生物多样性 ›› 2023, Vol. 31 ›› Issue (5): 23074. DOI: 10.17520/biods.2023074
所属专题: 昆虫多样性与生态功能
• 研究报告: 动物多样性 • 上一篇
段曼微1, 李香2, 周阳1, 赵敏欣1, 孙秀玲3, 韩冰4, 张刚5, 权子豪1, 李凯1,*()
收稿日期:
2023-03-11
接受日期:
2023-05-16
出版日期:
2023-05-20
发布日期:
2023-05-20
通讯作者:
* E-mail: 基金资助:
Manwei Duan1, Xiang Li2, Yang Zhou1, Minxin Zhao1, Xiuling Sun3, Bing Han4, Gang Zhang5, Zihao Quan1, Kai Li1,*()
Received:
2023-03-11
Accepted:
2023-05-16
Online:
2023-05-20
Published:
2023-05-20
Contact:
* E-mail: 摘要:
斑块状造林是当前国内营建人工林的主要方式之一, 在林内不同斑块间形成了大量的边缘环境。为探究人工林斑块间边缘效应的生物多样性特点, 本文基于北京平原造林中的毛白杨(Populus tomentosa)林-国槐(Styphnolobium japonicum)林、国槐林-栾树(Koelreuteria paniculata)林、栾树林-桧柏(Juniperus chinensis)林、旱柳(Salix matsudana)林-杜仲(Eucommia ulmoides)林4种树种组合, 选择与植物具有营养关系的蛾类为研究对象, 采用非度量多维尺度(NMDS)排序、Anosim分析、物种多样性指数等对蛾类数量、物种组成与多样性进行分析; 并基于林下植被特征因子调查, 使用Pearson相关性分析探讨了植被特征因子与蛾类群落特征的关系。结果表明: 本研究共采集到蛾类4,428只, 分属于24科144种。(1)斑块边缘的蛾类物种组成与斑块内存在差异, 边缘独有种比例占所在样地组合物种数的13.59%-18.32%。(2)边缘物种多样性指数多为相邻斑块中间值或略高于斑块内; 旱柳林-杜仲林边缘的Simpson指数显著高于杜仲林斑块, Shannon-Wiener多样性指数、Margalef丰富度指数显著高于旱柳林斑块, Pielou均匀度指数显著低于杜仲林斑块。(3)蛾类Simpson指数与植被的平均高度和平均盖度呈显著负相关关系; 而蛾类物种数与植被的平均高度和平均盖度呈显著正相关关系。(4) 4种边缘类型的边缘效应均呈正效应(IH′ >1), 其中旱柳林-杜仲林边缘的边缘效应强度最低(IC = 0.915185808)。斑块状人工林的边缘中存在对生境变化产生响应的蛾类类群, 这是斑块状人工林生物多样性提高的基础。不同树种组合斑块的边缘效应所呈现的生物多样性特点不同, 可能存在优势物种暴发的风险。本研究可为后续造林及林分管理提供指导意见。
段曼微, 李香, 周阳, 赵敏欣, 孙秀玲, 韩冰, 张刚, 权子豪, 李凯 (2023) 基于蛾类多样性研究人工林斑块的边缘效应. 生物多样性, 31, 23074. DOI: 10.17520/biods.2023074.
Manwei Duan, Xiang Li, Yang Zhou, Minxin Zhao, Xiuling Sun, Bing Han, Gang Zhang, Zihao Quan, Kai Li (2023) Edge effect in plantation patches based on moth diversity. Biodiversity Science, 31, 23074. DOI: 10.17520/biods.2023074.
平均树高 Average tree height (m) | 平均胸径 Average diameter at breast height (cm) | 株行距 Distance between trees (m) | 林下植被高度 Height of understory vegetation (m) | 林下植被盖度 Coverage of understory vegetation (%) | |
---|---|---|---|---|---|
毛白杨林 Populus tomentosa forest (mby) | 13.53 ± 1.05 | 20.00 ± 1.63 | 4 × 4 | 0.18 ± 0.11 | 3.00 ± 1.41b |
毛白杨林-国槐林1边缘 Edge of Populus tomentosa forest & Styphnolobium japonicum forest 1 (Eyh) | - | - | - | 0.28 ± 0.10 | 53.89 ± 20.65a |
国槐林1 Styphnolobium japonicum forest 1 (gh1) | 9.17 ± 0.62 | 32.67 ± 2.05 | 4 × 4 | 0.31 ± 0.24 | 48.00 ± 21.02ab |
栾树林 Koelreuteria paniculata forest (ls) | 6.83 ± 0.85 | 17.67 ± 2.05 | 3.5 × 3.5 | 0.18 ± 0.19 | 20.67 ± 24.99b |
栾树林-国槐林2边缘 Edge of Koelreuteria paniculata forest & Styphnolobium japonicum forest 2 (Elh) | - | - | - | 0.28 ± 0.35 | 50.33 ± 27.19a |
国槐林2 Styphnolobium japonicum forest 2 (gh2) | 8.67 ± 0.47 | 21.33 ± 2.62 | 4 × 4.5 | 0.16 ± 0.09 | 59.22 ± 32.26a |
桧柏林-国槐林2边缘 Edge of Juniperus chinensis forest & Styphnolobium japonicum forest 2 (Ebh) | - | - | - | 0.35 ± 0.20 | 48.78 ± 29.18a |
桧柏林 Juniperus chinensis forest (gb) | 3.17 ± 0.24 | 13.00 ± 2.16 | 3 × 3 | 0.28 ± 0.13 | 64.44 ± 27.33a |
旱柳林 Salix matsudana forest (hl) | 12.00 ± 0.82 | 22.67 ± 2.05 | 4 × 4 | 0.35 ± 0.15 | 61.11 ± 12.86a |
旱柳林-杜仲林边缘 Edge of Salix matsudana forest & Eucommia ulmoides forest (Ehd) | - | - | - | 0.19 ± 0.07 | 51.78 ± 24.89a |
杜仲林 Eucommia ulmoides forest (dz) | 8.33 ± 0.47 | 25.00 ± 4.08 | 3.5 × 3.5 | 0.18 ± 0.06 | 24.22 ± 21.26b |
表1 人工林斑块蛾类调查样地概况(平均值 ± SD)
Table 1 Plot overview of plantation patches moth survey (mean ± SD)
平均树高 Average tree height (m) | 平均胸径 Average diameter at breast height (cm) | 株行距 Distance between trees (m) | 林下植被高度 Height of understory vegetation (m) | 林下植被盖度 Coverage of understory vegetation (%) | |
---|---|---|---|---|---|
毛白杨林 Populus tomentosa forest (mby) | 13.53 ± 1.05 | 20.00 ± 1.63 | 4 × 4 | 0.18 ± 0.11 | 3.00 ± 1.41b |
毛白杨林-国槐林1边缘 Edge of Populus tomentosa forest & Styphnolobium japonicum forest 1 (Eyh) | - | - | - | 0.28 ± 0.10 | 53.89 ± 20.65a |
国槐林1 Styphnolobium japonicum forest 1 (gh1) | 9.17 ± 0.62 | 32.67 ± 2.05 | 4 × 4 | 0.31 ± 0.24 | 48.00 ± 21.02ab |
栾树林 Koelreuteria paniculata forest (ls) | 6.83 ± 0.85 | 17.67 ± 2.05 | 3.5 × 3.5 | 0.18 ± 0.19 | 20.67 ± 24.99b |
栾树林-国槐林2边缘 Edge of Koelreuteria paniculata forest & Styphnolobium japonicum forest 2 (Elh) | - | - | - | 0.28 ± 0.35 | 50.33 ± 27.19a |
国槐林2 Styphnolobium japonicum forest 2 (gh2) | 8.67 ± 0.47 | 21.33 ± 2.62 | 4 × 4.5 | 0.16 ± 0.09 | 59.22 ± 32.26a |
桧柏林-国槐林2边缘 Edge of Juniperus chinensis forest & Styphnolobium japonicum forest 2 (Ebh) | - | - | - | 0.35 ± 0.20 | 48.78 ± 29.18a |
桧柏林 Juniperus chinensis forest (gb) | 3.17 ± 0.24 | 13.00 ± 2.16 | 3 × 3 | 0.28 ± 0.13 | 64.44 ± 27.33a |
旱柳林 Salix matsudana forest (hl) | 12.00 ± 0.82 | 22.67 ± 2.05 | 4 × 4 | 0.35 ± 0.15 | 61.11 ± 12.86a |
旱柳林-杜仲林边缘 Edge of Salix matsudana forest & Eucommia ulmoides forest (Ehd) | - | - | - | 0.19 ± 0.07 | 51.78 ± 24.89a |
杜仲林 Eucommia ulmoides forest (dz) | 8.33 ± 0.47 | 25.00 ± 4.08 | 3.5 × 3.5 | 0.18 ± 0.06 | 24.22 ± 21.26b |
图2 毛白杨林-国槐林1样地情况(a)及灯诱装置实物图(b, c)
Fig. 2 Schematic representation of Populus tomentosa forest & Styphnolobium japonicum forest 1 and its edge (a) and diagram of light trap (b, c)
科 Family | mby | Eyh | gh1 | ls | Elh | gh2 | Ebh | gb | hl | Ehd | dz |
---|---|---|---|---|---|---|---|---|---|---|---|
夜蛾科 Noctuidae | 181 | 109 | 122 | 298 | 239 | 117 | 99 | 203 | 240 | 361 | 204 |
尺蛾科 Geometridae | 68 | 52 | 122 | 79 | 87 | 85 | 71 | 23 | 13 | 30 | 23 |
螟蛾科 Pyralidae | 21 | 30 | 59 | 100 | 106 | 72 | 38 | 40 | 33 | 62 | 67 |
菜蛾科 Plutellidae | 12 | 6 | 15 | 23 | 26 | 18 | 26 | 47 | 9 | 18 | 15 |
卷蛾科 Tortricidae | 4 | 21 | 8 | 17 | 24 | 30 | 16 | 23 | 22 | 22 | 16 |
织蛾科 Oecophoridae | 1 | 3 | 5 | 14 | 11 | 16 | 15 | 17 | 21 | 23 | 10 |
麦蛾科 Gelechiidae | 7 | 5 | 10 | 18 | 13 | 2 | 5 | 6 | 28 | 13 | 10 |
草螟科 Crambidae | 2 | 13 | 10 | 11 | 15 | 9 | 8 | 4 | 6 | 24 | 13 |
舟蛾科 Notodontidae | 6 | 5 | 2 | 1 | 1 | 4 | 2 | - | 3 | 14 | 6 |
瘤蛾科 Nolidae | - | - | 1 | - | 1 | - | 1 | - | 7 | 18 | 12 |
其他 Others | 1 | 7 | 3 | 17 | 14 | 13 | 7 | 16 | 4 | 12 | 10 |
合计 Total | 303 | 251 | 357 | 578 | 537 | 366 | 288 | 379 | 386 | 597 | 386 |
表2 人工林斑块及边缘蛾类个体数量
Table 2 Individuals of moth in plantations patches and edges
科 Family | mby | Eyh | gh1 | ls | Elh | gh2 | Ebh | gb | hl | Ehd | dz |
---|---|---|---|---|---|---|---|---|---|---|---|
夜蛾科 Noctuidae | 181 | 109 | 122 | 298 | 239 | 117 | 99 | 203 | 240 | 361 | 204 |
尺蛾科 Geometridae | 68 | 52 | 122 | 79 | 87 | 85 | 71 | 23 | 13 | 30 | 23 |
螟蛾科 Pyralidae | 21 | 30 | 59 | 100 | 106 | 72 | 38 | 40 | 33 | 62 | 67 |
菜蛾科 Plutellidae | 12 | 6 | 15 | 23 | 26 | 18 | 26 | 47 | 9 | 18 | 15 |
卷蛾科 Tortricidae | 4 | 21 | 8 | 17 | 24 | 30 | 16 | 23 | 22 | 22 | 16 |
织蛾科 Oecophoridae | 1 | 3 | 5 | 14 | 11 | 16 | 15 | 17 | 21 | 23 | 10 |
麦蛾科 Gelechiidae | 7 | 5 | 10 | 18 | 13 | 2 | 5 | 6 | 28 | 13 | 10 |
草螟科 Crambidae | 2 | 13 | 10 | 11 | 15 | 9 | 8 | 4 | 6 | 24 | 13 |
舟蛾科 Notodontidae | 6 | 5 | 2 | 1 | 1 | 4 | 2 | - | 3 | 14 | 6 |
瘤蛾科 Nolidae | - | - | 1 | - | 1 | - | 1 | - | 7 | 18 | 12 |
其他 Others | 1 | 7 | 3 | 17 | 14 | 13 | 7 | 16 | 4 | 12 | 10 |
合计 Total | 303 | 251 | 357 | 578 | 537 | 366 | 288 | 379 | 386 | 597 | 386 |
图3 人工林斑块及边缘蛾类物种数(a)和个体数(b) (平均值 ± SD)。*代表斑块与边缘间差异显著; 不同小写字母表示不同边缘间差异显著。缩写含义见表1。
Fig. 3 Moth species number (a) and individuals (b) of plantation patches and edges (mean ± SD). * represents significant difference, different lowercase letters represent significant differences between different edges. The abbreviations see Table 1.
图5 人工林斑块及边缘的蛾类群落非度量多维尺度(NMDS)排序图
Fig. 5 Ordination plot of non-metric multidimensional scaling (NMDS) of moth communities in plantation patches and edge
图6 人工林边缘类型蛾类物种占其所属样地物种数比例 (平均值 ± SD)。Pu代表独有种比例; Pr为剩余物种比例。缩写含义见表1。
Fig. 6 Proportion of moth species of plantation edge types in the number of species in the plot (mean ± SD). Pu represents the proportion of unique species; Pr represents the proportion of the remaining species. The abbreviations see Table 1.
图7 人工林斑块及边缘物种多样性指数(平均值 ± SD)。*代表斑块与边缘间差异显著; 不同小写字母表示不同边缘间差异显著。缩写含义见表1。
Fig. 7 The species diversity index of plantation patches and edges (mean ± SD). * represents significant difference, different lowercase letters represent significant differences between different edges. The abbreviations see Table 1.
图8 蛾类特征指数与环境因子相关性分析。(a)温度(平均值 ± SD); (b)湿度(平均值 ± SD); (c)蛾类特征指数与植被特征因子相关性分析图, 圆圈大小代表相关性强度, “×”表示不存在显著相关性。Vh: 林下植被平均高度; Vc: 林下植被平均盖度; S: 物种数; N: 个体数; C: Simpson指数; H′: Shannon-Wiener多样性指数; J: Pielou均匀度指数; D: Margalef丰富度指数。其余缩写含义见表1。
Fig. 8 Correlation analysis between moth characteristic index and environmental factors. (a) Temperature (mean ± SD); (b) Humidity (mean ± SD); (c) The plot of correlation analysis between moth characteristic index and vegetation characteristic factors. The circle size represents the correlation strength, “×” represents no significant correlation. Vh, Height of understory vegetation; Vc, Coverage of understory vegetation; S, Species numbers; N, Individuals; C, Simpson index; H′, Shannon-Wiener diversity index; J, Pielou evenness index; D, Margalef richness index. Other abbreviations see Table 1.
边缘效应强度 Edge effect intensity | 毛白杨林-国槐林1边缘 Eyh | 栾树林-国槐林2边缘 Elh | 桧柏林-国槐林2边缘 Ebh | 旱柳林-杜仲林边缘 Ehd |
---|---|---|---|---|
IH’ | 1.102593793 | 1.078513732 | 1.105394079 | 1.080308277 |
Ic | 0.862558656 | 0.854916806 | 0.771192529 | 0.915185808 |
表3 不同人工林边缘类型的边缘效应指数
Table 3 Edge effect index of different plantation edge types. The abbreviations see Table 1.
边缘效应强度 Edge effect intensity | 毛白杨林-国槐林1边缘 Eyh | 栾树林-国槐林2边缘 Elh | 桧柏林-国槐林2边缘 Ebh | 旱柳林-杜仲林边缘 Ehd |
---|---|---|---|---|
IH’ | 1.102593793 | 1.078513732 | 1.105394079 | 1.080308277 |
Ic | 0.862558656 | 0.854916806 | 0.771192529 | 0.915185808 |
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