
生物多样性 ›› 2026, Vol. 34 ›› Issue (4): 25406. DOI: 10.17520/biods.2025406 cstr: 32101.14.biods.2025406
黄语卓1(
), 王梓潆1(
), 周伟龙2, 莫佳瑶1(
), 张敏华1(
), 郝春晖1(
), 兰荣光3, 叶沛阳3, 刘宇1,4,*(
)(
)
收稿日期:2025-10-13
接受日期:2026-01-29
出版日期:2026-04-20
发布日期:2026-05-06
通讯作者:
刘宇
基金资助:
Yuzhuo Huang1(
), Ziying Wang1(
), Weilong Zhou2, Jiayao Mo1(
), Minhua Zhang1(
), Chunhui Hao1(
), Rongguang Lan3, Peiyang Ye3, Yu Liu1,4,*(
)(
)
Received:2025-10-13
Accepted:2026-01-29
Online:2026-04-20
Published:2026-05-06
Contact:
Yu Liu
Supported by:摘要:
植食性昆虫与木本植物的互作关系因其在生态系统中的重要作用而受到广泛关注。尽管已有大量研究探讨了森林中虫食强度的分布格局及其影响因素, 并提出了诸多理论假说, 但这些假说在不同森林群落中缺乏普适性, 尤其是对中亚热带常绿阔叶林的系统性验证较为有限。此外, 现有研究多聚焦于少数树种, 其结论能否推广至整个森林群落仍有待进一步检验与证实。为此, 本研究以浙江百山祖25 ha亚热带森林动态监测样地(简称百山祖样地)中149种阔叶树种的400株个体为研究对象, 比较了不同树种间虫食强度的差异, 其中虫食强度包括虫食率(即叶片虫食面积占比)和虫食频率(即虫食叶片占比); 基于样地监测数据, 采用广义线性混合效应模型探究了多种因素对虫食率的影响, 包括采样树种类别(按树木生活型和多度划分)、叶片大小、邻体树种多样性及其组成, 以及土壤养分等, 旨在揭示影响百山祖样地虫食率的主要驱动因素。结果表明: (1)样地内99.40%的虫食损伤由咀嚼类昆虫造成。平均虫食率为7.18%, 平均虫食频率为65.38%。不同树种的虫食率和虫食频率存在显著差异。其中, 常绿种的虫食率显著高于落叶种, 常见种的虫食率显著高于稀有种, 乔木的虫食率显著高于灌木。(2)树种类别对虫食率具有显著影响, 且虫食率与邻体树种系统发育多样性之间存在显著正相关关系。方差分解结果表明, 采样树的生活型(乔木vs.灌木)的相对贡献最大, 达62.33%。本研究结果支持昆虫植食作用的植物显性假说, 常绿、常见及乔木树种均因其在群落中的显性较高而遭受更强的虫食。同时, 研究也表明百山祖样地存在关联敏感效应, 即系统发育距离越远的树种混交更易吸引植食性昆虫取食。
黄语卓, 王梓潆, 周伟龙, 莫佳瑶, 张敏华, 郝春晖, 兰荣光, 叶沛阳, 刘宇 (2026) 浙江省百山祖25 ha亚热带森林动态监测样地木本植物叶片虫食强度分布格局及其影响因素. 生物多样性, 34, 25406. DOI: 10.17520/biods.2025406.
Yuzhuo Huang, Ziying Wang, Weilong Zhou, Jiayao Mo, Minhua Zhang, Chunhui Hao, Rongguang Lan, Peiyang Ye, Yu Liu (2026) Distribution patterns of leaf herbivory intensity and their influencing factors in woody plants across the 25-ha subtropical forest dynamics plot at Baishanzu, Zhejiang Province. Biodiversity Science, 34, 25406. DOI: 10.17520/biods.2025406.
图1 百山祖25 ha亚热带森林动态监测样地叶片虫食率(a)和虫食频率(b)在149个树种中的分布情况。树种名称后为采样株数, 各树种名称、类型、多度以及具体虫食率和虫食频率见附录2。
Fig. 1 Distribution patterns of leaf herbivory rate (a) and herbivory frequency (b) across 149 tree species in the 25-ha subtropical forest dynamics plot at Baishanzu. Number following the species name indicates number of sampled trees. See Appendix 2 for the names, types, and abundance information, as well as the specific herbivory rate and herbivory frequency of each species.
图2 百山祖25 ha亚热带森林动态监测样地149种树种叶片虫食率和虫食频率的关系(基于Spearman相关分析)。趋势线采用二次多项式拟合。
Fig. 2 Relationship between leaf herbivory rate and herbivory frequency across 149 species in the 25-ha subtropical forest dynamics plot at Baishanzu (based on Spearman correlation analysis). The trend line was fitted using a quadratic polynomial.
图3 百山祖25 ha亚热带森林动态监测样地不同树种类别的虫食率差异。(a)常绿种和落叶种; (b)常见种、中间种和稀有种; (c)乔木、小乔木和灌木。(b)和(c)中的P值经Bonferroni法校正。**P<0.01; ***P<0.001。
Fig. 3 Differences in leaf herbivory rate in the 25-ha subtropical forest dynamics plot at Baishanzu. (a) Evergreen species and deciduous species; (b) Common species, intermediate species, and rare species; (c) Trees, small trees and shrubs. P-values in (b) and (c) were adjusted using the Bonferroni correction. **P<0.01; ***P<0.001.
图4 最优模型中预测变量对虫食率的相对影响。模型包括采样树树种生长类型2 (乔木、小乔木和灌木)、树种多度分类(常见种、中间种和稀有种)、树种生长类型1 (常绿种和落叶种)、邻体树种系统发育多样性(MPD)以及土壤全氮含量(TN)。*P<0.05; **P<0.01; ***P<0.001。
Fig. 4 Relative effects of the predictors on leaf herbivory in the most parsimonious model. The model included the life form 2 of the sampled trees (trees, small trees and shrubs), abundance type (common species, intermediate species and rare species), life form 1 (evergreen species and deciduous species), neighboring tree phylogenetic diversity (MPD) and soil total nitrogen content (TN). *P<0.05; **P<0.01; ***P<0.001.
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