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草业学报 ›› 2009, Vol. 18 ›› Issue (4): 27-34.

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不同草灌配比对泌桐高速公路护坡植物群落特征的影响

张相锋1,马闯2*,董世魁1,张文辉2,刘新成2   

  1. 1.北京师范大学环境学院 环境模拟与污染控制国家重点联合实验室,北京 100875;
    2.天津师范大学化学与生命科学学院,天津 300387
  • 收稿日期:2008-09-02 出版日期:2009-08-20 发布日期:2009-08-20
  • 作者简介:张相锋(1973-),男,河南南阳人,博士。E-mail: zhangxf@bnu.edu.cn
  • 基金资助:
    国家863项目(2007AA063Z350)资助。

Influence of different ratios of herbage and shrubs on plant community characteristics for roadside deforestation and soil protection on the Bi-Tong Expressway

ZHANG Xiang-feng1, MA Chuang2, DONG Shi-kui1, ZHANG Wen-hui2, LIU Xin-cheng2   

  1. 1.School of Environment, Beijing Normal University, State Key Joint Laboratory of Environmental
    Simulation and Pollution Control, Beijing 100875, China; 2.College of Chemistry and
    Life Sciences, Tianjin Normal University, Tianjin 300387, China
  • Received:2008-09-02 Online:2009-08-20 Published:2009-08-20

摘要: 通过在泌桐高速公路典型边坡分别建立自然恢复样地、单一狗牙根播种样地和5个不同播种密度的草灌混播样地,调查统计植物种类分布和植物功能群类型,研究播种密度对群落的数量特点和多样性指标的影响,对不同样地之间进行相似性分析,结果表明,1)样地植物豆科、禾本科、菊科的植物所占比例较大,根据优势种变化,随着播种密度的增加,将草灌混播样地划分为:狗牙根草地(300~400株/m2)、狗牙根与紫花苜蓿共生草地(500~600株/m2)和紫花苜蓿草地(700株/m2);2)群落密度、盖度、高度和生物量均随着草本播种密度的增加表现为先减小后增加,并在草本播种密度700株/m2样地处达到最大;3)群落的物种丰富度、多样性指数以及均匀度指数,随着播种密度的增加呈单峰形变化,在草本播种密度500株/m2样地达到最大;4)随着播种密度增加,不同样地与自然恢复样地(BL)的相似性指数呈先下降后增加的趋势,决定群落差异的因素是人工播种组成成分,而与播种密度无关;5)草本播种密度大于500株/m2时,播种密度对群落高度、盖度、生物量以及多样性指数的变化影响无差异。选择合适的草种配比和合理的播种密度,可以节约成本,实现最佳的边坡恢复效果。

Abstract: The species composition, plant functional groups, community characteristics, and diversity index were investigated through building natural restoration. The Cynodon dactylon community and five kinds of mixture-planting plots of shrub and herbage on the Bi-Tong Expressway typical slope, and species similarity between different plots was analyzed. Plants of Leguminosae, Gramineae and Compositae occupied a fairly large proportion and played important roles in the reforestation plots. The mixture-planting plots of shrub and herbage could be divided into three patterns based on the change of dominate species. C. dactylon grassland (300-400 plants/m2), intergrowth land with C. dactylon and Medicago sativa(500-600 plants/m2), and M. sativa grassland (700 plants/m2). The density, coverage, height and biomass of reforestation communities tended to decrease and then increase as the density of herbage became higher. The maximum value was 700 plants/m2. The species richness (Margalef index),plant diversity (Shannon-Wiener index), and Pielou evenness index tended to increase, to a density of 500 plants/m2 then decrease. As the density of herbage became higher, species similarity between different plots and natural restoration tended to decrease and then increase, indicating that the composition of artificial restoration, not the herbage density, decided the community composition. The density had no serious effect on coverage, height, biomass and diversity of reforestation communities when the density was over 500 plants/m2. The cost should be reduced and the optimum effect of restoration achieved by choosing the appropriate proportion of species and density.

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