Gautam Pratima, Joshi Rajeev, Ayer Santosh, Gautam Jeetendra, Bhatta Kishor Prasad, Lamichhane Prakash
Department of General Forestry, Agriculture and Forestry University, Hetauda, Makwanpur 44107, Nepal.
Department of Silviculture and Forest Biology, College of Natural Resource Management, Faculty of Forestry, Agriculture and Forestry University, Katari, Udayapur 56310, Nepal.
Scientifica (Cairo). 2024 Dec 19;2024:5518089. doi: 10.1155/sci5/5518089. eCollection 2024.
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 (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 . We observed higher mean diameter growth rates in 0-25 cm and 101-125 cm tree diameter classes (0.318 cm·yr). 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. = 0.32) performed better than the linear mixed model (adj. = 0.23) and the multiple linear model (adj. = 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 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.
在存在复杂地理特征的情况下,模型的开发至关重要,而进行森林资源清查既耗时又昂贵,需要大量的人工测量。获取有关森林状况和未来发展的可靠数据对于做出明智的森林管理决策至关重要。因此,本研究旨在创建一个专门针对(B. Heyne. ex Roth)的单木直径生长模型。本研究在尼泊尔的特莱弧形景观区进行,该区域涵盖尼泊尔特莱和丘雷地区的14个区。通过尼泊尔政府为森林研究评估维护的673个样地,获取了三个不同时间段(2011年、2017年和2022年)的单木数据(胸径、树高、冠高、树冠覆盖度、经度和纬度),并估算了年直径生长量。采用多元线性、线性混合和广义相加模型来拟合单木直径生长的生长模型。我们观察到在0 - 25厘米和101 - 125厘米的树径等级中平均直径生长速率较高(0.318厘米·年)。不同树木质量等级的直径生长存在显著差异,但未观察到因树冠等级导致的显著差异。尽管广义相加模型(调整后 = 0.32)的表现优于线性混合模型(调整后 = 0.23)和多元线性模型(调整后 = 0.03),但它仍仅解释了直径生长变异的一小部分。这表明其他因素,如未测量的环境变量、生物相互作用或复杂的非线性关系,可能在解释变异方面发挥重要作用。此外,较低的 值表明模型可能需要进一步优化,可能通过纳入交互项、随机效应或其他可能的非线性方法。未来的研究还应考虑空间或时间异质性对生长动态的潜在影响。