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. 2024 Dec 19:2024:5518089.
doi: 10.1155/sci5/5518089. eCollection 2024.

Individual Diameter Growth Modeling of Terminalia alata (B. Heyne. ex Roth) in Terai Arc Landscape of Nepal

Affiliations

Individual Diameter Growth Modeling of Terminalia alata (B. Heyne. ex Roth) in Terai Arc Landscape of Nepal

Pratima Gautam et al. Scientifica (Cairo). .

Abstract

The development of a model is highly crucial in cases where there are intricate geographical features, and conducting a forest inventory is both time-consuming and expensive, requiring significant manual effort for measurement. Acquiring reliable data regarding the forest's condition and future progression is essential for making informed decisions about its management. Therefore, this research aimed to create an individual tree diameter growth model specifically for Terminalia alata (B. Heyne. ex Roth). This study was conducted in Terai Arc Landscape of Nepal, encompassing 14 districts in the Terai and Chure regions of Nepal. Individual tree data (diameter at breast height, tree height, crown height, crown cover, longitude, and latitude) from three different time periods (2011, 2017, and 2022) were obtained with 673 sample plots maintained for forest research assessment by Government of Nepal, and annual diameter growth was estimated. Multiple linear, linear mixed, and generalized additive models were employed to fit the growth modeling for individual tree diameter growth of T. alata. We observed higher mean diameter growth rates in 0-25 cm and 101-125 cm tree diameter classes (0.318 cm·yr-1). There were significant differences in diameter growth across tree quality classes, but no significant differences due to crown classes were observed. Although the generalized additive model (Adj. R 2 = 0.32) performed better than the linear mixed model (adj. R 2 = 0.23) and the multiple linear model (adj. R 2 = 0.03), it still explained only a small proportion of the variance in diameter growth. This suggests that other factors, such as unmeasured environmental variables, biotic interactions, or complex nonlinear relationships, may play a significant role in explaining the variation. In addition, the low R 2 values indicate that the models may need further refinement, possibly by incorporating interaction terms, random effects, or other possible nonlinear approaches. Future research should also consider the potential influence of spatial or temporal heterogeneity on the growth dynamics.

Keywords: Terai Arc Landscape; diameter measurement; forest inventory; individual growth modeling; regression models.

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Conflict of interest statement

The authors declare no conflicts of interest.

Figures

Figure 1
Figure 1
Study area map of TAL Nepal showing established 673 sample plots.
Figure 2
Figure 2
Layout of concentric sample plots for trees and subplots for soil and smaller vegetation (source: [24]).
Figure 3
Figure 3
The location of the trees (X-axis and Y-axis represent longitude and latitude, respectively).
Figure 4
Figure 4
Annual DBH growth in each crown class. X-axis represents crown class and Y-axis represent DBH growth (cm·yr−1).
Figure 5
Figure 5
Annual DBH growth in each quality class. X-axis and Y-axis represent quality class and DBH growth (cm·yr−1). The “n” value represents the number of trees within each quality class.

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