The Effects of the Functional Redundancy and Functional Diversity on the Community Stability in Different Stages of the Plant Communities Restoration in Karst Vegetation

doi:10.16258/j.cnki.1674-5906.2022.04.004

Ecology and Environment ›› 2022, Vol. 31 ›› Issue (4): 670-678.DOI: 10.16258/j.cnki.1674-5906.2022.04.004

• Research Articles • Previous Articles Next Articles

The Effects of the Functional Redundancy and Functional Diversity on the Community Stability in Different Stages of the Plant Communities Restoration in Karst Vegetation

FENG Ling¹^,²(), YU Lifei¹^,²^,^*(), WANG Yang¹^,², ZHANG Limin¹^,³, ZHAO Qing¹^,², LI Fangbing¹^,²

1. College of Life Sciences/Institute of Agro-bioengineering, Guizhou University, Guiyang 550025, P. R. China
2. Key laboratory of Plant Resource Conservation and Germplasm Innovation in Mountainous Region (Ministry of Education)/Collaborative Innovation Center of Mountain Ecology and Agricultural Bioengineering, Guiyang 550025, P. R. China
3. Guizhou Institute of Mountain Resources, Guiyang 550001, P. R. China

Received:2021-09-26 Online:2022-04-18 Published:2022-06-22
Contact: YU Lifei

喀斯特地区植被不同恢复阶段功能冗余和功能多样性对群落稳定性的影响

冯凌¹^,²(), 喻理飞¹^,²^,^*(), 王阳¹^,², 张丽敏¹^,³, 赵庆¹^,², 李方兵¹^,²

1.贵州大学生命科学学院/农业生物工程研究院,贵州贵阳 550025
2.贵州大学/山地植物资源保护与种质创新教育部重点实验室/山地生态与农业生物工程协同创新中心,贵州贵阳 550025
3.贵州省山地资源研究所,贵州贵阳 550001

通讯作者: 喻理飞
作者简介:冯凌（1993年生）,女,硕士研究生,研究方向为植物生态学。E-mail: 1047600511@qq.com
基金资助:
“十三五”国家重点研发计划(2016YFC0502604);贵州省生物学一流学科建设项目(GNYL[2017]009)

Abstract

Abstract:

Karst areas are ecologically fragile areas, due to the vulnerability of the environment itself and human disturbance, which makes vegetation restoration difficult. Therefore, the growth and maintenance of community stability in the process of vegetation restoration has become an important research area for guiding ecological restoration. This study investigates the relationship between functional diversity, functional redundancy and community stability through species functional traits, and clarifies the intrinsic factors that affect the growth and maintenance of community stability in the process of vegetation restoration. Using a “spatial instead of temporal” approach, plant communities at different stages of natural restoration of degraded karst vegetation (i.e., herbaceous stage, shrub-grass transition stage, shrub-shrub stage, shrub-tree transition stage and tree stage) were selected in the karst plateau area of Guizhou to investigate the differences in the effects of functional redundancy and functional diversity on community stability. The results showed that with the restoration of vegetation in the karst plateau area, (1) the stability of the community showed a gradual increase and both measurement methods obtained consistent resutls: the community stability index (C) increased from 0.393 to 1.206 and the M. Godron stability index method showed that the distance between the intersection of the curves and the stability point decreased from 10.49 to 2.32; (2) the functional redundancy increased gradually and reached the highest in the tree stage, with significant differences among the stages. The functional diversity increased first and then decreased, reaching the highest in the shrub-tree transition stage; (3) according to the stepwise regression results, both functional redundancy and functional diversity could improve the stability of the community, but their effects on stability were not consistent in different restoration stages. In the early restoration stage (herbaceous stage to the shrub-tree transition stage), functional diversity played a major role in maintaining community stability, while in the late restoration stage (tree stage), community stability was mainly determined by functional redundancy. Therefore, it is recommended that in order to improve and maintain the stability of the community during ecological restoration and forest management in karst areas, attention should be given to distinguishing different restoration stages and formulating targeted management measures.

Key words: functional redundancy, functional diversity, community stability, karst, species diversity, community

摘要：

喀斯特地区属于生态脆弱区,由于环境本身的脆弱性和人为的干扰,导致植被恢复难度较大。所以,在植被恢复过程中群落稳定性的增长和维持成为了重要的研究内容,对指导生态修复具有重要意义。该文通过物种功能性状研究功能多样性、功能冗余与群落稳定性的关系,阐明植被恢复过程中影响群落稳定性增长与维持的内在因素。采用“空间代替时间”的方法,在贵州喀斯特高原区选择处于退化喀斯特植被自然恢复不同阶段的植物群落,即草本群落阶段、灌草过渡阶段、灌木灌丛阶段、灌乔过渡阶段和乔木林阶段的植物群落,探究功能冗余和功能多样性对群落稳定性影响的差异。结果表明：在喀斯特高原区,随着植被的恢复（1）群落的稳定性呈现逐步递增的趋势,两种测定方式均得到一致的结果,群落稳定性指数（C）由0.393上升至1.206,M. Godron稳定性指数法也显示曲线交点与稳定点之间的距离由10.49缩短至2.32;（2）功能冗余逐步递增,在乔木林阶段达到最高,且各阶段具有显著性差异;功能多样性则是先增后减,在灌乔过渡阶段达到最高;（3）根据逐步回归结果显示,功能冗余和功能多样性均能提高群落的稳定性,但是在不同的恢复阶段两者对于稳定性的影响并不一致。在恢复前期（草本群落阶段至灌乔过渡阶段）,功能多样性对群落稳定性的维持起主要作用;而在恢复后期（乔木林阶段）,群落稳定性则主要由功能冗余决定。因此,建议在进行喀斯特地区生态恢复和森林经营管理时,为提高和维持群落的稳定性,要注意区分不同的恢复阶段,有针对性的制订管理措施。

关键词: 功能冗余, 功能多样性, 群落稳定性, 喀斯特, 物种多样性, 群落

CLC Number:

Q948
X173

FENG Ling, YU Lifei, WANG Yang, ZHANG Limin, ZHAO Qing, LI Fangbing. The Effects of the Functional Redundancy and Functional Diversity on the Community Stability in Different Stages of the Plant Communities Restoration in Karst Vegetation[J]. Ecology and Environment, 2022, 31(4): 670-678.

冯凌, 喻理飞, 王阳, 张丽敏, 赵庆, 李方兵. 喀斯特地区植被不同恢复阶段功能冗余和功能多样性对群落稳定性的影响[J]. 生态环境学报, 2022, 31(4): 670-678.

Figures/Tables 6

References 38

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样地号 Sample number	经度 Longitude/(°)	纬度 Latitude/(°)	海拔 Altitude/m	坡向 Aspect	坡度 Slope/(°)	样地面积 Area/m²
Ⅰ-1	105.831440	26.121520	1299	西南	8	30×30
Ⅰ-2	105.831390	26.121816	1295	西南	10	30×30
Ⅰ-3	105.831403	26.121454	1294	西南	10	30×30
Ⅱ-1	105.830819	26.122143	1326	东南	39	30×30
Ⅱ-2	105.830733	26.122364	1332	东南	30	30×30
Ⅱ-3	105.835735	26.118240	1338	西	35	30×30
Ⅲ-1	105.831537	26.122391	1240	西南	30	30×30
Ⅲ-2	105.831661	26.122272	1346	西南	30	30×30
Ⅲ-3	105.832622	26.121553	1345	西北	33	30×30
Ⅳ-1	105.830527	26.116990	1298	西北	40	30×30
Ⅳ-2	105.762302	26.117216	1323	西北	41	30×30
Ⅳ-3	105.830356	26.116761	1343	西北	42	30×30
Ⅴ-1	105.828362	26.128199	1239	东南	45	30×30
Ⅴ-2	105.828721	26.128599	1286	东南	48	30×30
Ⅴ-3	105.829093	26.128678	1296	东南	50	30×30

样地号 Sample number	经度 Longitude/(°)	纬度 Latitude/(°)	海拔 Altitude/m	坡向 Aspect	坡度 Slope/(°)	样地面积 Area/m²
Ⅰ-1	105.831440	26.121520	1299	西南	8	30×30
Ⅰ-2	105.831390	26.121816	1295	西南	10	30×30
Ⅰ-3	105.831403	26.121454	1294	西南	10	30×30
Ⅱ-1	105.830819	26.122143	1326	东南	39	30×30
Ⅱ-2	105.830733	26.122364	1332	东南	30	30×30
Ⅱ-3	105.835735	26.118240	1338	西	35	30×30
Ⅲ-1	105.831537	26.122391	1240	西南	30	30×30
Ⅲ-2	105.831661	26.122272	1346	西南	30	30×30
Ⅲ-3	105.832622	26.121553	1345	西北	33	30×30
Ⅳ-1	105.830527	26.116990	1298	西北	40	30×30
Ⅳ-2	105.762302	26.117216	1323	西北	41	30×30
Ⅳ-3	105.830356	26.116761	1343	西北	42	30×30
Ⅴ-1	105.828362	26.128199	1239	东南	45	30×30
Ⅴ-2	105.828721	26.128599	1286	东南	48	30×30
Ⅴ-3	105.829093	26.128678	1296	东南	50	30×30

功能性状 Functional traits	数据类型 Data type	特征类型 Feature type	生态学意义 Ecology significant
光合途径 Photosynthetic pathway	名称	C3、C4	代表不同的净光合速率和光呼吸速率（罗红艺, 2001）
生活型 Life form	名称	多年生、一年或两年生	反映植物对环境的适应能力
生长型 Growth form	名称	乔木、灌木、草本	反映植物对光的适应
叶表面特征 Leaf surface feature	名称	光滑、具毛、具刺	反映植物对光的利用
株高 Plant height/m	数值		反映植物对光、空间等资源的竞争能力（Westoby et al., 2002）
盖度 Coverage/%	数值		反映植物对环境的适应能力
叶厚 Leaf thickness/mm	数值		反映植物保水能力的强弱
叶面积 Leaf area/ cm²	数值		对叶的能量与水分平衡起着重要的作用（Ackerly et al., 2002）
叶长宽比 Leaf aspect ratio	数值		代表叶片中的水分向叶片表面扩散的阻力大小或者距离长短
比叶面积 Specific leaf area/(cm²∙g^-1)	数值		决定植物对光和CO₂的获取能力（Li et al., 2015）
叶绿素 Chlorophyll/%	数值		反映植物光合作用能力、环境胁迫、营养状态

功能性状 Functional traits	数据类型 Data type	特征类型 Feature type	生态学意义 Ecology significant
光合途径 Photosynthetic pathway	名称	C3、C4	代表不同的净光合速率和光呼吸速率（罗红艺, 2001）
生活型 Life form	名称	多年生、一年或两年生	反映植物对环境的适应能力
生长型 Growth form	名称	乔木、灌木、草本	反映植物对光的适应
叶表面特征 Leaf surface feature	名称	光滑、具毛、具刺	反映植物对光的利用
株高 Plant height/m	数值		反映植物对光、空间等资源的竞争能力（Westoby et al., 2002）
盖度 Coverage/%	数值		反映植物对环境的适应能力
叶厚 Leaf thickness/mm	数值		反映植物保水能力的强弱
叶面积 Leaf area/ cm²	数值		对叶的能量与水分平衡起着重要的作用（Ackerly et al., 2002）
叶长宽比 Leaf aspect ratio	数值		代表叶片中的水分向叶片表面扩散的阻力大小或者距离长短
比叶面积 Specific leaf area/(cm²∙g^-1)	数值		决定植物对光和CO₂的获取能力（Li et al., 2015）
叶绿素 Chlorophyll/%	数值		反映植物光合作用能力、环境胁迫、营养状态

恢复阶段 Restoration gradient	曲线 Curve	r²	交点坐标 Intersection coordinate	交点与稳定点距离 Distance between intersection and stable point
Ⅰ	y= -0.0011x²+0.2631x+84.286	0.926	(12.58, 87.42)	10.49
Ⅱ	y= -0.0065x²+1.1293x+49.663	0.882	(26.65, 74.35)	7.99
Ⅲ	y= -0.0071x²+1.2041x+48.465	0.970	(25.47, 74.53)	7.74
Ⅳ	y= -0.0054x²+0.9398x+58.070	0.956	(17.29, 82.71)	3.83
Ⅴ	y= -0.0101x²+1.4176x+52.418	0.722	(21.64, 78.36)	2.32

The Effects of the Functional Redundancy and Functional Diversity on the Community Stability in Different Stages of the Plant Communities Restoration in Karst Vegetation

喀斯特地区植被不同恢复阶段功能冗余和功能多样性对群落稳定性的影响

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恢复阶段 Restoration gradient	物种多样性(Simpson) Species diversity (Simpson)	功能多样性 Functional diversity	功能冗余 Functional redundancy	群落稳定性 Community stability
Ⅰ	0.336±0.013e	0.171±0.011d	0.165±0.008e	0.393±0.015e
Ⅱ	0.483±0.082d	0.274±0.013c	0.209±0.004d	0.478±0.09d
Ⅲ	0.648±0.009c	0.331±0.005b	0.317±0.005c	0.548±0.008c
Ⅳ	0.811±0.009b	0.443±0.005a	0.368±0.005b	0.693±0.008b
Ⅴ	0.892±0.053a	0.336±0.024b	0.556±0.029a	1.206±0.018a

恢复阶段 Restoration gradient	回归方程 Regression equations	r²	P	容忍度 Tolerance
Ⅰ	y=0.068+0.911x₁+0.907x₂	0.745	0.017	0.995
Ⅱ	y=0.081+0.918x₁+0.696x₂	0.928	0.000	0.807
Ⅲ	y=0.014+0.981x₁+0.757x₂	0.969	0.000	0.983
Ⅳ	y=0.003+0.870x₁+0.825x₂	0.869	0.002	0.999
Ⅴ	y=0.871+0.378x₁+0.392x₂	0.912	0.001	0.516

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