image, where each homogenous region represents a single tree.
Figure 4 depicts the working steps for segmentation (Ziegler et
al. 2000). The basis for these processing steps are first pulse
data which are resampled to a grid of 25 cm resolution and the
forest floor model described in Chapter 2.
Inverting R
Threshold Watershed
segmentaion
Smoothing
Maxima Auto-scale
detector selection
Tree Crown
height area
image segments
Figure 4: Working steps for single tree segmentation
Threshold filter
Most forests are a conglomerate of large trees, young trees,
bushes, grasses and other undergrowth. But the main interest of
forest economists is focused on large trees representing the
major part of timber volume, while young trees and under-
growth are only of minor interest for timber volume assessment.
Therefore, all pixel values representing heights less than a
certain threshold (6 m in this case) were not taken into account
for further processing. Another reason for neglecting these
small trees was that they mostly stand close together and thus
cannot easily be segmented. Although the spatial resolution of
the TopoSys laser scanner is higher than provided by other
systems, it is not high enough to capture every single crown.
Smoothing filter
In order to obtain optimal results for “tree top detection”
(maxima detector) and “crown diameter” (watershed segmenta-
tion)” each single tree should be represented by a blob with one
single intensity maximum at the position of the tree top. Opti-
mally, the gray values should decrease with the distance from
the top. Looking at geometrical models of some tree species
derived by ground measurements, one can see that most trees,
especially conical-shaped coniferous trees, come close to this
ideal shape. Nevertheless, as laser scanning data represent the
“real situation”, one single tree crown can be represented by
two or more intensity maxima and, thus, single trees do not
appear as compact blobs. This smoothing step was introduced to
eliminate smaller peaks and to approximate the height image to
the ideal model. Because of its unique properties a Gaussian
Kernel was chosen for the smoothing task. One of the advan-
tages of this filter, which was very important for this applica-
tion, is that Gaussian smoothing does not produce new extrema
when increasing the smoothing scale. In spite of the good per-
formance of the filter applied, single branches sometimes cause
local maxima even after smoothing. This circumstance must be
taken into account in the subsequent processing steps. Further
information about continuous discrete Gaussian smoothing
kernels, their properties and the setting of kernel parameters can
be found at Lindeberg (1993 and 1994).
Maxima detector and auto-scale selection
After smoothing, coniferous trees mostly show a characteristic
tip at the top of the tree. This is true if the local gray value
maxima within the data image can be interpreted as tree tops.
Local maxima must be interpreted carefully (see auto-scale
selection), since they are caused not only by tree tops but also
by the single branches remaining after filtering.
Maxima are localized by means of a maxima detector in a first
step. As tree crowns can present more than one local maximum
and each maximum would produce one segment in the subse-
quent watershed segmentation process, the number of tree tops
would be overestimated and large crowns would be split into
several segments. Hence, each detected maximum must be
reviewed. Assuming that single crowns appear as blobs with a
gray value maximum in the center and decreasing gray values
towards the edge, diameter and significance can be assessed for
blobs by means of a scale-space approach (Lindeberg 1994,
Roerdink & Meijster 1999). This algorithm searches within a
predicted range of blob diameters of typically 1m to 10m for
maximum responses. The resulting blob diameter (ideally pre-
senting a single crown) is then determined by the maximum
significance of all potential crowns.
The detection of blob diameters allows single crowns to be
identified in most cases. Errors are caused, if crown density is
very high (case 1), if larger crowns shadow smaller trees (case
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