银合欢成功入侵热带雨林先锋群落的关键因素

doi:10.17521/cjpe.2020.0137

植物生态学报 ›› 2020, Vol. 44 ›› Issue (12): 1215-1223.DOI: 10.17521/cjpe.2020.0137 cstr: 32100.14.cjpe.2020.0137

所属专题：入侵生态学

银合欢成功入侵热带雨林先锋群落的关键因素

罗金环¹, 谭照远²^,³, 陈斌⁴, 陈广武⁴, 姜凯²^,³, 何奇芳²^,³, 张辉²^,³^,^**()

¹三亚林业科学研究院, 海南三亚 572000
²海南大学林学院/海南五指山森林生态系统国家定位观测研究站, 海口 570228
³热带特色林木花卉遗传与种质创新教育部重点实验室, 海南大学林学院, 海口 570228
⁴三亚市林业局, 海南三亚 572000

收稿日期:2020-05-11 接受日期:2020-06-17 出版日期:2020-12-20 发布日期:2021-04-01
作者简介:**(993781@hainu.edu.cn)
第一联系人：
* 同等贡献Contributed equally to this work.

Key characteristics for facilitating Leucaena leucocephala to successfully invade pioneer communities of tropical rain forests

LUO Jin-Huan¹, TAN Zhao-Yuan²^,³, CHEN Bin⁴, CHEN Guang-Wu⁴, JIANG Kai²^,³, HEI Qi-Fang²^,³, ZHANG Hui²^,³^,^**()

¹Sanya Academy of Forestry, Sanya, Hainan 572000, China
²College of Forestry/Wuzhishan National Forest Ecosystem Monitoring Research Station, Hainan University, Haikou 570228, China
³Key Laboratory of Genetics and Germplasm Innovation of Tropical Special Forest Trees and Ornamental Plants (Hainan University), Ministry of Education, College of Forestry, Hainan University, Haikou 570228, China
⁴Sanya Forestry Bureau, Sanya, Hainan 572000, China

Received:2020-05-11 Accepted:2020-06-17 Online:2020-12-20 Published:2021-04-01
About author:**(993781@hainu.edu.cn)

摘要/Abstract

摘要：

由于生长速率高, 耐旱性强, 银合欢(Leucaena leucocephala)被广泛应用于世界各地退化热带亚热带森林的修复, 但它也是一种全球性的外来入侵植物。已经有研究发现高生长速率可以帮助银合欢成功入侵亚热带森林, 但是目前还不清楚高生长速率和强耐旱性是否能帮助银合欢成功入侵热带森林。该研究以位于中国三亚抱坡岭被银合欢入侵的热带雨林先锋群落为研究对象, 通过t检验比较干季和湿季银合欢和8个热带雨林先锋群落的本地优势种与快速生长(光合速率、气孔导度和蒸腾速率)和耐旱性(叶片膨压丧失点)紧密相关的功能性状的差异, 并利用主成分分析(PCA)研究这些功能性状是否能很好地区分银合欢和其他8个本地优势种。结果表明: 银合欢在干湿季均能快速地生长(比本地物种显著更高的光合速率、气孔导度和蒸腾速率), 且在干季拥有更强的耐旱性(比本地物种显著更低的叶片膨压丧失点)。PCA结果表明这些功能性状能够显著区分银合欢和其他8个本地优势种。因此干湿季的稳定的快速生长和干季的强耐旱性使银合欢成功入侵热带雨林先锋群落。未来可利用这些功能性状筛选合适的本地物种对入侵其他热带森林的银合欢进行有效的生物防治。

关键词: 耐旱性, 快速生长, 功能性状, 入侵, 热带雨林先锋群落

Abstract:

Aims Due to fast-growing and high drought stress tolerance, Leucaena leucocephala has been widely used for afforestation in degraded tropical forests worldwide, but it is also a global invasive exotic species. Studies have shown that fast-growing can help L. leucocephala successfully invade subtropical forests. In this study, we aimed to investigate whether fast-growing and high drought stress tolerance can help L. leucocephala invade tropical rain forests.
Methods The pioneer community of tropical rain forest which had been invaded by L. leucocephala in the Baopoling Mountain, Sanya, China was the research object. Through the t-test, we compared the differences in key functional traits that were related to growth rate (photosynthesis rate, stomatal conductance and transpiration rate) and drought stress tolerance (leaf turgor loss point) in both wet and dry seasons between L. leucocephala and eight dominant native species of pioneer community of tropical rain forest. And the principal component analysis (PCA) was used to investigate whether these functional traits can best discriminate between Leucaena leucocephala and the eight dominant native species.
Important findings Leucaena leucocephala could be invariably growing fast (photosynthesis rate, stomatal conductance and transpiration rate much higher than native species) from wet to dry seasons and had higher drought stress tolerance (leaf turgor loss point much lower than native species) in the dry season. The results of PCA showed that these functional traits could significantly discriminate between L. leucocephala and the eight dominant native species. Therefore, invariable fast-growing from wet to dry season and high drought stress tolerance in the dry season make L. leucocephala successfully invade pioneer communities of tropical rain forests. In the future, these functional traits can be used to select many native species to perform biological control of L. leucocephala in other tropical forests.

Key words: drought stress tolerance, fast-growing, functional trait, invasion, pioneer community of tropical rain forest

罗金环, 谭照远, 陈斌, 陈广武, 姜凯, 何奇芳, 张辉. 银合欢成功入侵热带雨林先锋群落的关键因素. 植物生态学报, 2020, 44(12): 1215-1223. DOI: 10.17521/cjpe.2020.0137

LUO Jin-Huan, TAN Zhao-Yuan, CHEN Bin, CHEN Guang-Wu, JIANG Kai, HEI Qi-Fang, ZHANG Hui. Key characteristics for facilitating Leucaena leucocephala to successfully invade pioneer communities of tropical rain forests. Chinese Journal of Plant Ecology, 2020, 44(12): 1215-1223. DOI: 10.17521/cjpe.2020.0137

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.plant-ecology.com/CN/10.17521/cjpe.2020.0137

https://www.plant-ecology.com/CN/Y2020/V44/I12/1215

图/表 6

图1 利用银合欢修复三亚抱坡岭极度退化的热带雨林前后的抱坡岭景观。

Fig. 1 Baopoling landscapes before and after using Leucaena leucocephala to perform reforestation in the extremely degraded tropical rain forest.

图2 银合欢从种植到入侵邻近热带雨林先锋群落的过程。

Fig. 2 Detail processes for describing how Leucaena leucocephala successfully invades the adjacent pioneer community of tropical rain forest.

图3 银合欢和三亚抱坡岭8个本地优势种在干湿季时的4种功能性状之间的差异(平均值+标准误差)。***, p < 0.05; NS, p > 0.05。

Fig. 3 Differences in four functional traits between dry and wet season for Leucaena leucocephala and the eight dominant native species in the Baopoling Mountain, Sanya, China (mean + SE). ***, p < 0.05; NS, p > 0.05.

图4 银合欢和三亚抱坡岭8个本地优势种在4种功能性状上的差异(平均值+标准误差)。 A, 银合欢; B, 土蜜树; C, 美叶菜豆树; D, 赤才; E, 石斑木; F, 翻白叶树; G, 瓜馥木; H, 九节; I, 葨芝。***, p < 0.05; NS, p > 0.05。

Fig. 4 Differences in four functional traits between Leucaena leucocephala and each of the eight dominant native plant species in the Baopoling Mountain, Sanya, China (mean + SE). A, Leucaena leucocephala; B, Bridelia tomentosa; C, Radermachera frondosa; D, Lepisanthes rubiginosa; E, Rhaphiolepis indica; F, Pterospermum heterophyllum; G, Fissistigma oldhamii; H, Psychotria asiatica; I, Maclura cochinchinensis. ***, p < 0.05; NS, p > 0.05

图5 银合欢和三亚抱坡岭8个本地优势种基于4种功能性状的主成分分析。 A, 干季。B, 湿季。

Fig. 5 Principal component analysis of the four functional traits between Leucaena leucocephala and the eight doimant native plant species in the Baopoling Mountain, Sanya, China. A, Dry season. B, Wet season.

表1 银合欢和三亚抱坡岭8个本地优势种基于4种功能性状的主成分分析前两轴

Table 1 The first two axes of a principal component analysis for Leucaena leucocephala and the eight dominant native species in the Baopoling Mountain, Sanya, China, based on four plant functional traits

功能性状 Functional trait	轴1 PC1	轴2 PC2
蒸腾速率 Transpiration rate	0.51	-0.16
最大光合速率 Maximum photosynthesis rate	0.77	-0.15
气孔导度 Stomatal conductance	0.58	-0.19
叶片膨压丧失点 Leaf turgor loss point	0.11	0.53

参考文献 45

[1]	Barros V, Melo A, Santos M, Nogueira L, Frosi G, Santos MG (2020). Different resource-use strategies of invasive and native woody species from a seasonally dry tropical forest under drought stress and recovery. Plant Physiology and Biochemistry, 147, 181-190. URL PMID
[2]	Bartlett MK, Scoffoni C, Sack L (2012). The determinants of leaf turgor loss point and prediction of drought tolerance of species and biomes: a global meta-analysis. Ecology Letters, 15, 393-405. URL PMID
[3]	Bartlett MK, Zhang Y, Yang J, Kreidler N, Sun SW, Lin L, Hu YH, Cao KF, Sack L (2015). Drought tolerance as a driver of tropical forest assembly: resolving spatial signatures for multiple processes. Ecology, 97,503-514. DOI URL PMID
[4]	Blackman CJ, Brodribb TJ, Jordan GJ (2010). Leaf hydraulic vulnerability is related to conduit dimensions and drought resistance across a diverse range of woody angiosperms. New Phytologist, 188, 1113-1123.
[5]	Bucci SJ, Carbonell-Silletta LM, Garré A, Cavallaro A, Efron ST, Arias NS, Goldstein G, Scholz FG (2019). Functional relationships between hydraulic traits and the timing of diurnal depression of photosynthesis. Plant, Cell & Environment, 42,1603-1614. URL PMID
[6]	Chiou CR, Chen YJ, Wang HH, Grant WE (2016). Predicted range expansion of the invasive plant Leucaena leucocephala in the Hengchun Peninsula, Taiwan. Biological Invasions, 18, 381-394.
[7]	dos Santos VAHF, Ferreira MJ, Rodrigues JVFC, Garcia MN, Ceron JVB, Nelson BW, Saleska SR (2018). Causes of reduced leaf-level photosynthesis during strong El Niño drought in a Central Amazon forest. Global Change Biology, 24, 4266-4279. URL PMID
[8]	Funk JL, Cleland EE, Suding KN, Zavaleta ES (2008). Restoration through reassembly: plant traits and invasion resistance. Trends in Ecology & Evolution, 23, 695-703. URL PMID
[9]	Gibson AH, Dreyfus BL, Dommergues YR (1982). Nitrogen Fixation by Legumes in the Tropics. Microbiology of Tropical Soils and Plant Productivity, Springer, Dordrecht, the Netherlands.
[10]	Goel VL, Behl HM (2002). Selection of Leucaena species for afforestation and amelioration of sodic soils. Land Degradation & Development, 13, 387-393.
[11]	Guan K, Pan M, Li H, Wolf A, Wu J, Medvigy D, Caylor KK, Sheffield J, Wood EF, Malhi Y, Liang M, Kimball JS, Saleska SR, Berry J, Joiner J, Lyapustin AI (2015). Photosynthetic seasonality of global tropical forests constrained by hydroclimate. Nature Geoscience, 8, 284-289.
[12]	Hua L, Chen Y, Zhang H, Fu P, Fan Z (2017). Stronger cooling effects of transpiration and morphology of the plants from a hot dry habitat than from a hot wet habitat. Functional Ecology, 31, 2202-2211.
[13]	Hulme PE, Pyšek P, Jarošík V, Pergl J, Schaffner U, Vila M (2013). Bias and error in understanding plant invasion impacts. Trends in Ecology & Evolution, 28, 212-218. URL PMID
[14]	Ishihara KL, Honda MD, Bageel A, Borthakur D (2018). Leucaena leucocephala: a leguminous tree suitable for eroded habitats of Hawaiian islands. Ravine Lands: Greening for Livelihood and Environmental Security, 413-431.
[15]	Ji ZH, Fang HD, Yang YX, Pan ZX, Yue XW, Li JZ (2010). Mechanism research of gully controlling with Leucaena leucocephala in the Yuanmou Arid Hot Valley. Journal of Soil and Water Conservation, 24, 19-22, 26.
	[ 纪中华, 方海东, 杨艳鲜, 潘志贤, 岳学文, 李建增 (2010). 银合欢对元谋干热河谷冲沟治理的机理研究. 水土保持学报, 24, 19-22, 26.]
[16]	Kirschbaum MU (2011). Does enhanced photosynthesis enhance growth? Lessons learned from CO₂ enrichment studies. Plant Physiology, 155, 117-124. URL PMID
[17]	Küster EC, Kühn I, Bruelheide H, Klotz S (2008). Trait interactions help explain plant invasion success in the German flora. Journal of Ecology, 96, 860-868.
[18]	Laughlin DC (2014). Applying trait-based models to achieve functional targets for theory-driven ecological restoration. Ecology Letters, 17, 771-784. DOI URL PMID
[19]	Lawson T, Vialet-Chabrand S (2019). Speedy stomata, photosynthesis and plant water use efficiency. New Phytologist, 221, 93-98.
[20]	Li HS, Cai HJ, Li JM, Deng HY, Zhong BL (2015). A preliminary study on the alien invasive plant species in Huangshanlu Forest Park, Guangzhou. Journal of Guangdong University of Education, 35(5), 73-77.
	[ 李海生, 蔡惠娟, 李济明, 邓华源, 钟碧玲 (2015). 广州南沙黄山鲁森林公园外来入侵植物初步研究. 广东第二师范学院学报, 35(5), 73-77.]
[21]	Liu F, Gao C, Chen M, Li K (2018). Above- and below-ground biomass relationships of Leucaena leucocephala(Lam.) de Wit in different plant stands. PLOS ONE, 13, e0207059. DOI: 10.1371/journal.pone.0207059.
[22]	Luo HX, Dai SP, Li MF, Xie ZH (2018). Analysis on climate change characteristics of Hainan Island from 1959 to 2015. Jiangsu Agricultural Sciences, 46, 261-268.
	[ 罗红霞, 戴声佩, 李茂芬, 谢铮辉 (2018). 海南岛1959-2015年气候变化特征分析. 江苏农业科学, 46, 261-268.]
[23]	MacArthur R, Levins R (1967). The limiting similarity, convergence, and divergence of coexisting species. The American Naturalist, 101, 377-385.
[24]	Maherali H, Sherrard ME, Clifford MH, Latta RG (2008). Leaf hydraulic conductance and photosynthesis are genetically correlated in an annual grass. New Phytologist, 180, 240-247.
[25]	McAusland L, Vialet-Chabrand S, Davey P, Baker NR, Brendel O, Lawson T (2016). Effects of kinetics of light-induced stomatal responses on photosynthesis and water-use efficiency. New Phytologist, 211, 1209-1220.
[26]	Mitchell PJ, Veneklaas EJ, Lambers H, Burgess SS (2008). Leaf water relations during summer water deficit: differential responses in turgor maintenance and variation in leaf structure among different plant communities in south- western Australia. Plant, Cell & Environment, 31, 1791-1802. URL PMID
[27]	Moran VC, Hoffmann JH, Zimmermann HG (2005). Biological control of invasive alien plants in South Africa: necessity, circumspection, and success. Frontiers in Ecology and the Environment, 3, 71-77.
[28]	Ostertag R, Warman L, Cordell S, Vitousek PM (2015). Using plant functional traits to restore Hawaiian rainforest. Journal of Applied Ecology, 52, 805-809.
[29]	Peng SH, Wang HH, Kuo YL (2019). Methods for preventing the invasion of Leucaena leucocephala in coastal forests of the Hengchun Peninsula, Taiwan. Taiwan Journal of Forest Science, 34, 99-112.
[30]	Peng Y (2008). Study on Diversity and Invasion in Plantation of Alien Tree Species—Take Eucalyptus spp. Acacia dealbata, Leucaena leucocephala for Example. Master degree dissertation, Southwest Forestry University, Kunming.
	[ 彭芸 (2008). 外来树种人工林下植物多样性及其入侵性研究——以桉树、银荆、银合欢为例. 硕士学位论文, 西南林业大学, 昆明.]
[31]	Richardson DM, Rejmánek M (2011). Trees and shrubs as invasive alien species—A global review. Diversity and Distributions, 17, 788-809.
[32]	Rowland L, da Costa ACL, Oliveira AAR, Almeida SS, Meir P (2018). Shock and stabilisation following long-term drought in tropical forest from 15 years of litterfall dynamics. Journal of Ecology, 106, 1673-1682.
[33]	Sack L, Cowan P, Jaikumar N, Holbrook N (2003). The “hydrology” of leaves: co-ordination of structure and function in temperate woody species. Plant, Cell & Environment, 26, 1343-1356.
[34]	Schulte P, Hinckley T (1985). A comparison of pressure-volume curve data analysis techniques. Journal of Experimental Botany, 36, 1590-1602.
[35]	Seastedt TR (2015). Biological control of invasive plant species: a reassessment for the Anthropocene. New Phytologist, 205, 490-502.
[36]	van Kleunen M, Weber E, Fischer M (2010). A meta-analysis of trait differences between invasive and non-invasive plant species. Ecology Letters, 13, 235-245. URL PMID
[37]	Wang C, Zhang H, Liu H, Jian S, Yan J, Liu N (2020). Application of a trait-based species screening framework for vegetation restoration in a tropical coral island of China. Functional Ecology, 267, 25-34.
[38]	Wang W, Zhang XM, Sha LH Cheng LS (2007). Roster of alien: invasive perilous species of animals and plants in Hainan Island (one). Chinese Journal of Tropical Agriculture, 27, 58-64.
	[ 王伟, 张先敏, 沙林华, 程立生 (2007). 海南岛外来入侵危险性动植物名录(一). 热带农业科学, 27, 58-64.]
[39]	Wolfe BT, van Bloem SJ (2012). Subtropical dry forest regeneration in grass-invaded areas of Puerto Rico: understanding why Leucaena leucocephala dominates and native species fail. Forest Ecology and Management, 267, 253-261.
[40]	Yang XB, Chen ZZ, Li DH (2019). Vegetation of Hainan. Science Press, Beijing.
	[ 杨小波, 陈宗铸, 李东海(2019). 海南植被志. 科学出版社, 北京.]
[41]	Zhang H, Chen HYH, Lian J, Chandran RJ, Li RH, Liu H, Ye W, Berninger F, Ye Q (2018a). Using functional trait diversity patterns to disentangle the scale-dependent ecological processes in a subtropical forest. Functional Ecology, 32, 1379-1389.
[42]	Zhang H, Chandran RJ, Zhu S, Liu H, Xu Q, Qi W, Liu K, Chen HYH, Ye Q (2018b). Shifts in functional trait-species abundance relationships over secondary subalpine meadow succession in the Qinghai-Tibetan Plateau. Oecologia, 188, 547-557. URL PMID
[43]	Zhou LP, He YJ, Ma HC, Zhu CF, Gao Z, Li W, Li FX (2010). Effects of fertilization treatment on seedlings drought tolerance of Leucaena leucephala under different water conditions. Jiangxi Science, 28, 311-319, 358.
	[ 周利平, 和亚珺, 马焕成, 朱存福, 高柱, 李伟, 李福秀 (2010). 不同水分条件下施肥对新银合欢苗木抗旱性的影响. 江西科学, 28, 311-319, 358.]
[44]	Zhu SD, Song JJ, Li RH, Ye Q (2013). Plant hydraulics and photosynthesis of 34 woody species from different successional stages of subtropical forests. Plant, Cell & Environment, 36, 879-891. URL PMID
[45]	Zou HP, Zhang JH, Chen XM, Liu SJ, Li WG (2015). Spatiotemporal change characteristics of agricultural climate resources in Hainan Island. Chinese Journal of Agrometeorology, 36, 417-427.
	[ 邹海平, 张京红, 陈小敏, 刘少军, 李伟光 (2015). 海南岛农业气候资源的时空变化特征. 中国农业气象, 36, 417-427.]

银合欢成功入侵热带雨林先锋群落的关键因素

Key characteristics for facilitating Leucaena leucocephala to successfully invade pioneer communities of tropical rain forests

全文

PDF (PC)

可视化

被引次数

摘要/Abstract

引用本文

使用本文

图/表 6

参考文献 45

相关文章 15

编辑推荐

Metrics

本文评价

[1]	段建林, 孟晟, 陈仁利, 熊林峰, 卢春洋, 席念勋. 全球变化因子多样性对菌根植物性状的影响[J]. , 2026, 50(预发表): 0-.
[2]	何青, 袁旭东, 任博申, 冯治洋, 鲁梦珍, 林巧玲, 姜庆虎, 杨林森, 余辉亮, 姚辉, 杨敬元, 刘峰, 江明喜. 一年蓬（Erigeron annuus）入侵对亚高山泥炭湿地植物群落结构与多样性的影响[J]. 植物生态学报, 2026, 50(预发表): 0-.
[3]	张安宁, 肖亚宁, 赵霞, 张淼, 崔瀚文, 陈书燕, 安黎哲. 青藏高原灌木化与氮添加对土壤线虫及功能性状的交互作用[J]. 植物生态学报, 2026, 50(预发表): 0-.
[4]	林琳琳, 肖劲祥, 黄深深, 赵杨梅, 张德旭, 程毅康, 龙文兴. 磷添加对热带云雾林幼苗及幼树功能性状的影响[J]. , 2026, 50(预发表): 0-.
[5]	饶朝康, 唐亮. 不同潮位红树植物叶际微生物群落特征及其影响因素[J]. 植物生态学报, 2026, 50(预发表): 1-.
[6]	封逸凡, 朱时应, 周淑荣, 江乐乐, 陈隆, 王苗, 邓国芳, 刘兰. 热带次生林恢复中土壤微生物对菌根化树苗存活和生长性状的影响[J]. 植物生态学报, 2026, 50(预发表): 1-.
[7]	邹纪开, 吴佳怡, 谷云懿, 陈宝明. 不同形态氮添加与丛枝菌根真菌对外来入侵植物白花鬼针草竞争力的影响[J]. 植物生态学报, 2026, 50(3): 722-730.
[8]	任曦彤, 李颖, 张雨, 熊胡安赫, 张蕊科, 祁珊珊, 戴志聪, 杜道林. 丛枝菌根真菌与凋落物互作有助于加拿大一枝黄花应对营养胁迫[J]. 植物生态学报, 2026, 50(3): 710-721.
[9]	张永军, 李敬东, 安琦, 洪翎桂, 任正炜, 张蕊, 周小龙. 氮添加和增温对天山高寒草地群落性状的影响[J]. 植物生态学报, 2026, 50(2): 417-428.
[10]	张静, 陈洁, 李艳朋, 盘李军, 许涵, 李意德, 何海生. 南亚热带针阔混交人工林植物生物量比较及其影响因子分析[J]. 植物生态学报, 2026, 50(2): 400-416.
[11]	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[J]. 植物生态学报, 2026, 50(2): 442-460.
[12]	王爽, 陈雅轩, 陈艳梅, 王佳乐, 刘倩愿. 太行山典型区不同生境酸枣根系资源获取策略[J]. 植物生态学报, 2026, 50(2): 374-387.
[13]	陈雅轩, 韩雨音, 陈艳梅, 刘倩愿. 华北不同林龄人工林植物功能性状与碳氮化学计量[J]. 植物生态学报, 2026, 50(2): 318-333.
[14]	梁天豪, 吴帆, 黄锦学, 景陈鸿, 傅贺菁, 杨智杰, 熊德成. 增温对中亚热带格氏栲天然林细根生长量及形态特征的影响[J]. 植物生态学报, 2026, 50(1): 94-106.
[15]	郑子仪, 陈江慧, 刘慧颖. 气候变暖提高青藏高原高寒草甸优势物种的根系分泌速率[J]. 植物生态学报, 2025, 49(9): 1363-1373.