生物多样性

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广东南岭16个1-ha动态监测样地植物群落组成与结构

黄莉1#, 刘志发2#, 龚粤宁2, 李步杭1, 张健1*   

  1. 1中山大学生命科学学院,广州 510275; 2 广东南岭国家级自然保护区, 广东乳源 512727
  • 收稿日期:2025-09-04 修回日期:2026-01-21 接受日期:2026-03-16
  • 通讯作者: 张健

Plant community composition and structure of sixteen 1-ha dynamics monitoring plots of Nanling Mountains in Guangdong province

Li Huang1#, Zhifa Liu2#, Yuening Gong2, Buhang Li1, Jian Zhang1*   

  1. 1 School of Life Sciences, Sun Yat-sen University, Guangzhou 510275, China 

    2 Guangdong Nanling National Nature Reserve, Ruyuan, Guangdong 512727, China

  • Received:2025-09-04 Revised:2026-01-21 Accepted:2026-03-16
  • Contact: Jian Zhang

摘要: 南岭山地是中国中亚热带与南亚热带过渡的核心生态廊道, 热带和温带植物区系在此交汇过渡, 是众多植物分布的南北界限。本研究基于广东南岭国家级自然保护区内建立的跨越整个保护区、覆盖代表性森林类型的16个1-ha长期森林动态监测样地, 调查与分析了样地内胸径 ≥ 1 cm的木本植物物种组成、区系特征、径级分布以及物种空间分布。结果表明:16个样地共记录木本植物独立个体75,141株(含分枝为100,923株), 隶属于78科220属582种, 其中热带成分共137属398种, 温带成分共80属174种, 分别占总属数的62%和36%, 占总种数的68%和30%, 其余3属10种为世界分布成分。物种数最高的样地有229种, 物种数最低的样地仅87种。各样地乔木层重要值最高的物种都不相同, 较好地代表了南岭山地主要森林类型。所有样地整体径级结构均呈倒J型, 但各样地优势树种和同一树种在不同样地呈不同的径级结构。种-面积曲线揭示16个样地物种数随面积的增长速度与饱和阈值存在明显差异; 平均来说, 当取样面积400 m²时, 所含物种数仅占总物种数的30%, 达90%物种覆盖需6,600 m²。物种空间分布在不同植被类型和径级间存在较大差异, 且各样地不同优势种呈现不同的生境偏好, 同一物种(如:木荷Schima superba、马尾松Pinus massoniana等)在不同样地呈现不同的分布格局。本研究揭示了南岭山地不同植被类型在物种组成、群落结构与空间分布格局等方面的差异, 为亚热带山地森林生物多样性长期监测体系的构建及国家公园的规划建设提供了科学依据。

关键词: 南岭山地, 亚热带森林, 常绿阔叶林, 群落结构, 物种多样性

Abstract

Aims: The Nanling mountains serve as a key ecological corridor and transition zone between the mid- and south-subtropical regions of China. Both the tropical and temperate floras converge in this region, and therefore it is the northern or southern distributional boundaries of many plant species. 

Methods: Based on 16 1-ha forest dynamic monitoring plots established across the Guangdong Nanling National Nature Reserve, covering all main vegetation types spanning the whole region, we analyzed the species composition, floristic characteristics, size distribution, and spatial distributions of woody plants with ≥ 1 cm DBH (diameter at breast height). 

Results: There were 75,141 individual trees and shrubs (100,923 stems including branches) in these 16 plots, belonging to 582 species, 220 genera, and 78 families. Among them, we identified 137 tropical genera (398 species; 62% of total genera, 68% of total species) and 80 temperate genera (174 species; 36% of total genera, 30% of total species), and 3 cosmopolitan genera (10 species). The plot with the highest richness had 229 species, while the plot with the lowest had only 87 species. The dominant species in the tree layer varied across plots, effectively representing the main forest types in the Nanling Mountains. Overall, all the plots exhibited stable inverse J-shaped size distributions for all the individuals together, but dominant species in each plot and the same species among the plots varied considerably in size distribution. The results of species-area curves suggested dramatic differences in the species accumulation rates and saturation thresholds among the 16 plots. On average, when a 400 m² plot is sampled, only 30% of total plant richness is covered, while 90% species coverage is achieved when the plot size of 6,600 m².is surveyed. Spatial distribution patterns varied significantly across different vegetation types and diameter classes. Dominant species showed distinct habitat preferences, and the same species (e.g., Schima superba and Pinus massoniana) displayed divergent spatial patterns across plots. 

Conclusion: This study demonstrates large variations in plant species composition, community structure, and species’ spatial distributions among distinct vegetation types of the Nanling Mountains. These results provide the basis for long-term biodiversity monitoring in subtropical montane forests and the development of the national park network.

Key words: Nanling Mountains, subtropical forest, evergreen broad-leaved forest, community structure, species diversity