生物多样性 ›› 2022, Vol. 30 ›› Issue (4): 21340. DOI: 10.17520/biods.2021340
鲁梦珍1,2,3, 曾馥平1,2,3, 宋同清1,2, 彭晚霞1,2, 张浩1,2, 苏樑1,2, 刘坤平1,2, 谭卫宁4, 杜虎1,2,*()
收稿日期:
2021-08-29
接受日期:
2022-01-06
出版日期:
2022-04-20
发布日期:
2022-04-20
通讯作者:
杜虎
作者简介:
*E-mail: hudu@isa.ac.cn基金资助:
Mengzhen Lu1,2,3, Fuping Zeng1,2,3, Tongqing Song1,2, Wanxia Peng1,2, Hao Zhang1,2, Liang Su1,2, Kunping Liu1,2, Weining Tan4, Hu Du1,2,*()
Received:
2021-08-29
Accepted:
2022-01-06
Online:
2022-04-20
Published:
2022-04-20
Contact:
Hu Du
摘要:
树木死亡在森林动态中发挥着重要作用, 环境因子是影响树木死亡的重要因素。为了阐明喀斯特常绿落叶阔叶林死亡个体空间分布格局及其与环境的相关性, 本研究以木论25 ha森林动态监测样地的两次木本植物调查数据为基础, 分析了死亡个体的物种组成、径级结构、分布格局及其与生境的关联。结果表明, 样地内共有死亡个体17,306株, 隶属57科130属194种; 其中, 死亡率排名前三的科和属分别为八角枫科、蔷薇科、大风子科以及山麻杆属(Alchornea)、火棘属(Pyracantha)、八角枫属(Alangium); 在物种水平上, 山麻杆(Alchornea trewioides)、毛桐(Mallotus barbatus)、野桐(Mallotus japonicus)等死亡率较高。样地内死亡个体的平均胸径为3.83 cm, 最大47.11 cm; 径级分布呈倒“J”型。从分布格局来看, 样地内大部分死亡个体在0-50 m的尺度上呈聚集分布, 部分大径级树木死亡个体趋向于随机分布。生境关联分析发现, 个体死亡率与山顶、陡坡、缓坡、洼地呈正关联的物种数分别为41种、13种、41种和38种, 呈负关联的物种数分别为38种、67种、33种和10种, 与各生境无关联的物种数分别为4种、3种、9种和35种; 多度排名前20的物种其个体死亡率均与4种生境类型呈现出正关联或者负关联; 不同径级个体死亡率都与山顶生境呈正关联, 与缓坡生境呈负关联, 其中5 cm ≤ DBH < 10 cm和10 cm ≤ DBH < 15 cm个体死亡率均与洼地生境呈正关联; DBH ≥ 15 cm个体死亡率与陡坡生境呈正关联, 与洼地生境呈负关联。在喀斯特亚热带常绿落叶阔叶林中, 死亡个体空间分布格局总体表现为聚集分布, 树木死亡受生境作用的影响较大。
鲁梦珍, 曾馥平, 宋同清, 彭晚霞, 张浩, 苏樑, 刘坤平, 谭卫宁, 杜虎 (2022) 喀斯特常绿落叶阔叶林死亡个体空间分布格局及生境关联. 生物多样性, 30, 21340. DOI: 10.17520/biods.2021340.
Mengzhen Lu, Fuping Zeng, Tongqing Song, Wanxia Peng, Hao Zhang, Liang Su, Kunping Liu, Weining Tan, Hu Du (2022) Spatial distribution pattern and habitat-association of snags in karst evergreen deciduous broad-leaved mixed forests. Biodiversity Science, 30, 21340. DOI: 10.17520/biods.2021340.
图1 木论25 ha森林动态监测样地内死亡个体数排名前五的科(A)、属(B)和种(C)
Fig. 1 The top five families (A), genera (B) and species (C) of snags in the 25 ha Mulun forest dynamic plot
科名 Families | 死亡率 Mortality rate (%) | 属名 Genera | 死亡率 Mortality rate (%) | 种名 Species | 死亡率 Mortality rate (%) |
---|---|---|---|---|---|
八角枫科 Alangiaceae | 39.21 | 山麻杆属 Alchornea | 60.15 | 山麻杆 Alchornea trewioides | 60.2 |
蔷薇科 Rosaceae | 35.28 | 火棘属 Pyracantha | 42.08 | 毛桐 Mallotus barbatus | 55.57 |
大风子科 Flacourtiaceae | 32.25 | 八角枫属 Alangium | 39.21 | 野桐 Mallotus japonicus | 42.7 |
马鞭草科 Verbenaceae | 27.31 | 花椒属 Zanthoxylum | 37.19 | 火棘 Pyracantha fortuneana | 42.08 |
木犀科 Oleaceae | 24.58 | 柞木属 Xylosma | 34.65 | 紫麻 Oreocnide frutescens | 40.4 |
表1 木论25 ha森林动态监测样地内死亡率排名前五的科、属、种
Table 1 The top five families, genera and species of mortality rate in the 25 ha Mulun forest dynamic plot
科名 Families | 死亡率 Mortality rate (%) | 属名 Genera | 死亡率 Mortality rate (%) | 种名 Species | 死亡率 Mortality rate (%) |
---|---|---|---|---|---|
八角枫科 Alangiaceae | 39.21 | 山麻杆属 Alchornea | 60.15 | 山麻杆 Alchornea trewioides | 60.2 |
蔷薇科 Rosaceae | 35.28 | 火棘属 Pyracantha | 42.08 | 毛桐 Mallotus barbatus | 55.57 |
大风子科 Flacourtiaceae | 32.25 | 八角枫属 Alangium | 39.21 | 野桐 Mallotus japonicus | 42.7 |
马鞭草科 Verbenaceae | 27.31 | 花椒属 Zanthoxylum | 37.19 | 火棘 Pyracantha fortuneana | 42.08 |
木犀科 Oleaceae | 24.58 | 柞木属 Xylosma | 34.65 | 紫麻 Oreocnide frutescens | 40.4 |
图3 木论25 ha森林动态监测样地不同径级死亡个体空间分布图(A、C、E、G、I)及点格局分析(B、D、F、H、J)。A、B: 所有个体; C、D: 1 cm ≤ DBH < 5 cm; E、F: 5 cm ≤ DBH < 10 cm; G、H: 10 cm ≤ DBH < 15 cm; I、J: DBH ≥ 15 cm。
Fig. 3 Spatial distribution (A, C, E, G, I) and point pattern analysis (B, D, F, H, J) of snags with different DBH classes in the 25 ha Mulun forest dynamic plot. A, B, All individuals; C, D, 1 cm ≤ DBH < 5 cm; E, F, 5 cm ≤ DBH < 10 cm; G, H, 10 cm ≤ DBH < 15 cm; I, J, DBH ≥ 15 cm.
图4 木论25 ha森林动态监测样地个体死亡率与4种生境呈不同关联性的物种数
Fig. 4 Number of species whose individual mortality associated with each of the four habitat types in the 25 ha Mulun forest dynamic plot
物种 Species | 死亡率 Mortality rate (%) | 多度 Abundance | 山顶 Hilltop | 陡坡 Steep slope | 缓坡 Gentle slope | 洼地 Depression |
---|---|---|---|---|---|---|
小果厚壳桂 Cryptocarya metcalfiana | 8.52 | 2,702 | + | - | - | - |
香叶树 Lindera communis | 33.83 | 1,416 | + | + | - | - |
圆果化香树 Platycarya longipes | 12.40 | 439 | - | - | + | 0 |
栀子皮 Itoa orientalis | 31.85 | 969 | + | + | - | - |
罗伞 Brassaiopsis glomerulata | 14.71 | 427 | + | - | - | + |
子楝树 Decaspermum gracilentum | 15.11 | 422 | - | - | + | + |
小叶山柿 Diospyros dumetorum | 21.79 | 556 | + | - | + | - |
齿叶黄皮 Clausena dunniana | 11.05 | 323 | - | - | + | + |
火棘 Pyracantha fortuneana | 40.08 | 906 | - | - | + | 0 |
密花树 Rapanea neriifolia | 12.03 | 232 | - | - | + | 0 |
滇丁香 Luculia intermedia | 33.18 | 582 | - | - | 0 | 0 |
小巴豆 Croton tiglium | 29.25 | 466 | + | - | + | 0 |
广西海桐 Pittosporum kwangsiense | 16.29 | 326 | + | - | - | + |
伞花木 Eurycorymbus cavaleriei | 17.14 | 260 | + | + | - | - |
四子海桐 Pittosporum tonkinense | 18.61 | 369 | - | - | 0 | 0 |
青篱柴 Tirpitzia sinensis | 21.03 | 225 | - | - | + | 0 |
杜茎山 Maesa japonica | 31.91 | 285 | + | - | - | + |
矮小天仙果 Ficus erecta | 23.59 | 188 | - | - | + | + |
野桐 Mallotus japonicus | 42.68 | 188 | + | - | - | 0 |
南岭柞木 Xylosma controversum | 34.65 | 228 | + | + | - | - |
表2 木论25 ha森林动态监测样地死亡个体数前20物种的个体死亡率与生境关联
Table 2 Habitat associations of individual mortality among 20 species with the most snags in the 25 ha Mulun forest dynamic plot
物种 Species | 死亡率 Mortality rate (%) | 多度 Abundance | 山顶 Hilltop | 陡坡 Steep slope | 缓坡 Gentle slope | 洼地 Depression |
---|---|---|---|---|---|---|
小果厚壳桂 Cryptocarya metcalfiana | 8.52 | 2,702 | + | - | - | - |
香叶树 Lindera communis | 33.83 | 1,416 | + | + | - | - |
圆果化香树 Platycarya longipes | 12.40 | 439 | - | - | + | 0 |
栀子皮 Itoa orientalis | 31.85 | 969 | + | + | - | - |
罗伞 Brassaiopsis glomerulata | 14.71 | 427 | + | - | - | + |
子楝树 Decaspermum gracilentum | 15.11 | 422 | - | - | + | + |
小叶山柿 Diospyros dumetorum | 21.79 | 556 | + | - | + | - |
齿叶黄皮 Clausena dunniana | 11.05 | 323 | - | - | + | + |
火棘 Pyracantha fortuneana | 40.08 | 906 | - | - | + | 0 |
密花树 Rapanea neriifolia | 12.03 | 232 | - | - | + | 0 |
滇丁香 Luculia intermedia | 33.18 | 582 | - | - | 0 | 0 |
小巴豆 Croton tiglium | 29.25 | 466 | + | - | + | 0 |
广西海桐 Pittosporum kwangsiense | 16.29 | 326 | + | - | - | + |
伞花木 Eurycorymbus cavaleriei | 17.14 | 260 | + | + | - | - |
四子海桐 Pittosporum tonkinense | 18.61 | 369 | - | - | 0 | 0 |
青篱柴 Tirpitzia sinensis | 21.03 | 225 | - | - | + | 0 |
杜茎山 Maesa japonica | 31.91 | 285 | + | - | - | + |
矮小天仙果 Ficus erecta | 23.59 | 188 | - | - | + | + |
野桐 Mallotus japonicus | 42.68 | 188 | + | - | - | 0 |
南岭柞木 Xylosma controversum | 34.65 | 228 | + | + | - | - |
径级 DBH classes | 山顶 Hilltop | 陡坡 Steep slope | 缓坡 Gentle slope | 洼地 Depression |
---|---|---|---|---|
1 cm ≤ DBH < 5 cm | + | - | - | 0 |
5 cm ≤ DBH < 10 cm | + | - | - | + |
10 cm ≤ DBH <1 5 cm | + | - | - | + |
15cm ≤ DBH | + | + | - | - |
总体 All individuals | + | - | - | 0 |
表3 木论25 ha森林动态监测样地死亡个体径级生境关联性分析
Table 3 Habitat associations of DBH classes of the snags in the 25 ha Mulun forest dynamic plot
径级 DBH classes | 山顶 Hilltop | 陡坡 Steep slope | 缓坡 Gentle slope | 洼地 Depression |
---|---|---|---|---|
1 cm ≤ DBH < 5 cm | + | - | - | 0 |
5 cm ≤ DBH < 10 cm | + | - | - | + |
10 cm ≤ DBH <1 5 cm | + | - | - | + |
15cm ≤ DBH | + | + | - | - |
总体 All individuals | + | - | - | 0 |
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