林业科学 ›› 2026, Vol. 62 ›› Issue (4): 55-67.doi: 10.11707/j.1001-7488.LYKX20250710
收稿日期:2025-11-25
出版日期:2026-04-15
发布日期:2026-04-11
通讯作者:
雷相东
E-mail:xdlei@ifirit.ac.cn
基金资助:
Wenqiang Gao1,Xiangdong Lei1,*(
),Xiao He1,Yutang Li2
Received:2025-11-25
Online:2026-04-15
Published:2026-04-11
Contact:
Xiangdong Lei
E-mail:xdlei@ifirit.ac.cn
摘要:
目的: 分析东北温带森林树种多样性与地上生物量的关系随森林类型和发育阶段的变化规律,揭示生态位互补效应和质量比效应在其中的作用机制,为通过优化树种组成提升东北林区次生林质量的经营实践提供科学依据。方法: 基于吉林省国家森林资源连续清查样地数据,采用线性混合效应模型,在控制气候、土壤和林分因子的基础上,分析不同森林类型(阔叶纯林、阔叶混交林和针阔混交林)和发育阶段下树种多维多样性(物种丰富度、功能多样性、谱系多样性和群落加权平均性状值)对地上生物量的影响。应用广义可加模型,揭示多样性效应随森林发育阶段的动态变化,并借助结构方程模型,解析环境因子、森林类型、发育阶段和林分密度对树种多样性与地上生物量关系的直接和间接影响。结果: 1) 在3类温带森林中,物种丰富度、功能多样性和谱系多样性均对地上生物量具有显著正效应,群落加权平均性状值则表现出显著的正向或负向影响,表明生态位互补效应和质量比效应在温带森林地上生物量积累过程中共同发挥作用。2) 树种多样性对地上生物量的影响随森林发育阶段变化呈现显著的森林类型依赖性。3类森林的多样性(物种丰富度、功能多样性、谱系多样性)效应均从幼龄林到成熟林阶段表现为递减趋势;阔叶纯林和针阔混交林的群落加权平均性状值效应(质量比效应)均在幼龄林、成熟林和过熟林较高,阔叶混交林的群落加权平均性状值效应随森林发育阶段变化无明显趋势。阔叶混交林和针阔混交林在成熟林和过熟林阶段的群落加权平均性状值效应均大于功能多样性效应。3) 结构方程模型分析表明,环境因素(气候、土壤)、林分特征、森林类型和发育阶段共同调控森林生物多样性和地上生物量,其中森林类型和发育阶段通过调控林分密度和生物多样性间接影响地上生物量。结论: 在东北温带森林中,物种丰富度、功能多样性、谱系多样性和群落加权平均性状值均对地上生物量具有显著影响,但其影响强度因森林类型和发育阶段而异。在森林管理和生态恢复实践中,应依据具体森林类型和发育阶段分类实施精准管理:幼龄林阶段,除增加树种多样性外,还应着重培育资源获取能力强的树种;成熟林阶段,则应注重发展和保留具有长寿、保守性状的优势树种,注重目标树培育。
中图分类号:
高文强,雷相东,何潇,李玉堂. 东北温带森林类型和发育阶段的树种多样性−地上生物量关系分异性[J]. 林业科学, 2026, 62(4): 55-67.
Wenqiang Gao,Xiangdong Lei,Xiao He,Yutang Li. Variability in Tree Species Diversity-Aboveground Biomass Relationship in Temperate Forest Types and Developmental Stages in Northeast China[J]. Scientia Silvae Sinicae, 2026, 62(4): 55-67.
表1
不同森林类型5个发育阶段的林分平均年龄统计量①"
| 发育阶段 Developmental stage | 样地数量 Number of plots | 林分平均年龄 Stand average age/a | ||
| 阔叶纯林 Broad-leaved pure forest | 阔叶混交林 Broad-leaved mixed forest | 针阔混交林 Coniferous and broad-leaved mixed forest | ||
| 幼龄林 Young forest | 220 | 23 (5~30) | 25 (4~30) | 23 (5~30) |
| 中龄林 Middle-aged forest | 459 | 42 (6~50) | 42 (6~50) | 42 (7~50) |
| 近熟林 Near-mature forest | 843 | 62 (6~70) | 61 (6~70) | 60 (5~70) |
| 成熟林 Mature forest | 525 | 81 (9~100) | 81 (8~100) | 85 (8~100) |
| 过熟林 Over-mature forest | 345 | 126 (16~168) | 125 (16~203) | 134 (22~202) |
表2
树种多样性计算公式①"
| 指标Index | 计算公式Formula |
| 物种丰富度Species richness (S) | S=Ns |
| 功能多样性Functional diversity (FD) | |
| 群落加权平均性状值 Community weighted mean trait values (CWM) | |
| 谱系多样性Phylogenetic diversity (PD) |
表3
树种功能性状统计"
| 树种功能性状 Tree species functional traits | 单位 Units | 平均值 ± 标准差 Mean value ± standard deviation |
| 最大树高Maximum tree height | m | 23.824±11.061 |
| 叶面积Leaf area | m2 | 0.003±0.005 |
| 比叶面积Specific leaf area | m2·kg?1 | 19.904±10.168 |
| 单位面积叶质量 Leaf dry mass per unit area | kg·m?2 | 0.084±0.069 |
| 叶碳含量 Leaf carbon content | g·kg?1 | 422.288±84.501 |
| 叶氮含量Leaf nitrogen content | g·kg?1 | 18.914±7.422 |
| 叶磷含量Leaf phosphorus content | g·kg?1 | 1.786±0.753 |
| 木材密度Wood density | g·cm?3 | 0.512±0.121 |
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