
生物多样性 ›› 2025, Vol. 33 ›› Issue (11): 25309. DOI: 10.17520/biods.2025309 cstr: 32101.14.biods.2025309
仝蟠龙1,2, 张瀚文2,3, 王艳梅1,*(
), 王顺忠2,*, 祝燕2,*(
)
收稿日期:2025-08-04
接受日期:2025-10-22
出版日期:2025-11-20
发布日期:2025-12-26
通讯作者:
王艳梅,王顺忠,祝燕
基金资助:
Panlong Tong1,2, Hanwen Zhang2,3, Yanmei Wang1,*(
), Shunzhong Wang2,*, Yan Zhu2,*(
)
Received:2025-08-04
Accepted:2025-10-22
Online:2025-11-20
Published:2025-12-26
Contact:
Yanmei Wang, Shunzhong Wang, Yan Zhu
Supported by:摘要:
揭示暖温带森林幼苗群落物种组成的时间动态规律及驱动机制, 对理解森林更新过程和制定科学抚育措施具有重要意义。本研究基于北京东灵山20 ha森林动态监测样地内1 m × 1 m幼苗样方2021-2024年的连续监测数据, 采用时间beta多样性指数(temporal beta diversity index, TBI)及其损失(losses)/增益(gains)组分, 分析了幼苗群落组成的时间变化特征, 并评估了与幼苗生长指标、林分结构、土壤和地形因子的关系, 以确定其主要驱动因子。结果表明: 幼苗群落的TBI呈缓慢上升趋势, 其中2022-2023年物种损失大于增益, 2021-2022及2023-2024年则以物种增益为主。TBI与幼苗平均高度显著负相关, 与幼苗总盖度和树木多度正相关, 未发现其与土壤和地形因子有显著关联。幼苗群落的时间动态呈阶段性变化: 2022-2023年度主要由林分结构驱动, 导致以物种损失为主; 2023-2024年度则转入资源释放阶段, 促进了物种增益, 该动态主要受幼苗生长指标调控, 未来可通过长期监测更好地明确幼苗更新的动态过程。研究结果可为暖温带次生林抚育与可持续经营提供理论依据。
仝蟠龙, 张瀚文, 王艳梅, 王顺忠, 祝燕 (2025) 北京东灵山木本幼苗时间beta多样性的变化驱动因子. 生物多样性, 33, 25309. DOI: 10.17520/biods.2025309.
Panlong Tong, Hanwen Zhang, Yanmei Wang, Shunzhong Wang, Yan Zhu (2025) Drivers of temporal beta diversity in woody seedlings in Donglingshan, Beijing. Biodiversity Science, 33, 25309. DOI: 10.17520/biods.2025309.
图1 东灵山20 ha暖温带落叶阔叶林动态监测样地幼苗群落物种时间beta多样性指数(TBI)和损失(Losses)/增益(Gains)在2021-2024年的变化。Losses和Gains分别代表物种的损失和收益。如果TBI值为1, 代表这个区域随着时间跨度的物种组成完全不同。如果Losses值为1, 代表这个区域随着时间跨度全部由物种损失所主导。反之, Gains值为1, 代表这个区域随着时间跨度全部由物种增益所主导。
Fig. 1 Changes in temporal beta diversity index (TBI) and its components, losses and gains, in the seedling community of 20-ha warm temperate deciduous broad-leaved forest dynamics plot in Donglingshan from 2021 to 2024. Losses represents species loss, and Gains represents species gain. A TBI value of 1 indicates that the species composition of the area has completely changed over the time span. A Losses value of 1 indicates that the area is dominated entirely by species loss over the time span. A Gains value of 1 indicates that the area is dominated entirely by species gain over the time span.
图2 东灵山20 ha暖温带落叶阔叶林动态监测样地幼苗群落增益/损失图。Losses和Gains分别代表物种的损失和收益。正方形(增益)和圆形(损失)分别代表450个幼苗样方(点)。红线与绿线平行(即斜率为1)。符号大小与TBI统计成正比。如果绿线在红线之上, 表明物种损失占主导地位; 反之, 则物种增益占主导地位。
Fig. 2 Gains/losses of seedling communities in the 20-ha warm temperate deciduous broad-leaved forest dynamics plot in Donglingshan. Squares (Gains) and circles (Losses) represent 450 seedling quadrats (points). The red and yellow lines are parallel (with a slope of 1). The size of the symbols is proportional to the TBI statistic. If the yellow line is above the red line, it indicates that species losses dominate; conversely, species gains dominate.
图3 东灵山20 ha暖温带落叶阔叶林动态监测样地幼苗群落2022-2024年生物(a、d)、地形(b、e)和土壤(c、f)因子对时间beta多样性指数(TBI)的影响。Height: 幼苗平均高度; Trunk.B: 幼苗平均主干叶片数量; Root.B: 幼苗平均根萌叶片数量; Total.C: 幼苗总盖度; ABUN.S: 幼苗多度; ABUN.T: 树木多度; Dbh.T: 树木胸径; Canopy.C: 冠层盖度; Elev: 海拔; Convex: 凹凸度; Slope: 坡度; TOC: 总有机碳; TIC: 总无机碳; 圆圈和短线分别代表标准化回归系数估计值和95%置信区间。实心圆代表效应显著(P < 0.05), 空心圆代表不显著(P ≥ 0.05)。
Fig. 3 Effects of biotic (a, d), topographic (b, e), and soil (c, f) factors on temporal beta diversity index (TBI) in the 20 ha warm temperate deciduous broad-leaved forest dynamic plot in Donglingshan seedling communities from 2022-2024. Height, Average height of seedlings; Trunk.B, Average number of main leaves on the seedlings; Root.B, Average number of root-derived leaves per seedling; Total.C, Total seedling coverage; ABUN.S, Seedling abundance; ABUN.T, Tree abundance; Dbh.T, Tree DBH; Canopy.C, Canopy cover; Elev, Elevation; Convex, Convexity; Slope, Slope; TOC, Total organic carbon; TIC, Total inorganic carbon. The circles and short lines represent the estimated values of standardized regression coefficients and the 95% confidence interval, respectively. A solid circle means the effect is significant (P < 0.05), while a hollow circle is not significant (P ≥ 0.05).
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