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Article

Quantifying the Variability of Internode Allometry within and between Trees for Pinus tabulaeformis Carr. Using a Multilevel Nonlinear Mixed-Effect Model

1
Institute of Forest Resource Information Techniques, Chinese Academy of Forestry, Beijing 100091, China
2
East China Forest Inventory and Planning Institute, State Forestry Administration, Hangzhou 310019, China
*
Author to whom correspondence should be addressed.
Forests 2014, 5(11), 2825-2845; https://doi.org/10.3390/f5112825
Submission received: 17 June 2014 / Revised: 10 November 2014 / Accepted: 11 November 2014 / Published: 21 November 2014

Abstract

:
Allometric models of internodes are an important component of Functional-Structural Plant Models (FSPMs), which represent the shape of internodes in tree architecture and help our understanding of resource allocation in organisms. Constant allometry is always assumed in these models. In this paper, multilevel nonlinear mixed-effect models were used to characterize the variability of internode allometry, describing the relationship between the last internode length and biomass of Pinus tabulaeformis Carr. trees within the GreenLab framework. We demonstrated that there is significant variability in allometric relationships at the tree and different-order branch levels, and the variability decreases among levels from trees to first-order branches and, subsequently, to second-order branches. The variability was partially explained by the random effects of site characteristics, stand age, density, and topological position of the internode. Tree- and branch-level-specific allometric models are recommended because they produce unbiased and accurate internode length estimates. The model and method developed in this study are useful for understanding and describing the structure and functioning of trees.

1. Introduction

Plant allometry has been used extensively to describe the relationship between individual size and other attributes, such as form and process [1,2]. It allows plant organ size to be estimated, commonly from the plant’s biomass, and links plant architecture and physiological activities. It is particularly useful in functional-structural plant models (FSPMs), which explicitly describe the development of the 3D architecture or structure of plants over time as governed by physiological processes and environmental factors [3,4]. In these FSPMs, such as GreenLab [5,6], stem morphology (length and diameter) is an important component because it requires an accurate description of the geometric and topological structure of the plant and canopy. It is well known that plants often display large differences in morphological characters. As a tree grows in response to the local climate, site conditions, and management practices, its components change in size and shape in a coordinated manner. Within a single species, genotypes often vary intrinsically in their phenotypic trait values [7]. The ability to change a phenotype in response to the environment is an important feature of plants, especially for trees living in heterogeneous environmental conditions over both a long generation time and a large geographical area. The 3D architecture of a forest canopy is a highly heterogeneous and dynamic system at all scales. The length, diameter and number of internodes within branches at different levels affect visual appearance but also reflect the resource allocation of a tree, which is driven by the environment and physiological processes. The geometry of tree branches can have a considerable effect on their efficiency in terms of carbon export per unit carbon investment in structure [8].
It has been observed from experiments that there are great variations in internode growth within and between trees, even for branches of similar positions and vigor [9,10,11]. For example, distinct quantitative trait loci between the trunk and branches for internode lengthening were detected in apple hybrids [12]; internode length varies regularly with node order [13]. Numerous empirical works have provided evidence of the variability of structural traits within species, between species, and over time [14,15,16]. Pretzsch and Dieler [17] provided empirical evidence that trees exhibit plastic rather than fixed structural scaling; plastic scaling is relevant for space occupation and competition at the individual tree level. Chen et al. [18] found strong elongation of petioles upon submergence as well as both inter- and intra-population variation. Intraspecific functional variability in terms of the extent, structure, and sources of variation was also investigated [19]. There is increasing evidence challenging the assumption that intraspecific variability is much lower than interspecific variability [20,21]. Moreover, the variability of plant allometric equations (scale laws) for relationships such as metabolic rate-biomass [22], tree height-diameter [23,24,25,26], tree productivity-biomass [27], biomass-diameter [28,29], branch radius-branch length [24,30], and foliage and woody mass in crowns [31] has been extensively examined.
Quantifying the variation in allometric growth is of interest for FSPMs because understanding the variation in allometric internode growth within and between trees should allow us to better understand the underlying tree structure and function. Little is known about the variability in internode allometry; however, such information is essential, both for improving the accuracy of FSPMs and for understanding the mechanisms of tree functioning. It is expected that the allometric relationship of an individual tree deviates from that of a modeled population. Furthermore, the same genetic material occurs within trees; thus, the specification of internodes within trees (i.e. nested random effects) is necessary to model the hierarchical data structure. Internode measurements (length, diameter, and biomass) that are derived from the same tree and branch are not independent. These issues have rarely been described for FSPMs [32,33,34,35,36], with the exception of a single study [37]. There is increasing interest in including the variation among individuals in the modeling of population growth with hierarchical models, in which some parameters are estimated at the level of the population, whereas other parameters are assumed to vary among individuals according to a specific distribution where the mean and the variance of the distribution can be estimated [38,39,40,41]. Recent developments in statistical theory and computational power allow for the specification of multilevel nonlinear mixed-effect models that can generate notable improvements in parameter estimation [42,43]. Analyses of the allometric growth patterns of internodes with mixed-effects models have been limited up until now and could potentially provide valuable biological insights into plant plasticity for FSPMs [37].
Chinese pine (Pinus tabulaeformis Carr.), an important native tree species in China, grows across 14 provinces and plays a significant role in forestry and social development. A Chinese pine tree only produces one internode for both the stem and a branch during one year and is characterized by branches in whorls on each internode. Third-order branches are common and very few fourth-order branches are observed. To better understand inter-tree competition on a source-sink balance, a functional-structural model of Chinese pine was calibrated using the GreenLab framework with the assumption that the internode allometry for the same level branches is identical [43].
The main goal of this study was to examine the variability of internode allometry within and between trees and branches for the Chinese pine. The base allometric model from GreenLab describes the primary growth of the internode. A multi-level nonlinear mixed-effects model approach was adopted based on observed allometric data. We aimed to verify that significant variation exists in internode allometry within and between trees and branches; this needs to be modeled and quantified.

2. Materials and Methods

2.1. Site Description and Data

Data were collected at the Longtoushan forest farm, Weichang county (116°51′–117°45′ E, 41°47′–42°06′ N), Hebei Province, China in April 2011. The mean elevation in the area is 985 m. The mean annual rainfall is 465 mm. Temperatures range from −12.9 °C to 38.9 °C with an average of 2.4 °C. The soil is primarily brown soil.
In this paper, a sampling protocol similar to the one described in the study of Guo et al. [44] was designed to investigate tree architecture and biomass to develop functional-structural models of the Chinese pine. Sixteen Chinese pine trees of different ages and from different sites (S1 to S4) with varying densities (decreased from 1 to 4) were randomly sampled and investigated (Table 1). For each tree, the diameter at breast height (1.3 m) was first measured. After the tree was felled, the total height, the total number of internodes, and their corresponding locations along the stem were measured and recorded. For each internode on the trunk, one representative first-order branch was selected and the length, diameter, fresh biomass, and the corresponding location of each internode on the selected first-order branch were measured. For each internode on the selected first-order branch, one representative second-order branch was selected and the same information was measured as for the first-order branch. The measurements for the third-order branch were the same as for the first and second-order branches. In the GreenLab model, the growth of internodes is described by two processes. The first one is primary growth. The internode grows in length and diameter for a short period and length and diameter are linked by an allometric function during the primary growth. The second one is secondary growth. Internode length is then static but the diameter continues to grow, as long as the branch is alive. For these reasons, the relationships between length and diameter can be linked only for current-year shoots, usually represented by the last internodes of branches [5]. In that sense, we remake allometry only on the last internode of branches, where the secondary growth is negligible. For Chinese pines, the last internode of a branch is commonly used to develop the allometric model, which describes the primary growth of internodes [45,46]. A total of 211 internodes on first-order branches, 969 internodes on second-order branches and 431 internodes on third-order branches were collected. Summary statistics for the last internodes of branches are shown in Table 2. We neglected the fourth order or higher branches because the number of these branches was very limited.
Table 1. Description of 16 sampled Chinese pine trees.
Table 1. Description of 16 sampled Chinese pine trees.
Tree No.Tree Age (Year)Age GroupDiameter at Breast Height (cm)Tree Height (m)Site LocationDensity Group
15A11.8 *0.9311
25A11.7 *0.8211
38A22.52.0611
48A22.22.1911
547A320.213.8024
647A317.313.0224
747A314.412.9524
847A320.416.2523
947A315.713.8023
1047A320.415.8523
1121A413.87.4732
1221A412.47.2932
1321A413.47.1032
1411A55.34.0241
1511A53.12.8541
1611A53.43.2441
Note: * indicates ground diameter.
Table 2. Summary statistics of the last sampled internodes on Chinese pine branches.
Table 2. Summary statistics of the last sampled internodes on Chinese pine branches.
Branch OrderInternode SizeMaximumMinimumMeanStandard DeviationCoefficient of Variation (CV)Sample Size
1length (cm)37.600.3213.339.600.72211
fresh biomass (g)24.980.033.964.881.23
2length (cm)18.700.103.142.140.68969
fresh biomass (g)3.440.010.450.761.69
3length (cm)3.010.201.140.600.53431
fresh biomass (g)0.600.010.120.100.83

2.2. Base Allometry Model

The base allometry model is from GreenLab; in this study, the internode is represented as a cylinder [47], and a power function is adopted to describe the allometry of internodes with the specification of Equation (1) [45] in the GreenLab model. This has been validated by previous studies [33,34,44], and is also well indicated by most of the scatter plots between internode length and biomass for Chinese pine in this study (Figure 1). The model only accounts for primary growth of the internode.
L ( K ) = β 1 Q ( K ) 1 + β 2 2 + ε
where L(K) and Q(K) are the length and biomass of internode K, respectively; β1 and β2 are the shape parameter and geometric parameter of the internode in the GreenLab model, respectively; and ε is an error term.
Figure 1. Scatter plots of internode length and biomass for Chinese pine (A: the first-order branches; B: the second-order branches; C: the third-order branches).
Figure 1. Scatter plots of internode length and biomass for Chinese pine (A: the first-order branches; B: the second-order branches; C: the third-order branches).
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2.3. Multi-Level Nonlinear Mixed Model

Mixed-effects models can incorporate the hierarchical structure of data into the analysis, and the variation in the parameter estimates is known at each level of the hierarchical sampling structure, thus providing unbiased estimates of model parameters [48]. Using random effects to capture branch-to-branch and tree-to-tree variability allows for modeling the length of the individual tree (subject-specific) as well as the length of the average tree (population-specific). The mixed-effects model for estimating the lengths of internodes on different order branches is specified in Equations (2)–(4):
L i   j ( K ) = ( β 1 + b 1 , i ) Q i j ( K ) 1 + ( β 2 + b 2 , i ) 2 + ε i , j
L i j m ( K ) = ( β 1 + b 1 , i + b 1 , i j ) Q i j m ( K ) 1 + ( β 2 + b 2 , i + b 2 , i j ) 2 + ε i , j m
L i j m l ( K ) = ( β 1 + b 1 , i + b 1 , i j + b 1 , i j m ) Q i j m l ( K ) 1 + ( β 2 + b 2 , i + b 2 , i j + b 2 , i j m ) 2 + ε i , j m l ,
where Lij(K), Lijm(K), and Lijml(K) are the lengths of internode K for the first-order branch j, the second-order branch m is located on the first-order branch j, and the third-order branch l is located on the second-order branch m on branch j for tree i, respectively. Qij(K), Qijm(K), and Qijml(K) are the biomasses of internode K for different order branches denoted with the same conventions as for length, β1 and β2 are fixed parameters, b1,i and b2,i are random parameters specific to tree i describing between-tree random effects, b1,ij and b2,ij are random parameters specific to the jth first-order branch of tree i describing between-first-order-branch random effects, b1,ijm and b2,imj are random parameters specific to second-order branch m on branch j of tree i describing between-second-order-branch random effects, and εi,j, εi,jm, and εi,jml are model errors. The random parameter vector (b1,k, b2,k) and model error εi,k, in which k is the object the random parameters are specific to, are assumed to be normally distributed with means of zero and variance-covariance matrices D and R, respectively. R is assumed to be δi,k2I, where δi,k2I, is the error variance and I is an identity matrix. D is assumed to be an unstructured variance-covariance matrix:
D = ( σ 1 , k 2 σ 12 , k σ 21 , k σ 2 , k 2 )
where σ 1 , k 2 and σ 2 , k 2 are the variance of random parameters b1,k and b2,k on the k level, which describe the inter-tree and -branch variability of the parameters; σ 12 , k and σ 21 , k are the covariance between random parameters b1,k and b2,k in the Equations (2)–(4); and σ 12 , k = σ 21 , k .
In this study, both shape and geometric parameters (or only one of them in the base model (Equation (1)) were assumed to be mixed, including fixed and random component parameters. They present random effects at the tree, first-order branch, and second-order branch levels. So, in total, we have three, nine, and 27 models to be tested with the combinations of random parameters for internodes on the first-, second-, and third-order branches, respectively (Table 3, Table 4 and Table 5).
Table 3. Values of AIC and BIC of mixed-effect models and the base model for first-order branches.
Table 3. Values of AIC and BIC of mixed-effect models and the base model for first-order branches.
Model No.Mixed-Effect ParametersAICBIC
1β1, β2891.6911.2
2β1910.3923.3
3β21100.21113.2
Base model 1220.21223.0
Table 4. Values of AIC and BIC of mixed-effect models and the base model for the second-order branches.
Table 4. Values of AIC and BIC of mixed-effect models and the base model for the second-order branches.
Model No.Mixed-Effect ParametersAICBIC
Tree LevelFirst-Order Branch Level
1β1, β2β1, β22098.22141.7
2β1, β2β12140.72174.6
3β1, β2β22165.42199.3
4β1β1, β22117.02150.9
5β1β12255.52279.7
6β1β22192.42216.6
7β2β1, β2misconvergence
8β2β12355.02379.3
9β2β23154.13178.3
Base model 3376.03390.5
Table 5. Values of AIC and BIC of mixed-effect models and the base model for the third-order branches.
Table 5. Values of AIC and BIC of mixed-effect models and the base model for the third-order branches.
Model No.Mixed-Effect ParametersAICBIC
Tree LevelFirst-Order Branch LevelSecond-Order Branch Level
1β1, β2β1, β2β1, β2misconvergence
2β1, β2β1, β2β1misconvergence
3β1, β2β1, β2β2572.4613.5
4β1, β2β1β1, β2misconvergence
5β1, β2β1β1585.6618.5
6β1, β2β1β2616.4649.4
7β1, β2β2β1, β2misconvergence
8β1, β2β2β1558.0590.9
9β1, β2β2β2622.9655.8
10β1β1, β2β1, β2misconvergence
11β1β1, β2β1555.7588.6
12β1β1, β2β2572.1605.1
13β1β1β1, β2misconvergence
14β1β1β1604.8629.5
15β1β1β2637.3662.0
16β1β2β1, β2misconvergence
17β1β2β1564.6589.3
18β1β2β2633.6658.3
19β2β1, β2β1, β2misconvergence
20β2β1, β2β1554.0587.0
21β2β1, β2β2570.2603.1
22β2β1β1, β2misconvergence
23β2β1β1586.5611.2
24β2β1β2621.6646.3
25β2β2β1, β2misconvergence
26β2β2β1569.0593.7
27β2β2β2696.5721.2
Base model 763.8776.2

2.4. Statistical Analysis

Model performances for different combinations of random parameters were evaluated using Akaike’s information criterion (AIC) and Schwarz’s Bayesian information criterion (BIC). The smaller the values of AIC and BIC, the better the model fits [49,50]. The significance of random effects was evaluated using the likelihood-ratio test. Comparison of the prediction capacities of the base model and mixed models was based on the graphical and numerical analysis of the residuals and the following goodness-of-fit statistics: average relative error (ARE) and root mean square error (RMSE). These were calculated by Equations (5) and (6):
A R E = 1 n i = 1 n y i y ^ i y i × 100 %
RMSE= i=1 n ( y i y ^ i ) 2 nk
where yi is the observed value, y ^ i is the predicted value, n the sample size, and k the number of model parameters.
Among the 16 trees measured, the data for 13 Chinese pine trees were randomly selected for model calibration and the other three trees for model validation. All statistical computations were implemented in R by means of the nlme package [51].

3. Results

3.1. Variability in Internode Size and Biomass within and among Trees

The variability of internode length and biomass was measured by the coefficient of variation (CV). The average CVs of the length and biomass of internodes within trees were 0.664 and 0.709, 0.782 and 1.031, and 1.195 and 1.184 for the first-, second-, and third-order branches, respectively. The biomass of the internodes presented higher variation than the length, and that variation increased with branch order. This indicates that there are obvious size variations within trees. Similar trends were also observed among trees. The average CVs for the length and biomass of internodes among trees were 0.396 and 0.412, 0.754 and 0.593, and 0.588 and 1.717 for the first-, second-, and third-order branches, respectively.
Scatter plots of internode length and biomass for the different branch orders illustrate the variation of the curves (Figure 1). Figure 2 provides the approximate 95% confidence intervals for parameters β1 and β2 in Equation (1) for the tree at the first-order branch and second-order branch levels. Substantial variation was noted in the allometric relationships between internode length and biomass within and among trees. We further used box-plots to check the distribution of parameters (Figure 3), which also indicated the difference in the median and mean values among branches. Parameter β1 is right-skewed, but β2 is left-skewed or right-skewed. Therefore, parameters β1 and β2 can reasonably be considered random effects.
Figure 2. Confidence intervals of parameters β1 and β2 for individual Chinese pine trees or for branches (A: trees; B: the first-order branches; C: the second-order branches).
Figure 2. Confidence intervals of parameters β1 and β2 for individual Chinese pine trees or for branches (A: trees; B: the first-order branches; C: the second-order branches).
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Figure 3. Box-plots of parameters β1 and β2 for the first-order branches, the second-order branches, and the third-order branches (dashed line indicates the mean value).
Figure 3. Box-plots of parameters β1 and β2 for the first-order branches, the second-order branches, and the third-order branches (dashed line indicates the mean value).
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3.2. Model Fitting and Validation

All models with fixed and random parameters were evaluated based on the fit statistics AIC and BIC listed in Table 3, Table 4 and Table 5. The values of AIC and BIC for all mixed-effects models were smaller than those of the base models. We selected the three models with the smallest AIC and BIC for first-, second-, and third-order branches for further calibration.
For the first-order branches, the mixed-effect model 1 with two random effect parameters, b1,i and b2,i, was selected (Table 3). Model 1 in Table 4 was selected as the calibrated model for the internodes on the second-order branches, where the random effects of fixed parameters β1 and β2 were considered at both the tree and first-order branch levels. For the internodes on the third-order branches, model 20 (Table 5) was selected for further calibration, where the random effect of fixed parameter β2 at the tree level, the random effects of fixed parameters β1 and β2 at the first-order branch level, and the random effects of fixed parameter β1 at the third-order branch level were considered.
The parameters of the fixed part and the variance and covariance of the random part of each mixed-effect model are listed in Table 6. All random effects were statistically significant with the exception of the tree-level effect on β1 and the second-order branch-level effect on β2 for models of third-order branches, demonstrating significant variability in fixed parameters between and within trees, and within and between branches, and indicating the necessity of including random effects in the allometric model. Random effects accounted for a high proportion of the variance, but the importance of the hierarchal levels differed (Table 6). Parameters β1 and β2 varied much more between trees than between branches, which indicates that the random effects resulting from different trees are stronger than those resulting from different branches. For branches of the same order, the random effects characterized by their variance in allometric models decreased with increasing branch order (Table 6). To examine possible reasons behind the pattern of variability, we used box-plots of random effects for parameters β1 and β2 for the second- and third-order branches among different sites, ages and densities to illustrate the parameter distribution (Figure 4 and Figure 5). Those for the first-order branches were not plotted because of the scarcity of data. They indicated that the distributions of random parameters clearly differ among sites, ages, and densities.
Table 6. Estimates of parameters for mixed models.
Table 6. Estimates of parameters for mixed models.
Fixed PartParameterFirst-Order BranchesSecond-Order BranchesThird-Order Branches
β194.792 (20.954)59.992(13.234)4.043(0.286)
β20.122(0.042)0.361(0.068)0.513(0.036)
Random Part Tree LevelTree LevelFirst-Order Branch LevelTree LevelFirst-Order Branch LevelSecond-Order Branch Level
σ 1 , k 2 5.478×1032.153×10393.700-2.6510.248
σ 2 , k 2 1.646 × 10−24.836 × 10−23.323 × 10−21.676 × 10−23.562 × 10−3-
σ 12 , k 2 −0.525−0.5920.709-0.879-
δ 2 3.514 0.378 0.116
Note: Standard errors are shown in parentheses.
Figure 4. Box-plots of random effects for parameters β1 and β2 for the second-order branches by site (S1–S4), age (A1–A5), and density (D1–D4) (dashed line denotes the mean value).
Figure 4. Box-plots of random effects for parameters β1 and β2 for the second-order branches by site (S1–S4), age (A1–A5), and density (D1–D4) (dashed line denotes the mean value).
Forests 05 02825 g004
Figure 5. Box-plots of random effects for parameters β1 and β2 for the third-order branches by site (S1–S4), age (A1–A5), and density (D1–D4) (dashed line denotes the mean value).
Figure 5. Box-plots of random effects for parameters β1 and β2 for the third-order branches by site (S1–S4), age (A1–A5), and density (D1–D4) (dashed line denotes the mean value).
Forests 05 02825 g005
The likelihood ratio test indicated that the model performances were improved by including random effects for all orders of branches. Compared with the base models for the first-, second- and third-order branches, the average relative error (ARE) and root mean squared error (RMSE) decreased by 69.14% and 60.82%, 46.43% and 25.35%, and 40.74% and 55.32%, respectively (Table 7). Residual distribution plots were constructed for the mixed-effect and base models (Figure 6). The inclusion of random effects in the models, which accounts for a large portion of the variability, effectively decreased the residuals and removed the heterogeneous residual variance. A one-sample Kolmogorov—Smirnov test indicated that the residuals of the mixed models are normally distributed (p = 0.383, 0.081, and 0.064 for Equations (2)–(4), respectively).
Table 7. Comparison between the base model and mixed model calibrations.
Table 7. Comparison between the base model and mixed model calibrations.
Branch OrderModelsAREARE Reduction (%)RMSERMSE Reduction (%)
1Base model0.071−25.355.745−69.14
Mixed model0.0531.773
2Base model0.027−40.741.460−60.82
Mixed model0.0160.572
3Base model0.047−55.320.560−46.43
Mixed model0.0210.300
Figure 6. The distributions of residuals for the base models and mixed-effect models (A: First-order branches; B: Second-order branches; C: Third-order branches).
Figure 6. The distributions of residuals for the base models and mixed-effect models (A: First-order branches; B: Second-order branches; C: Third-order branches).
Forests 05 02825 g006
The internode length predicted by the mixed models was compared to the observed values on the basis of bias and precision using the reserved validation data (three trees). The ARE and RMSE were calculated for each branch order for model validation (Table 8). The results indicated that both the ARE and RMSE of the mixed-effect models decreased compared with those of the base models for all branch orders. The ARE and RMSE decreased by 13.97% and 41.67%, 37.68% and 13.63%, and by 85.16% and 56.06% compared with the base models for the first-, second- and third-order branches, respectively.
Table 8. Comparison between base model and mixed model validation.
Table 8. Comparison between base model and mixed model validation.
Branch OrderModelsAREARE Reduction (%)RMSERMSEReduction (%)
1Base model0.087−13.974.616−13.63
Mixed model0.0753.594
2Base model0.036−41.671.226−85.16
Mixed model0.0210.182
3Base model0.069−37.680.503−56.06
Mixed model0.0430.221

4. Discussion

Allometric relationships in organisms are considered a universal phenomenon; however, the fact that universal scaling exponents cannot be defined for trees has previously been noted [23,52]. Here we have, for the first time, been able to attribute internode allometry to trees and branches of different orders, and showed the variation of internode allometry at different levels using hierarchical nonlinear mixed-effect models. These mixed models provided more accurate parameter estimations. We found significant variability in internode allometry within and between trees and branches, which was quantified as the variances of the random effects of shape and geometric parameters in the model. Of the random variation, the variation in the allometric relationships occurring between trees was much greater than that between branches, and variation between lower-order branches was much greater than between higher-order branches. We also tested Equation (1) after log-transformation of both sides, i.e. Ln(L) and Ln (Q) were treated as dependent and independent variables, respectively. The log-transformed equation, however, did not change our conclusion on the variation of allometry among different scales. Additionally, the values of scaling coefficient increased from the first- to third-level branches but the values of scaling exponent showed the opposite, which implies a complicated biomass allocation pattern. This may be attributed to the nonlinear relationship between biomass and length, characterized as a convex downward curve on the log-log coordinates. It is tempting to consider our findings with regard to the debate surrounding the mechanistic basis of metabolic scaling explained through the West, Brown, and Enquist (WBE) theory [53] or the Dynamic Energy Budget (DEB) theory [54,55,56,57,58,59,60]. Our results on the allometry between internode length and biomass were inconsistent with universal models such as elastic similarity, stress similarity, geometric similarity, and WBE, according to the results of Price [15]. This may further confirm the conclusion that universal scaling exponents cannot be defined for trees [23,52].
Many biotic and abiotic factors, as suggested by previous studies, may potentially affect allometric relationships, including genetics, ontogeny, size, age, structure, site, climate, and their interactions [2,25,26,31,54,61,62,63]. As shown in Figure 4 and Figure 5, parameters of the allometric equations for different sites, age groups, and stand densities were heterogeneous at different scales, which implied that site, age, and stand density are attributed to the variation of internode allometry within and among Chinese pine trees. Trees in different development stages have different growth patterns caused by chronological changes in light conditions, as illustrated by dynamic height-diameter allometry [64]. Site characteristics reflect local climate, soil, and topology, which affect internode (last internode of branches in this study) growth. Trees within a high-density stand always have strong competition from neighbors, which means they may receive limited light intensity, water, and nutrition during primary growth. Such competition-related phenotypic plasticity has been observed [41,65]. Besides the effects of stand age, site, and density, the topological position and the orientation of branches within trees are possible sources of variability, which can lead to a heterogeneous light environment; however, their effects are low compared with the allometric relationships among trees.
A constant allometry rule between the length and biomass of internodes in the GreenLab model (where branches belonging to the same order are identical) has been validated for crops and tree species in the literature [32,44]; however, random processes for growth, death, and branch pattern have also been applied to characterize stochastic structure and functioning in different versions of the GreenLab functional-structural model [66,67], especially stochastic modeling of annual tree shoot dynamics in the recent GL5 version [68]. In this study, single-level, nested two-level and nested three-level nonlinear mixed-effect models were developed for the internode allometry of first-, second-, and third-order branches of Chinese Pine, respectively. The random effects of the mixed models were significant at the tree, first-order, and second-order branch levels. The mixed models address coherence and variation by setting the structure of variance and covariance in the random part, thus improving the prediction accuracy of the model. The results indicated that all errors in the mixed models decrease compared to those of the base models for all branch orders. Ma et al. [69] evaluated the stability of GreenLab parameters in response to maize individuals from a common population, individuals from populations subjected to different environments (seasons), and different development stages of the same individuals by comparing their CVs. They concluded that parameter values were largely independent of developmental stage, but mean allometric mass ratios (the mean of the ratios of leaf blade to above-ground, leaf sheath to above-ground, internode/above-ground, and cob/above-ground), only showed 12.5% and 2.1% variation among seasons, inter- and intra-season, respectively. Unlike crops, trees have a complicated architecture and a more heterogeneous environment. There are some implications for the application of FSPM from our above findings. Tree- or branch-specific allometric models should be developed instead of averaged models to obtain unbiased and accurate internode length predictions. Such models will be useful in determining internode shape and generating stochastic structure as simulated using stochastic models [35,68,70], which will affect light interception, photosynthesis, and tree architecture in functional-structural modeling. Information about the allometric relationships of trees can be used in models to constrain the form and structure of trees to ensure that they conform to natural systems. The variation among trees and branches leads us to suggest that replication of the mid-internode sampling is required for accurate estimates of the internode mean. The study did not prove that estimation of internode allometry could improve the model quality of GreenLab since we neglected the functional part, but the tree- and branch-specific shape parameters and geometric parameters of internodes can be applied and tested in the GreenLab model in the future. Although we quantified the variation in internode allometry within the GreenLab framework, the methodology and conclusion have universal implications for functional-structural tree models.

5. Conclusions

An allometric model of internodes is of great importance for determining the shape of internodes in functional-structural tree modeling. We examined the variability of internode allometry by describing the relationship between internode length and biomass in Pinus tabulaeformis Carr. trees using a multilevel nonlinear mixed-effect model. We found that there was significant variability in allometry at the tree and different-order branch levels, and the variability decreased from trees, first-order branches to second-order branches. Therefore, tree- and branch-specific allometric models are recommended to produce unbiased and accurate internode length estimations with biological significance. The new model can be useful for improved descriptions and understanding of the structure and functioning of trees.

Acknowledgments

This study was supported by the Natural Science Foundation of China (Grant No. 30872022, 31100474). We thank Wei Xiang from Beijing Forestry University for helpful discussion on modelling. We acknowledge the three anonymous referees for their constructive comments and suggestions, which improved the manuscript.

Author Contributions

Jun Diao was the principal investigator for this study. He undertook tree sampling and measurements, performed the main data analyses, and wrote the manuscript. Xiangdong Lei supervised the research project and contributed to the study design, data collection and analysis, interpretation of results, and the writing and revision of earlier drafts until final approval. Jingcai Wang contributed to the presentation of the statistical results and revised the text. Jun Lu, Hong Guo, Liyong Fu, Chenchen Shen, Wu Ma, and Jianbo Shen contributed to the field tree measurements, results, discussion, and manuscript preparation.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Peters, R.H. The Ecological Implications of Body Size; Cambridge University Press: New York, NY, USA, 1983; pp. 197–198. [Google Scholar]
  2. Niklas, K.J. Plant Allometry: The Scaling of Form and Process; University Chicago Press: Chicago, IL, USA, 1994. [Google Scholar]
  3. Sievanen, R.; Nikinmaa, E.; Nygren, P.; Ozier-Lafontaine, H.; Perttunen, J.; Hakula, H. Components of functional-structural tree models. Ann. For. Sci. 2000, 57, 399–412. [Google Scholar]
  4. Vos, J.; Evers, J.B.; Buck-Sorlin, G.H.; Andrieu, B.; Chelle, M.; de Visser, P.H.B. Functional-structural plant modelling: A new versatile tool in crop science. J. Exp. Bot. 2010, 61, 2101–2115. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  5. Yan, H.P.; Kang, M.Z.; de Reffye, P.; Dingkuhn, M. A dynamic, architectural plant model simulating resource-dependent growth. Ann. Bot. 2004, 93, 591–602. [Google Scholar] [CrossRef] [PubMed]
  6. Cournède, P.H.; Mathieu, A.; Houllier, F.; Barthélémy, D.; de Reffye, P. Computing competition for light in the GREENLAB model of plant growth: A contribution to the study of the effects of density on resource acquisition and architectural development. Ann. Bot. 2008, 101, 1207–1219. [Google Scholar] [CrossRef] [PubMed]
  7. Evans, R.; Turkington, R. Maintenance of morphological variation in a biotically patchy environment. New Phytol. 1988, 109, 369–376. [Google Scholar] [CrossRef]
  8. Farnsworth, K.D.; van Gardingen, P.R. Allometric analysis of Sitka spruce branches: Mechanical versus hydraulic design principles. Trees Struct. Funct. 1995, 10, 1–12. [Google Scholar] [CrossRef]
  9. De Reffye, P.; Houllier, F.; Blaise, F.; Barthélémy, D.; Dauzat, J.; Auclair, D. A model simulating above- and below-ground tree architecture with agroforestry applications. Agrofor. Syst. 1995, 30, 175–197. [Google Scholar]
  10. Welham, C.V.J.; Turkington, R.; Sayre, C. Morphological plasticity of white clover (Trifolium repens L.) in response to spatial and temporal resource heterogeneity. Oecologia 2002, 130, 231–238. [Google Scholar]
  11. Salminen, H.; Jalkanen, R. Modelling variation of needle density of Scots pine at high latitudes. Silva Fenn. 2006, 40, 183–194. [Google Scholar] [CrossRef]
  12. Segura, V.; Denancé, C.; Durel, C.E.; Costes, E. Wide range QTL analysis for complex architectural traits in a 1-year-old apple progeny. Genome 2007, 50, 159–171. [Google Scholar] [CrossRef] [PubMed]
  13. Freeman, D.C.; Graham, J.H.; Emlen, J.M. Developmental stability in plants: Symmetries, stress and epigenesis. Genetica 1993, 89, 97–119. [Google Scholar] [CrossRef]
  14. Price, C.A.; Ogle, K.; White, E.P.; Weitz, J.S. Evaluating scaling models in biology using hierarchical Bayesian approaches. Ecol. Lett. 2009, 12, 641–651. [Google Scholar] [CrossRef] [PubMed]
  15. Duursma, R.A.; Mäkelä, A.; Reid, D.E.B.; Jokela, E.J.; Porté, A.J.; Roberts, S.D. Self-shading effects allometric scaling in trees. Funct. Ecol. 2010, 24, 723–730. [Google Scholar] [CrossRef]
  16. Kolokotrones, T.; van, S.; Deeds, E.J.; Fontana, W. Curvature in metabolic scaling. Nature 2010, 464, 753–756. [Google Scholar] [CrossRef] [PubMed]
  17. Pretzsch, H.; Dieler, J. Evidence of variant intra- and interspecific scaling of tree crown structure and relevance for allometric theory. Oecologia 2012, 169, 637–649. [Google Scholar] [CrossRef] [PubMed]
  18. Chen, X.; Huber, H.; de Kroon, H.; Peeters, A.J.M.; Poorter, H.; Voesenek, L.A.C.J.; Visser, E.J.W. Intraspecific variation in the magnitude and pattern of flooding-induced shoot elongation in Rumex palustris. Ann. Bot. 2009, 104, 1057–1067. [Google Scholar] [CrossRef] [PubMed]
  19. Albert, C.H.; Thuiller, W.; Yoccoz, N.G.; Soudant, A.; Boucher, F.; Saccone, P.; Lavorel, S. Intraspecific functional variability: Extent, structure and sources of variation. J. Ecol. 2010, 98, 604–613. [Google Scholar] [CrossRef]
  20. Albert, C.H.; de Bello, F.; Boulangeat, I.; Pellet, G.; Lavorel, S.; Thuillet, W. On the importance of intraspecific variability for the quantification of functional diversity. Oikos 2012, 121, 116–126. [Google Scholar] [CrossRef]
  21. Bolnick, D.I.; Amarasekare, P.; Araújo, M.S.; Bürger, R.; Levine, J.; Novak, M.; Rudolf, V.H.; Schreiber, S.; Urban, M.; Vasseur, D.; et al. Why intraspecific trait variation matters in community ecology. Trends. Ecol. Evol. 2011, 26, 183–192. [Google Scholar] [CrossRef] [PubMed]
  22. White, C.R.; Cassey, P.; Blackburn, T.M. Allometric exponents do not support a universal metabolic allometry. Ecology 2007, 88, 315–323. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  23. Niklas, K.J. Size-dependent allometry of tree height, diameter and trunk taper. Ann. Bot. 1995, 75, 217–227. [Google Scholar] [CrossRef]
  24. Kaitaniemi, P.; Lintunen, A. Precision of allometric scaling equations for trees can be improved by including the effect of ecological interactions. Trees Struct. Funct. 2008, 22, 579–584. [Google Scholar] [CrossRef]
  25. Feldpausch, T.R.; Banin, L.; Phillips, O.L.; Baker, T.R.; Lewis, S.L.; Quesada, C.A.; Affum-Baffoe, K.; Arets, E.J.M.M.; Berry, N.J.; Bird, M.; Brondizio, E.S.; de Camargo, P. Height-diameter allometry of tropical forest trees. Biogeosciences 2011, 8, 1081–1106. [Google Scholar] [CrossRef] [Green Version]
  26. Ducey, M.J. Evergreenness and wood density predict height-iameter scaling in trees of the northeastern United States. For. Ecol. Manag. 2012, 279, 21–26. [Google Scholar] [CrossRef]
  27. Hui, D.F.; Wang, J.; Le, X.; Shen, W.J.; Ren, H. Influences of biotic and abiotic factors on the relationship between tree productivity and biomass in China. For. Ecol. Manag. 2012, 264, 72–80. [Google Scholar] [CrossRef]
  28. Pretzsch, H. Species-specific allometric scaling under self-thinning: Evidence from long-term 28 plots in forest stands. Oecologia 2006, 146, 572–583. [Google Scholar] [CrossRef] [PubMed]
  29. Pretzsch, H. Re-evaluation of allometry: State-of-the-art and perspective regarding individuals and stands of woody plants. Prog. Bot. 2010, 71, 339–369. [Google Scholar]
  30. Dahle, G.A.; Grabosky, J.C. Allometric patterns in Acer platanoides (Aceraceae) branches. Trees Struct. Funct. 2009, 24, 321–326. [Google Scholar] [CrossRef]
  31. Mäkelä, A.; Valentine, A.; Valentine, H. Crown ratio influences allometric scaling in trees. Ecology 2006, 87, 967–972. [Google Scholar] [CrossRef]
  32. Letort, V.; Cournède, P.H.; Mathieu, A.; de Reffye, P.; Constant, T. Parametric identification of a functional structural tree growth model and application to beech trees (Fagus Sylvatica.). Funct. Plant Biol. 2008, 35, 951–963. [Google Scholar] [CrossRef]
  33. Guo, H.; Lei, X.D.; Letort, V.; Lu, Y.C.; de Reffye, P. A functional-structural model GreenLab for Pinus tabulaeformis. Chin. J. Plant Ecol. 2009, 33, 950–957. [Google Scholar]
  34. Guo, H.; Lei, X.D.; Letort, V.; Lu, Y.C. A functional-structural model for adults of Pinus tabulaeformis based on GreenLab. Chin. J. Plant Ecol. 2011, 35, 422–430. [Google Scholar] [CrossRef]
  35. Wang, F.; Kang, M.Z.; Lu, Q.; Han, H.; Letort, V.; Guo, Y.; de Reffye, P.H.; Li, B.G. Calibration of topological development in the procedure of parametric identification: Application of the stochastic GreenLab model for Pinus sylvestris var. mongolica. In Proceedings of the Third International Symposium on Plant Growth Modeling, Simulation, Visualization and Applications—PMA’09. IEEE Computer Society, Beijing, China, 9–13 November 2010; pp. 26–33.
  36. Wang, F.; Kang, M.Z.; Lu, Q.; Letort, V.; Han, H.; Guo, Y.; de Reffye, P.; Li, B.G. A stochastic model of tree architecture and biomass partitioning: Application to Mongolian Scots pines. Ann. Bot. 2011, 107, 781–792. [Google Scholar] [CrossRef] [PubMed]
  37. Segura, V.; Cilas, C.; Laurens, F.; Costes, E. Dissecting apple tree architecture into genetic, ontogenetic and environmental effects: Mixed linear modelling of repeated spatial and temporal measures. New Phytol. 2008, 178, 302–314. [Google Scholar] [CrossRef] [PubMed]
  38. Fox, J.P.; Glas, C.A.W. Bayesian estimation of a multilevel IRT model using Gibbs sampling. Psychometrika 2001, 66, 271–288. [Google Scholar] [CrossRef]
  39. Cam, E.; Link, W.; Cooch, E.; Monnat, J.; Danchin, E. Individual covariation in life-history traits: Seeing the trees despite the forest. Am. Nat. 2002, 159, 96–105. [Google Scholar] [CrossRef] [PubMed]
  40. Clark, J.S.; LaDeau, S.; Ibanez, I. Fecundity of trees and the colonizationcompetition hypothesis. Ecol. Monogr. 2004, 74, 415–442. [Google Scholar] [CrossRef]
  41. Schneider, M.K.; Law, R.; Illian, J.B. Quantification of neighborhood-dependent plant growth by Bayesian hierarchical modelling. J. Ecol. 2006, 94, 310–321. [Google Scholar] [CrossRef]
  42. Lindstrom, M.J.; Bates, D.M. Nonlinear mixed effects models for repeated measures data. Biometrics 1990, 4, 673–687. [Google Scholar] [CrossRef]
  43. Hall, D.B.; Bailey, R.L. Modeling and prediction of forest growth variables based on multilevel nonlinear mixed models. For. Sci. 2001, 47, 311–321. [Google Scholar]
  44. Guo, H.; Lei, X.D.; Cournede, P.; Letort, V. Characterization of the effects of inter-tree competition on source-sink balance in Chinese pine trees with the GreenLab model. Trees Struct. Funct. 2012, 26, 1057–1067. [Google Scholar] [CrossRef]
  45. De Reffye, P.; Blaise, F.; Chemouny, S.; Jaffuel, S.; Fourcaud, T.; Houllier, F. Calibration of a hydraulic architecture-based growth model of cotton plants. Agronomie 1999, 19, 265–280. [Google Scholar] [CrossRef]
  46. Song, Y.H.; Guo, Y.; de Reffye, P.H. Plant morphological constructing based on organ biomass accumulation. Acta Entomol. 2003, 23, 2579–2586. [Google Scholar]
  47. Zhan, Z.G. Study on a structure-function model of plant growth and its calibration. Ph.D. Thesis, China Agricultural University, Beijing, China, 2001; p. 25. [Google Scholar]
  48. Pinheiro, J.C.; Bates, D.M. Mixed-Effects Models in s and s-Plus; Springer-Verlag: New York, NY, USA, 2000. [Google Scholar]
  49. Nothdurft, A.; Kublin, E.; Lappi, J. A non-linear hierarchical mixed model to describe tree height growth. Eur. J. For. Res. 2006, 125, 281–289. [Google Scholar] [CrossRef]
  50. Dorado, F.C.; Ulises, D.A.; Diéguez-Aranda, U.; Marcos, B.A.; Anta, M.B.; Rodríguez, M.S.; von Gadow, K. A generalized height-diameter model including random components for radiata pine plantations in northwestern Spain. For. Ecol. Manag. 2006, 229, 202–213. [Google Scholar] [CrossRef]
  51. R Development Core Team. R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing: Vienna, Austria, 2013. ISBN 3-900051-07-0. Available online: http://www.r-project.org (accessed on 13 October 2013).
  52. Chambers, J.Q.; Dos Santos, J.; Ribeiro, R.J.; Higuchi, N. Tree damage, allometric relationships, and aboveground net primary production in central Amazon forest. For. Ecol. Manag. 2001, 152, 73–84. [Google Scholar] [CrossRef]
  53. West, G.B.; Brown, J.H.; Enquist, B.J. A general model for the origin of allometric scaling laws in biology. Science 1997, 276, 122–126. [Google Scholar] [CrossRef] [PubMed]
  54. Kooijman, S.A.L.M. Dynamic Energy and Mass Budgets in Biological Systems, 2nd ed.; Cambridge University Press: England, Cambridge, 2000. [Google Scholar]
  55. Kozlowski, J.; Konarzewski, M. Is West, Brown and Enquist’s model of allometric scaling mathematically correct and biologically relevant? Funct. Ecol. 2004, 18, 283–289. [Google Scholar] [CrossRef]
  56. Kozlowski, J.; Konarzewski, M. West, Brown and Enquist’s model of allometric scaling again: The same questions remain. Funct. Ecol. 2005, 19, 739–743. [Google Scholar] [CrossRef]
  57. Brown, J.; West, G.; Enquist, B. Yes, West, Brown and Enquist’s model of allometric scaling is both mathematically correct and biologically relevant. Funct. Ecol. 2005, 19, 735–738. [Google Scholar] [CrossRef]
  58. Muller-Landau, H.C.; Condit, R.S.; Chave, J.; Thomas, S.C.; Bohlman, S.A.; Bunyavejchewin, S.; Davies, S.; Foster, R.; Gunatilleke, S.; Gunatilleke, N.; Harms, K.E.; et al. Testing metabolic ecology theory for allometric scaling of tree size, growth and mortality in tropical forests. Ecol. Lett. 2006, 9, 575–588. [Google Scholar] [CrossRef] [PubMed]
  59. Price, C.A.; Gilooly, J.F.; Allen, A.P.; Weitz, J.S.; Niklas, K.J. The metabolic theory of ecology: Prospects and challenges for plant biology. New Phytol. 2010, 188, 696–710. [Google Scholar] [CrossRef] [PubMed]
  60. Price, C.A.; Weitz, J.S.; Savage, V.M.; Stegen, J.; Clarke, A.; Coomes, D.A.; Dodds, P.S.; Etienne, R.S.; Kerkhoff, A.J.; McCulloh, K.; Niklas, K.J.; Olff, H.; Swenson, N.G. Testing the metabolic theory of ecology. Ecol. Lett. 2012, 15, 1465–1474. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  61. Wang, X.; Fang, J.; Tang, Z.; Zhu, B. Climatic control of primary forest structure and DBH-height allometry in Northeast China. For. Ecol. Manag. 2006, 234, 264–274. [Google Scholar] [CrossRef]
  62. Hein, S.; Spiecker, H. Crown and tree allometry of open-grown ash (Fraxinus excelsior L.) and sycamore (Acer pseudoplatanus L.). Agrofor. Syst. 2008, 73, 205–218. [Google Scholar]
  63. Puntieri, J.G.; Ghirardi, S. Growth-unit structure in trees: Effects of branch category and position in Nothofagus nervosa, N. obliqua and their hybrids (Nothofagaceae). Trees Struct. Funct. 2010, 24, 657–665. [Google Scholar] [CrossRef]
  64. Henry, H.A.L.; Aarssen, L.W. The interpretation of stem diameter-height allometry in trees: Biomechanical constraints, neighbour effects, or biased regressions? Ecol. Lett. 1999, 2, 89–97. [Google Scholar] [CrossRef]
  65. Vieilledent, G.; Courbaud, B.; Kunstler, G.; Dhôte, J.F.; Clark, J.S. Individual variability in tree allometries determines light resource allocation in forest ecosystems: A hierarchical Bayesian approach. Oecologia 2010, 163, 759–773. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  66. Kang, M.Z.; Cournède, P.H.; de Reffye, P.; Hu, B.G. Analytic study of a stochastic plant growth model: Application to the GreenLab model. Math. Comput. Simul. 2008, 78, 57–75. [Google Scholar] [CrossRef]
  67. Mathieu, A.; Cournède, P.H.; Letort, V.; Barthélémy, D.; de Reffye, P. A dynamic model of plant growth with interactions between development and functional mechanisms to study plant structural plasticity related to trophic competition. Ann. Bot. 2009, 103, 1173–1186. [Google Scholar] [CrossRef] [PubMed]
  68. De Reffye, P.; Kang, M.Z.; Hua, J.; Auclair, D. Stochastic modelling of tree annual shoot dynamics. Ann. For. Sci. 2012, 69, 153–169. [Google Scholar] [CrossRef]
  69. Ma, Y.T.; Li, B.G.; Zhan, Z.G.; Guo, Y.; Luquet, D.; de Reffye, P.; Dingkuhn, M. Parameter stability of the functional-structural plant model GREENLAB as affected by variation within populations, among seasons and among growth stages. Ann. Bot. 2007, 99, 61–73. [Google Scholar] [CrossRef] [PubMed]
  70. Diao, J.; de Reffye, P.; Lei, X.D.; Guo, H.; Letort, V. Simulation of the topological development of young eucalyptus using a stochastic model and sampling measurement strategy. Comput. Electron. Agric. 2012, 80, 105–114. [Google Scholar] [CrossRef] [Green Version]

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Diao, J.; Lei, X.; Wang, J.; Lu, J.; Guo, H.; Fu, L.; Shen, C.; Ma, W.; Shen, J. Quantifying the Variability of Internode Allometry within and between Trees for Pinus tabulaeformis Carr. Using a Multilevel Nonlinear Mixed-Effect Model. Forests 2014, 5, 2825-2845. https://doi.org/10.3390/f5112825

AMA Style

Diao J, Lei X, Wang J, Lu J, Guo H, Fu L, Shen C, Ma W, Shen J. Quantifying the Variability of Internode Allometry within and between Trees for Pinus tabulaeformis Carr. Using a Multilevel Nonlinear Mixed-Effect Model. Forests. 2014; 5(11):2825-2845. https://doi.org/10.3390/f5112825

Chicago/Turabian Style

Diao, Jun, Xiangdong Lei, Jingcai Wang, Jun Lu, Hong Guo, Liyong Fu, Chenchen Shen, Wu Ma, and Jianbo Shen. 2014. "Quantifying the Variability of Internode Allometry within and between Trees for Pinus tabulaeformis Carr. Using a Multilevel Nonlinear Mixed-Effect Model" Forests 5, no. 11: 2825-2845. https://doi.org/10.3390/f5112825

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