植物生态学报 ›› 2026, Vol. 50 ›› Issue (2): 442-460.DOI: 10.17521/cjpe.2024.0394 cstr: 32100.14.cjpe.2024.0394
戴丽君1,2,3, 向玲艺4, 蹇陈1,2,3, 王晓锋1,2,3,*(
)
收稿日期:2024-11-05
接受日期:2025-05-01
出版日期:2026-02-28
发布日期:2026-04-01
通讯作者:
*王晓锋(xiaofeng6540@163.com)基金资助:
DAI Li-Jun1,2,3, XIANG Ling-Yi4, JIAN Chen1,2,3, WANG Xiao-Feng1,2,3,*(
)
Received:2024-11-05
Accepted:2025-05-01
Online:2026-02-28
Published:2026-04-01
Contact:
*WANG Xiao-Feng (xiaofeng6540@163.com)Supported by:摘要:
三峡水库蓄水导致大量自然河岸带转变为反季节水位涨落的水库消落带, 形成了局域范围内生境的彻底转变, 对植物性状分化产生重要影响。该研究旨在探讨三峡回水扰动下入库小流域“河岸-消落带”生境转变对适生草本植物功能性状分异的影响及植物的适应策略。该研究以三峡库区入库小流域——白家溪为例, 选取了狗牙根(Cynodon dactylon)、狼杷草(Bidens tripartita)、苍耳(Xanthium strumarium)、水蓼(Polygonum hydropiper)等4种主要适生草本植物为对象, 分析了上游河岸带向下游消落带生境转变中17个植物功能性状指标的空间分异特征, 采用Pearson相关性分析植物各功能性状间的协同演变关联, 利用冗余分析分析生境因子对植物功能性状分异的影响。主要结果: (1)随着自然河岸带向消落带转变, 4种植物形态性状变异明显, 植株高度均增加, 根长变短, 这主要与消落带生境的生长期限制以及植物群落结构相对单一、竞争减弱有关; 同时, 大部分植物叶片厚度增加, 叶面积增大, 主要受夏季消落带干旱环境加剧的驱动; 三峡回水扰动显著增加了物种在局域范围内的形态变异。(2) 4种植物叶片的叶绿素含量和净光合速率在消落带明显高于自然河岸带, 表明植物在消落带生境的生长期限制下可能形成了光合效率提高、生长速度加快的适应策略。(3)在三峡回水的环境筛选作用下, 4种植物形成了独特的“生长-耐旱”的权衡策略, 并表现出明显的趋同适应; 但狗牙根的性状变异性较强, 尤其是其光合性状变异性强于其他3种植物, 表明狗牙根对生境转变具有更强的适应能力; 相比之下, 狼杷草、苍耳和水蓼形成了较为保守的适应对策。(4)冗余分析显示, 4种植物功能性状的变异特征在上游自然河岸带主要与土壤水分含量有关; 而在中游过渡带和下游消落带, 则主要与淹水深度、土壤pH、土壤温度有关, 表明淹水环境差异对植物功能性状的分异起到了促进作用。
戴丽君, 向玲艺, 蹇陈, 王晓锋. 三峡回水扰动增强入库小流域河岸带典型草本植物功能性状的局域分化. 植物生态学报, 2026, 50(2): 442-460. DOI: 10.17521/cjpe.2024.0394
DAI Li-Jun, XIANG Ling-Yi, JIAN Chen, WANG Xiao-Feng. Intensified local differentiation in plant functional traits among typical herbaceous plants by backwater disturbance within riparian zone of small watersheds in the Three Gorges Reservoir area. Chinese Journal of Plant Ecology, 2026, 50(2): 442-460. DOI: 10.17521/cjpe.2024.0394
图1 白家溪消落带采样点布设。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。
Fig. 1 Layout of sampling site in the drawdown zone of Baijiaxi. S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone.
| 断面 Transect | 土壤pH Soil pH | 土壤温度 Soil temperature (℃) | 土壤湿度 Soil humidity (%) | 土壤含水量 Soil water content (%) | 植物群落 Phytocoenosium | |
|---|---|---|---|---|---|---|
| 优势种 Dominant species | 盖度 Coverage (%) | |||||
| 1 | 7.39 ± 0.37c | 34.3 ± 4.6ab | 49.7 ± 14.7a | 35.4 ± 9.8a | 水蓼、空心莲子草、狗牙根、苍耳 Polygonum hydropiper, Alternanthera philoxeroides, Cynodon dactylon, Xanthium strumarium | 83-100 |
| 2 | 7.29 ± 0.49c | 33.0 ± 5.2b | 30.5 ± 11.6b | 20.9 ± 4.5b | 空心莲子草、狗牙根、狼杷草 Alternanthera philoxeroides, Cynodon dactylon, Bidens tripartite | 88-100 |
| 3 | 7.84 ± 0.50b | 37.3 ± 5.4a | 22.3 ± 5.2b | 14.0 ± 3.8c | 狗牙根、苍耳、水蓼、狼杷草、香附子 Cynodon dactylon, Xanthium strumarium, Polygonum hydropiper, Bidens tripartite, Cyperus rotundus | 95-100 |
| 4 | 7.84 ± 0.32b | 35.7 ± 3.6ab | 20.0 ± 6.0b | 12.8 ± 4.2c | 狗牙根、苍耳、水蓼、苘麻、狼杷草、香附子 Cynodon dactylon, Xanthium strumarium, Polygonum hydropiper, Abutilon theophrasti, Bidens tripartite, Cyperus rotundus | 95-100 |
| 5 | 8.17 ± 0.53ab | 36.5 ± 3.5ab | 21.3 ± 4.3b | 10.0 ± 2.1c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 6 | 8.09 ± 0.26ab | 36.4 ± 2.3ab | 22.1 ± 4.9b | 7.8 ± 1.6c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 7 | 8.36 ± 0.4a | 38.3 ± 4.7a | 21.6 ± 3.5b | 7.9 ± 1.8c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 8 | 8.31 ± 0.56a | 35.6 ± 2.9ab | 21.3 ± 3.2b | 7.7 ± 0.9c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
表1 白家溪流域自然河岸带至消落带土壤物理性状及植物群落状况
Table 1 Soil physical properties from natural riparian zone to subsidence zone in Baijiaxi Watershed
| 断面 Transect | 土壤pH Soil pH | 土壤温度 Soil temperature (℃) | 土壤湿度 Soil humidity (%) | 土壤含水量 Soil water content (%) | 植物群落 Phytocoenosium | |
|---|---|---|---|---|---|---|
| 优势种 Dominant species | 盖度 Coverage (%) | |||||
| 1 | 7.39 ± 0.37c | 34.3 ± 4.6ab | 49.7 ± 14.7a | 35.4 ± 9.8a | 水蓼、空心莲子草、狗牙根、苍耳 Polygonum hydropiper, Alternanthera philoxeroides, Cynodon dactylon, Xanthium strumarium | 83-100 |
| 2 | 7.29 ± 0.49c | 33.0 ± 5.2b | 30.5 ± 11.6b | 20.9 ± 4.5b | 空心莲子草、狗牙根、狼杷草 Alternanthera philoxeroides, Cynodon dactylon, Bidens tripartite | 88-100 |
| 3 | 7.84 ± 0.50b | 37.3 ± 5.4a | 22.3 ± 5.2b | 14.0 ± 3.8c | 狗牙根、苍耳、水蓼、狼杷草、香附子 Cynodon dactylon, Xanthium strumarium, Polygonum hydropiper, Bidens tripartite, Cyperus rotundus | 95-100 |
| 4 | 7.84 ± 0.32b | 35.7 ± 3.6ab | 20.0 ± 6.0b | 12.8 ± 4.2c | 狗牙根、苍耳、水蓼、苘麻、狼杷草、香附子 Cynodon dactylon, Xanthium strumarium, Polygonum hydropiper, Abutilon theophrasti, Bidens tripartite, Cyperus rotundus | 95-100 |
| 5 | 8.17 ± 0.53ab | 36.5 ± 3.5ab | 21.3 ± 4.3b | 10.0 ± 2.1c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 6 | 8.09 ± 0.26ab | 36.4 ± 2.3ab | 22.1 ± 4.9b | 7.8 ± 1.6c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 7 | 8.36 ± 0.4a | 38.3 ± 4.7a | 21.6 ± 3.5b | 7.9 ± 1.8c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
| 8 | 8.31 ± 0.56a | 35.6 ± 2.9ab | 21.3 ± 3.2b | 7.7 ± 0.9c | 狗牙根、苍耳、苘麻、水蓼、狼杷草 Cynodon dactylon, Xanthium strumarium, Abutilon theophrasti, Polygonum hydropiper, Bidens tripartite | 100 |
图2 白家溪4种植物叶形态沿河流纵向的空间分布特征。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。不同小写字母表示不同采样点间差异显著(p < 0.05)。
Fig. 2 Spatial distribution characteristics of leaf morphology of four species in Baijiaxi along the river. S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone. Lowercase letters in the figure represent significant difference (p < 0.05).
图3 白家溪植物根茎形态的纵向空间分布特征(平均值±标准差)。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。C为标准化后的植物根长。F为标准化后的植株高度。图中小写字母表示差异显著(p < 0.05)。
Fig. 3 Longitudinal spatial distribution characteristics of root and stem morphology of plants in Baijiaxi (mean ± SD). S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone. C is the plant root length after standardization. F is the plant height after standardization. Lowercase letters in the figure represent significant difference (p < 0.05).
图4 白家溪植物根茎叶鲜质量和干质量的纵向空间分布。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。p < 0.05表示线性关系显著; p > 0.05表示线性关系不显著。
Fig. 4 Longitudinal spatial distribution of fresh mass and dry mass of plant roots, stems and leaves in Baijiaxi Watershed. S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone. p < 0.05 indicates a significant linear relationship; p > 0.05 indicates that the linear relationship is not significant.
图5 白家溪植物根茎叶相对生物量及含水量纵向空间分布。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。
Fig. 5 Longitudinal zonation of relative biomass and water content in roots, stems, and leaves of Baijiaxi plants. S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone.
图6 白家溪植物光合性状的纵向空间分布。S1, S2, 自然河岸带; S3-S5, 过渡带; S6-S8, 消落带。p < 0.05表示线性关系显著; p > 0.05表示线性关系不显著。
Fig. 6 Longitudinal spatial distribution of photosynthetic traits in Baijiaxi plants. S1, S2, natural riparian zone; S3-S5, transition zone; S6-S8, drawdown zone. p < 0.05 indicates a significant linear relationship; p > 0.05 indicates that the linear relationship is not significant. Chl, chlorophyll; Pn, net photosynthetic rate.
| 性状 Trait | 狗牙根 Cynodon dactylon | 苍耳 Bidens tripartita | 狼杷草 Xanthium strumarium | 水蓼 Polygonum hydropiper |
|---|---|---|---|---|
| 植株高度 Plant height | 25 | 11 | 7 | 26 |
| 根长 Root length | 22 | 18 | 20 | 31 |
| 叶长 Leaf length | 9 | 11 | 6 | 30 |
| 叶厚 Leaf thickness | 42 | 24 | 19 | 48 |
| 叶面积 Leaf area | 22 | 25 | 27 | 34 |
| 比叶面积 Specific leaf area | 34 | 16 | 36 | 13 |
| 叶鲜质量 Leaf fresh mass | 34 | 16 | 25 | 33 |
| 叶干质量 Leaf dry mass | 43 | 17 | 20 | 34 |
| 茎鲜质量 Stem fresh mass | 30 | 31 | 29 | 19 |
| 茎干质量 Stem dry mass | 28 | 26 | 29 | 23 |
| 根鲜质量 Root fresh mass | 31 | 34 | 23 | 16 |
| 根干质量 Root dry mass | 33 | 41 | 32 | 14 |
| 叶绿素含量 Chlorophyll content | 27 | 8 | 14 | 13 |
| 净光合速率 Net photosynthetic rate | 29 | 14 | 22 | 14 |
| 叶含水量 Leaf water content | 19 | 2 | 5 | 8 |
| 茎含水量 Stem water content | 19 | 9 | 5 | 7 |
| 根含水量 Root water content | 31 | 18 | 11 | 9 |
表2 4种植物功能性状沿河流纵向空间分布的变异系数(%)
Table 2 Coefficient of variation (%) of 4 plants functional traits in longitudinal spatial distribution along the river
| 性状 Trait | 狗牙根 Cynodon dactylon | 苍耳 Bidens tripartita | 狼杷草 Xanthium strumarium | 水蓼 Polygonum hydropiper |
|---|---|---|---|---|
| 植株高度 Plant height | 25 | 11 | 7 | 26 |
| 根长 Root length | 22 | 18 | 20 | 31 |
| 叶长 Leaf length | 9 | 11 | 6 | 30 |
| 叶厚 Leaf thickness | 42 | 24 | 19 | 48 |
| 叶面积 Leaf area | 22 | 25 | 27 | 34 |
| 比叶面积 Specific leaf area | 34 | 16 | 36 | 13 |
| 叶鲜质量 Leaf fresh mass | 34 | 16 | 25 | 33 |
| 叶干质量 Leaf dry mass | 43 | 17 | 20 | 34 |
| 茎鲜质量 Stem fresh mass | 30 | 31 | 29 | 19 |
| 茎干质量 Stem dry mass | 28 | 26 | 29 | 23 |
| 根鲜质量 Root fresh mass | 31 | 34 | 23 | 16 |
| 根干质量 Root dry mass | 33 | 41 | 32 | 14 |
| 叶绿素含量 Chlorophyll content | 27 | 8 | 14 | 13 |
| 净光合速率 Net photosynthetic rate | 29 | 14 | 22 | 14 |
| 叶含水量 Leaf water content | 19 | 2 | 5 | 8 |
| 茎含水量 Stem water content | 19 | 9 | 5 | 7 |
| 根含水量 Root water content | 31 | 18 | 11 | 9 |
图7 白家溪4种植物功能性状沿河流纵向空间分布的相关性。蓝色代表正相关, 红色代表负相关, 颜色越深则表示相关关系越强。Chl, 叶绿素含量; LA, 叶面积; LDM, 叶干质量; LFM, 叶鲜质量; LL, 叶长; LT, 叶厚度; LWC, 叶含水量; PH, 植株高度; Pn, 净光合速率; RDM, 根干质量; RFM, 根鲜质量; RL, 根长; RWC, 根含水量; SDM, 茎干质量; SFM, 茎鲜质量; SLA, 比叶面积; SWC, 茎含水量。*, p < 0.05; **, p < 0.01; ***, p < 0.001。
Fig. 7 Correlation of functional traits among four plant species along the longitudinal river gradient in Baijiaxi. Blue represents a positive correlation, red represents a negative correlation, and the darker the color, the greater the correlation. Chl, chlorophyll content; LA, leaf area; LDM, leaf dry mass; LFM, leaf fresh mass; LL, leaf length; LT, leaf thickness; LWC, leaf water content; PH, plant height; Pn, net photosynthetic rate; RDM, root dry mass; RFM, root fresh mass; RL, root length; RWC, root water content; SDM, stem dry mass; SFM, stem fresh mass; SLA, specific leaf area; SWC, stem water content. *, p < 0.05; **, p < 0.01; ***, p < 0.001.
图8 白家溪流域自然河岸带至消落带不同植物功能性状与环境因子的冗余分析(RDA)。环境变量对功能形状的解释度见附录II。1, 2, 自然河岸带; 3-5, 过渡带; 6-8, 消落带。Chl, 叶绿素含量; Hs, 土壤湿度; IT, 淹水时长; LA, 叶面积; LDM, 叶干质量; LFM, 叶鲜质量; LL, 叶长; LT, 叶厚度; LWC, 叶含水量; PH, 植株高度; pH, 酸碱度; Pn, 净光合速率; RDM, 根干质量; RFM, 根鲜质量; RL, 根长; RWC, 根含水量; SDM, 茎干质量; SFM, 茎鲜质量; SLA, 比叶面积; SWC, 茎含水量; Ts, 土壤温度; WC, 土壤含水量; WD, 淹水深度。
Fig. 8 Redundancy analysis (RDA) analysis of plant functional traits and environmental factors from natural riparian zone to water level zone in Baijiaxi Watershed. Contribution of environmental variables to functional traits is presented in Appendix II. 1, 2, natural riparian zone; 3-5, transition zone; 6-8, drawdown zone. Chl, chlorophyll content; Hs, soil humidity; IT, inundation time; LA, leaf area; LDM, leaf dry mass; LFM, leaf fresh mass; LL, leaf length; LT, leaf thickness; LWC, leaf water content; PH, plant height; Pn, net photosynthetic rate; RDM, root dry mass; RFM, root fresh mass; RL, root length; RWC, root water content; SDM, stem dry mass; SFM, stem fresh mass; SLA, specific leaf area; SWC, stem water content; Ts, soil temperature; WC, soil water content; WD, water depth.
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