生物多样性 ›› 2024, Vol. 32 ›› Issue (12): 24282. DOI: 10.17520/biods.2024282 cstr: 32101.14.biods.2024282
陈明苗1, 张楚然2,3, 邓云2,4, 李生发5, 李逢昌5, 唐志忠5, 魏兆喆1, 张彩彩1,*()(
), 林露湘2,4,*(
)(
)
收稿日期:
2024-07-01
接受日期:
2024-10-11
出版日期:
2024-12-20
发布日期:
2025-01-10
通讯作者:
E-mail: 基金资助:
Mingmiao Chen1, Churan Zhang2,3, Yun Deng2,4, Shengfa Li5, Fengchang Li5, Zhizhong Tang5, Zhaozhe Wei1, Caicai Zhang1,*()(
), Luxiang Lin2,4,*(
)(
)
Received:
2024-07-01
Accepted:
2024-10-11
Online:
2024-12-20
Published:
2025-01-10
Contact:
E-mail: Supported by:
摘要: 萌生更新是森林更新的主要策略之一, 在个体存活、种群延续及群落生物多样性维持中起着关键作用。本研究基于云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地的木本植物调查数据, 分析了胸径(DBH) ≥ 1 cm的木本植物在物种和群落水平上萌生能力(萌生率、萌茎率、基部萌生率和基部萌茎率)的差异, 并探讨了萌生能力与地形因子之间的关系。结果表明: (1)样地内共有63种木本植物存在萌生现象, 占总物种数的68.5%, 其中58种发生基部萌生, 占总物种数的64.1%。萌生和基部萌生的个体数分别为9,668株和6,778株, 分别占总个体数的22.0%和15.4%。(2)乔木层植物的萌生率最高, 其次为亚乔木层, 灌木层最低; 乔木层和亚乔木层植物的萌茎率和基部萌生率显著高于灌木层; 而亚乔木层植物的基部萌茎率显著高于乔木层和灌木层。常绿植物的4个萌生指标均显著高于落叶植物。(3)乔木层植物的基部萌生率和基部萌茎率与海拔显著正相关; 亚乔木层植物的萌生率与凹凸度显著正相关, 萌茎率与坡度和凹凸度显著正相关, 而灌木层植物的萌生能力与4个地形因子无显著关联。常绿植物的萌生能力仅与凹凸度相关, 而落叶植物的萌生能力则受海拔和坡度的影响。总之, 鸡足山样地的萌生更新现象较为普遍, 主要受海拔和坡度等地形因素的影响。此外, 森林不同垂直层植物的萌生更新受地形因子的调控存在差异, 落叶植物较常绿植物更易受地形因子的影响。因此, 在研究环境对植物萌生更新的影响时, 需结合不同功能群的差异, 以更深入地理解萌生更新策略及其潜在生态学机制。
陈明苗, 张楚然, 邓云, 李生发, 李逢昌, 唐志忠, 魏兆喆, 张彩彩, 林露湘 (2024) 地形因子对亚热带半湿润常绿阔叶林木本植物萌生特征的影响. 生物多样性, 32, 24282. DOI: 10.17520/biods.2024282.
Mingmiao Chen, Churan Zhang, Yun Deng, Shengfa Li, Fengchang Li, Zhizhong Tang, Zhaozhe Wei, Caicai Zhang, Luxiang Lin (2024) Effect of topographic factors on sprouting characteristics of woody plants in subtropical semi-humid evergreen broad-leaved forests. Biodiversity Science, 32, 24282. DOI: 10.17520/biods.2024282.
萌生指标 Sprouting indicators | 种 Species | 科 Family | 属 Genus |
---|---|---|---|
总物种数 Total species number | 92 | 31 | 57 |
萌生/基部萌生物种数 Sprouting/basal sprouting species number | 63/58 | 21/19 | 38/35 |
物种萌生率/物种基部萌生率 Sprouting ratio of species/basal sprouting ratio of species (%) | 68.5/64.1 | 63.6/57.6 | 69.0/63.6 |
总个体数 Number of individuals | 44,015 | - | - |
萌生/基部萌生个体数 Number of sprouting/basal sprouting individuals | 9,668/6,778 | - | - |
萌生/基部萌生个体占比 Proportion of sprouting/basal sprouting individuals (%) | 22.0/15.4 | - | - |
萌生/基部萌生率中值 Median of sprouting/basal sprouting ratio (%) | 17.3/17.1 | 11.7/11.2 | 21.4/12.0 |
萌茎率/基部萌茎率 Sprouting stems ratio/basal sprouting stems ratio (%) | 36.1/22.9 | - | - |
萌茎率中值/基部萌茎率中值 Median of sprouting/basal sprouting stems ratio (%) | 34.2/22.9 | 29.1/17.8 | 30.0/17.8 |
表1 云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地木本植物萌生特征统计
Table 1 Sprouting characteristics of woody plant in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan
萌生指标 Sprouting indicators | 种 Species | 科 Family | 属 Genus |
---|---|---|---|
总物种数 Total species number | 92 | 31 | 57 |
萌生/基部萌生物种数 Sprouting/basal sprouting species number | 63/58 | 21/19 | 38/35 |
物种萌生率/物种基部萌生率 Sprouting ratio of species/basal sprouting ratio of species (%) | 68.5/64.1 | 63.6/57.6 | 69.0/63.6 |
总个体数 Number of individuals | 44,015 | - | - |
萌生/基部萌生个体数 Number of sprouting/basal sprouting individuals | 9,668/6,778 | - | - |
萌生/基部萌生个体占比 Proportion of sprouting/basal sprouting individuals (%) | 22.0/15.4 | - | - |
萌生/基部萌生率中值 Median of sprouting/basal sprouting ratio (%) | 17.3/17.1 | 11.7/11.2 | 21.4/12.0 |
萌茎率/基部萌茎率 Sprouting stems ratio/basal sprouting stems ratio (%) | 36.1/22.9 | - | - |
萌茎率中值/基部萌茎率中值 Median of sprouting/basal sprouting stems ratio (%) | 34.2/22.9 | 29.1/17.8 | 30.0/17.8 |
图1 云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地萌生植株萌茎数频次和每个20 m × 20 m样方的萌茎数
Fig. 1 Frequency of sprouting stems and total number of sprouting stems per 20 m × 20 m plot were monitored in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan
物种 Species | 重要值 Importance value (%) | 萌生率 Sprouting ratio (%) | 萌茎率 Sprouting stems ratio (%) | 基部萌生率 Basal sprouting ratio (%) | 基部萌茎率 Basal sprouting stems ratio (%) |
---|---|---|---|---|---|
银木荷 Schima argentea | 22.09 | 15.73 | 22.95 | 10.61 | 14.47 |
白柯 Lithocarpus dealbatus | 17.72 | 23.73 | 32.12 | 17.54 | 22.65 |
响叶杨 Populus adenopoda | 5.56 | 4.66 | 5.10 | 3.24 | 3.48 |
尼泊尔桤木 Alnus nepalensis | 5.53 | 10.66 | 12.21 | 4.07 | 4.65 |
五柱滇山茶 Camellia yunnanensis | 4.33 | 35.50 | 67.07 | 22.62 | 35.37 |
元江锥 Castanopsis orthacantha | 3.21 | 31.11 | 47.96 | 23.51 | 32.88 |
厚皮香 Ternstroemia gymnanthera | 3.17 | 16.03 | 21.15 | 12.03 | 15.10 |
云南凹脉柃 Eurya cavinervis | 3.16 | 23.59 | 37.38 | 18.94 | 28.54 |
云南越橘 Vaccinium duclouxii | 3.05 | 53.73 | 110.75 | 42.66 | 80.13 |
紫药女贞 Ligustrum delavayanum | 2.69 | 31.89 | 57.16 | 21.77 | 33.16 |
表2 云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地重要值排名前10位物种的萌生指标
Table 2 Sprouting indictors of the top 10 species with importance value in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan
物种 Species | 重要值 Importance value (%) | 萌生率 Sprouting ratio (%) | 萌茎率 Sprouting stems ratio (%) | 基部萌生率 Basal sprouting ratio (%) | 基部萌茎率 Basal sprouting stems ratio (%) |
---|---|---|---|---|---|
银木荷 Schima argentea | 22.09 | 15.73 | 22.95 | 10.61 | 14.47 |
白柯 Lithocarpus dealbatus | 17.72 | 23.73 | 32.12 | 17.54 | 22.65 |
响叶杨 Populus adenopoda | 5.56 | 4.66 | 5.10 | 3.24 | 3.48 |
尼泊尔桤木 Alnus nepalensis | 5.53 | 10.66 | 12.21 | 4.07 | 4.65 |
五柱滇山茶 Camellia yunnanensis | 4.33 | 35.50 | 67.07 | 22.62 | 35.37 |
元江锥 Castanopsis orthacantha | 3.21 | 31.11 | 47.96 | 23.51 | 32.88 |
厚皮香 Ternstroemia gymnanthera | 3.17 | 16.03 | 21.15 | 12.03 | 15.10 |
云南凹脉柃 Eurya cavinervis | 3.16 | 23.59 | 37.38 | 18.94 | 28.54 |
云南越橘 Vaccinium duclouxii | 3.05 | 53.73 | 110.75 | 42.66 | 80.13 |
紫药女贞 Ligustrum delavayanum | 2.69 | 31.89 | 57.16 | 21.77 | 33.16 |
图2 云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地不同垂直层次植物(a)和不同叶习性植物(b)的萌生能力(平均值 ± 标准误)。不同小写字母表示同一萌生指标在不同垂直层次和不同叶习性间的差异显著(P < 0.05)。
Fig. 2 Sprouting ability of plants at different vertical levels (a) and different leaf habits (b) in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan (mean ± SE). Different lowercase letters indicate significant differences in vertical levels and leaf habits for the same sprouting index (P < 0.05).
图3 地形因子对云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地不同垂直层次植物萌生能力的影响。* P < 0.05。横坐标代表地形因子对植物萌生能力影响的标准化系数。实心点和水平直线分别表示标准化系数的中值和95%的置信区间。
Fig. 3 Effect of topographic factors on plant sprouting ability at different vertical levels in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan. * P < 0.05. The horizontal axis represents the standardized coefficients of the impact of topography factors on the sprouting ability of plants. Solid points and bar lines indicate the medians and 95% confidence intervals of coefficients, respectively.
图4 地形因子对云南鸡足山亚热带半湿润常绿阔叶林20 ha动态监测样地不同叶习性植物萌生能力的影响。* P < 0.05。横坐标代表地形因子对植物萌生能力影响的标准化系数。实心点和水平直线分别表示标准化系数的中值和95%的置信区间。
Fig. 4 Effect of topography factors on plants sprouting ability at different leaf habits in the 20 ha forest dynamics plot of subtropical semi-humid evergreen broad-leaved forest in the Jizu Mountains, Yunnan. * P < 0.05. The horizontal axis represents the standardized coefficients of the impact of topography factors on the sprouting ability of plants. Solid points and bar lines indicate the medians and 95% confidence intervals of coefficients, respectively.
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