本地群落多样性和时间稳定性对加拿大一枝黄花生物量的影响

doi:10.17520/biods.2024263

生物多样性 ›› 2024, Vol. 32 ›› Issue (11): 24263. DOI: 10.17520/biods.2024263 cstr: 32101.14.biods.2024263

本地群落多样性和时间稳定性对加拿大一枝黄花生物量的影响

龙诗怡¹, 张博博¹, 夏宇辰¹, 费杨帆¹, 孟亚妮¹, 吕冰薇¹, 宋月青¹, 郑普¹, 郭陶然², 张健¹^,³(), 黎绍鹏¹^,^*()()

1.华东师范大学生态与环境科学学院, 浙江天童森林生态系统国家野外科学观测研究站, 上海 200241
2.上海天渊生态科技有限公司, 上海 201112
3.中山大学生命科学学院, 广州 510275

收稿日期:2024-06-28 接受日期:2024-11-05 出版日期:2024-11-20 发布日期:2024-12-09
通讯作者: *E-mail: spli@des.ecnu.edu.cn
基金资助:
国家重点研发计划(2023YFC2604500);国家自然科学基金(32222051);华东师范大学未来领军英才卓越学术计划进阶项目(2024ZY-015)

Effects of diversity and temporal stability of native communities on the biomass of invasive species Solidago canadensis

Shiyi Long¹, Bobo Zhang¹, Yuchen Xia¹, Yangfan Fei¹, Yani Meng¹, Bingwei Lü¹, Yueqing Song¹, Pu Zheng¹, Taoran Guo², Jian Zhang¹^,³(), Shaopeng Li¹^,^*()()

1. Zhejiang Tiantong Forest Ecosystem National Observation and Research Station, School of Ecological and Environmental Sciences, East China Normal University, Shanghai 200241, China
2. Tianyuan Ecology Technology Co., Ltd., Shanghai 201112, China
3. School of Life Sciences, Sun Yat-sen University, Guangzhou 510275, China

Received:2024-06-28 Accepted:2024-11-05 Online:2024-11-20 Published:2024-12-09
Contact: *E-mail: spli@des.ecnu.edu.cn
Supported by:
National Key Research and Development Program of China(2023YFC2604500);National Natural Science Foundation of China(32222051);East China Normal University Outstanding Academic Training Program for Future Leading Talents(2024ZY-015)

摘要/Abstract

摘要：

“多样性-可入侵性”和“多样性-稳定性”之间的关系是当前生态学研究的前沿领域和热门话题, 然而少有研究将二者有机结合。多样性是否通过提高群落的时间稳定性进而抑制入侵, 即群落时间稳定性的提高是否是多样性抵御入侵的关键途径, 是尚未解决的关键科学问题。本研究于上海乡土生态科普示范基地开展野外原位控制实验, 通过向不同的本地植物群落移栽加拿大一枝黄花(Solidago canadensis)幼苗模拟外来物种入侵, 并监测移栽后入侵种的生物量, 以揭示本地群落的物种多样性和谱系多样性、时间稳定性和样方郁闭度与加拿大一枝黄花生长表现的相关关系。结果表明: 本地群落的物种多样性和谱系多样性(尤其是盖度加权后)与入侵种的生物量正相关。同时, 本地群落的物种多样性和谱系多样性(尤其是盖度加权时)与本地群落的时间稳定性正相关。然而, 入侵种生物量与本地群落的时间稳定性无显著相关关系, 但与林冠郁闭度显著负相关。结构方程模型结果显示: 在物种多样性较高且样方郁闭度较低的群落中, 入侵种的生物量相对较高; 物种多样性与入侵种生物量存在强正相关路径, 抵消了物种多样性通过提高时间稳定性进而对入侵种生物量产生的抑制作用。本研究揭示了物种多样性和谱系多样性及时间稳定性与群落可入侵性的复杂关联, 为探讨“多样性-可入侵性”关系的作用途径和机制提供了新的研究视角。

关键词: 物种多样性, 谱系多样性, 时间稳定性, 入侵种, 加拿大一枝黄花

Abstract

Aim: Elton’s foundational ideas on “diversity-invasibility” and “diversity-stability” relationships have long been central to ecological research, yet the link between these concepts remains largely unexplored. It remains unclear whether diversity reduces invasions by enhancing community temporal stability, and thereby making stability a primary mechanism by which diversity resists invasion.

Methods: We conducted an in situ experiment at the Shanghai Urban Biodiversity Education Base to simulate the invasion processes by transplanting Solidago canadensisseedlings into native herbaceous communities. We then measured the biomass of the invader, to assess the relationship between species diversity, phylogenetic diversity, temporal stability, canopy closure of the native communties, and the growth performance of the invader.

Results: We found that both species diversity and phylogenetic diversity of native communities, particularly when assessed by cover-weighted measures, were generally positively correlated with invader biomass. These diversity measures also generally showed a positive correlation with the temporal stability of native communities. However, invader biomass was not significantly related to community temporal stability but was negatively related to canopy closure. Structural equation modeling indicated that higher diversity and lower canopy closure of native communities increased invader biomass, and the positive relationship between diversity and invader biomass offset the potential negative effect of diversity on invasion by enhancing temporal stability.

Conclusions: This study elucidates that species diversity and phylogenetic diversity, along with temporal stability, can exert complex influences on community invasibility, providing new insights into the mechanisms underlying the “diversity-invasibility” relationship.

Key words: species diversity, phylogenetic diversity, temporal stability, invader, Solidago canadensis

龙诗怡, 张博博, 夏宇辰, 费杨帆, 孟亚妮, 吕冰薇, 宋月青, 郑普, 郭陶然, 张健, 黎绍鹏 (2024) 本地群落多样性和时间稳定性对加拿大一枝黄花生物量的影响. 生物多样性, 32, 24263. DOI: 10.17520/biods.2024263.

Shiyi Long, Bobo Zhang, Yuchen Xia, Yangfan Fei, Yani Meng, Bingwei Lü, Yueqing Song, Pu Zheng, Taoran Guo, Jian Zhang, Shaopeng Li (2024) Effects of diversity and temporal stability of native communities on the biomass of invasive species Solidago canadensis. Biodiversity Science, 32, 24263. DOI: 10.17520/biods.2024263.

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链接本文: https://www.biodiversity-science.net/CN/10.17520/biods.2024263

https://www.biodiversity-science.net/CN/Y2024/V32/I11/24263

图/表 5

图1 上海乡土生态科普示范基地样方分布和实验设计示意图

Fig. 1 Distribution of sample plots and experimental design in Shanghai Urban Biodiversity Education Base

图2 本地群落的物种多样性和谱系多样性与入侵种加拿大一枝黄花生物量的关系。A: 物种多样性和谱系多样性与入侵种生物量关系的森林图; B、C、D分别指阶数为2的希尔数、Faith’s谱系多样性指数和盖度加权后的平均成对谱系距离与入侵种生物量的线性拟合图。R2反映了自变量对因变量的解释程度, P值为统计显著性, 显著性阈值为P = 0.05。森林图中实心点和空心点分别表示显著和不显著的效应值。实线和虚线分别表示线性拟合显著和不显著。

Fig. 2 Relationships between species diversity, phylogenetic diversity, and the biomass of the invasive species Solidago canadensis. A, Forest plot summarizing the effects of species diversity and phylogenetic diversity on invader biomass; B, C, D were Linear regressions illustrating the relationships between invader biomass and the Hill number (q = 2), Faith’s phylogenetic diversity (PD), and abundance-weighted mean phylogenetic distance (MPDab), respectively. R2 represents the proportion of variance in the dependent variable explained by the independent variable, while the P value indicates statistical significance, with a threshold of P = 0.05. In the forest plot, solid points indicate significant correlation, while hollow points indicate non-significant correlation. Linear fits are displayed as solid lines for significant relationships and dashed lines for non-significant relationships.

图3 本地群落物种多样性、谱系多样性与本地植物群落时间稳定性的关系。A: 物种多样性和谱系多样性与时间稳定性关系的森林图; B、C、D分别指阶数为2的希尔数、Faith’s谱系多样性指数和盖度加权后的平均成对谱系距离与时间稳定性的线性拟合图。R2反映了自变量对因变量的解释程度, P值反映统计显著性, 显著性阈值为P = 0.05。森林图中实心点和空心点分别表示显著和不显著的效应值。实线和虚线分别表示线性拟合显著和不显著。

Fig. 3 Relationships between species diversity, phylogenetic diversity, and temporal stability of native plant communities. A, Forest plot summarizing the effects of species diversity and phylogenetic diversity on temporal stability; B, C, D were Linear regressions of temporal stability as a function of Hill number (q = 2), Faith’s phylogenetic diversity (PD), and abundance-weighted mean phylogenetic distance (MPDab), respectively. R2 represents the proportion of variance in the dependent variable explained by the independent variable, while the P value indicates statistical significance, with a threshold of P = 0.05. In the forest plot, solid points indicate significant correlation, while hollow points indicate non-significant correlation. Linear fits are displayed as solid lines for significant relationships and dashed lines for non-significant relationships.

图4 本地群落时间稳定性及其组分、样方郁闭度与入侵种加拿大一枝黄花生物量的线性拟合图。A: 本地群落盖度均值; B: 本地群落盖度标准差; C: 时间稳定性; D: 郁闭度。R2反映自变量对因变量的解释程度, 显著性阈值为P = 0.05。实线和虚线分别表示线性拟合显著和不显著。

Fig. 4 Linear regressions of invader biomass as a function of temporal stability (A), mean coverage of local community (B), standard deviation (SD) of coverage of local community (C) and canopy closure (D). R2 represents the proportion of variance in the dependent variable explained by the independent variable, while the P value indicates statistical significance, with a threshold of P = 0.05. Linear fits are displayed as solid lines for significant relationships and dashed lines for non-significant relationships.

图5 物种多样性和郁闭度与入侵种加拿大一枝黄花生物量关系的结构方程模型。A: 时间稳定性被拆分为平均值和标准差两个组分; B: 时间稳定性被拆分为物种异步性和物种稳定性两个组分。蓝色箭头表示正相关关系, 红色箭头表示负相关关系; 实线箭头表示影响显著, 虚线箭头表示影响不显著; 箭头宽度表示标准化路径系数的强度, 箭头上方的数字为标准化路径系数; R2表示模型解释的方差; * P < 0.05; ** P < 0.01; *** P < 0.001。用卡方检验和赤池信息量准则(AIC)对模型的充分性进行检验, AIC值最小的模型被认为是最佳模型。

Fig. 5 Structural equation models depicting the relationships between species diversity, canopy closure, and the biomass of the invasive species Solidago canadensis. A, Temporal stability is divided into two components: mean and standard deviation (SD); B, Temporal stability is divided into species asynchrony and species stability. Blue arrows represent positive relationships, while red arrows denote negative relationships. Solid arrows indicate statistically significant effects, and dashed arrows indicate non-significant effects. The width of the arrows reflects the magnitude of standardized path coefficients, with numerical values provided alongside arrows. R² values indicate the proportion of variance explained by the model. * P < 0.05; ** P < 0.01; *** P < 0.001. Model adequacy was evaluated using the χ² test and Akaike Information Criterion (AIC). The model with the lowest AIC value was selected as the best fit.

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本地群落多样性和时间稳定性对加拿大一枝黄花生物量的影响

Effects of diversity and temporal stability of native communities on the biomass of invasive species Solidago canadensis

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