植物生态学报 ›› 2014, Vol. 38 ›› Issue (2): 178-187.DOI: 10.3724/SP.J.1258.2014.00016
收稿日期:
2013-05-20
接受日期:
2013-10-19
出版日期:
2014-05-20
发布日期:
2014-02-12
通讯作者:
白永飞
作者简介:
*(E-mail: yfbai@ibcas.ac.cn)基金资助:
LI Wen-Huai1,2, ZHENG Shu-Xia1,3, BAI Yong-Fei1,*()
Received:
2013-05-20
Accepted:
2013-10-19
Online:
2014-05-20
Published:
2014-02-12
Contact:
BAI Yong-Fei
摘要:
为了更好地理解放牧对草原生态系统物种多度分布格局的影响, 以及常见种和稀有种对维持群落多样性的作用, 以内蒙古典型草原为研究对象, 基于长期放牧控制实验平台(包括7个载畜率水平(0、1.5、3.0、4.5、6.0、7.5、9.0 sheep·hm-2)和两种地形系统(平地和坡地)), 研究了群落内全部物种、常见种和稀有种的丰富度和多度对放牧强度的响应规律, 并选取对数正态模型、对数级数模型和幂分割模型, 对物种多度数据进行拟合。结果表明: 1)平地系统中, 物种丰富度和多度在低放牧强度下(1.5、3.0 sheep·hm-2)增加, 而在中、高度放牧强度下(4.5-9.0 sheep·hm-2)降低, 全部物种的多度分布在大多数放牧强度下符合幂分割模型, 在高放牧强度下也符合对数正态模型; 坡地系统中, 物种丰富度和多度随着放牧强度增加而显著降低, 全部物种的多度分布在各个放牧强度下, 均符合幂分割模型和对数正态模型。2)随着放牧强度增加, 常见种的多度响应趋势与全部物种的响应趋势一致, 其多度分布均符合幂分割模型和对数正态模型; 稀有种的丰富度响应趋势与全部物种的响应趋势一致, 其多度分布符合幂分割模型, 同时也部分符合对数正态和对数级数模型。总之, 适宜的载畜率有利于生物多样性和初级生产力的提高, 平地系统中物种多度的响应在一定程度上支持放牧优化假说; 而坡地系统中不同物种多度的响应差异说明: 确定最佳载畜率时, 还需要考虑地形因素的影响。此外, 模型的拟合结果表明: 生态位分化机制对内蒙古典型草原物种多度分布起着主要作用, 常见种和稀有种通过不同的响应方式共同维持着草原生态系统的物种多样性。
李文怀, 郑淑霞, 白永飞. 放牧强度和地形对内蒙古典型草原物种多度分布的影响. 植物生态学报, 2014, 38(2): 178-187. DOI: 10.3724/SP.J.1258.2014.00016
LI Wen-Huai, ZHENG Shu-Xia, BAI Yong-Fei. Effects of grazing intensity and topography on species abundance distribution in a typical steppe of Inner Mongolia. Chinese Journal of Plant Ecology, 2014, 38(2): 178-187. DOI: 10.3724/SP.J.1258.2014.00016
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 102.59 | 139.36 | 38.83 | ||
1.5 | 258.62 | 189.75 | 129.53 | |||
3.0 | 257.22 | 355.39 | 196.32 | |||
4.5 | 124.60 | 10 728.30 | 70.35 | |||
6.0 | 121.09 | 4 138.05 | 113.39 | |||
7.5 | 20.74 | 309.06 | 51.78 | |||
9.0 | 86.56 | 251.41 | 97.29 | |||
坡地 Slope | 0 | 61.93 | 2 273.79 | 69.84 | ||
1.5 | 113.16 | 12 875.49 | 61.00 | |||
3.0 | 10.11 | 158.85 | 28.38 | |||
4.5 | 17.19 | 209.91 | 50.66 | |||
6.0 | 85.96 | 11 951.14 | 64.37 | |||
7.5 | 21.11 | 911.77 | 26.30 | |||
9.0 | 18.60 | 593.32 | 30.48 |
表1 平地和坡地系统中不同载畜率下全部物种多度分布的模型拟合结果
Table 1 Test of model fitting for abundance distribution of entire species at different stocking rates on flat and slopes
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 102.59 | 139.36 | 38.83 | ||
1.5 | 258.62 | 189.75 | 129.53 | |||
3.0 | 257.22 | 355.39 | 196.32 | |||
4.5 | 124.60 | 10 728.30 | 70.35 | |||
6.0 | 121.09 | 4 138.05 | 113.39 | |||
7.5 | 20.74 | 309.06 | 51.78 | |||
9.0 | 86.56 | 251.41 | 97.29 | |||
坡地 Slope | 0 | 61.93 | 2 273.79 | 69.84 | ||
1.5 | 113.16 | 12 875.49 | 61.00 | |||
3.0 | 10.11 | 158.85 | 28.38 | |||
4.5 | 17.19 | 209.91 | 50.66 | |||
6.0 | 85.96 | 11 951.14 | 64.37 | |||
7.5 | 21.11 | 911.77 | 26.30 | |||
9.0 | 18.60 | 593.32 | 30.48 |
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 6.74 | 499 524.71 | 1.41 | ||
1.5 | 14.75 | 971.90 | 11.56 | |||
3.0 | 5.38 | 424.30 | 3.34 | |||
4.5 | 4.71 | 464.07 | 2.58 | |||
6.0 | 7.19 | 1 143.67 | 3.65 | |||
7.5 | 8.58 | 382.30 | 5.77 | |||
9.0 | 5.44 | 209.68 | 6.29 | |||
坡地 Slope | 0 | 1.66 | 209 543.72 | 2.13 | ||
1.5 | 8.08 | 565.44 | 8.67 | |||
3.0 | 5.79 | 399.67 | 5.71 | |||
4.5 | 6.61 | 510.48 | 4.74 | |||
6.0 | 9.65 | 1 033.60 | 10.04 | |||
7.5 | 8.96 | 1 694.28 | 8.09 | |||
9.0 | 7.78 | 1 483.75 | 6.09 |
表2 平地和坡地系统中不同载畜率下常见种多度分布的模型拟合结果
Table 2 Test of model ?tting for abundance distribution of common species at different stocking rates on flat and slopes
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 6.74 | 499 524.71 | 1.41 | ||
1.5 | 14.75 | 971.90 | 11.56 | |||
3.0 | 5.38 | 424.30 | 3.34 | |||
4.5 | 4.71 | 464.07 | 2.58 | |||
6.0 | 7.19 | 1 143.67 | 3.65 | |||
7.5 | 8.58 | 382.30 | 5.77 | |||
9.0 | 5.44 | 209.68 | 6.29 | |||
坡地 Slope | 0 | 1.66 | 209 543.72 | 2.13 | ||
1.5 | 8.08 | 565.44 | 8.67 | |||
3.0 | 5.79 | 399.67 | 5.71 | |||
4.5 | 6.61 | 510.48 | 4.74 | |||
6.0 | 9.65 | 1 033.60 | 10.04 | |||
7.5 | 8.96 | 1 694.28 | 8.09 | |||
9.0 | 7.78 | 1 483.75 | 6.09 |
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 23.13 | 56.11 | 18.58 | ||
1.5 | 80.15 | 56.24 | 74.73 | |||
3.0 | 113.70 | 9 781.84 | 154.24 | |||
4.5 | 44.96 | 784.52 | 34.67 | |||
6.0 | 336.39 | 314.85 | 83.12 | |||
7.5 | 34.10 | 172 703.88 | 18.34 | |||
9.0 | 27.33 | 71.58 | 27.74 | |||
坡地 Slope | 0 | 40.46 | 25 043.12 | 54.60 | ||
1.5 | 3.00 | 147.06 | 2.49 | |||
3.0 | 9.06 | 429 739.72 | 6.87 | |||
4.5 | 5.24 | 559.83 | 5.56 | |||
6.0 | 49.32 | 390.53 | 18.02 | |||
7.5 | - | - | - | |||
9.0 | - | - | - |
表3 平地和坡地系统中不同载畜率下稀有种多度分布的模型拟合结果
Table 3 Test of model ?tting for abundance distribution of rare species at different stocking rates on flat and slopes
地形Topography | 载畜率 Stocking rate (sheep·hm-2) | 对数正态模型 Log-normal model | 对数级数模型 Log-series model | 幂分割模型 Power fraction model | ||
---|---|---|---|---|---|---|
拟合值 Fitted value r | 拟合值 Fitted value r | 拟合值 Fitted value r | ||||
平地 Flat | 0 | 23.13 | 56.11 | 18.58 | ||
1.5 | 80.15 | 56.24 | 74.73 | |||
3.0 | 113.70 | 9 781.84 | 154.24 | |||
4.5 | 44.96 | 784.52 | 34.67 | |||
6.0 | 336.39 | 314.85 | 83.12 | |||
7.5 | 34.10 | 172 703.88 | 18.34 | |||
9.0 | 27.33 | 71.58 | 27.74 | |||
坡地 Slope | 0 | 40.46 | 25 043.12 | 54.60 | ||
1.5 | 3.00 | 147.06 | 2.49 | |||
3.0 | 9.06 | 429 739.72 | 6.87 | |||
4.5 | 5.24 | 559.83 | 5.56 | |||
6.0 | 49.32 | 390.53 | 18.02 | |||
7.5 | - | - | - | |||
9.0 | - | - | - |
图1 全部物种、常见种和稀有种的丰富度和多度对放牧强度的响应。
Fig. 1 Responses of species richness and abundance of entire species, common species, and rare species to grazing intensity.
地形 Topography | 载畜率 Stocking rate (sheep·hm-2) | 全部物种 Entire species | 常见种 Common species | 稀有种 Rare species | ||||||
---|---|---|---|---|---|---|---|---|---|---|
丰富度 Richness | 多度 Abundance | 丰富度 Richness | 多度 Abundance | 丰富度 Richness | 多度 Abundance | |||||
平地 Flat | 0 | 1.00 ± 0.09ab | 1.00 ± 0.25ab | 1.00 ± 0a | 1.00 ± 0.25ab | 1.00 ± 0.12ab | 1.00 ± 0.15b | |||
1.5 | 1.37 ± 0.30a | 1.61 ± 0.52ab | 1.00 ± 0a | 1.59 ± 0.52ab | 1.49 ± 0.40a | 3.05 ± 0.29a | ||||
3.0 | 0.92 ± 0.30abc | 1.76 ± 0.63a | 1.00 ± 0a | 1.78 ± 0.63a | 0.89 ± 0.40abc | 0.58 ± 0.33b | ||||
4.5 | 0.41 ± 0.05cd | 0.62 ± 0.05b | 0.94 ± 0.06a | 0.61 ± 0.05b | 0.25 ± 0.06cd | 1.24 ± 1.17b | ||||
6.0 | 0.63 ± 0.05bcd | 0.89 ± 0.10ab | 0.94 ± 0.06a | 0.89 ± 0.10ab | 0.52 ± 0.05bcd | 0.84 ± 0.62b | ||||
7.5 | 0.35 ± 0.03d | 0.67 ± 0.04ab | 1.00 ± 0a | 0.67 ± 0.04ab | 0.14 ± 0.03d | 0.11 ± 0.06b | ||||
9.0 | 0.69 ± 0.05bcd | 0.84 ± 0.06ab | 1.00 ± 0a | 0.85 ± 0.06ab | 0.59 ± 0.06bcd | 0.31 ± 0.07b | ||||
坡地 Slope | 0 | 1.00 ± 0.05a | 1.00 ± 0.03ab | 1.00 ± 0a | 1.00 ± 0.03ab | 1.00 ± 0.08a | 1.00 ± 0.11a | |||
1.5 | 0.69 ± 0.09b | 1.19 ± 0.30a | 1.00 ± 0a | 1.20 ± 0.30a | 0.50 ± 0.15b | 0.24 ± 0.14bc | ||||
3.0 | 0.55 ± 0.03bc | 0.87 ± 0.05ab | 1.00 ± 0a | 0.88 ± 0.05ab | 0.26 ± 0.05bc | 0.17 ± 0.10bc | ||||
4.5 | 0.62 ± 0.07b | 0.72 ± 0.11b | 1.00 ± 0a | 0.72 ± 0.11b | 0.38 ± 0.12bc | 0.07 ± 0.01bc | ||||
6.0 | 0.63 ± 0.02b | 0.80 ± 0.13ab | 0.90 ± 0.10ab | 0.80 ± 0.13ab | 0.47 ± 0.08b | 0.38 ± 0.16b | ||||
7.5 | 0.38 ± 0.03c | 0.70 ± 0.02b | 0.86 ± 0bc | 0.70 ± 0.02b | 0.09 ± 0.05c | 0.01 ± 0.01c | ||||
9.0 | 0.42 ± 0.04c | 0.76 ± 0.10ab | 0.76 ± 0.05c | 0.76 ± 0.10ab | 0.21 ± 0.08bc | 0.08 ± 0.04bc |
表4 不同放牧强度下全部物种、常见种和稀有种的丰富度和多度响应值比较(平均值±标准误差, n = 3)
Table 4 Comparisons of the response values in species richness and abundance among different stocking rates for entire species, common species, and rare species (mean ± SE, n = 3)
地形 Topography | 载畜率 Stocking rate (sheep·hm-2) | 全部物种 Entire species | 常见种 Common species | 稀有种 Rare species | ||||||
---|---|---|---|---|---|---|---|---|---|---|
丰富度 Richness | 多度 Abundance | 丰富度 Richness | 多度 Abundance | 丰富度 Richness | 多度 Abundance | |||||
平地 Flat | 0 | 1.00 ± 0.09ab | 1.00 ± 0.25ab | 1.00 ± 0a | 1.00 ± 0.25ab | 1.00 ± 0.12ab | 1.00 ± 0.15b | |||
1.5 | 1.37 ± 0.30a | 1.61 ± 0.52ab | 1.00 ± 0a | 1.59 ± 0.52ab | 1.49 ± 0.40a | 3.05 ± 0.29a | ||||
3.0 | 0.92 ± 0.30abc | 1.76 ± 0.63a | 1.00 ± 0a | 1.78 ± 0.63a | 0.89 ± 0.40abc | 0.58 ± 0.33b | ||||
4.5 | 0.41 ± 0.05cd | 0.62 ± 0.05b | 0.94 ± 0.06a | 0.61 ± 0.05b | 0.25 ± 0.06cd | 1.24 ± 1.17b | ||||
6.0 | 0.63 ± 0.05bcd | 0.89 ± 0.10ab | 0.94 ± 0.06a | 0.89 ± 0.10ab | 0.52 ± 0.05bcd | 0.84 ± 0.62b | ||||
7.5 | 0.35 ± 0.03d | 0.67 ± 0.04ab | 1.00 ± 0a | 0.67 ± 0.04ab | 0.14 ± 0.03d | 0.11 ± 0.06b | ||||
9.0 | 0.69 ± 0.05bcd | 0.84 ± 0.06ab | 1.00 ± 0a | 0.85 ± 0.06ab | 0.59 ± 0.06bcd | 0.31 ± 0.07b | ||||
坡地 Slope | 0 | 1.00 ± 0.05a | 1.00 ± 0.03ab | 1.00 ± 0a | 1.00 ± 0.03ab | 1.00 ± 0.08a | 1.00 ± 0.11a | |||
1.5 | 0.69 ± 0.09b | 1.19 ± 0.30a | 1.00 ± 0a | 1.20 ± 0.30a | 0.50 ± 0.15b | 0.24 ± 0.14bc | ||||
3.0 | 0.55 ± 0.03bc | 0.87 ± 0.05ab | 1.00 ± 0a | 0.88 ± 0.05ab | 0.26 ± 0.05bc | 0.17 ± 0.10bc | ||||
4.5 | 0.62 ± 0.07b | 0.72 ± 0.11b | 1.00 ± 0a | 0.72 ± 0.11b | 0.38 ± 0.12bc | 0.07 ± 0.01bc | ||||
6.0 | 0.63 ± 0.02b | 0.80 ± 0.13ab | 0.90 ± 0.10ab | 0.80 ± 0.13ab | 0.47 ± 0.08b | 0.38 ± 0.16b | ||||
7.5 | 0.38 ± 0.03c | 0.70 ± 0.02b | 0.86 ± 0bc | 0.70 ± 0.02b | 0.09 ± 0.05c | 0.01 ± 0.01c | ||||
9.0 | 0.42 ± 0.04c | 0.76 ± 0.10ab | 0.76 ± 0.05c | 0.76 ± 0.10ab | 0.21 ± 0.08bc | 0.08 ± 0.04bc |
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