生物多样性 ›› 2023, Vol. 31 ›› Issue (11): 23217. DOI: 10.17520/biods.2023217
王晓凤1, 饶杰生1, 杨涛1, 刘文聪1, 田希1, 陈稀1, 刘其明2, 徐衍潇2, 张秋雨1, 张洪强3, 张旭3, 欧晓昆1, 沈泽昊2,1,*()
收稿日期:
2023-06-25
接受日期:
2023-08-29
出版日期:
2023-11-20
发布日期:
2023-12-23
通讯作者:
* E-mail: 基金资助:
Xiaofeng Wang1, Jiesheng Rao1, Tao Yang1, Wencong Liu1, Xi Tian1, Xi Chen1, Qiming Liu2, Yanxiao Xu2, Qiuyu Zhang1, Hongqiang Zhang3, Xu Zhang3, Xiaokun Ou1, Zehao Shen2,1,*()
Received:
2023-06-25
Accepted:
2023-08-29
Online:
2023-11-20
Published:
2023-12-23
Contact:
* E-mail: 摘要:
生物多样性格局是生物群落构建过程的反映, 有助于理解生态系统的物种共存机制。半湿润常绿阔叶林是亚热带西部半湿润气候下的地带性植被类型, 对其群落内物种多样性的空间异质格局及影响因子的认识还比较缺乏, 基于大样地的研究还未见报道。本文基于鸡足山20.16 ha森林动态监测样地504个样方的木本植物调查数据和TWINSPAN群落分类结果, 分析了样方尺度上α多样性和β多样性的空间分布格局及其环境影响因子。结果表明: (1)样地内云南松(Pinus yunnanensis)群落及其乔木和灌木的物种丰富度均高于高山栲(Castanopsis delavayi)群落和元江栲(C. orthacantha)群落; 高山栲群落及其灌木物种丰富度低于元江栲群落, 乔木物种丰富度则高于元江栲群落。相反, 元江栲群落的Shannon-Wiener多样性指数最高, 其次为高山栲群落, 云南松群落的最低。基于净种间亲缘关系指数, 元江栲群落、高山栲群落、云南松群落的谱系结构分别为聚集、随机、发散。(2)对物种丰富度存在普遍性影响的因子有土壤总氮、pH值、相对海拔高度、木本植物的胸高断面积之和; 导致乔木种丰富度变化的主要因子有土壤总氮、pH值、胸高断面积之和; 导致灌木种丰富度变化的主要因子是相对海拔高度、土壤总氮、坡度和地形湿度指数。(3)物种β多样性格局显示, 随着空间距离和环境距离的增大, 物种差异性和物种周转率增大, 即环境越相似, 群落越相似。上述结果表明, 鸡足山样地中先锋性的云南松群落与稳定的元江栲群落和高山栲群落在物种多样性和构成上存在显著差异, 指示了半湿润常绿阔叶林异质斑块所对应的物种共存和物种多样性维持特征, 为进一步的机理性研究提供了有效证据。
王晓凤, 饶杰生, 杨涛, 刘文聪, 田希, 陈稀, 刘其明, 徐衍潇, 张秋雨, 张洪强, 张旭, 欧晓昆, 沈泽昊 (2023) 云南鸡足山半湿润常绿阔叶林群落木本植物多样性格局与环境解释. 生物多样性, 31, 23217. DOI: 10.17520/biods.2023217.
Xiaofeng Wang, Jiesheng Rao, Tao Yang, Wencong Liu, Xi Tian, Xi Chen, Qiming Liu, Yanxiao Xu, Qiuyu Zhang, Hongqiang Zhang, Xu Zhang, Xiaokun Ou, Zehao Shen (2023) Spatial variation and determinants of woody plant species diversity in a semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan. Biodiversity Science, 31, 23217. DOI: 10.17520/biods.2023217.
群落类型 Community type | 样方数量 Number of quadrats | 面积 Area (ha) | 群落 Community | 乔木 Trees | 灌木 Shrubs | |||
---|---|---|---|---|---|---|---|---|
物种数量 Species number | 物种密度 Species density (species/ha) | 物种数量 Species number | 物种密度 Species density (species/ha) | 物种数量 Species number | 物种密度 Species dendity (species/ha) | |||
云南松群落 Pinus yunnanensis community | 67 | 2.68 | 71 | 26.49 | 26 | 9.70 | 45 | 16.79 |
高山栲群落 Castanopsis delavayi community | 203 | 8.12 | 72 | 8.87 | 31 | 3.82 | 41 | 5.05 |
元江栲群落 C. orthacantha community | 234 | 9.36 | 82 | 8.76 | 31 | 3.31 | 51 | 5.45 |
总计 Total | 504 | 20.16 | 103 | 5.11 | 38 | 1.88 | 65 | 3.22 |
表1 鸡足山半湿润常绿阔叶林动态监测样地3个群落的物种数量统计
Table 1 Statistics of species numbers of three communities in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains
群落类型 Community type | 样方数量 Number of quadrats | 面积 Area (ha) | 群落 Community | 乔木 Trees | 灌木 Shrubs | |||
---|---|---|---|---|---|---|---|---|
物种数量 Species number | 物种密度 Species density (species/ha) | 物种数量 Species number | 物种密度 Species density (species/ha) | 物种数量 Species number | 物种密度 Species dendity (species/ha) | |||
云南松群落 Pinus yunnanensis community | 67 | 2.68 | 71 | 26.49 | 26 | 9.70 | 45 | 16.79 |
高山栲群落 Castanopsis delavayi community | 203 | 8.12 | 72 | 8.87 | 31 | 3.82 | 41 | 5.05 |
元江栲群落 C. orthacantha community | 234 | 9.36 | 82 | 8.76 | 31 | 3.31 | 51 | 5.45 |
总计 Total | 504 | 20.16 | 103 | 5.11 | 38 | 1.88 | 65 | 3.22 |
图1 鸡足山半湿润常绿阔叶林动态监测样地3个群落的种-面积曲线(a, b, c)和种-多度曲线(d, e)。(a)木本植物; (b)乔木; (c)灌木; (d)木本植物; (e)常绿阔叶种和落叶阔叶种。图中虚线部分为实际种-面积对数函数模型的拟合延长线。
Fig. 1 Species-area curves (a, b, c) and species-abundance curves (d, e) of the three communities in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains. (a) Woody plant; (b) Trees; (c) Shrubs; (d) Woody plant; (e) Evergreen and deciduous broad-leaved species. The dashed line in the figure represents the fitting extension of the actual species-area logarithmic function model.
图2 鸡足山半湿润常绿阔叶林动态监测样地504个样方的α多样性和谱系多样性空间格局。(a)物种丰富度(SR); (b) Shannon-Wiener多样性指数(H′); (c)净种间亲缘关系指数(NRI)。
Fig. 2 Spatial variation of α diversity and lineage diversity among 504 quadrats in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains. (a) Species richness (SR); (b) Shannon-Wiener diversity index (H′); (c) Net interspecific relationship index (NRI).
尺度 Scale | 多样性指数 Diversity index | 云南松群落 Pinus yunnanensis community | 高山栲群落 Castanopsis delavayi community | 元江栲群落 C. orthacantha community | |||
---|---|---|---|---|---|---|---|
OLS | GWR | OLS | GWR | OLS | GWR | ||
木本植物 Woody plant | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.661 | 0.798 | 0.358 | 0.777 | 0.254 | 0.637 |
物种丰富度 Species richness | 0.25 | 0.43 | 0.303 | 0.533 | 0.314 | 0.474 | |
乔木 Trees | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.557 | 0.734 | 0.396 | 0.811 | 0.282 | 0.819 |
物种丰富度 Species richness | 0.248 | 0.336 | 0.179 | 0.465 | 0.185 | 0.546 | |
灌木 Shrubs | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.537 | 0.664 | 0.310 | 0.655 | 0.294 | 0.566 |
物种丰富度 Species richness | 0.157 | 0.341 | 0.363 | 0.583 | 0.409 | 0.468 |
表2 鸡足山半湿润常绿阔叶林动态监测样地3个群落木本植物、乔木、灌木的Shannon-Wiener多样性指数、物种丰富度格局的普通最小二乘(OLS)回归模型和地理加权回归(GWR)模型拟合优度(R2)
Table 2 Fitting degrees (R2) of ordinary least squares (OLS) regression model and geographically weighted regression (GWR) model on patterns of Shannon-Wiener diversity index and species richness of woody plants, trees and shrubs of the three communities in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains
尺度 Scale | 多样性指数 Diversity index | 云南松群落 Pinus yunnanensis community | 高山栲群落 Castanopsis delavayi community | 元江栲群落 C. orthacantha community | |||
---|---|---|---|---|---|---|---|
OLS | GWR | OLS | GWR | OLS | GWR | ||
木本植物 Woody plant | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.661 | 0.798 | 0.358 | 0.777 | 0.254 | 0.637 |
物种丰富度 Species richness | 0.25 | 0.43 | 0.303 | 0.533 | 0.314 | 0.474 | |
乔木 Trees | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.557 | 0.734 | 0.396 | 0.811 | 0.282 | 0.819 |
物种丰富度 Species richness | 0.248 | 0.336 | 0.179 | 0.465 | 0.185 | 0.546 | |
灌木 Shrubs | Shannon-Wiener多样性指数 Shannon-Wiener diversity index | 0.537 | 0.664 | 0.310 | 0.655 | 0.294 | 0.566 |
物种丰富度 Species richness | 0.157 | 0.341 | 0.363 | 0.583 | 0.409 | 0.468 |
图3 基于普通最小二乘(OLS)回归模型(a)和地理加权回归(GWR)模型(b)解释鸡足山半湿润常绿阔叶林动态监测样地3个群落的木本植物、乔木、灌木的物种丰富度格局。Age: 群落年龄; BasA: 胸高断面积之和; Clay: 黏粒含量; Silt: 粉粒含量; Sand: 砂粒含量; OrgC: 有机碳; TotN: 总氮; AvaP: 有效磷; pH: pH值; Alti: 相对海拔高度; Slop: 坡度; Aspe: 坡向; Curv: 曲率; Roug: 粗糙度; Twi: 地形湿度指数。
Fig. 3 Explanation of species richness patterns of woody plant, trees, and shrubs of the three communities in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains based on ordinary least squares (OLS) regression model (a) and geographically weighted regression (GWR) (b) model. Age, Community age; BasA, Sum of basal area; Clay, Clay content; Silt, Silt content; Sand, Sand content; OrgC, Organic carbon; TotN, Total nitrogen; AvaP, Available phosphorus; pH, pH value; Alti, Relative altitude; Slop, Slope; Aspe, Aspect; Curv, Curvature; Roug, Roughness; Twi, Topographic wetness index.
图4 鸡足山半湿润常绿阔叶林动态监测样地在20 m粒度的Whittaker指数和物种周转率与环境距离和空间距离的关系。Age: 群落年龄; BasA: 胸高断面积之和; Clay: 黏粒含量; Silt: 粉粒含量; Sand: 砂粒含量; OrgC: 有机碳; TotN: 总氮; AvaP: 有效磷; pH: pH值; Alti: 相对海拔高度; Slop: 坡度; Aspe: 坡向; Curv: 曲率; Roug: 粗糙度; Twi: 地形湿度指数; Spa: 空间距离。
Fig. 4 Relationship between Whittaker’s index and species turnover rate with environmental distance and spatial distance at 20 m grain, estimated within the forest dynamics plot of the semi-humid evergreen broad-leaved forests in the Jizu Mountains. Age, Community age; BasA, Sum of basal area; Clay, Clay content; Silt, Silt content; Sand, Sand content; OrgC, Organic carbon; TotN, Total nitrogen; AvaP, Available phosphorus; pH, pH value; Alti, Relative altitude; Slop, Slope; Aspe, Aspect; Curv, Curvature; Roug, Roughness; Twi, Topographic wetness index; Spa, Spatial distance.
Whittaker指数 βW | 环境距离 Env | 空间距离 Spa | |
---|---|---|---|
Whittaker指数 Whittaker’s index (βW) | - | 0.325, P = 0.001 | 0.456, P = 0.001 |
环境距离 Environment distance (Env) | 0.253, P = 0.001 | - | 0.233, P = 0.001 |
空间距离 Spatial distance (Spa) | 0.413, P = 0.001 | 0.101, P = 0.001 | - |
表3 鸡足山半湿润常绿阔叶林动态监测样地在20 m粒度的Whittaker指数与环境距离和空间距离的Mantel (对角线上方)和偏Mantel (对角线下方)检验结果
Table 3 Mantel (above the diagonal) and partial Mantel (below the diagonal) tests for the relationships between Whittaker’s index and environmental and spatial distances at 20 m grain in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains
Whittaker指数 βW | 环境距离 Env | 空间距离 Spa | |
---|---|---|---|
Whittaker指数 Whittaker’s index (βW) | - | 0.325, P = 0.001 | 0.456, P = 0.001 |
环境距离 Environment distance (Env) | 0.253, P = 0.001 | - | 0.233, P = 0.001 |
空间距离 Spatial distance (Spa) | 0.413, P = 0.001 | 0.101, P = 0.001 | - |
物种周转率 βtu | 环境距离 Env | 空间距离 Spa | |
---|---|---|---|
物种周转率 Species turnover rate (βtu) | - | 0.317, P = 0.001 | 0.431, P = 0.001 |
环境距离 Environment distance (Env) | 0.247, P = 0.001 | - | 0.233, P = 0.001 |
空间距离 Spatial distance (Spa) | 0.387, P = 0.001 | 0.113, P = 0.001 | - |
表4 鸡足山半湿润常绿阔叶林动态监测样地在20 m粒度的物种周转率与环境距离和空间距离的Mantel (对角线上方)和偏Mantel (对角线下方)检验结果
Table 4 Mantel (above the diagonal) and partial Mantel (below the diagonal) tests for the relationships between species turnover rate and environmental and spatial distances at 20 m grain in the forest dynamics plot in a semi-humid evergreen broad-leaved forest in the Jizu Mountains
物种周转率 βtu | 环境距离 Env | 空间距离 Spa | |
---|---|---|---|
物种周转率 Species turnover rate (βtu) | - | 0.317, P = 0.001 | 0.431, P = 0.001 |
环境距离 Environment distance (Env) | 0.247, P = 0.001 | - | 0.233, P = 0.001 |
空间距离 Spatial distance (Spa) | 0.387, P = 0.001 | 0.113, P = 0.001 | - |
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