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引用本文:王世雄, 夏婷婷, 王孝安.黄土高原油松和辽东栎林下植物β多样性差异及影响因素[J].广西植物,2021,41(3):362-371.[点击复制]
WANG Shixiong, XIA Tingting, WANG Xiaoan.Understory β diversity differences and influential factors between Pinus tabulaeformis plantation and natural Quercus wutaishanica forest on the Loess Plateau[J].Guihaia,2021,41(3):362-371.[点击复制]
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黄土高原油松和辽东栎林下植物β多样性差异及影响因素
王世雄1, 2, 3*, 夏婷婷2, 王孝安3
1. 青海师范大学 生命科学学院, 高原科学与可持续发展研究院, 西宁 810008; 2. 贵州大学 林学院, 贵阳 550025; 3. 陕西师范大学 生命科学学院, 西安 710119
摘要:
β多样性是生态学研究的热点论题,相同的β多样性格局可能由不同的生态过程所决定。该文通过构建零假说模型和典范变异分解的方法,比较了黄土高原油松人工林(Form. Pinus tabulaeformis)和辽东栎天然林(Form. Quercus wutaishanica)林下植物群落β多样性,确定了环境过滤和扩散限制在β多样性形成过程中的相对重要性。结果表明:(1)油松人工林和辽东栎天然林的林下群落均具有相似的β多样性大小,均呈现明显的种内聚集过程。(2)环境和空间共同解释了两种林型林下物种组成的较大变化(草本层[E+S]为33%~45%; 灌木层[E+S]为21%~35%),且主要以环境解释量为主(包括纯环境变量[E | S]和空间化的环境变量[E ∩ S])。(3)油松人工林和辽东栎天然林林下群落β多样性形成的不同过程主要体现在生境异质性差异以及特定的环境因子间,例如,海拔梯度、枯落物厚度以及土壤养分(速效氮和速效钾)是引起两种林型林下物种差异的显著环境因子。综上结果认为,黄土高原的油松人工林和辽东栎天然林的群落构建均由确定性的环境过滤为主导,但两种林型的环境过滤过程并不一样,主要表现为生境异质性的差异和不同的环境限制因子。对于黄土高原区域生态环境建设,首先应该保证不同群落的生境异质性,同时不能忽视扩散限制及其与生境异质性二者交互作用对β多样性的影响。
关键词:  生境异质性, 扩散限制, 人工林, 种内聚集, 典范变异分解
DOI:10.11931/guihaia.gxzw201911027
分类号:Q948.15
文章编号:1000-3142(2021)03-0362-10
基金项目:贵州省自然科学基金(黔科合基础[2019]1060); 贵州省教育厅青年科技人才成长项目(黔教合KY字[2018] 098); 贵州大学引进人才科研项目(贵大人基合字[2017]38号); 青海师范大学中青年科研基金(2019zr011)[Supported by Natural Science Foundation of Guizhou Province([2019]1060); Youth Science and Technology Talent Growth Program of Guizhou Provincial Department of Education([2018]098); Program of Introducing Talents of Discipline to Guizhou University([2017]38); Youth Foundation of Qinghai Normal University(2019zr011)]。
Understory β diversity differences and influential factors between Pinus tabulaeformis plantation and natural Quercus wutaishanica forest on the Loess Plateau
WANG Shixiong1,2,3*, XIA Tingting2, WANG Xiaoan3
1. College of Life Sciences, Academy of Plateau Science and Sustainability, Qinghai Normal University, Xining 810008, China; 2. College of Forestry, Guizhou University, Guiyang 550025, China; 3. College of Life Sciences, Shaanxi Normal University, Xi'an 710119, China
Abstract:
Beta diversity is a hot topic in ecology, and the same patterns of β diversity may be determined by different ecological processes. Null model and canonical variation partitioning methods were used to determine the relative importance between environmental filter and dispersal limitation on community assembly between Pinus tabulaeformis plantation and natural Quercus wutaishanica forest. The results were as follows:(1)The understory communities of Pinus tabulaeformis plantation and natural Quercus wutaishanica forest had similar β diversities and similar β deviations with strong intraspecific aggregations of most species.(2)Environmental and spatial variables jointly explained the great variation of species composition of understory plant community in the two forest types(Herb layer: [E + S] was 33%-45%; Shrub layer: [E + S] was 21%-35%), and dominated by the environmental explanations(including pure environmental variables [E | S] and spatial environmental variables [E ∩ S]).(3)Although Pinus tabulaeformis plantation and natural Quercus wutaishanica forest on the Loess Plateau were both dominated by environmental filter, β diversities in both forests reflected dissimilar mechanisms of community assembly. It was mainly reflected in the differences of habitat heterogeneity and specific environmental factors between these two forests. Such as, altitude, litter depth and soil nutrients(available nitrogen and available potassium)were significant environmental factors that caused species differentiation between the two forest types. Therefore, it suggests that even if the same environmental filter process, it is necessary to compare the differences of regional environmental heterogeneity and further analyze the differences of the specific environmental factors that cause environmental filter. To restore species diversity effectively on the Loess Plateau, habitat heterogeneity is an important guarantee. At the same time, dispersal limitation caused by geographical distance should not be neglected, and special attention should be paid to interaction between dispersal limitation and habitat heterogeneity on β diversity.
Key words:  habitat heterogeneity, dispersal limitation, plantation forest, intraspecific aggregation, canonical variation partitioning
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