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    金沙江干热河谷植物α多样性和群落谱系结构对环境因子的响应

    The response of plant alpha diversity and community lineage structure in the dry-hot valley of the Jinsha River to environmental factors

    • 摘要:
      目的 探究干热河谷植物物种α多样性和谱系结构的海拔梯度格局,定量识别与分析驱动植被垂直分布的关键环境因子,以期为中国干热河谷区的植被研究理论创新与生态环境保护恢复提供重要参考。
      方法 在金沙江永仁段干热河谷典型地区石坎子大箐流域沿着1 200 ~ 1 800 m设置7条垂直海拔梯度样带,通过典型样地的植物群落、生境调查,结合云南永仁自然资源要素综合观测研究站气象等长期定位观测数据,从物种组成、群落α多样性和谱系结构3个维度来揭示干热河谷区植物多样性的海拔分布格局,并通过相关性分析和冗余分析进一步探究植物多样性和谱系结构对气候、地形、土壤等因子的响应机制。
      结果 (1)样地植物物种共有34种,分属于23科33属,禾本科和豆科在研究区植物分布中占有重要地位,且在各海拔梯度的分布中均扮演重要角色。(2)群落总盖度、灌木层盖度和 海拔呈正相关关系,草本层盖度则呈相反趋势。这表明低海拔以耐旱草本为主,海拔升高改善了生境,灌木占比提升。(3)物种丰富度指数、Shannon-Wiener物种多样性指数、Simpson生态优势度指数和Pielou群落均匀度指数随着海拔梯度的增加均呈现先增加后减小的趋势,整体呈“中峰模式”,各指数均在1 500 ~ 1 700 m处出现峰值,中海拔生境最优,物种多样性最高。(4)净种间亲缘关系指数NRI在海拔1 200 ~ 1 700 m范围内均为正值,1 800 m处为负值,表明随着海拔的升高群落谱系结构呈先聚集后发散的趋势,影响主导因素由生境过滤变成种间的竞争排斥作用。(5)气温年较差作为主导因子,对α物种多样性和谱系结构的解释度为21.3%;另外,土壤pH、土壤厚度也是影响α物种多样性和谱系结构的重要因子。
      结论 干热河谷区植被整体稀少,木本植物中的豆科物种在各海拔段均广泛分布,可作为干热河谷植被恢复的先锋树种。谱系结构在低海拔的干热河谷区聚集,表明干热河谷植被群落的构建受生境过滤的控制,建议积极关注气温年较差、土壤pH和土壤厚度等关键因子变化,以服务于金沙江干热河谷区植被恢复。

       

      Abstract:
      Objective To explore the spatial pattern changes of plant species alpha diversity and lineage structure in dry-hot river valleys at altitude gradients, quantitatively identify and analyze the key environmental factors driving the vertical distribution of vegetation, with the aim of providing important references for theoretical innovation in vegetation research and ecological environment protection and restoration in dry-hot river valleys in China.
      Method Seven vertical altitude gradient sample zones were set up along 1 200 to 1 800 meters in the typical dry-hot river valley area of Shikanzi Daqing in the Yongren section of the Jinsha River. Through the investigation of plant communities and habitats in the typical sample plots, combined with long-term positioning observation data such as meteorology from the Yongren Comprehensive Observation and Research Station of Natural Resources Elements in Yunnan Province, this study investigated the altitudinal distribution patterns of plant diversity in the dry-hot valley from three perspectives: species composition, community α-diversity, and phylogenetic structure. Furthermore, correlation analysis and redundancy analysis were employed to explore the response mechanisms of plant diversity and phylogenetic structure to climatic, topographic, and soil factors.
      Result (1) There were a total of 34 plant species in the sample plot, belonging to 23 families and 33 genera. The Poaceae and leguminous families occupied an important position in the plant distribution of the study area and were significant across all altitude gradients.(2) The total community coverage, shrub layer coverage and altitude were positively correlated, while the herb layer coverage showed the opposite trend. This indicated that drought-tolerant herbs were dominant at low altitudes, while at higher altitudes, the habitat improved and the proportion of shrubs increased. (3) The species richness index, Shannon-Wiener species diversity index, Simpson ecological dominance index and Pielou community evenness index all showed a trend of increasing first and then decreasing with the increase of the altitude gradient. Overall, they presented a “mid-peak model”, with peaks appearing at 1 500-1 700 m for each index. The mid-altitude habitat was the best and had the highest diversity. (4) The net relatedness index (NRI) was positive in the altitude range of 1 200- 1 700 m and negative at 1 800 m, indicating that the community phylogenetic structure showed a trend of aggregation and divergence with the increase of altitude. Accordingly, the dominant driving force shifts from habitat filtering to interspecific competitive exclusion. (5) The annual temperature range was the dominant factor, explaining 21.3% of the α species diversity and phylogenetic structure. In addition, soil pH and soil thickness were also important factors affecting α species diversity and phylogenetic structure.
      Conclusion The vegetation in the dry-hot valley area is generally scarce. Among them, leguminous species in woody plants are widely distributed at all altitudes and can be used as pioneer tree species for the restoration of dry-hot valley vegetation. The phylogenetic structure is aggregated in the low-altitude dry-hot valley area, indicating that the construction of dry-hot valley vegetation communities is controlled by habitat filtering. It is recommended to pay close attention to the changes of key factors such as the annual temperature range, soil pH and soil thickness to serve the restoration of vegetation in the dry-hot valley area of the Jinsha River.
      Conclusion Vegetation in the dry-hot valley area is generally scarce. Among them, leguminous species of woody plants are widely distributed at all altitudes and can be used as pioneer tree species for the restoration of dry-hot valley vegetation. The phylogenetic structure is aggregated in the low-altitude dry-hot valley area, indicating that the construction of dry-hot valley vegetation communities is controlled by habitat filtering. It is suggested to pay close attention to the changes of key factors such as the annual temperature range, soil pH and soil thickness to serve the restoration of vegetation in the dry-hot valley area of the Jinsha River.

       

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