ISRN Forestry

Volume 2013, Article ID 196832, 12 pages

http://dx.doi.org/10.1155/2013/196832

## Individual Growth Model for *Eucalyptus* Stands in Brazil Using Artificial Neural Network

^{1}Department of Forestry, Faculty of Technology, University of Brasília, Campus Darcy Ribeiro, 70904-970 Brasília, DF, Brazil^{2}Department of Forestry, Federal University of Viçosa, Campus UFV, 36570-000 Viçosa, MG, Brazil^{3}Department of Forestry, Federal University of the Valleys of Jequitinhonha and Mucuri, Campus Diamantina, 39100-000 Diamantina, MG, Brazil^{4}Natural Resources Institute, Federal University of Itajubá, Campus Itajubá, 37500-903 Itajubá, MG, Brazil

Received 13 December 2012; Accepted 14 February 2013

Academic Editors: J. Kaitera, P. Newton, T. L. Noland, and P. Robakowski

Copyright © 2013 Renato Vinícius Oliveira Castro et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

#### Abstract

This work aimed to model the growth and yield of *Eucalyptus* stands located in northern Brazil, at the individual tree level, by using artificial neural networks (ANNs). Data from permanent plots were used for training the neural networks to predict tree height and diameter as well as mortality probability. Once trained, the networks were evaluated using an independent data set. The first group was composed of 33 plots (11 in each productive capacity class) and was used for artificial neural network training. In five measurements, this group totaled 8,735 cases (measurements of individual trees), as each plot had 53 trees on average throughout this evaluation. The second group was composed of 30 plots (10 in each productive capacity class) and was used for model validation. This group totaled 7,756 cases. Were tested different network architectures Multilayer Perceptron (MLP). Results revealed an underestimation bias for number of surviving trees. However, estimates of diameter, height, and volume per hectare were found to be accurate. This indicates that artificial neural networks are a viable alternative to the traditional growth and yield modeling approach in the forestry sector.

#### 1. Introduction

Individual tree models are constituted by a set of submodels that estimate diameter and height growth as well as mortality probability through tree- and stand-related variables and through competition data [1–3]. According to Munro [4], these models may be categorized according to how they consider the competition among trees, as represented by distance-dependent and distance-independent models.

Since Newnham [5], many studies have been conducted worldwide in an attempt to improve growth models at the individual tree level and the relevant submodels. Methods to estimate parameters as well as different explanatory variables have been evaluated in an attempt to produce accurate, unbiased estimates of diameter and height growth and also tree mortality [6, 7]. In Brazil, few studies have been conducted that used these types of growth model for *Eucalyptus* [8, 9], a genus whose planted area intended to supply the processing industry amounts to 4.75 million hectares [10]. Some models have been developed and fitted for some species, including canjerana (*Cabralea canjerana*), black cinnamon (*Nectandra megapotamica*), cedar (*Cedrela fissilis*), and araucaria (*Araucaria angustifolia*), in natural forest conditions, yet without computing all the submodels that compose an individual tree model [11–14].

Typically, estimates of equation parameters for the models are derived from linear and nonlinear regressions [15, 16]. However, other estimation techniques that include artificial neural networks have been successfully used in forest mensuration [17–22], providing just as accurate estimates as those derived through regression, models [23–25].

Artificial neural networks (ANNs) are a type of artificial intelligence system similar to human brain, having a computational capability which is acquired through learning [26]. They can be used in data classification, time series analysis or regression, and pattern recognition [27–29].

Artificial neurons are processing units composed of an activation function which is also known as transfer function. This function is applied to a linear combination among the input variables and weights that reach a given neuron and then returns an output value [19, 28].

The architecture of an artificial neural network refers to how neurons are organized. They comprise three layers: an input layer where variables are introduced to the network, a hidden or intermediate layer where most of the signal processing occurs, and an output layer where the end result is completed and presented.

MLP (Multilayer Perceptron) is the most widely used artificial neural network model for predicting continuous variables. In MLP training, network functioning is as follows: each neuron is connected to every neuron in the subsequent layer; there are no connections between neurons in the same layer; it has at least one processing hidden layer and a high connectivity level between neurons, which is defined by synaptic weights.

The input layer distributes the inputs to subsequent layers. Input nodes have liner activation functions and no thresholds. Each hidden unit node and each output node have thresholds associated with them in addition to the weights. The hidden unit nodes have nonlinear activation functions and the outputs have linear activation functions. Hence, each signal feeding into anode in a subsequent layer has the original input multiplied by a weight with a threshold added and then is passed through an activation function that may be linear or nonlinear (hidden units) [28]. Only three layer MLPs will be considered in this work since these networks have been shown to approximate any continuous function.

According to this architecture, an approximation was obtained of an unknown function that describes the mapping of input ()-output() pairs of a set of training patterns [28].

The ANN method was successfully used for modeling regular mortality of individual trees of *Quercus coccínea* [30] and survival of *Pinus resinosa* [31]; for predicting some functional characteristics of ecosystems [23]; for classifying wood using CT scans [32]; for modeling growth rings using climate variables in *Pseudotsuga menziesii* [33]; for comparing different types of ANN in mortality estimates of *Picea abies *[19]; for classifying forest inventory methods [34]; for predicting forest attributes using treetop, soil, and tree size variables [35]; for estimating volume outside bark of *Pinus brutia* [20]; for estimating trunk volume of *Pinus brutia*, *Abies cilicica*, *Cedrus libani,* and *Pinus sylvestris* [36] among others. All studies being cited demonstrate the great potential of ANNs for the use in several forest engineering fields, in particular forest mensuration and management.

In Brazil, despite there being more than 4 million hectares planted with *Eucalyptus* species [10], the use of neural networks as an alternative methodology to regression models is still incipient [20, 36]; the latter is the traditional method for growth and yield modeling in the forestry sector. With that in mind, this work aimed to model the growth of *Eucalyptus* stands at the individual tree level by using artificial neural networks.

#### 2. Material and Methods

##### 2.1. Data

Data were obtained from 63 permanent plots, approximately 500 m² in area, containing clonal stands of *Eucalyptus grandis × Eucalyptus urophylla*, with initial spacing of m between plants (Table 1). This study was conducted in the municipality of Monte Dourado, Pará state, on the banks of river Jari, northern Brazil (Figure 1). The equations to estimate volume with bark are presented in Table 2. Local soil types include yellow latosols, cambisols, and podzols. The local climate is characterized as equatorial, hot, and humid, with a rainfall regime (average annual rainfall of 2,115 mm) marked by two well-defined seasons, with a rainy period from January to July which accounts for about 80% of the annual precipitation and a dry period from August to December. Regards the wind regime, the average wind speed is 2 to 4 m s^{−1}. Wind blasts are nonetheless common, potentially exceeding 100 km h^{−1} in some cases. The predominant natural vegetation is the submontane and montane dense moist forest type. The average annual temperature is 26.4°C [9, 37].

In every permanent plot, measurements were taken of the diameter at breast height (d.b.h.) using a measuring tape, and total height (Ht) of each tree, using a digital hypsometer, for five annual measurements (24, 36, 48, 60, and 72 months). The last measurement is equivalent to the age of cutting forest. The volume with bark () was derived using equations provided by a local forest company. The height of dominant trees (m) was used for productive capacity classification through site indices () [15]. The site index curves were constructed employing the guide curve method assuming the index age of 60 months.

The set of permanent plots was randomly divided into two groups. The first group was composed of 33 plots (11 in each productive capacity class) and was used for artificial neural network training. In five measurements, this group totaled 8,735 cases (measurements of individual trees), as each plot had 53 trees on average throughout this evaluation. The second group was composed of the remaining 30 plots (10 in each productive capacity class) and was used for model validation. This group totaled 7,756 cases.

The annual mortality probability () for each mensuration period was obtained by calculating the proportion of dead trees per diameter class, in-between mensuration, through the following equation [39–45]: where is the number of living trees in the th diameter class, at the start of the period, is the number of living trees in the th diameter class at the end of the period. This stand was not observed ingrowth of trees.

Distance-independent competition indices () being evaluated included [2, 40, 46] where is diameter of the subject tree, is arithmetic mean diameter of trees in the plot, is total height of the subject tree, is average total height of trees in the plot, is quadratic diameter, and is aggregate basal area of trees larger than the subject tree.

##### 2.2. Neural Network Training

Five hundred artificial neural networks were trained for the following output variables: annual mortality probability (), height at a future age (), and diameter at a future age (d.b.h._{2}), using for each output variable a set with different input variables (Table 3).

For the training of artificial neural networks, software Statistica 8.0 [47] was used, testing different architectures of Multilayer Perceptron (MLP) networks.

MLP networks are feedforward multilayer networks having one or more layers of neurons between the input and output layers, known as hidden layer [48]. These hidden layers are able to extract nonlinear data patterns [49]. According to [28], with one hidden layer an MLP network can implement any continuous function, while two hidden layers enable approximating any function. In this network model, each neuron is connected to every neuron in the subsequent layer, but there are no connections between neurons within the same layer nor there is any feedback.

The feedforward type of training was used, by the supervised method. In this procedure, the data flow algorithm moves in only one, noncyclic direction, to initially define the synapse weights, excluding the input variables with low-weight synapses, while the supervised method indicates the input and output variables [28].

The training stages, such as preprocessing, actual training, with selection of architectures and stopping methods, and postprocessing, were performed by the optimization tool Intelligent Problem Solver (IPS), from software Statistica. 500 networks were initially trained in order to estimate each variable. Without precise and accurate networks, this number would be increased.

This software normalizes data in the range 0-1 and tests various architectures and network models. In the supervised method, input and output variables are set by the user. In the feedforward procedure, the data flow algorithm moves in only one, noncyclic direction, to initially determine the synapse weights. The back-propagation algorithm corrects the initial synapse weights so as to minimize prediction error. Therefore, in this process, initial input variables can be excluded during training for not helping (low synapse weight) minimize prediction error [28].

The definition of network architecture, that is, number of neurons per layer, number of layers, and parameterization was optimized by the tool Intelligent Problem Solver, from software Statistica.

The selection of best network for each output variable was based on the following criteria [50–53]: (a) coefficient of correlation between observed and estimated values (), (b) coefficient of variation (CV %), (c) root mean square error (RMSE), (d) bias, (e) bias %, (f) absolute mean differences (AMD), and (g) graphic analysis of observed versus estimated values.

##### 2.3. Validation

The validation of selected networks was done by annually projecting the tree mortality, the height and diameter of living trees, and the volume per hectare of plots until age of 72 months, according to the flowchart of basic steps and decisions for an individual tree model [2].

To verify network behavior under different growing conditions, the plots were divided into three productivity classes (high, medium, and low) based on site indices () (; 26; 20 m).

The tree mortality rule was the one that is used by Pretzsch et al., [54], whereby after estimating mortality probability for each tree, a random number between zero and one was generated () and compared to the estimated mortality probability (). If the tree will die, otherwise the tree will remain alive and its dimensions should be projected to the next age through neural networks. The possibility of adding new trees was not considered.

In order to evaluate the accuracy of mortality estimates, a graphical analysis was performed of the estimated number of surviving trees in relation to observations. For the variables height and diameter, the *F*-test was used [55] (), scatter plots were generated, and the statistics , CV %, RMSE, bias, bias %, AMD were calculated. Estimates of volume per hectare, as projected until age of 72 months in each productivity class, were compared to observed values using Student’s *t*-test ().

#### 3. Results

##### 3.1. Training of Artificial Neural Networks (ANNs)

The network with the best performance to estimate annual mortality probability was , with three neurons in the input layer (variables), four neurons in the hidden layer, and one neuron in the output layer. Although not with the best statistics (Table 4), this network provided a better trend regarding the distribution of observed values in relation to estimated values (Figure 2). With only the competition index as input variable, was the network with the poorest performance.

The best networks for the variables height and diameter were and , respectively, with special mention of the estimate accuracy (Table 4 and Figure 2). The networks for these variables comprised five input layers (variables), seven and five hidden layers, respectively, and one output layer.

##### 3.2. Validation

The projection of the number of surviving trees per hectare indicates a slight underestimation bias in the validation plots (Figure 3). The estimates can be considered reasonable, since mortality is a random event which is difficult to measure and estimate, consequently obstructing the good performance of probability models [56].

The neural networks selected for the variables diameter and height provided accurate estimates, regardless of the productivity class (Table 5 and Figure 4), with an error increase tendency as age advanced, due to error propagation. However, no difference was found between estimated and observed values, according to the *F*-test ().

Estimates of volume outside bark per hectare, as projected until age of 72 months (Figure 5), did not differ statistically from observed values (), in all productive capacity classes and ages, according to the *t*-test. Percentage differences between estimated and observed volumetric stocks at age of 72 months were 7%, 0%, and −6% for the high, medium, and low productivity class, respectively. Similarly to height and diameter estimates (Table 5), the older the age, the higher the error in volumetric stock estimates, due to error propagation.

#### 4. Discussion

In recent decades, a major concern in the field of forest mensuration has been to develop growth and yield models using individual trees [40, 57–60]. Modeling growth and yield can be difficult and complex if relying on individual trees as the basic modeling unit [61] due to the high resolution level required [62]. This type of modeling consists of establishing different equations to predict diameter and height growth as well as mortality, including tree- and stand-related data as explanatory variables which represent the competitive status of a tree [63–65], among others.

A widely used resource in this type of modeling is regression analysis through linear and nonlinear functions [6]. The different fit functions and the functional form with which these variables are included in the model are the greatest stumbling block to modeling growth and yield at the individual tree level. Numerous studies have been conducted to compare and provide the best fit function (linear and nonlinear) for predicting growth using different explanatory variables [9, 59, 60, 65, 66]. However, fitting these models requires knowledge of the functional relationship of variables, knowledge of modeling tools, in addition to accurate estimates. Even where such requirements are met, there is neither proven advantage of one function over another nor an indication of which are the most suitable explanatory variables to be used in the model, leading to uncertainty in growth and yield modeling for an individual tree. Additionally, the high resolution level of this model type is accompanied by problems caused by cumulative errors [62]. Therefore, using ANNs may work as an alternative to the traditional procedure for modeling an individual tree [31].

ANNs are increasingly becoming a popular tool in forest mensuration [16, 20, 36] and in estimation of individual tree growth and yield [30, 31], requiring no presuppositions about the functional form of variables or fit functions. Instead, ANNs are trained to find such relationship. An ANN is capable of achieving optimum growth estimates without mentioning the functional form of the relationship between input and output layers [23]. Also, an ANN may help identify the most critical input variables to predict diameter and height growth as well as mortality probability and provide a better understanding of the dynamic of models at the individual tree level, becoming a valuable tool for *Eucalyptus* forest management.

A large number of authors have discussed the structure, technique, and operation of ANNs [18, 26, 27, 29]. Yet only in the past decade interest in using ANNs has been stirred up, with an increasing number of practical applications in environmental and forest modeling [67]. Applications for use in forest mensuration and management include forest classification and mapping, growth and forest dynamics modeling, spatial data analysis, analysis of forest inventory types, and dendroclimatology modeling [25, 36, 68].

As far as results found in this study are concerned, the competition index of the network selected as best for mortality probability () is , that is, the sum of basal areas of trees larger than the subject tree. According to this index, the smaller the tree is, the less competitive it is and the greater its mortality probability is [69–71]. Hasenauer et al. [19] found better prediction results for tree mortality using neural networks, in which IID_{5} (BAL) was one of the variables used in network training.

Studies involving individual tree mortality through regression models usually estimate mortality probability only as a function of the competition index as independent variable [9, 40, 69, 72]. However, besides the competition index, Guan and Gertner [30], Monserud and Sterba [71], and Palahí and Pukkala [73] recommend using tree- and stand-related variables to improve mortality estimates. In this study, the networks with the best performance included these input variables (Table 4).

Network input variables for estimating height and diameter include the , also known in literature as Basal Area Index (BAI). According to Daniels [58], this competition index was found to be the most correlated one with diameter and height growth in loblolly pine trees. Martins [9] observed that the provided the highest partial contribution, if compared to other competition indices, in diameter and height growth models for *Eucalyptus* trees. Explanations for best performance include the ease of calculation and the biological realism of the index.

Other than the competition index, tree- and stand-related variables such as age and site index are also widely used to express height and diameter growth at the individual tree level, using linear and nonlinear regression [53, 60, 74]. The selection of these variables in the best networks () demonstrates realism in network estimates, adequately capturing height and diameter growth (Figure 3 and Table 4).

Martins [9] used the same data as this study for modeling individual trees yet using regression models. The fitted equations to estimate mortality probability were inferior if compared to the obtained statistics using artificial neural network training. As to the fitted equations to estimate diameter and height in future ages, the equations obtained using regression models were as accurate as the trained neural networks. However, in model validation, using independent data from regression fitting and network training, the projections of tree growth and mortality using the neural network model discussed in this work were proved to be superior. The bias % values at the individual tree level for height and diameter obtained by the previously mentioned author were in the order of 1.5%, while in this work they were in the order of 0.5%.

In the validation at the stand level, the percentage errors using artificial neural networks were in the order of 0.5%, while those using regression models were in the order of 6% for total volume per hectare.

Since the same data were used, with the same methodology, it can be said that the tool artificial neural networks is effective in individual tree modeling and provides superior results if compared to regression models, particularly in the model generalization or validation stage.

Considering the results found, artificial neural networks should be studied for describing the structure and dynamics of natural tropical forests, with all of their complexity resulting from size and species diversity [3], which are usually difficult to model through traditional growth and yield methods.

#### 5. Conclusions

Results in this study confirm the use potential of MLP artificial neural networks, through the supervised learning method, for individual tree modeling of commercial *Eucalyptus* plantations, given the precision of estimates found. Yet further investigation is required to improve this methodology, seeking to evaluate other types of artificial neural networks, as, for instance, RBF (*Radial Bases Function*) networks, and to study the effects of including qualitative input variables in the networks.

#### Acknowledgments

The authors wish to thank Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPQ), Brazil, for granting the scholarship and Monica Castellani for English revision.

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