Terrestrial laser scanning as a tool for assessing tree growth

Author
Jonathan Sheppard ⁽¹⁾, Christopher Morhart ⁽¹⁾, Jan Hackenberg ^(1-2-3), Heinrich Spiecker ⁽¹⁾

Abstract:

 Terrestrial laser scanning (TLS) technology is a powerful tool for assessing tree growth based on time series analysis, as it allows a level of scrutiny not achievable using established destructive techniques. We applied TLS technology to 21 wild cherry trees grown in a research plot near Breisach (southern Germany) in order to build quantitative structure models (QSMs) for each tree. Scans were carried out over three subsequent years (2012-2014), so that three QSMs per each tree were constructed. Using the above approach, we were able to assess the annual growth of the individual wild cherry trees in terms of diameter and height, stem and branch volume, and the merchantable timber fraction. In addition, the growth of single branches of sample trees was detected and quantified. The availability of QSMs based on TLS-derived data allowed the accurate determination of crown length and width, as well as the volume reduction as the result of the tree pruning applied after the first scan (2012). The aboveground biomass (AGB) was assessed for each tree based on the QSM-derived volume and published wood density values for wild cherry, and then compared with AGB values estimated with standard allometric methods, obtaining a very high correlation (r²_adj = 0.941). We concluded that the proposed approach is an effective non-destructive technique to accurately assess the increase of tree biomass, and discuss its future application in the forestry sector.

   

Introduction 

Since the beginning of the last decade, terrestrial laser scanning (TLS) has been applied in forestry with the aim of estimating tree physical parameters ([3], [14], [33]). Eysn et al. ([11]) and Dassot et al. ([10]) proposed methods which rely on heavy manual interaction with the scan data to derive geometrical tree models, including (in part) the branching structure. Recently, more advanced methods have been proposed to build fully automatic, highly accurate and complete tree models (from the tree root collar to its tip), based on cylinders as geometric building blocks ([18], [36], [15]). Each cylinder is characterised by the spatial information concerning itself and the neighbouring cylinders (including its growth direction), so that sequential cylinders can be followed from root collar to tip. The resulting models are referred to as quantitative structure models (QSM). QSMs allow for the analysis of volume distribution within a single tree (e.g., see [8]). QSMs can also be produced from TLS point clouds obtained from trees under leaf-on conditions by applying appropriate de-noising procedures ([6], [17]). However, QSMs using alternative geometrical methodology have been proposed, e.g., based on ellipses ([1]). The use of building blocks other than cylinders was investigated by Akerblom et al. ([2]).

Comprehensive literature reviews concerning the application of TLS in forestry have already been published ([26], [37], [47], [48], [32], [25]). Recent developments have explored the detection of merchantable wood volume ([10]) and residual biomass after the extraction of the merchantable timber ([12]). Indeed, TLS provides highly detailed information on many tree parameters with a resolution that is unfeasible by conventional field methods. For example, Moorthy et al. ([29]), Bayer et al. ([5]) and Metz et al. ([28]) have evaluated the crown properties of selected species, the latter applying this technique for assessing the aboveground intra- and inter-specific competition and its effects on tree growth. Thies et al. ([44]) and Liang et al. ([24]) assessed stem taper, while Kretschmer et al. ([22]) applied the TLS methodology for the detection of branch scars as an indication of internal wood quality.

Empirical time series analysis of tree growth has been previously carried out for the assessment of biomass in poplar (Populus spp.) plantations ([27]). Case-study analysis of plot-level biomass changes using temporal repeated scans has also been performed ([23], [43]). Such approaches rely on statistical modelling of the aboveground biomass using traditional tree parameters such as DBH and tree height as input variables ([7]). To date, the application of TLS methodology to time series analysis has been limited. Time series analysis can be performed by scanning the same tree or groups of trees over time. For example, Kaasalainen et al. ([20]) have been able to detect branch extension and bole diameter increase of a single tree by carrying out five repeat scans over three subsequent years. Van Laar & Akça ([46]) stated that the age, stem diameter and form, basal area, total and merchantable height and volume are important single-tree characteristics that can be used to infer information about the growth of single trees, and consequently the growth of the wider stand; all of these attributes can be deduced from TLS data point clouds . Stem growth and crown development are intrinsically linked ([4]). Important parameters such as crown projection area, crown width and crown length can be efficiently quantified using the TLS methodology.

The application of precise measurement of standing volume may allow the quantification of wood products. Veneer production is a major product of the high-quality wild cherry (Prunus avium L.) timber. Production goals for such a product stipulate branch free log lengths free of defects. However, wild cherry do not self-prune well ([35]) as shaded branches quickly die, often leading to the formation of dead knots which are detrimental to wood quality and can be the starting point of wood decay caused by fungi ([41]). Therefore, to obtain high quality butt logs artificial pruning is necessary ([45]), removing branches before they reach a maximum diameter of 2.5 cm ([40]). The classical pruning treatment provides branch removal up to a defined height, while selective pruning removes only only large diameter branches from the entire length of the potential veneer log, as well as small branches that form steep angles with the stem ([42]). All remaining branches continue to contribute to tree growth, and they will eventually be pruned in the following years. The average annual diameter increment is significantly lower when intensive conventional pruning is applied (leaving only the top 3 whorls intact) as compared with intensive selective pruning ([42]).

Annual scans of the same tree can reveal detailed information which can be used to estimate the growth rate of both tree stem and crown. Moreover, such an approach provides a powerful tool to evaluate the effectiveness of silvicultural management interventions such as pruning or thinning. The aim of this paper is to present an example of the application of TLS technology to the forestry sector.

    

Materials and methods 

The studied trees were located at a agroforestry research plot close to Breisach, southern Germany (48° 4′ 24″ N, 7° 35′ 26″ E - 182 m a.s.l.). Site conditions, climate and growth of wild cherry in this area are comprehensively described by Morhart et al. ([31]). Twenty-one wild cherry trees planted in 1997 as two year old saplings have been scanned in late 2012, 2013, and 2014 under leafless conditions. A terrestrial laser scanner (Imager 5006^®, Zoller and Frohlich GmbH, Germany) was used for the 2012 scanning campaign and a second scanner (Imager 5010^®) for the 2013 and 2014 campaigns. Technical specifications and data acquisition parameters are given in Tab. 1. Scan points were marked with durable permanent markers to ensure that the scanner was located in the same position between years. All scans were conducted using the multi-scan mode described by Liang et al. ([25]) to provide a high-resolution point cloud data and minimize the occlusion, ensuring between five and seven scan points per tree group. A map of the scanning positions within the study plot is reported in Fig. 1. Scanned areas were targeted with laminated Z+F paper targets (Zoller and Frohlich GmbH, Germany). The site was cleared of annual understory vegetation. All the scans were undertaken on days without precipitation and wind to ensure high-quality capture.

Tab. 1 - Laser scanner technical specifications and data acquisition parameters.

Parameter	Year of scan campaign
	2012	2013 & 2014
Scanner model	Z+F Imager 5006	Z+F Imager 5010
Field of view	310° × 360°	320° × 360°
Beam diameter	3.0 mm (1.0m distance)	~3.5 mm (0.1m distance)
Beam divergence	0.22 mrad	<0.3 mrad
Range	79 m	187.3 m
Accuracy (horizontal x vertical)	0.007° rms × 0.007° rms	0.007° rms × 0.007° rms
Resolution range	0.1 mm	0.1 mm
Resolution (horizontal + vertical)	10.000 pixel/360°	10.000 pixel/360°

Enlarge/Reduce

Fig. 1 - Tree pruning variants and TLS scanning positions within the Breisach agroforestry research plot.

Enlarge/Shrink Full Size

Three groups of trees were analysed within the study plot, each group grown under a specific management regime: (i) an unpruned control variant (N, n=3) and (ii) a pruned variant (P, n=13), where pruning regimes of differing intensities and techniques were carried out during a single intervention in 2007 (see [42] for more details); (iii) a pruned crop tree variant (Z, n=5) encompassing trees pruned in 2007 and 2010, followed by a final pruning treatment to a height of approximately 6 m during late spring 2013. The position on the ground of all scanned trees is also reported in Fig. 1.

Point clouds belonging to the same tree-group were co-referenced and placed into a common coordinate system using the software LaserControl^® (Zoller and Frohlich GmbH, Germany). Individual trees were cut out of the raw point cloud with the LaserControl software, and then exported in ASCII format. All further processing was performed using the open-source software tool “SimpleTree” ([16]) based on the method proposed by Hackenberg et al. ([15]) which relies on the Point Cloud Library (PCL - [38]). Ghost points were removed with the statistical outlier removal tool. The trees were isolated by Euclidean clustering and (when needed) by manually including artificial gaps with the crop sphere tool.

The QSMs for the studied trees were built through the following steps. To follow the branching structure of a tree, a sphere centered on the tree skeleton with a radius larger than that of the underlying branch segment was used to extract the sub point cloud on the sphere surface. This sub cloud included the circular structures representing the cross sectional areas of the underlying branch (or branches in the location of branch junctions) into which a circle / number of circles were fitted with the random sample consensus (RANSAC) algorithm ([13]). The sphere center served as a start point of a finite cylinder, the circle center as the end point and the circle radius as the radius of the preliminary detected cylinder. Fitting to the cylinders was improved during the post-processing with a RANSAC implementation. The automatic parameter search proposed in Hackenberg et al. ([17]) was used to ensure complete models and an allometric correction procedure to prevent overestimated twig cylinders ([16], [17]).

Cylinder radius outputs were grouped in diameter classes (DC) during data analysis, so that DC1 included diameters in the range 0-1 cm, DC2 included 1-2 cm diameters, and so forth. Branch angles were calculated by the conversion of Cartesian coordinates [x, y, z] to a spherical coordinate system [ρ, θ, φ], where ρ is the distance of a point from the origin (here the branch origin on the stem), θ is the azimuthal angle and φ is the zenith angle (hereafter branch angle), which was obtained as follows (eqn. 1):

ϕ=tan−1x2+y2−−−−−−√z(1)$$\begin{array}{}\text{(1)}& \varphi ta{n}^1\frac{\sqrt{x^2{y}^2}}{z}\end{array}$$

Branch angles were determined from the coordinates of the cylinders located within the first 50 cm of the main (1^storder) branch, since branch tips could not be used as reference points due to an observed downward movement over time.

The aboveground woody biomass (AGB) of trees was estimated based on the volume derived from TLS data and the homogenised wood density value for wild cherry (0.474 g cm^-3) proposed by Chave et al. ([9]) and Zanne et al. ([50]). Such estimates were compared with those obtained using the allometric function set up for the same site and species by Morhart et al. ([31] - eqn. 2):

AGB=0.109⋅(d1.3)2.45(2)$$\begin{array}{}\text{(2)}& AGB0.109d_{1.3}{}^{2.45}\end{array}$$

    

Results and discussion 

TLS methodology for time series analysis allows a greater level of scrutiny compared to manual forest mensuration. The accuracy of the method applied here has been previously proven by comparing destructive field measurements with those obtained by a simple tree algorithm model ([15], [16], [17]). In this work, we applied a multi-scan methodology to individual trees; however, its extension to assess growth at the stand level is straightforward.

Fig. 2 shows the cylinder models (QSMs) obtained by laser-scanning a sample crop tree (Z) at the plot site in the three consecutive years. The tree was pruned in late spring between the first and second scan, as it can be noticed from the absence of pruned branches in the following years. The increase in tree height and the development of the crown was evident across the three study years.

Fig. 2 - Fig. 2 - Virtual representation (QSM model) of the growth and treatment effects on a pruned crop tree using TLS-derived data over three scan years. Colours represent the diameter class (DC) of the modelled cylinders (red: small DCs; yellow: intermediate DCs; green: large DCs). Colours and scale are consistent across years. The represented tree was pruned to a height of 6 m after the first scan (2012).

Enlarge/Shrink Full Size

The basic tree parameters for each tree and year could be extracted based on the obtained cylinder model. The main structural parameters, such as the diameter at breast height (d_1.3), height (h) and crown width (cw), obtained for each pruning variant over the three years are summarised in Tab. 2. The observed decrease in cw for crop trees (Z) between 2012 and 2013 can be attributed to the application of the classical pruning treatment, as the trees were pruned up to about 6 m of height in June 2013.

Tab. 2 - Diameter at breast height (d_1.3), height (h) and crown width (cw) of wild cherry trees in the years 2012-2014 obtained using TLS-derived data. Values are means ± standard deviation. (N): unpruned trees; (P) pruned trees; (Z): pruned crop trees. (*): trees pruned to a height of ca. 6 m in June 2013.

Parameter	Pruning Variant	n	2012	2013	2014
d1.3 (cm)	N	3	10.88 ± 1.66	11.80 ± 1.97	12.92 ± 2.41
	P	13	10.31 ± 2.72	10.94 ± 2.88	11.80 ± 3.11
	Z*	5	12.64 ± 1.91	13.48 ± 1.87	14.54 ± 2.15
h (m)	N	3	8.48 ± 0.70	9.22 ± 0.76	9.87 ± 0.95
	P	13	9.02 ± 1.43	9.74 ± 1.54	10.23 ± 1.55
	Z*	5	10.76 ± 0.88	11.54 ± 1.05	12.18 ± 1.00
cw (m)	N	3	2.03 ± 0.12	2.31 ± 0.04	2.47 ± 0.06
	P	13	1.54 ± 0.29	1.68 ± 0.35	1.81 ± 0.33
	Z*	5	2.14 ± 0.19	1.85 ± 0.18	2.03 ± 0.22

Enlarge/Reduce

Only young trees were scanned (<20 years), therefore, inferences of stem form and volume are not fully indicative of future tree and stem attributes. Nonetheless, the results obtained through the TLS methodology and the application of SimpleTree software can be used to evaluate if corrective cultural interventions are needed. As only young trees were analysed, changes between years were most pronounced. Juvenile growth of wild cherry trees (especially in height) is expected to peak between 7 and 15 years of age ([19]). Changes in mature trees across growing seasons may be harder to be detected, and the data files to be processed for mature trees are expected to be much larger than for juvenile trees.

In this study, a stand height curve was produced, based on TLS derived data. The grey lines in Fig. 3 depict the relationship between height and diameter of individual trees (n=21) over the three studied years, while the black trend lines represent the mean development of the stand in the three years. The observed H/D relationships had the typical characteristics of an even-aged single-species stand. Differences in dominance class between individual trees could be clearly observed, shifting as time advances ([34]).

Fig. 3 - Stand height curve for the scanned wild cherry trees (n=21) in 2012, 2013 and 2014.

Enlarge/Shrink Full Size

The red line in Fig. 3 represent the mean tree growth across the scanning years. The arithmetic mean of d_1.3 from all trees was 10.9, 11.7 and 12.6 cm in winter 2012, 2013 and 2014, respectively, corresponding to a mean height of 9.8, 10.6 and 11.2 m for wild cherry trees at this site. This result can be used as a metric for assessing the mean growth of the stand. However, individual tree growth may be affected by tree hierarchy, as well as by a range of factors including microsite and climatic variables. Furthermore, pruning and other management operations may have largely impacted individual tree growth. In any case, the applied methodology allowed to obtain stand height curves, which are valuable tools for practitioners. It is also worth to stress that growth parameters were obtained for a large number of individuals in a relatively short time.

Crop trees (Z) displayed an approximate reduction of 50% in crown volume as a result of the pruning treatment applied in spring 2013. After one further season, most trees still displayed a reduced crown (by 30-40% compared to the pre-pruning crown volume). The total, stem (root to tip) and branch volume was compared between an unpruned (Fig. 4a) and a pruned tree (Fig. 4b). A reduction in the total and branch volume was evident for the pruned tree (Fig. 4b) as a direct consequence the pruning applied in late spring 2013. However, in the following year (2014) pruned crop trees did regenerate their crowns to almost pre-pruning volumes. However, differences in crown growth among crop trees were observed, likely due to differences in individual tree vigor, microsite and/or provenance.

Fig. 4 - Total tree volume, stem volume and branch volume by pruning treatment and year for: (a) an unpruned tree; and (b) a crop tree pruned in 2013 after the first scan campaign.

Enlarge/Shrink Full Size

Pruning treatment is often adjusted by the operators according to individual tree vigor and development stage, in order to ensure the best tree growth. For this reason, the pruning variant groups considered in this study reflected a continuum of variation rather than fully distinct groups. Indeed, some pruned trees considered in this study showed growth characteristics closer to unpruned trees than to other pruned individuals. However, this did not weaken the main results obtained in this study.

The proposed approach allows for the accurate scrutiny of selected parts of the scanned trees within given thresholds. For example, the merchantable timber volume (i.e., stem or branches with diameter > 7 cm - [46]) can be easily estimated and small increases of the tree parts could be observed over the three years of the study. The largest observed increase was 51.7 dm³ for the stem of a crop tree, whose crown was reduced by the applied pruning. The fastest growing trees increased their total volume by 100 dm³ during the two examined growing seasons, of which 42-52 dm³ was merchantable timber volume. Weaker trees accumulated less volume, but in general the increase in merchantable timber volume was 40-60% of the total increase in tree volume.

The most productive trees showed a 80-110% increase in crown volume during the two studied growing seasons. The greatest increase (113%) was detected for a smaller individual (d_1.3 = 9.1 cm in 2014) that was previously pruned (in 2012) with an intense classical whorl-wise approach (C2 - [42]). Similar high growth rates were quite common at the study site, as a consequence of the low initial stocking density which determined a limited competition among trees.

Above-ground biomass for wild cherry at the same site under the same management was already assessed by Morhart et al. ([31]) using a destructive sampling methodology. In that study, the total tree biomass (oven dry weight), the stem and the branch fractions could be predicted based on d_1.3. Using the same regression variable suggested by Morhart et al. ([31]), we estimated that the total annual growth of the scanned trees can reach 13 kg, as predicted by the SimpleTree software; this equate to a volume increase of 50 dm³ when considering Z variant trees. Such biomass estimate was obtained based on the volume derived from the TLS data, using the homogenised density value of 0.474 g cm^-3 for wild cherry given by Chave et al. ([9]) and Zanne et al. ([50]). However, wood density has been reported to vary both among and within trees ([49]). To verify the consistency of the method used in this study, TLS-derived biomass values were plotted against the total tree aboveground woody biomass values calculated using the allometric function (eqn. 2) proposed by Morhart et al. ([31]) for wild cherry at the same site. The results revealed that biomass estimates obtained by the two aforementioned methods are highly correlated (r = 0.971; r²_adj = 0.941; df = 1.61; p < 0.001 - Fig. 5). Based on the above results, we conclude that TLS-derived data provide reliable estimates of total aboveground tree biomass. However, a combination of the two approaches can increase the accuracy of estimations and can be used as a basis for the evaluation of their effectiveness.

Fig. 5 - Fig. 5 - Relationship between biomass values calculated using TLS-derived data (x-axis) and using the allometric power function (eqn. 2) after Morhart et al. ([31]) based on wild cherry trees from the same site (r²_adj = 0.941; df = 1.61; p= <0.001).

Enlarge/Shrink Full Size

As mentioned above, the use of TLS data in biomass estimation provides the opportunity to examine trees with a very high resolution. Contrastingly, the manual calculation of biomass within diameter classes usually requires an extensive and time consuming destructive sampling, which prevent the same individual tree to be further assessed. In this case, a comparable goal could be attained by relying on empirical studies and published allometric biomass equations, as carried out for example by Morhart et al. ([30]) for hybrid poplar (Populus spp.) in a short rotation coppice.

Fig. 6 displays the variation in biomass distribution across diameter classes (DC) for a single sampled tree over the three scanning dates. As expected, total biomass increased with time in all the considered DCs, though the largest increase was observed for smaller diameters from the crown (DC1-DC3) and for larger diameters from the lower stem (DC15-DC17), while in the other diameter classes the changes were relatively small. As a general trend, peaks in biomass could be detected in DC3 and DC13-15 (dependent on the tree size) in both pruned and unpruned individuals (not shown).

Fig. 6 - Within-tree biomass distribution among different diameter classes (DC1 = 0-1 cm; DC2 = 1-2 cm; etc.) in the years 2012-2014 for a single unpruned wild cherry tree.

Enlarge/Shrink Full Size

To assess the growth of single branches based on TLS-derived data, 23 branches from three unpruned trees (N variant) were randomly selected and their growth was assessed based on 2012 and 2014 scans. Two branches showing implausible results (negative or exaggerated growth, attributable to either occlusion errors or errors occurring in the cylinder fitting process) were excluded from this analysis. Fig. 7 displays the relationship between the increase in branch volume and the corresponding branch angle (r²_adj = 0.386; df 1.19; p=0.002). In this case, values of branch angles (in degrees) were measured from the stem axis below the branch to the central axis of the studied branch after Pretzsch ([34]), and steeply angled branches (grey vertical line in Fig. 7) were defined according to Springmann et al. ([42]). Despite the low number of samples analysed, the results confirmed that steeply angled branches grow faster (as previously suggested by [39]), and for this reason they should be removed early in the rotation to avoid large knots after pruning. Branch comparison using manual methods is time consuming and prone to error without careful cross-checking. Hence, a reliable automated methodology is required in order to scale up this research based on the TLS data.

Fig. 7 - Relationship between branch angle and branch volume increase of 3 wild cherry trees (r²_adj = 0.386; df 1.19; p=0.002). Branches falling on the left of the grey dotted line were considered steeply angled (>140°).

Enlarge/Shrink Full Size

As already mentioned, difficulties can arise for the automated identification of individual branches across years using TLS-derived data. This can be attributed to their increase in diameter and total length over time, but also to the tendency of branch tips to move downwards as the branch grows, thereby it no longer occupies the same position as identified in previous time series scans. Such occurrence can be measured through time series scans. As an example, Fig. 8 shows the downward movement of a single branch over time based on three consecutive scan points. In this case, the linear branch length and the complementary linear branch angle were defined as in Pretzsch ([34]). The upper portion of the sample branch displayed in Fig. 8 has moved downward by 14.5° from 2012 to 2014, while the smaller branch portion below by 6.1° at the branch tip over the same period. Indeed, downward movement of the branch tip can be assumed to be a function of branch weight, diameter, length and the angle of origin. The determination of the branch angle by laser scanning is efficient, while the measurement of branch angles represents a challenge using traditional field measurement techniques, in particular when multiple trees over multiple years are considered.

Fig. 8 - Example of downward movements (in degrees from the vertical) of a sample individual branch of a wild cherry tree over time, showing the branch position in the space at different TLS scan years (different colours).

Enlarge/Shrink Full Size

The application of TLS methodology for analysis of tree structural parameters over time is a novel and promising area of research. This research differs from previous investigations insofar that a number of individual trees were scanned as groups, whereas other previous studies have focused on single trees. The algorithm used in this study has shown a high accuracy in the construction of model cylinders. Indeed, the occurrence of incorrect cylinders or their over- or underestimation may cause noise or systematic errors, as previously assessed by Hackenberg et al. ([15], [16], [17]). In this study, the validation of the technique was not carried out and we assumed that modelled cylinders provide a good average fit quality, as confirmed by a visual validation. However, the method can present errors mainly concerning the incorrect attribution of branches or stems, as already reported by Kaasalainen et al. ([20]). Occlusion errors remain a shortfall of the current TLS methodology ([21]) which can be minimised by using multiple scan positions with sufficient targets to ensure that scans are geo-referenced. Nonetheless, the applied automated parameter search method is able to detect configurations which allow spheres to bridge small occlusion gaps ([16]). We recommend scans to be conducted under suitable weather conditions (i.e., no precipitation and low wind) to maximise the data comparability between can years.

    

Conclusion 

The objective of this manuscript was to test the use of TLS methodology as a tool for assessing tree growth. Our results demonstrated that such an approach can be successfully applied to detect growth and changes in the structure and form of trees, even over a short time period. The proposed method has proven to be effective in detecting differences among trees in crown length, crown density and bole dimensions, as resulted from the application of many different pruning regimes. Using TLS-derived data, we were able to detect tree volume growth and the reduction in total volume and crown dimensions after pruning, as well as height and diameter growth and changes in crown dimensions both within trees and among different pruning regimes. Furthermore, the rate of growth of individual branches and their spatial positioning could be assessed. The application of such an approach to the same tree over time allows a level of investigation not previously attained using established destructive techniques.

Further application of the TLS methodology may include longer temporal measurements on a wider spatial scale, in order to reveal the effect of silvicultural treatments on the growth of remaining trees, and at the same time the potential biomass within harvested individuals. Moreover, the use of TLS-derived data for assessing stem attributes (e.g., sweep, lean, taper, eccentricity and ovality) can provide a straightforward method of tree quality grading, aiding the pre-planning of timber assortments. In conclusion, the methodology proposed here may provide a powerful tool for many applications, such as forest modelling, monitoring and management.

    

Acknowledgements 

The authors thank Georgios Skiadaresis for data pre-processing and Felix Baab for continued technical support. This research was supported by the EU FP7 project “StarTree” (Grant no. 311919), by the Federal Ministry of Education and Research of germany (BMBF) within the Sino-German Lin2- Value project (no. 033L049A), and the German Federal Ministry of Food and Agriculture (BMEL) within the project “Agro-Wertholz” (support code 22031112).

   

References

(1) 

Aiteanu F, Klein R (2014). Hybrid tree reconstruction from inhomogeneous point clouds. The Visual Computer 30: 763-771.
::CrossRef::Google Scholar::

(2) 

Akerblom M, Raumonen P, Kaasalainen M, Casella E (2015). Analysis of geometric primitives in quantitative structure models of tree stems. Remote Sensing 7: 4581-4603.
::CrossRef::Google Scholar::

(3) 

Aschoff T, Spiecker H (2004). Algorithms for the automatic detection of trees in laser scanner data. In: “International Archives of Photogrammetry”. Remote Sensing and Spatial Information Sciences, XXXVI, 8/W2, pp. 71-75. -
::Online::Google Scholar::

(4) 

Assmann E (1970). The principles of forest yield study. Pergamon Press, Oxford, UK, pp. 506.
::Google Scholar::

(5) 

Bayer D, Seifert S, Pretzsch H (2013). Structural crown properties of Norway spruce (Picea abies [L.] Karst.) and European beech (Fagus sylvatica [L.]) in mixed versus pure stands revealed by terrestrial laser scanning. Trees 27: 1035-1047.
::CrossRef::Google Scholar::

(6) 

Belton D, Moncrieff S, Chapman J (2013). Processing tree point clouds using Gaussian Mixture Models. In: Proceedings of the “ISPRS Workshop Laser Scanning 2013” (Scaioni M, Lindenbergh S, Oude Elberink S, Schneider D, Pirotti F eds). Antalya (Turkey) 11-13 Nov 2013. ISPRS, pp. 43-48.
::Online::Google Scholar::

(7) 

Burkhart HE, Tomé M (2012). Modeling forest trees and stands. Springer, Dordrecht, Heidelberg, New York, London, pp. 458.
::Online::Google Scholar::

(8) 

Calders K, Newnham G, Burt A, Murphy S, Raumonen P, Herold M, Culvenor DS, Avitabile V, Disney M, Armston J (2015). Nondestructive estimates of above-ground biomass using terrestrial laser scanning. Methods in Ecology and Evolution 6: 198-208.
::CrossRef::Google Scholar::

(9) 

Chave J, Coomes DA, Jansen S, Lewis SL, Swenson NG, Zanne AE (2009). Towards a worldwide wood economics spectrum. Ecology Letters 12 (4): 351-366.
::CrossRef::Google Scholar::

(10) 

Dassot M, Colin A, Santenoise P, Fournier M, Constant T (2012). Terrestrial laser scanning for measuring the solid wood volume, including branches, of adult standing trees in the forest environment. Computers and Electronics in Agriculture 89: 86-93.
::CrossRef::Google Scholar::

(11) 

Eysn L, Pfeifer N, Ressl C, Hollaus M, Grafl A, Morsdorf F (2013). A practical approach for extracting tree models in forest environments based on equirectangular projections of terrestrial laser scans. Remote Sensing 5: 5424-5448.
::CrossRef::Google Scholar::

(12) 

Fernández-Sarría A, Velázquez-Martí B, Sajdak M, Martínez L, Estornell J (2013). Residual biomass calculation from individual tree architecture using terrestrial laser scanner and ground-level measurements. Computers and Electronics in Agriculture 93: 90-97.
::CrossRef::Google Scholar::

(13) 

Fischler MA, Bolles RC (1981). Random sample consensus: a paradigm for model fitting with applications to image analysis and automated cartography. Communications of the ACM 24: 381-395.
::CrossRef::Google Scholar::

(14) 

Gorte B, Winterhalder D (2004). Reconstruction of laser-scanned trees using filter operations in the 3D-raster domain. In: Proceedings of the ISPRS working group VIII/2 “Laser-Scanners for Forest and Landscape Assessment” (Thies M, Koch B, Spiecker H, Weinacker H eds). Freiburg (Germany) 3-6 Oct 2004. ISPRS International Archives, vol. XXXVI-8/W2, pp. 39-44. -
::Online::Google Scholar::

(15) 

Hackenberg J, Morhart CD, Sheppard JP, Spiecker H, Disney M (2014). Highly accurate tree models derived from terrestrial laser scan data: a method description. Forests 5: 1069-1105.
::CrossRef::Google Scholar::

(16) 

Hackenberg J, Spiecker H, Calders K, Disney M, Raumonen P (2015a). SimpleTree - an efficient open source tool to build tree models from TLS clouds. Forests 6: 4245-4294.
::CrossRef::Google Scholar::

(17) 

Hackenberg J, Wassenberg M, Spiecker H, Sun D (2015b). Non destructive method for biomass prediction combining TLS derived tree volume and wood density. Forests 6: 1274-1300.
::CrossRef::Google Scholar::

(18) 

Jayaratna S (2009). Baumrekonstruktion aus 3D-Punktwolken [Tree reconstruction from 3D point clouds]. Diploma Thesis, Institut für Informatik, Rheinische Friedrich-Wilhelms-Universität, Bonn, Germany, pp. 73. [in German]
::Google Scholar::

(19) 

Joyce PM, Huss J, McCarthy R, Pfeifer A, Hendrick E (1998). Growing broadleaves: silvicultural guidelines for ash, sycamore, wild cherry, beech and oak in Ireland. COFORD, Dublin, pp. 144.
::Google Scholar::

(20) 

Kaasalainen S, Krooks A, Liski J, Raumonen P, Kaartinen H, Kaasalainen M, Puttonen E, Anttila K, Mäkipää R (2014). Change detection of tree biomass with terrestrial laser scanning and quantitative structure modelling. Remote Sensing 6: 3906-3922.
::CrossRef::Google Scholar::

(21) 

Kankare V, Joensuu M, Vauhkonen J, Holopainen M, Tanhuanpää T, Vastaranta M, Hyyppä J, Hyyppä H, Alho P, Rikala J, Sipi M (2014). Estimation of the timber quality of Scots pine with terrestrial laser scanning. Forests 5: 1879.
::CrossRef::Google Scholar::

(22) 

Kretschmer U, Kirchner N, Morhart CD, Spiecker H (2013). A new approach to assessing tree stem quality characteristics using terrestrial laser scans. Silva Fennica 47 (5): article id 1071.
::CrossRef::Google Scholar::

(23) 

Liang X, Hyyppä J, Kaartinen H, Holopainen M, Melkas T (2012). Detecting changes in forest structure over time with bi-temporal terrestrial laser scanning data. ISPRS International Journal of Geo-Information 1: 242-255.
::CrossRef::Google Scholar::

(24) 

Liang X, Kankare V, Yu X, Hyyppä J, Holopainen M (2014). Automated stem curve measurement using terrestrial laser scanning. IEEE Transactions on Geoscience and Remote Sensing 52: 1739-1748.
::CrossRef::Google Scholar::

(25) 

Liang X, Kankare V, Hyyppä J, Wang Y, Kukko A, Haggrén H, Yu X, Kaartinen H, Jaakkola A, Guan F, Holopainen M, Vastaranta M (2016). Terrestrial laser scanning in forest inventories. Theme issue: “State-of-the-art in photogrammetry, remote sensing and spatial information science” 115: 63-77.
::CrossRef::Google Scholar::

(26) 

Lim K, Treitz P, Wulder MA, St-Onge B, Flood M (2003). LiDAR remote sensing of forest structure. Progress in Physical Geography 27: 88-106.
::CrossRef::Google Scholar::

(27) 

Lodhiyal LS, Singh RP, Singh SP (1995). Structure and function of an age series of poplar plantationsin central Himalaya: I. Dry matter dynamics. Annals of Botany 76 (2): 191-199.
::CrossRef::Google Scholar::

(28) 

Metz J, Seidel D, Schall P, Scheffer D, Schulze E, Ammer C (2013). Crown modeling by terrestrial laser scanning as an approach to assess the effect of aboveground intra- and interspecific competition on tree growth. Forest Ecology and Management 310: 275-288.
::CrossRef::Google Scholar::

(29) 

Moorthy I, Miller JR, Berni JAJ, Zarco-Tejada PJ, Hu B, Chen J (2011). Field characterization of olive (Olea europaea L.) tree crown architecture using terrestrial laser scanning data. Agricultural and Forest Meteorology 151: 204-214.
::CrossRef::Google Scholar::

(30) 

Morhart CD, Sheppard JP, Spiecker H (2013). Above ground leafless woody biomass and nutrient content within different compartments of a P. maximowicii × P. trichocarpa poplar clone. Forests 4: 471-487.
::CrossRef::Google Scholar::

(31) 

Morhart CD, Sheppard JP, Schuler JK, Spiecker H (2016). Above-ground woody biomass allocation and within tree carbon and nutrient distribution of wild cherry (Prunus avium L.) - a case study. Forest Ecosystems 3: 1-15.
::CrossRef::Google Scholar::

(32) 

Newnham GJ, Armston JD, Calders K, Disney MI, Lovell JL, Schaaf CB, Strahler AH, Danson FM (2015). Terrestrial laser scanning for plot-scale forest measurement. Current Forestry Reports 1: 239-251.
::CrossRef::Google Scholar::

(33) 

Pfeifer N, Gorte B, Winterhalder D (2004). Automatic reconstruction of single trees from terrestrial laser scan data. In: Proceedings of the 20th ISPRS Congress “Geo-Imagery Bridging Continents” (Altan MO ed). Istanbul (Turkey) 12-23 Jul 2004. IASPR, vol.XXXV, pp. 114-119.
::Online::Google Scholar::

(34) 

Pretzsch H (2002). Grundlagen der Waldwachstumsforschung [Principles of forest growth research]. Parey, Berlin, Germany, pp. 23.
::Google Scholar::

(35) 

Pryor SN (1988). The silviculture and yield of wild cherry. Forestry Commission bulletin, vol 75. Her Majesty’s Stationery Office, London, UK, pp. 23.
::Google Scholar::

(36) 

Raumonen P, Kaasalainen M, Akerblom M, Kaasalainen S, Kaartinen H, Vastaranta M, Holopainen M, Disney M, Lewis P (2013). Fast automatic precision tree models from terrestrial laser scanner data. Remote Sensing 5: 491-520.
::CrossRef::Google Scholar::

(37) 

Roberts JW, Tesfamichael S, Gebreslasie M, Van Aardt J, Ahmed FB (2007). Forest structural assessment using remote sensing technologies: an overview of the current state of the art. Southern Hemisphere Forestry Journal 69: 183-203.
::CrossRef::Google Scholar::

(38) 

Rusu RB, Cousins S (2011). 3D is here: Point Cloud Library (PCL). In: International Conference on Robotics and Automation (ICRA). Shanghai (China) 9-13 May 2011. IEEE Xplore Digital Library, pp. 1-4.
::Online::Google Scholar::

(39) 

Schuler J (2011). Astenwicklung und Astreinigung in Abhängigkeit vom Dickenwachstum bei Buche (Fagus sylvatica L.) und Eiche (Quercus petraea (Matt.) Liebl.; Quercus robur L.) [Branch development and natural pruning processes related to diameter growth of beech (Fagus sylvatica L.) and oak (Quercus petraea (Matt.) Liebl.; Quercus robur L.)]. Doctoral Dissertation, Institut für Waldwachstum, Albert-Ludwigs-Universität Freiburg i. Br., Freiburg, Germany, pp. 285. [in German]
::Online::Google Scholar::

(40) 

Sheppard JP, Urmes M, Morhart CD, Spiecker H (2016). Factors affecting branch wound occlusion and associated decay following pruning - a case study with wild cherry (Prunus avium L.). Annals of Silvicultural Research 40 (2): 16-22.
::Google Scholar::

(41) 

Spiecker M (1994). Wachstum und Erziehung wertvoller Waldkirschen [Growth and tending of valuable wild cherries]. Mitteilungen der Forstlichen Versuchs- und Forschungsanstalt Baden-Württemberg Band 181, pp. 92. [in German]
::Google Scholar::

(42) 

Springmann S, Rogers R, Spiecker H (2011). Impact of artificial pruning on growth and secondary shoot development of wild cherry (Prunus avium L.). Forest Ecology and Management 261: 764-769.
::CrossRef::Google Scholar::

(43) 

Srinivasan S, Popescu SC, Eriksson M, Sheridan RD, Ku N (2014). Multi-temporal terrestrial laser scanning for modeling tree biomass change. Forest Ecology and Management 318: 304-317.
::CrossRef::Google Scholar::

(44) 

Thies M, Pfeifer N, Winterhalder D, Gorte B (2004). Three-dimensional reconstruction of stems for assessment of taper, sweep and lean based on laser scanning of standing trees. Scandinavian Journal of Forest Research: 571-581.
::CrossRef::Google Scholar::

(45) 

Thies M, Hein S, Spiecker H (2009). Results of a questionnaire on management of valuable broadleaved forests in Europe. In: “Valuable broadleaved forests in Europe” (Spiecker H, Hein S, Makkonen-Spiecker K, Thies M eds). Brill, Leiden, Netherlands and Boston, MS, USA, pp. 27-42.
::Google Scholar::

(46) 

Van Laar A, Akça A (1997). Forest mensuration (1st edn). Cuvillier, Göttingen, Germany, pp. 418.
::Google Scholar::

(47) 

Van Leeuwen M, Nieuwenhuis M (2010). Retrieval of forest structural parameters using LiDAR remote sensing. European Journal of Forest Research 129: 749-770.
::CrossRef::Google Scholar::

(48) 

Van Leeuwen M, Hilker T, Coops NC, Frazer G, Wulder MA, Newnham GJ, Culvenor DS (2011). Assessment of standing wood and fiber quality using ground and airborne laser scanning: A review. Forest Ecology and Management 261: 1467-1478.
::CrossRef::Google Scholar::

(49) 

Wassenberg M, Chiu H, Guo W, Spiecker H (2015). Analysis of wood density profiles of tree stems: incorporating vertical variations to optimize wood sampling strategies for density and biomass estimations. Trees 29: 551-561.
::CrossRef::Google Scholar::

(50) 

Zanne AE, Lopez-Gonzalez G, Coomes DA, Ilic J, Jansen S, Lewis SL, Miller RB, Swenson NG, Wiemann MC, Chave J (2009). Data from: “Towards a worldwide wood economics spectrum”. Dryad Digital Repository, Website.
::CrossRef::Google Scholar::

For further details log on website :
http://www.sisef.it/iforest/contents/?id=ifor2138-009