生物多样性 ›› 2013, Vol. 21 ›› Issue (1): 80-89. DOI: 10.3724/SP.J.1003.2013.10132
谢一鸣1,2, 许月1,2, 康蒙1,2, 阎恩荣1,2,*()
收稿日期:
2012-06-20
接受日期:
2012-12-05
出版日期:
2013-01-20
发布日期:
2013-02-04
通讯作者:
阎恩荣
基金资助:
Yiming Xie1,2, Yue Xu1,2, Meng Kang1,2, Enrong Yan1,2,*()
Received:
2012-06-20
Accepted:
2012-12-05
Online:
2013-01-20
Published:
2013-02-04
Contact:
Yan Enrong
摘要:
揭示群落物种组成与环境的关联性对于理解物种共存机制具有重要意义。传统生态种组划分不仅带有主观性, 且难以定量种组-环境的关联程度。本研究以浙江天童31个处于不同生境的植物群落为研究材料, 以群落实际物种组成作为研究对象, 利用物种多度分别构建了各群落的最大、实际和相对环境选择性指数, 并以随机模拟的群落环境关联性作为零假设, 通过与实际群落相比较来揭示群落物种组成的环境关联程度; 最后, 利用环境选择指数(environmental dependence index)与群落生境马氏距离(Mahalanobis distance)的相关分析来确认群落物种组成与环境的关联性。结果表明: 最大环境选择指数反映的是现有生境在理论上的最优群落配置组合的环境选择性, 实际选择指数可反映群落物种组成对现状生境的选择性, 相对环境选择指数可综合反映群落物种组成与环境间的关联性; 相对环境选择指数与单独生境因子的相关性不显著, 而与表征综合环境特征的Mahalanobis距离显著正相关; 随生境异质性增大, 群落物种组成的环境专一性更强。此结果为天童常绿阔叶林的群落物种组成与生境关联性提供了新证据, 也为如何完善物种与环境之间关系的定量化研究提供了借鉴。
谢一鸣, 许月, 康蒙, 阎恩荣 (2013) 基于植物多度的群落物种组成与环境关联性分析. 生物多样性, 21, 80-89. DOI: 10.3724/SP.J.1003.2013.10132.
Yiming Xie,Yue Xu,Meng Kang,Enrong Yan (2013) Analysis of plant abundance-based association between community species composition and environmental properties. Biodiversity Science, 21, 80-89. DOI: 10.3724/SP.J.1003.2013.10132.
编号 Code | 群落类型 Community types | 生境类型 Habitat types | 年龄a Yr | 海拔 Altitude (m) | 坡度 Slope | 坡向 Exposure | 群落高度 Height (m) | 丰富度b Species richness | 马氏距离c Mahalanobis distance |
---|---|---|---|---|---|---|---|---|---|
1 | 马尾松草灌 Pinus massoniana and herbosa mixed shrub | 坡底 Bottom slope | 10 | 82 | 25º | SE40º | 7 | 9 | 4.06 |
2 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 161 | 15º | SE10º | 6 | 16 | 0.79 |
3 | 栲树+木荷群落 Castanopsis fargesii+Schima superba Comm. | 坡中 Central slope | 120 | 272 | 30º | SE20º | 23 | 12 | 7.58 |
4 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 245 | 20º | SE25º | 21 | 13 | 2.95 |
5 | 马尾松+木荷群落 Pinus massoniana+Schima superba Comm. | 坡中 Central slope | 25 | 129 | 23º | SE20º | 12 | 12 | 3.16 |
6 | 木荷+米槠群落 Schima superba+Castanopsis carlesii Comm. | 坡底 Bottom slope | 30 | 98 | 20º | SE80º | 15 | 8 | 3.61 |
7 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 26º | SE45º | 25 | 26 | 6.48 |
8 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 22º | SE45º | 25 | 24 | 6.70 |
9 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 21º | SE45º | 24 | 16 | 3.88 |
10 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 157 | 20º | SE15º | 13 | 12 | 0.84 |
11 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 159 | 18º | SE18º | 12 | 14 | 1.48 |
12 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 160 | 18º | SE17º | 11 | 11 | 1.09 |
13 | 落叶灌丛 Deciduous shrub | 坡中 Central slope | 10 | 59 | 10º | SE60º | 6 | 7 | 3.61 |
14 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 111 | 20º | SE70º | 22 | 20 | 5.86 |
15 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 55 | 111 | 20º | SE70º | 21 | 15 | 3.38 |
16 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 111 | 20º | SE70º | 22 | 18 | 2.26 |
17 | 赤皮青冈群落 Cyclobalanopsis gilva Comm. | 沟谷 Ravine | 65 | 153 | 26º | SE5º | 25 | 13 | 10.40 |
18 | 枫香群落 Liquidambar formosana Comm. | 沟谷 Ravine | 55 | 242 | 20º | SE18º | 25 | 6 | 9.02 |
19 | 栲树+木荷群落 Castanopsis fargesii+Schima superba Comm. | 山脊 Hill ridge | 80 | 235 | 40º | SE80º | 24 | 15 | 1.94 |
20 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 65 | 199 | 25º | SE70º | 23 | 14 | 2.50 |
21 | 常绿灌丛 Evergreen shrub | 山脊 Hill ridge | 10 | 230 | 20º | SE15º | 5 | 17 | 1.70 |
22 | 落叶灌丛 Deciduous shrub | 坡底 Bottom slope | 8 | 125 | 30º | SE35º | 5 | 7 | 10.69 |
23 | 南酸枣群落 Choerospondias axillaris Comm. | 沟谷 Ravine | 120 | 233 | 30º | SE40º | 26 | 15 | 15.09 |
24 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 386 | 20º | SE60º | 25 | 13 | 11.16 |
25 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 388 | 25º | SE60º | 24 | 11 | 5.85 |
26 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 373 | 20º | SE63º | 23 | 13 | 6.23 |
27 | 云山青冈群落 Cyclobalanopsis sessilifolia Comm. | 山顶 Peak | 120 | 446 | 25º | SE55º | 22 | 14 | 21.51 |
28 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 116 | 26º | SE20º | 6 | 16 | 6.03 |
29 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 116 | 25º | SE20º | 7 | 20 | 3.85 |
30 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 117 | 25º | SE20º | 6 | 16 | 8.21 |
31 | 马尾松草灌 Pinus massoniana and herbosa mixed shrub | 坡中 Central slope | 10 | 47 | 30º | SE30º | 5 | 7 | 8.10 |
表1 浙江天童及周边地区31个群落的样地特征
Table 1 Characteristics of selected 31 plots in Tiantong and the surrounding areas, Zhejiang Province
编号 Code | 群落类型 Community types | 生境类型 Habitat types | 年龄a Yr | 海拔 Altitude (m) | 坡度 Slope | 坡向 Exposure | 群落高度 Height (m) | 丰富度b Species richness | 马氏距离c Mahalanobis distance |
---|---|---|---|---|---|---|---|---|---|
1 | 马尾松草灌 Pinus massoniana and herbosa mixed shrub | 坡底 Bottom slope | 10 | 82 | 25º | SE40º | 7 | 9 | 4.06 |
2 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 161 | 15º | SE10º | 6 | 16 | 0.79 |
3 | 栲树+木荷群落 Castanopsis fargesii+Schima superba Comm. | 坡中 Central slope | 120 | 272 | 30º | SE20º | 23 | 12 | 7.58 |
4 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 245 | 20º | SE25º | 21 | 13 | 2.95 |
5 | 马尾松+木荷群落 Pinus massoniana+Schima superba Comm. | 坡中 Central slope | 25 | 129 | 23º | SE20º | 12 | 12 | 3.16 |
6 | 木荷+米槠群落 Schima superba+Castanopsis carlesii Comm. | 坡底 Bottom slope | 30 | 98 | 20º | SE80º | 15 | 8 | 3.61 |
7 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 26º | SE45º | 25 | 26 | 6.48 |
8 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 22º | SE45º | 25 | 24 | 6.70 |
9 | 栲树群落 Castanopsis fargesii Comm. | 坡中 Central slope | 150 | 110 | 21º | SE45º | 24 | 16 | 3.88 |
10 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 157 | 20º | SE15º | 13 | 12 | 0.84 |
11 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 159 | 18º | SE18º | 12 | 14 | 1.48 |
12 | 马尾松群落 Pinus massoniana Comm. | 山脊 Hill ridge | 20 | 160 | 18º | SE17º | 11 | 11 | 1.09 |
13 | 落叶灌丛 Deciduous shrub | 坡中 Central slope | 10 | 59 | 10º | SE60º | 6 | 7 | 3.61 |
14 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 111 | 20º | SE70º | 22 | 20 | 5.86 |
15 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 55 | 111 | 20º | SE70º | 21 | 15 | 3.38 |
16 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 60 | 111 | 20º | SE70º | 22 | 18 | 2.26 |
17 | 赤皮青冈群落 Cyclobalanopsis gilva Comm. | 沟谷 Ravine | 65 | 153 | 26º | SE5º | 25 | 13 | 10.40 |
18 | 枫香群落 Liquidambar formosana Comm. | 沟谷 Ravine | 55 | 242 | 20º | SE18º | 25 | 6 | 9.02 |
19 | 栲树+木荷群落 Castanopsis fargesii+Schima superba Comm. | 山脊 Hill ridge | 80 | 235 | 40º | SE80º | 24 | 15 | 1.94 |
20 | 木荷群落 Schima superba Comm. | 坡中 Central slope | 65 | 199 | 25º | SE70º | 23 | 14 | 2.50 |
21 | 常绿灌丛 Evergreen shrub | 山脊 Hill ridge | 10 | 230 | 20º | SE15º | 5 | 17 | 1.70 |
22 | 落叶灌丛 Deciduous shrub | 坡底 Bottom slope | 8 | 125 | 30º | SE35º | 5 | 7 | 10.69 |
23 | 南酸枣群落 Choerospondias axillaris Comm. | 沟谷 Ravine | 120 | 233 | 30º | SE40º | 26 | 15 | 15.09 |
24 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 386 | 20º | SE60º | 25 | 13 | 11.16 |
25 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 388 | 25º | SE60º | 24 | 11 | 5.85 |
26 | 褐叶青冈群落 Cyclobalanopsis stewardiana Comm. | 山顶 Peak | 130 | 373 | 20º | SE63º | 23 | 13 | 6.23 |
27 | 云山青冈群落 Cyclobalanopsis sessilifolia Comm. | 山顶 Peak | 120 | 446 | 25º | SE55º | 22 | 14 | 21.51 |
28 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 116 | 26º | SE20º | 6 | 16 | 6.03 |
29 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 116 | 25º | SE20º | 7 | 20 | 3.85 |
30 | 常绿灌丛 Evergreen shrub | 坡中 Central slope | 15 | 117 | 25º | SE20º | 6 | 16 | 8.21 |
31 | 马尾松草灌 Pinus massoniana and herbosa mixed shrub | 坡中 Central slope | 10 | 47 | 30º | SE30º | 5 | 7 | 8.10 |
非线性回归模型 Nonlinear regression model | 模型公式 Model |
---|---|
指数模型 Exponential | y=y0 + Ae-x/t{Invalid MML} |
幂函数模型 Power | y=axb |
对数模型 Logarithm | y=a - bln(x + c) |
多项式模型 Polynomial | y=a0 + a1x + a2x2 + a3x3 |
表2 拟合最大环境选择指数与物种丰富度关系的4种非线性回归模型
Table 2 Four nonlinear regression models used to fitting species richness against indices of maximum environmental dependence
非线性回归模型 Nonlinear regression model | 模型公式 Model |
---|---|
指数模型 Exponential | y=y0 + Ae-x/t{Invalid MML} |
幂函数模型 Power | y=axb |
对数模型 Logarithm | y=a - bln(x + c) |
多项式模型 Polynomial | y=a0 + a1x + a2x2 + a3x3 |
图2 浙江天童及周边地区31个群落类型的实际、最大和相对环境选择指数比较。群落编号见表1。
Fig. 2 Comparisons of actual, maximum and relative indices in environmental dependence among 31 plant communities in the Tiantong and surrounding areas. Community codes listed in Table 1.
群落号 Community code | 实际值 Actual | 最大Maximum | 相对值 Relative | 拟合最 大值a Fitted maximum | 拟合相 对值a Fitted relative |
---|---|---|---|---|---|
1 | 0.258 | 0.734 | 0.351 | 0.805 | 0.320 |
2 | 0.100 | 0.583 | 0.172 | 0.588 | 0.170 |
3 | 0.029 | 0.596 | 0.049 | 0.678 | 0.043 |
4 | 0.164 | 0.730 | 0.224 | 0.649 | 0.252 |
5 | 0.196 | 0.606 | 0.324 | 0.678 | 0.289 |
6 | 0.169 | 1.000 | 0.169 | 0.865 | 0.195 |
7 | 0.252 | 0.520 | 0.484 | 0.517 | 0.487 |
8 | 0.330 | 0.525 | 0.628 | 0.523 | 0.630 |
9 | 0.178 | 0.664 | 0.268 | 0.588 | 0.302 |
10 | 0.266 | 0.783 | 0.339 | 0.678 | 0.391 |
11 | 0.279 | 0.664 | 0.421 | 0.625 | 0.447 |
12 | 0.293 | 0.619 | 0.473 | 0.713 | 0.410 |
13 | 0.243 | 0.906 | 0.269 | 0.937 | 0.260 |
14 | 0.121 | 0.532 | 0.227 | 0.544 | 0.222 |
15 | 0.172 | 0.618 | 0.278 | 0.605 | 0.284 |
16 | 0.179 | 0.562 | 0.318 | 0.562 | 0.318 |
17 | 0.175 | 0.630 | 0.278 | 0.649 | 0.270 |
18 | 0.465 | 1.000 | 0.465 | 1.023 | 0.454 |
19 | 0.097 | 0.583 | 0.166 | 0.605 | 0.160 |
20 | 0.052 | 0.647 | 0.081 | 0.625 | 0.084 |
21 | 0.225 | 0.559 | 0.402 | 0.574 | 0.392 |
22 | 0.714 | 0.982 | 0.727 | 0.937 | 0.762 |
23 | 0.685 | 0.599 | 1.144 | 0.605 | 1.132 |
24 | 0.366 | 0.617 | 0.594 | 0.649 | 0.564 |
25 | 0.165 | 0.773 | 0.213 | 0.713 | 0.231 |
26 | 0.229 | 0.631 | 0.363 | 0.649 | 0.352 |
27 | 0.262 | 0.591 | 0.443 | 0.625 | 0.419 |
28 | 0.161 | 0.652 | 0.247 | 0.588 | 0.274 |
29 | 0.253 | 0.525 | 0.481 | 0.544 | 0.465 |
30 | 0.142 | 0.536 | 0.266 | 0.588 | 0.242 |
31 | 0.270 | 0.906 | 0.298 | 0.937 | 0.289 |
均值 Mean | 0.242 | 0.673 | 0.360 | 0.673 | 0.358 |
标准差 SD. | 0.152 | 0.145 | 0.212 | 0.135 | 0.209 |
范围 Range | 0.685 | 0.480 | 1.095 | 0.506 | 1.089 |
最大值 Max. | 0.714 | 1.000 | 1.144 | 1.023 | 1.132 |
最小值 Min. | 0.029 | 0.520 | 0.049 | 0.517 | 0.043 |
表3 浙江天童及周边地区31个植物群落类型环境选择指数
Table 3 Indices of environmental dependence for 31 plant communities in the Tiantong region and surrounding area
群落号 Community code | 实际值 Actual | 最大Maximum | 相对值 Relative | 拟合最 大值a Fitted maximum | 拟合相 对值a Fitted relative |
---|---|---|---|---|---|
1 | 0.258 | 0.734 | 0.351 | 0.805 | 0.320 |
2 | 0.100 | 0.583 | 0.172 | 0.588 | 0.170 |
3 | 0.029 | 0.596 | 0.049 | 0.678 | 0.043 |
4 | 0.164 | 0.730 | 0.224 | 0.649 | 0.252 |
5 | 0.196 | 0.606 | 0.324 | 0.678 | 0.289 |
6 | 0.169 | 1.000 | 0.169 | 0.865 | 0.195 |
7 | 0.252 | 0.520 | 0.484 | 0.517 | 0.487 |
8 | 0.330 | 0.525 | 0.628 | 0.523 | 0.630 |
9 | 0.178 | 0.664 | 0.268 | 0.588 | 0.302 |
10 | 0.266 | 0.783 | 0.339 | 0.678 | 0.391 |
11 | 0.279 | 0.664 | 0.421 | 0.625 | 0.447 |
12 | 0.293 | 0.619 | 0.473 | 0.713 | 0.410 |
13 | 0.243 | 0.906 | 0.269 | 0.937 | 0.260 |
14 | 0.121 | 0.532 | 0.227 | 0.544 | 0.222 |
15 | 0.172 | 0.618 | 0.278 | 0.605 | 0.284 |
16 | 0.179 | 0.562 | 0.318 | 0.562 | 0.318 |
17 | 0.175 | 0.630 | 0.278 | 0.649 | 0.270 |
18 | 0.465 | 1.000 | 0.465 | 1.023 | 0.454 |
19 | 0.097 | 0.583 | 0.166 | 0.605 | 0.160 |
20 | 0.052 | 0.647 | 0.081 | 0.625 | 0.084 |
21 | 0.225 | 0.559 | 0.402 | 0.574 | 0.392 |
22 | 0.714 | 0.982 | 0.727 | 0.937 | 0.762 |
23 | 0.685 | 0.599 | 1.144 | 0.605 | 1.132 |
24 | 0.366 | 0.617 | 0.594 | 0.649 | 0.564 |
25 | 0.165 | 0.773 | 0.213 | 0.713 | 0.231 |
26 | 0.229 | 0.631 | 0.363 | 0.649 | 0.352 |
27 | 0.262 | 0.591 | 0.443 | 0.625 | 0.419 |
28 | 0.161 | 0.652 | 0.247 | 0.588 | 0.274 |
29 | 0.253 | 0.525 | 0.481 | 0.544 | 0.465 |
30 | 0.142 | 0.536 | 0.266 | 0.588 | 0.242 |
31 | 0.270 | 0.906 | 0.298 | 0.937 | 0.289 |
均值 Mean | 0.242 | 0.673 | 0.360 | 0.673 | 0.358 |
标准差 SD. | 0.152 | 0.145 | 0.212 | 0.135 | 0.209 |
范围 Range | 0.685 | 0.480 | 1.095 | 0.506 | 1.089 |
最大值 Max. | 0.714 | 1.000 | 1.144 | 1.023 | 1.132 |
最小值 Min. | 0.029 | 0.520 | 0.049 | 0.517 | 0.043 |
海拔高度 Altitude | 土壤水分 Soil water content | 光照强度 Light intensity | 土壤pH Soil pH | 土壤温度 Soil temperature | 空气温度 Air temperature | |
---|---|---|---|---|---|---|
R2 | 0.075 | 0.149 | -0.105 | 0.167 | -0.337 | -0.524 |
P | 0.689 | 0.424 | 0.575 | 0.370 | 0.063 | 0.002* |
95% CI | (-0.287, 0.418) | (-0.217, 0.478) | (-0.442, 0.259) | (-0.199, 0.492) | (-0.618, 0.019) | (-0.741, -0.208) |
表4 相对环境选择指数与6个环境因子的Pearson相关分析结果
Table 4 Pearson correlations between index of relative environmental dependence and each of 6 environmental variables
海拔高度 Altitude | 土壤水分 Soil water content | 光照强度 Light intensity | 土壤pH Soil pH | 土壤温度 Soil temperature | 空气温度 Air temperature | |
---|---|---|---|---|---|---|
R2 | 0.075 | 0.149 | -0.105 | 0.167 | -0.337 | -0.524 |
P | 0.689 | 0.424 | 0.575 | 0.370 | 0.063 | 0.002* |
95% CI | (-0.287, 0.418) | (-0.217, 0.478) | (-0.442, 0.259) | (-0.199, 0.492) | (-0.618, 0.019) | (-0.741, -0.208) |
1 | Abella SR, Shelburne VB (2004) Ecological species groups of South Carolina’s Jocassee Gorges, southern Appalachian Mountains.Journal of the Torrey Botanical Society, 131, 220-231. |
2 | Abella SR, Covington WW (2006) Vegetation-environment relationships and ecological species groups of an Arizona Pinus ponderosa landscape, USA.Plant Ecology, 185, 255-268. |
3 | Chave J (2004) Neutral theory and community ecology.Ecology Letters, 7, 241-253. |
4 | Ding SY (丁圣彦) (1999) Comparative Ecology of Successive Serial of Evergreen Broad-leaved Forest (常绿阔叶林演替系列比较生态学). Henan University Press, Kaifeng. (in Chinese) |
5 | Ellenberg H (1950) Unkrautgemeinschaften als Zeiger für Klima und Boden. Eugen Ulmer, Ludwigsburg. |
6 | Ellenberg H (1952) Wiesen und Weiden und ihre standortliche Bewertung. Eugen Ulmer, Ludwigsburg. |
7 | Gotelli JN (2000) Null model analysis of species co-occurrence patterns.Ecology, 81, 2606-2621. |
8 | Harper JL (1977) Population Biology of Plants. Academic Press, London. |
9 | Harms KE, Condit R, Hubbell SP, Foster RB(2001) Habitat associations of trees and shrubs in a 50 ha neotropical forest plot.Journal of Ecology, 89, 947-959. |
10 | Hubbell SP (2001) The Unified Neutral Theory of Biodiversity and Biogeography. Princeton University Press, Princeton, NJ. |
11 | Hubbell SP, Foster RB (1986) Biology, Chance and History and the Structure of Tropical Rain Forest Tree Communities. Harper & Row, New York. |
12 | Hubbell SP, Foster RB, O’Brien ST, Harms KE, Condit R, Wechsler B, Wright SJ, Loo de Lao S (1999) Light-gap disturbances, recruitment limitation, and tree diversity in a neotropical forest.Science, 283, 554-557. |
13 | Hughes RN (1988) A Functional Biology of Clinal Animals. Croom Helm, Beckenham. |
14 | Jiao L (焦磊), Zhang F (张峰) (2011) Ecological species groups of wetland vegetation on Lianbotan in Fen River, Shanxi.Scientia Silvae Sinicae(林业科学), 47, 7-12. (in Chinese with English abstract) |
15 | MacArthur RH (1965) Patterns of species diversity.Biological Reviews, 40, 510-533. |
16 | Mahalanobis PC (1936) On the generalised distance in statistics.Proceedings of the National Institute of Sciences of India, 2, 49-55. |
17 | McIntosh RP (1967) The continuum concept of vegetation.Botanical Review, 33, 130-187. |
18 | Moles AT, Warton DI, Warman L, Swenson NG, Laffan SW, Zanne AE, Pitman A, Hemmings FA, Leishman MR (2009) Global patterns in plant height.Journal of Ecology, 97, 923-932. |
19 | Ordoñez JC, van Bodegom PM, Witte JPM, Wright IJ, Reich PB, Aerts R (2009) A global study of relationships between leaf traits, climate and soil measures of nutrient fertility.Global Ecology and Biogeography, 18, 137-149. |
20 | Ozkan K (2009) Environmental factors as influencing vegetation communities in Acipayam district of Turkey.Journal of Environmental Biology, 30, 741-746. |
21 | Quesada CA, Lloyd J, Schwarz M, Baker TR, Phillips OL, Patiño S, Czimczik C, Hodnett MG, Herrera R, Arneth A, Lloyd G, Malhi Y, Dezzeo N, Luizão FJ, Santos AJB, Schmerler J, Arroyo L, Silveira M, Priante Filho N, Jimenez EM, Paiva R, Vieira I, Neill DA, Silva N, Peñuela MC, Monteagudo A, Vásquez R, Prieto A, Rudas A, Almeida S, Higuchi N, Lezama AT, López-González G, Peacock J, Fyllas NM, Alvarez Dávila E, Erwin T, di Fiore A, Chao KJ, Honorio E, Killeen T, Peña Cruz A, Pitman N, Núñez Var-gas P, Salomão R, Terborgh J, Ramírez H (2009) Regional and large-scale patterns in Amazon forest structure and function are mediated by variations in soil physical and chemical properties.Biogeosciences Discussions, 6, 3993-4057. |
22 | R Development Core Team (2012) R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna, Austria. URL |
23 | Song YC (宋永昌) (2001) Vegetation Ecology (植被生态学). East China Normal University Press, Shanghai. (in Chinese) |
24 | Song YC (宋永昌), Wang XR (王祥荣) (1995) Vegetation and Flora of Tiantong National Forest Park, Zhejiang Province (浙江天童国家森林公园的植被和区系). Shanghai Scientific and Technical Document Publishing House, Shanghai. (in Chinese) |
25 | Wang W (王伟), Luo ZR (骆争荣), Zhou RF (周荣飞), Xu DM (许大明), Ai JG (哀建国), Ding BY (丁炳扬) (2011) Habitat associations of woody plant species in Baishanzu subtropical broad-leaved evergreen forest.Biodiversity Science(生物多样性), 19, 134-142. (in Chinese with English abstract) |
26 | Wang XR (王祥荣) (1993) Analysis of the ecological characteristics of evergreen broad-leaved forest in Tiantong National Forest Park. Journal of Hubei University Natural Science Edition(湖北大学学报自然科学版), 15, 301-306. (in Chinese) |
27 | Westoby M, Wright IJ (2006) Land-plant ecology on the basis of functional traits.Trends in Ecology and Evolution, 21, 261-268. |
28 | Whittaker RH (1965) Dominance and diversity in land plant communities.Science, 147, 250-260. |
29 | Yan ER, Wang XH, Huang JJ (2006) Shifts in plant nutrient use strategies under secondary forest succession.Plant and Soil, 289, 187-197. |
30 | Zhang JT (张金屯) (2011) Quantitative Ecology, 2nd edn. (数量生态学第二版). Science Press, Beijing. (in Chinese) |
31 | Zhang JT (张金屯), Jiao R (焦蓉) (2003) Interspecific association between woody plants in shenweigou of Guandi Mountains, Shanxi province.Bulletin of Botanical Research(植物研究), 23, 458-463. (in Chinese) |
[1] | 赵勇强, 阎玺羽, 谢加琪, 侯梦婷, 陈丹梅, 臧丽鹏, 刘庆福, 隋明浈, 张广奇. 退化喀斯特森林自然恢复中不同生活史阶段木本植物物种多样性与群落构建[J]. 生物多样性, 2024, 32(5): 23462-. |
[2] | 林迪, 陈双林, 杜榷, 宋文龙, 饶固, 闫淑珍. 大别山黏菌的物种多样性调查[J]. 生物多样性, 2024, 32(2): 23242-. |
[3] | 陈哲涵, 尹进, 叶吉, 刘冬伟, 毛子昆, 房帅, 蔺菲, 王绪高. 增温对东北温带次生林草本群落季节动态的影响[J]. 生物多样性, 2023, 31(5): 23059-. |
[4] | 王晓凤, 米湘成, 王希华, 江明喜, 杨涛, 张健, 沈泽昊. 中国中亚热带常绿阔叶林群落木本植物多样性比较[J]. 生物多样性, 2023, 31(11): 23296-. |
[5] | 杨涛, 沈泽昊, 王晓凤, 饶杰生, 刘文聪, 田希, 陈稀, 张秋雨, 刘倩, 钱恒君, 解宇阳, 刘其明, 徐衍潇, 涂梦灵, 单子铭, 张玉坤, 侯波, 李建斌, 欧晓昆. 滇中高原亚热带半湿润常绿阔叶林植物群落多样性特征[J]. 生物多样性, 2023, 31(11): 23238-. |
[6] | 李正飞, 蒋小明, 王军, 孟星亮, 张君倩, 谢志才. 雅鲁藏布江中下游底栖动物物种多样性及其影响因素[J]. 生物多样性, 2022, 30(6): 21431-. |
[7] | 赵琦, 蒋际宝, 张曾鲁, 金清, 李佳丽, 邱江平. 海南岛蚯蚓物种组成及其系统发育分析[J]. 生物多样性, 2022, 30(12): 22224-. |
[8] | 李敏岚, 王超, 王瑞武. 路径依赖下的物种形成机制[J]. 生物多样性, 2021, 29(3): 409-418. |
[9] | 李世雄, 王彦龙, 王玉琴, 尹亚丽. 土壤细菌群落特征对高寒草甸退化的响应[J]. 生物多样性, 2021, 29(1): 53-64. |
[10] | 黄敦元, 黄世贵, 王建皓, 李红英, 窦飞越, 张可, 朱祥龙, 马方舟. 齐云山国家级自然保护区蝴蝶群落多样性[J]. 生物多样性, 2020, 28(8): 958-964. |
[11] | 刘丹, 郭忠玲, 崔晓阳, 范春楠. 5种东北红豆杉植物群丛及其物种多样性的比较[J]. 生物多样性, 2020, 28(3): 340-349. |
[12] | 李宝泉, 姜少玉, 吕卷章, 陈琳琳, 闫朗, 刘春云, 李晓静, 宋博, 李新正. 黄河三角洲潮间带及近岸浅海大型底栖动物物种组成及长周期变化[J]. 生物多样性, 2020, 28(12): 1511-1522. |
[13] | 邓亨宁, 鞠文彬, 高云东, 张君议, 李诗琦, 高信芬, 徐波. 新建川藏铁路(雅安-昌都段)沿线外来入侵植物种类及分布特征[J]. 生物多样性, 2020, 28(10): 1174-1181. |
[14] | 谢峰淋,周全,史航,舒枭,张克荣,李涛,冯水园,张全发,党海山. 秦岭落叶阔叶林25 ha森林动态监测样地物种组成与群落特征[J]. 生物多样性, 2019, 27(4): 439-448. |
[15] | 张田田, 王璇, 任海保, 余建平, 金毅, 钱海源, 宋小友, 马克平, 于明坚. 浙江古田山次生与老龄常绿阔叶林群落特征的比较[J]. 生物多样性, 2019, 27(10): 1069-1080. |
阅读次数 | ||||||
全文 |
|
|||||
摘要 |
|
|||||
备案号:京ICP备16067583号-7
Copyright © 2022 版权所有 《生物多样性》编辑部
地址: 北京香山南辛村20号, 邮编:100093
电话: 010-62836137, 62836665 E-mail: biodiversity@ibcas.ac.cn