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林业科学 ›› 2017, Vol. 53 ›› Issue (10): 13-21.doi: 10.11707/j.1001-7488.20171002

• 论文与研究报告 • 上一篇    下一篇

基于林层的典型中亚热带天然阔叶林树种组成与多样性

马志波1, 黄清麟1, 庄崇洋1, 郑群瑞2, 王宏1   

  1. 1. 中国林业科学研究院资源信息研究所 国家林业局林业遥感与信息技术重点实验室 北京 100091;
    2. 建瓯万木林省级自然保护区管理处 建瓯 353105
  • 收稿日期:2017-03-27 修回日期:2017-09-13 出版日期:2017-10-25 发布日期:2017-11-29
  • 基金资助:
    国家自然基金科学项目"中亚热带天然阔叶林林层特征研究"(31370633)。

Species Composition and Diversity of Typical Natural Broad-Leaved Forest in Central Subtropical:Based on Arbor Layer Stratification

Ma Zhibo1, Huang Qinglin1, Zhuang Chongyang1, Zheng Qunrui2, Wang Hong1   

  1. 1. Key Laboratory of Forestry Remote Sensing and Information Technology, State Forestry Administration Research Institute of Forest Resource Information Techniques, Chinese Academy of Forestry Beijing 100091;
    2. Administrative Office of Wanmulin Provincial Nature Reserve Jian'ou 353105
  • Received:2017-03-27 Revised:2017-09-13 Online:2017-10-25 Published:2017-11-29

摘要: [目的]分析各林层物种组成及多样性,探讨各林层之间的联系和群落结构的形成机制,以期为深入了解典型森林群落组成成分在垂直空间中的分布规律、揭示生物多样性维持机制提供依据。[方法]在福建万木林自然保护区内设5块50 m×50 m标准地,使用最大受光面法自上而下将乔木层划分为第Ⅰ,Ⅱ和Ⅲ亚层,第I,Ⅱ亚层属于受光层,第Ⅲ亚层为非受光层,采用常见物种多样性指标分析各层的组成与多样性,用相似性系数探讨各层之间的联系。[结果]5块标准地均表现为由第Ⅰ亚层降至第Ⅲ亚层物种丰富度和多样性增加;各样地相同亚层的物种组成及数量各不相同;调查到的所有树种中,有35个树种可生长到第Ⅰ亚层,最大树高为30~40 m,但是各样地累计只有10个树种在乔木层的3个亚层连续分布,有20个树种(含4种灌木)能生长到第Ⅱ亚层,最大树高约为25 m,有30个树种(含13种灌木)只能分布在第Ⅲ亚层,最大树高为16~17 m;受光层内的树种是乔木层的优势种和重要伴生树种,包括常绿树种木荷、浙江桂、香樟、刨花楠、观光木、福建含笑、乐东拟单性木兰和栲类等,也包括落叶树种枫香、拟赤杨、蓝果树和苦枥木;最大高度限于非受光层即第Ⅲ亚层的常绿树种有野含笑、水丝梨、椤木石楠、虎皮楠和厚皮香,落叶树种有合欢、野柿和南岭黄檀;标准地内的大部分灌木树种只分布在第Ⅲ亚层,但山矾、黄瑞木、弯蒴杜鹃和尖叶水丝梨除外,它们也可生长到第Ⅱ亚层;第Ⅰ和第Ⅱ亚层的物种组成相似性大于第Ⅰ和第Ⅲ亚层及第Ⅰ和整个乔木层的相似性;第Ⅰ亚层树种的更新储备主要分布于第Ⅱ亚层;受光层的树种丰富度与多样性和非受光层有明显差异,二者的分界面也是空间生态位分化最显著的界面,而该界面正是最大受光面。[结论]5块标准地乔木层内的优势种和重要伴生树种主要分布在受光层;生态位分化最显著的位置是最大受光面,按最大受光面划分出的受光层和非受光层,在组成种的丰富性和多样性方面也具有明显的差别,受光层和非受光层分化对近自然经营中目标树的选择具有潜在的指导意义;可生长到最高层的树种中,只有个别树种可在3个亚层连续分布,暗示受光层中的优势树种是不固定的,说明除了生态位分化,群落物种组成与丰富度还受随机因素影响。

关键词: 天然常绿阔叶林, 中亚热带, 乔木层, 成层性, 相似性

Abstract: [Objective]The study was to determine the species composition and diversity of different forest layers and to determine how vertical distribution of trees affect the community structure and its underlying mechanisms with the view of arbor layer's stratification.[Method]Five 50 m×50 m sample plots were investigated in Wanmulin Provincial Nature Reserve, Fujian Province. With maximum light receiving plane (MLRP) method, arbor layer of each plots were divided into three sub-layers from top to bottom, the sub-layer I, Ⅱ and Ⅲ. The sub-layer I and Ⅱ belonged to light receiving layer (LRL), the sub-layer Ⅲ was non-light receiving layer (NLRL). Then the species composition and diversity of each sub-layer were studied using importance value, diversity index and similarity index.[Result]The species richness and diversity increased when the arbor layer decreased from sub-layer I to sub-layer Ⅲ of the five plots. The composition and number of species varied in the same sub-layers of different plots. The maximum tree height of 35 tree species can reach about 30 m even 40 m and they have the potential to distribute at top layer of the community, i.e. sub-layer I, but there were only 10 tree species could successive distribute at all the three sub-layers among all species of all plots. The maximum height of 16 tree species and 4 shrub species was about 25 m and sub-layer Ⅱ was the limit of what they could reach. The maximum height of 17 tree species and 13 shrub species was 16-17 m and sub-layer Ⅲ was the limit of what they could reach. Tree species in LRL were dominant species and important associated species of arbor layer, including evergreen trees Schima superba, Cinnamomum chekiangense, C. camphora, Machilus pauhoi, Tsoongiodendron odorum, Michelia fujianensis, Parakmeria lotungensis and some trees species of Castanopsis, and Liquidambar formosana, Alniphyllum fortunei, Nyssa sinensis and Fraxinus insularis. Tree species only distributed in NLRL included evergreen trees M. skinneriana, Sycopsis sinensis, Photinia davidsoniae, Daphniphyllum oldhami, Ternstroemia gymnanthera, and deciduous trees Albizia julibrissin, Diospyros kaki var. silvestris and Dalbergia balansae. Most shrubs species could only distribute in NLRL except Symplocos sumuntia, Adinandra millettii, Rhododendron henryi and S. dunnii could reach to sub-layer. Priority should be given to dominant species of sub-layer I when determining dominant species of the community, because their basal areas were obviously bigger than trees of other sub-layers. The similarity of sub-layer I and Ⅱ was bigger than that of sub-layer I and Ⅲ or sub-layer I and arbor layer. The differentiation was prominent at the critical plane LRL and NLRL when the similarity was the degree of differentiation and the arbor layer was the reference, suggesting spatial niche separation being prominent at MLRP.[Conclusion]In the five sample plots, dominant species and important associated tree species of arbor layer were mainly distributed in the LRL. Niche differentiation was prominent at MLRP. There were obvious difference between LRL and NLRL in species richness and diversity, which were identified according to MLRP. The differentiation of the LRL and the NLRL has potential practical significance for the selection of target trees in close-to-nature management so that the relationship between the two should be further studied in the future. Very few tree species could distribute in 3 successive sub-layers of each plots among all tree species that could grow to sub-layer I, suggesting that there were almost no particular species could be permanent dominant species in the LRL and species composition and richness in the 5 plots appeared to be caused also by random species replacement, which needs to be further studied in future.

Key words: natural evergreen broad-leaved forest, mid-subtropical zone, arbor layer, stratification, similarity

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