植物生态学报 ›› 2012, Vol. 36 ›› Issue (5): 411-419.DOI: 10.3724/SP.J.1258.2012.00411
所属专题: 生物多样性
发布日期:
2012-05-04
通讯作者:
杨永兴
作者简介:
* E-mail: yxyang56@126.com
HAN Da-Yong1, YANG Yong-Xing1,*(), YANG Yang2
Published:
2012-05-04
Contact:
YANG Yong-Xing
摘要:
植物多样性与种间相关性是植物群落生态学和生物多样性研究的核心问题, 然而有关二者之间关系的综合研究尚不多见。该文以若尔盖高原排水干扰下不同退化阶段的沼泽湿地植被为研究对象, 应用Spearman秩相关、回归分析等方法, 分析了沼泽植物群落物种多样性和种间相关性的变化及二者相互关系。结果表明: 沿排水梯度, 从相对原生沼泽至极度退化沼泽, 不同植物种群均有其特定的生态分布范围; 群落总种数、样方物种丰富度、Shannon-Wiener指数和Whittaker指数均单调增加; 植物种间相关强度增加; 正相关种对比例呈逐渐增加的趋势, 以极重度和极度退化阶段的较高, 相对原生沼泽和轻度退化阶段的较低, 负相关种对比例的变化趋势与之相反; Shannon-Wiener指数与正负相关种对比例均具有显著线性关系(p < 0.05), Whittaker指数均无显著关系(p > 0.05)。人为排水作用通过提高群落生境异质性, 促进正相关种对的共存, 增加沼泽群落植物多样性。
韩大勇, 杨永兴, 杨杨. 若尔盖高原退化沼泽群落植物多样性及种间相关性沿排水梯度的变化. 植物生态学报, 2012, 36(5): 411-419. DOI: 10.3724/SP.J.1258.2012.00411
HAN Da-Yong, YANG Yong-Xing, YANG Yang. Changes of plant species diversity and interspecific correlation in a degraded swamp community along drainage gradients on the Zoigê Plateau of China. Chinese Journal of Plant Ecology, 2012, 36(5): 411-419. DOI: 10.3724/SP.J.1258.2012.00411
退化阶段 Degradation stage | 群落类型 Community type | 地表积水状况 Surface water regime | 土壤类型 Soil type | 地貌 Geomorphy | 距排水沟距离 Distance to drainage ditch (m) |
---|---|---|---|---|---|
相对原生沼泽 Relative pristine swamp | 乌拉薹草 Carex meyeriana | 常年积水, 18-25 cm Permanent water regime, 18-25 cm | 泥炭土 Peat soil | 谷地中心 Valley center | 200-240 |
轻度退化 Light degradation | 乌拉薹草-矮地榆 Carex meyeriana- Sanguisorba filiformis | 常年积水, 5-20 cm Permanent water regime, 5-20 cm | 泥炭土 Peat soil | 谷地中心 Valley center | 150-210 |
中度退化 Moderate degradation | 木里薹草 Carex muliensis | 季节性积水, 0-15 cm Seasonal water regime, 0-15 cm | 泥炭土 Peat soil | 谷地边缘 Valley margin | 120-180 |
重度退化 Heavy degradation | 华扁穗草-矮地榆 Blysmus sinocompressus -Sanguisorba filiformis | 偶有积水, 0-5 cm Occasional water regime, 0-5 cm | 泥炭沼泽土 Peat swamp soil | 谷地边缘 Valley margin | 80-150 |
极重度退化 Severe degradation | 华扁穗草-发草 Blysmus sinocompressus- Deschampsia caespitosa | 无积水, 地表过湿 No water, over-humid surface | 沼泽化草甸土 Swamp meadow soil | 坡麓 Footslope | 50-100 |
极度退化 Extreme degradation | 西藏嵩草-蕨麻 Kobresia tibetica- Potentilla anserina | 无积水, 地表湿润 No water, humid surface | 沼泽化草甸土 Swamp meadow soil | 坡面 Slope | 10-30 |
表1 若尔盖高原排水沼泽不同退化阶段样地环境因子概况
Table 1 A survey of environment factors of sample area at different degradation stages in drained swamp on the Zoigê Plateau
退化阶段 Degradation stage | 群落类型 Community type | 地表积水状况 Surface water regime | 土壤类型 Soil type | 地貌 Geomorphy | 距排水沟距离 Distance to drainage ditch (m) |
---|---|---|---|---|---|
相对原生沼泽 Relative pristine swamp | 乌拉薹草 Carex meyeriana | 常年积水, 18-25 cm Permanent water regime, 18-25 cm | 泥炭土 Peat soil | 谷地中心 Valley center | 200-240 |
轻度退化 Light degradation | 乌拉薹草-矮地榆 Carex meyeriana- Sanguisorba filiformis | 常年积水, 5-20 cm Permanent water regime, 5-20 cm | 泥炭土 Peat soil | 谷地中心 Valley center | 150-210 |
中度退化 Moderate degradation | 木里薹草 Carex muliensis | 季节性积水, 0-15 cm Seasonal water regime, 0-15 cm | 泥炭土 Peat soil | 谷地边缘 Valley margin | 120-180 |
重度退化 Heavy degradation | 华扁穗草-矮地榆 Blysmus sinocompressus -Sanguisorba filiformis | 偶有积水, 0-5 cm Occasional water regime, 0-5 cm | 泥炭沼泽土 Peat swamp soil | 谷地边缘 Valley margin | 80-150 |
极重度退化 Severe degradation | 华扁穗草-发草 Blysmus sinocompressus- Deschampsia caespitosa | 无积水, 地表过湿 No water, over-humid surface | 沼泽化草甸土 Swamp meadow soil | 坡麓 Footslope | 50-100 |
极度退化 Extreme degradation | 西藏嵩草-蕨麻 Kobresia tibetica- Potentilla anserina | 无积水, 地表湿润 No water, humid surface | 沼泽化草甸土 Swamp meadow soil | 坡面 Slope | 10-30 |
图1 若尔盖高原沼泽植物群落优势植物沿排水梯度的生态分布。
Fig. 1 Ecological distribution of dominant species in swamp plant community along drainage gradients on the Zoigê Plateau.
图2 若尔盖高原排水沼泽不同退化阶段物种多样性的变化 (平均值±标准偏差)。ED, 极度退化; HD, 重度退化; LD, 轻度退化; MD, 中度退化; PS, 相对原生沼泽; SD, 极重度退化。
Fig. 2 Changes of species diversity at different degradation stages in drained swamp on the Zoigê Plateau (mean ± SD). ED, extreme degradation; HD, heavy degradation; LD, light degradation; MD, moderate degradation; PS, relative pristine swamp; SD, severe degradation.
退化阶段 Degradation stage | 显著正相关 Significant positive correlation | 显著负相关 Significant negative correlation | |||
---|---|---|---|---|---|
种对 Species pairs | r (i,k) | 种对 Species pairs | r (i, k) | ||
相对原生沼泽 Relative pristine swamp | 矮泽芹-斑唇马先蒿 Chamaesium paradoxum- Pedicularis longiflora var. tubiformis | 0.650** | 矮地榆-海韭菜 Sanguisorba filiformis- Triglochin maritimum | -0.489* | |
海韭菜-花葶驴蹄草 Triglochin maritimum-Caltha scaposa | -0.542* | ||||
黄花狸藻-乌拉薹草 Utricularia aurea-Carex meyeriana | -0.487* | ||||
轻度退化 Light degradation | 华丽龙胆-乌拉薹草 Gentiana sino-ornata-Carex meyeriana | 0.626** | 灯心草-花葶驴蹄草 Juncus effusus-Caltha scaposa | -0.604* | |
花葶驴蹄草-水木贼 Caltha scaposa-Hippochaete heleocharis | 0.618* | 黄花狸藻-华丽龙胆 Utricularia aurea-Gentiana sino-ornata | -0.586* | ||
木里薹草-乌拉薹草 Carex muliensis-Carex meyeriana | -0.570* | ||||
中度退化 Moderate degradation | 黄花狸藻-长茎毛茛 Utricularia aurea-Ranunculus longicaulis | 0.603* | 华扁穗草-水木贼 Blysmus sinocompressus- Hippochaete heleocharis | -0.697** | |
褐毛垂头菊-花葶驴蹄草 Cremanthodium brunneo-pilosum-Caltha scaposa | 0.569* | 褐毛垂头菊-水木贼 Cremanthodium brunneo- pilosum-Hippochaete heleocharis | -0.615* | ||
矮泽芹-黄花狸藻 Chamaesium paradoxum-Utricularia aurea | 0.553* | 矮地榆-黄花狸藻 Sanguisorba filiformis-Utricularia aurea | -0.604* | ||
重度退化 Heavy degradation | 矮地榆-湿生扁蕾 Sanguisorba filiformis-Gentianopsis paludosa | 0.501* | 毒芹-花葶驴蹄草 Cicuta virosa-Caltha scaposa | -0.637** | |
矮地榆-褐毛垂头菊 Sanguisorba filiformis- Cremanthodium brunneo-pilosum | 0.448* | 褐毛垂头菊-花葶驴蹄草 Cremanthodium brunneo-pilosum-Caltha scaposa | -0.635** | ||
发草-华扁穗草 Deschampsia caespitosa- Blysmus sinocompressus | 0.457* | 毒芹-华扁穗草 Cicuta virosa-Blysmus sinocompressus | -0.563* | ||
极重度退化 Severe degradation | 毒芹-发草 Cicuta virosa-Deschampsia caespitosa | 0.749** | 褐果薹草-湿生扁蕾 Carex brunnea-Gentianopsis paludosa | -0.719** | |
西藏嵩草-灯心草 Kobresia tibetica-Juncus effusus | 0.653** | 发草-高原毛茛 Deschampsia caespitosa- Ranunculus tanguticus | -0.697** | ||
高原毛茛-褐果薹草 Ranunculus tanguticus-Carex brunnea | 0.600* | 蕨麻-高原毛茛 Potentilla anserina- Ranunculus tanguticus | -0.679** | ||
极度退化 Extreme degradation | 矮地榆-花葶驴蹄草 Sanguisorba filiformis-Caltha scaposa | 0.727** | 火绒草-湿生扁蕾 Leontopodium leontopodioides-Gentianopsis paludosa | -0.746** | |
蕨麻-火绒草 Potentilla anserina- Leontopodium leontopodioides | 0.703** | 西藏嵩草-蕨麻 Kobresia tibetica-Potentilla anserina | -0.689** | ||
华扁穗草-火绒草 Blysmus sinocompressus- Leontopodium leontopodioides | 0.591* | 西藏嵩草-华扁穗草 Kobresia tibetica-Blysmus sinocompressus | -0.654** |
表2 若尔盖高原排水沼泽植物群落不同退化阶段秩相关系数(r (i, k))最高的前3对显著相关种对
Table 2 The first three species pairs with significant correlation ranked by Spearman’s rank correlation coefficients (r (i, k)) at different degradation stages in drained swamp plant community on the Zoigê Plateau
退化阶段 Degradation stage | 显著正相关 Significant positive correlation | 显著负相关 Significant negative correlation | |||
---|---|---|---|---|---|
种对 Species pairs | r (i,k) | 种对 Species pairs | r (i, k) | ||
相对原生沼泽 Relative pristine swamp | 矮泽芹-斑唇马先蒿 Chamaesium paradoxum- Pedicularis longiflora var. tubiformis | 0.650** | 矮地榆-海韭菜 Sanguisorba filiformis- Triglochin maritimum | -0.489* | |
海韭菜-花葶驴蹄草 Triglochin maritimum-Caltha scaposa | -0.542* | ||||
黄花狸藻-乌拉薹草 Utricularia aurea-Carex meyeriana | -0.487* | ||||
轻度退化 Light degradation | 华丽龙胆-乌拉薹草 Gentiana sino-ornata-Carex meyeriana | 0.626** | 灯心草-花葶驴蹄草 Juncus effusus-Caltha scaposa | -0.604* | |
花葶驴蹄草-水木贼 Caltha scaposa-Hippochaete heleocharis | 0.618* | 黄花狸藻-华丽龙胆 Utricularia aurea-Gentiana sino-ornata | -0.586* | ||
木里薹草-乌拉薹草 Carex muliensis-Carex meyeriana | -0.570* | ||||
中度退化 Moderate degradation | 黄花狸藻-长茎毛茛 Utricularia aurea-Ranunculus longicaulis | 0.603* | 华扁穗草-水木贼 Blysmus sinocompressus- Hippochaete heleocharis | -0.697** | |
褐毛垂头菊-花葶驴蹄草 Cremanthodium brunneo-pilosum-Caltha scaposa | 0.569* | 褐毛垂头菊-水木贼 Cremanthodium brunneo- pilosum-Hippochaete heleocharis | -0.615* | ||
矮泽芹-黄花狸藻 Chamaesium paradoxum-Utricularia aurea | 0.553* | 矮地榆-黄花狸藻 Sanguisorba filiformis-Utricularia aurea | -0.604* | ||
重度退化 Heavy degradation | 矮地榆-湿生扁蕾 Sanguisorba filiformis-Gentianopsis paludosa | 0.501* | 毒芹-花葶驴蹄草 Cicuta virosa-Caltha scaposa | -0.637** | |
矮地榆-褐毛垂头菊 Sanguisorba filiformis- Cremanthodium brunneo-pilosum | 0.448* | 褐毛垂头菊-花葶驴蹄草 Cremanthodium brunneo-pilosum-Caltha scaposa | -0.635** | ||
发草-华扁穗草 Deschampsia caespitosa- Blysmus sinocompressus | 0.457* | 毒芹-华扁穗草 Cicuta virosa-Blysmus sinocompressus | -0.563* | ||
极重度退化 Severe degradation | 毒芹-发草 Cicuta virosa-Deschampsia caespitosa | 0.749** | 褐果薹草-湿生扁蕾 Carex brunnea-Gentianopsis paludosa | -0.719** | |
西藏嵩草-灯心草 Kobresia tibetica-Juncus effusus | 0.653** | 发草-高原毛茛 Deschampsia caespitosa- Ranunculus tanguticus | -0.697** | ||
高原毛茛-褐果薹草 Ranunculus tanguticus-Carex brunnea | 0.600* | 蕨麻-高原毛茛 Potentilla anserina- Ranunculus tanguticus | -0.679** | ||
极度退化 Extreme degradation | 矮地榆-花葶驴蹄草 Sanguisorba filiformis-Caltha scaposa | 0.727** | 火绒草-湿生扁蕾 Leontopodium leontopodioides-Gentianopsis paludosa | -0.746** | |
蕨麻-火绒草 Potentilla anserina- Leontopodium leontopodioides | 0.703** | 西藏嵩草-蕨麻 Kobresia tibetica-Potentilla anserina | -0.689** | ||
华扁穗草-火绒草 Blysmus sinocompressus- Leontopodium leontopodioides | 0.591* | 西藏嵩草-华扁穗草 Kobresia tibetica-Blysmus sinocompressus | -0.654** |
图3 若尔盖高原沼泽植物群落种间相关植物种对比例沿排水梯度的变化。ED, 极度退化; HD, 重度退化; LD, 轻度退化; MD, 中度退化; PS, 相对原生沼泽; SD, 极重度退化。
Fig. 3 Changes of proportion of correlated plant species pairs in swamp plant community along drainage gradients on the Zoigê Plateau. ED, extreme degradation; HD, heavy degradation; LD, light degradation; MD, moderate degradation; PS, relative pristine swamp; SD, severe degradation.
图4 若尔盖高原沼泽植物群落沿排水梯度正负相关种对比例与Shannon-Wiener指数(A)和Whittaker指数(B)的关系。
Fig. 4 Relationships between the proportion of plant species pairs with positive and negative correlation and Shannon-Wiener indexes (A) and Whittaker indexes (B) in swamp plant community along drainage gradients on the Zoigê Plateau.
[1] | Bai JH (白军红), Ouyang H (欧阳华), Wang QG (王庆改), Gao HF (高海峰), Ding QY (丁秋祎) (2009). Changes in landscape patterns of alpine wetlands in Roige Plateau before and after drainage. Transactions of the Chinese Society of Agricultural Engineering (农业工程学报), 25(Supp1.), 64-68. (in Chinese with English abstract) |
[2] |
Bertness MD, Callaway R (1994). Positive interactions in communities. Tree, 9, 191-193.
URL PMID |
[3] |
Callaway RM, Brooker RW, Choler P, Kikvidze Z, Lortie CJ, Michalet R, Paolini L, Pugnaire FI, Newingham B, Achehoug ET, Armas C, Kikodze D, Cook BJ (2002). Positive interactions among alpine plants increase with stress. Nature, 417, 844-847.
URL PMID |
[4] | Cardinale BJ, Palmer MA, Collins SL (2002). Species diversity enhances ecosystem functioning through interspecific facilitation. Nature, 415, 426-429. |
[5] | Chen X (陈旭), Pu ZJ (卜兆君), Wang SZ (王升忠), Li HK (李鸿凯), Zhao HY (赵红艳) (2009). Interspecific relationships of bryophytes and vascular plants in two habitats of Hani peatland in Changbai Mountain. Acta Prataculturae Sinica (草业学报), 18(2), 108-114. (in Chinese with English abstract) |
[6] | Guo LJ (郭连金), Zhang WH (张文辉), Liu GB (刘国彬) (2007). Species diversity and interspecific association in development sequence of Hippophae rhamnoides plantations in Loess Hilly region. Chinese Journal of Applied Ecology (应用生态学报), 18, 9-15. (in Chinese with English abstract) |
[7] | Hacker SD, Gaines SD (1997). Some implications of direct positive interactions for community species diversity. Ecology, 78, 1990-2003. |
[8] | Han DY (韩大勇), Yang YX (杨永兴), Yang Y (杨杨), Li K (李珂) (2011). Species composition and succession of swamp vegetation along grazing gradients in the Zoigê Plateau, China. Acta Ecologica Sinica (生态学报), 31, 5946-5955. (in Chinese with English abstract) |
[9] | Hu N (胡楠), Fan YL (范玉龙), Ding SY (丁圣彦), Lu XL (卢训令) (2008). Classification of plant functional types based on dominant tree species in the forest ecosystem at Funiu Mountain National Reserve, East China. Journal of Plant Ecology (Chinese Version) (植物生态学报), 32, 1104-1115. (in Chinese with English abstract) |
[10] | Jian MF (简敏菲), Liu QJ (刘琪璟), Zhu D (朱笃), You H (游海) (2009). Inter-specific correlations among dominant populations of tree layer species in evergreen broad-leaved forest in Jiulianshan Mountain of subtropical China. Chinese Journal of Plant Ecology (植物生态学报), 33, 672-680. (in Chinese with English abstract) |
[11] | Li G (李刚), Zhu ZH (朱志红), Wang XA (王孝安), Guo H (郭华) (2008). Analysis of interspecific association for forest successional series of arbors in Ziwu Mountain. Journal of Northeast Forestry University (东北林业大学学报), 36(11), 25-28. (in Chinese with English abstract) |
[12] | Li JD (李建东), Zheng HY (郑慧莹) (1983). Über die anwendung der Braun-Blanquet’s methode in der steppen-untersuchung. Acta Phytoecologica et Geobotanica Sinica (植物生态学与地植物学丛刊), 7, 186-203. (in Chinese) |
[13] | Li YD, Xu H, Chen DX, Luo TS, Mo JH, Luo W, Chen HQ, Jiang ZL (2008). Division of ecological species groups and functional groups based on interspecific association — a case study of the tree layer in the tropical lowland rainforest of Jianfenling in Hainan Island, China. Frontiers of Forestry in China, 3, 407-415. |
[14] | Lou YJ (娄彦景), Zhao KY (赵魁义) (2008). Analysis of interspecific associations of Carex lasiocarpa community in recent 30-year succession in Sanjiang Plain. Chinese Journal of Ecology (生态学杂志), 27, 509-513. (in Chinese with English abstract) |
[15] | Ma KP (马克平), Liu CR (刘灿然), Liu YM (刘玉明) (1995). The measurement of community diversity II. The measurement of β diversity. Chinese Biodiversity (生物多样性), 3, 38-43. (in Chinese with English abstract) |
[16] | Nichols PWB, Morris EC, Keith DA (2010). Testing a facilitation model for ecosystem restoration: does tree planting restore ground layer species in a grassy woodland? Austral Ecology, 35, 888-897. |
[17] | O’Connor I, Aarssen LW (1987). Species association patterns in abandoned sand quarries. Plant Ecology, 73, 101-109. |
[18] | Qi K (奇凯), Zhang CY (张春雨), Hou JH (侯继华), Zhao XH (赵秀海) (2010). Dynamics of species diversity and interspecific associations of herbaceous plants in a Pinus tabulaeformis forest on a sandy site in Chifeng, China. Acta Ecologica Sinica (生态学报), 30, 5106-5112. (in Chinese with English abstract) |
[19] | Ren H (任海), Cai XA (蔡锡安), Rao XQ (饶兴权), Zhang QM (张倩媚), Liu SZ (刘世忠) (2001). The theory on succession of plant community. Ecologic Science (生态科学), 20(4), 59-67. (in Chinese with English abstract) |
[20] |
Silliman BR, Bertness MD, Altieri AH, Griffin JN, Bazterrica MC, Hidalgo FJ, Crain CM, Reyna MV, Vollmer S (2011). Whole-community facilitation regulates biodiver- sity on patagonian rocky shores. PloS ONE, 6, e24502.
URL PMID |
[21] | Sun GY (孙广友), Zhang WF (张文芬), Zhang JJ (张家驹), Yi FK (易富科), Zhao KY (赵魁义), Yang FM (杨福明), Luo J (罗佳) (1998). The Mire and Peatland of the Hengduan Mountains Region (横断山区沼泽与泥炭). Science Press, Beijing. 75-78. (in Chinese) |
[22] | Whittaker RH (1972). Evolution and measurement of species diversity. Taxon, 21, 213-251. |
[23] | Xing F (邢福), Guo JX (郭继勋) (2001). Comparative analysis of interspecific association for three grazing successional stages of Cleistogenes squarrosa steppe. Acta Phytoecologica Sinica (植物生态学报), 25, 693-698. (in Chinese with English abstract) |
[24] | Yang XD (杨晓东), Lü GH (吕光辉), Tian YH (田幼华), Yang J (杨军), Zhang XM (张雪梅) (2009). Ecological groups of plants in Ebinur Lake Wetland Nature Reserve of Xinjiang. Chinese Journal of Ecology (生态学杂志), 28, 2489-2494. (in Chinese with English abstract) |
[25] | Yang YX (杨永兴) (1999). Ecological environment deterioration, mire degeneration and their formation mechanism in the Zoigê Plateau. Journal of Mountain Science (山地学报), 17, 318-323. (in Chinese with English abstract) |
[26] | Zhang JL, Ding Q, Huang JH (2010). Species Association Analysis, version 0.2.0. http://cran.r-project.org/. Cited 3 September 2010. |
[27] | Zhang JT (张金屯) (2004). Quantitative Ecology (数量生态学). Science Press, Beijing. 98-109. (in Chinese) |
[28] | 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 with English abstract) |
[29] | Zhou XY (周先叶), Wang BS (王伯荪), Li MG (李鸣光), Zan QJ (昝启杰) (2000). An analysis of interspecific associations in secondary succession forest communities in Heishiding Natural Reserve, Guangdong Province. Acta Phytoecologica Sinica (植物生态学报), 24, 332-339. (in Chinese with English abstract) |
[30] | Zhu TC (祝廷成), Zhong ZC (钟章成), Li JD (李建东) (1988). Plant Ecology (植物生态学). Higher Education Press, Beijing. 185-187. (in Chinese) |
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