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呼伦贝尔沙化草地不同生态修复阶段植物群落特征研究

郝颢晶 关潇 曹明 李俊生

郝颢晶,关潇,曹明,等.呼伦贝尔沙化草地不同生态修复阶段植物群落特征研究[J].环境工程技术学报,2023,13(4):1573-1585 doi: 10.12153/j.issn.1674-991X.20220877
引用本文: 郝颢晶,关潇,曹明,等.呼伦贝尔沙化草地不同生态修复阶段植物群落特征研究[J].环境工程技术学报,2023,13(4):1573-1585 doi: 10.12153/j.issn.1674-991X.20220877
HAO H J,GUAN X,Cao M,et al.Study on the characteristics of plant communities in different ecological restoration stages of Hulun Buir sandy grassland[J].Journal of Environmental Engineering Technology,2023,13(4):1573-1585 doi: 10.12153/j.issn.1674-991X.20220877
Citation: HAO H J,GUAN X,Cao M,et al.Study on the characteristics of plant communities in different ecological restoration stages of Hulun Buir sandy grassland[J].Journal of Environmental Engineering Technology,2023,13(4):1573-1585 doi: 10.12153/j.issn.1674-991X.20220877

呼伦贝尔沙化草地不同生态修复阶段植物群落特征研究

doi: 10.12153/j.issn.1674-991X.20220877
基金项目: 国家自然科学基金项目(41807109);第二次青藏高原综合科学考察研究项目
详细信息
    作者简介:

    郝颢晶(1998—),女,硕士研究生,主要从事沙地植被修复研究,whwh20@126.com

    通讯作者:

    李俊生(1968—),男,研究员,博士,主要从事生物多样性研究,lijunsheng@cgs.gov.cn

  • 中图分类号: X83

Study on the characteristics of plant communities in different ecological restoration stages of Hulun Buir sandy grassland

  • 摘要:

    人工植被修复是减缓草地沙化与生态重建的重要措施,理解不同修复阶段的沙地植物群落演替特征及其影响因素有利于沙地植被的持续修复。以呼伦贝尔市甘珠尔沙地植被修复为例,分别调查了修复9、11、13、15 a共4个不同修复阶段植物群落结构特征及土壤理化性质,探索甘珠尔沙地人工修复植物群落演替变化及其对环境因子的响应。结果表明:研究区共发现植物42种,隶属于17科35属。草本39种,以菊科、禾本科、蔷薇科和豆科为主;灌木3种,为豆科和菊科。不同修复年限物种数变化依次表现为28种(15 a)、25种(13 a)、19种(9 a)和16种(11 a)。各年限内多年生草本物种数均明显高于一年生和一/二年生植物。草本与灌木在不同修复阶段其优势种、地上生物量及物种多样性均存在波动变化,具体表现为草本植物中地梢瓜(Cynanchum thesioides)、虫实(Corispermum hyssopifolium)、披碱草(Elymus dahuricus)、糙隐子草(Cleistogenes squarrosa)、羊草(Leymus chinensis)与狗尾草(Setaria viridis)的优势度较高,灌木以小叶锦鸡儿(Caragana microphylla)为主要优势种。草本植物地上生物量和总盖度整体呈现波动增加的趋势但差异不显著。灌木总盖度15 a显著高于9 a,地上生物量整体呈现逐渐增加的趋势,表现为11、13、15 a均显著高于9 a。不同修复阶段的物种多样性指数在草本中无显著差异,但在灌木层表现为15 a显著高于9 a。随机森林模型表明,沙化草地的修复过程中气候及土壤因子对植物群落结构特征贡献度存在差异。土壤总氮含量、总钾含量、有机质含量、年降水量和年均风速是影响甘珠尔沙地草本植物多样性的主导因子,其中除年均风速外均为正相关。因此,建议在沙地植被修复中适当增加含氮、钾、有机质等营养物质的肥料,促进沙化生态系统的植物群落结构重建与多样性的恢复。

     

  • 图  1  研究区采样点示意

    Figure  1.  Location map of the study area and sampling points

    图  2  不同修复年限研究区草本植物重要值雷达图

    Figure  2.  Radar map of important values of herbaceous plants in the study area with different recovery years

    图  3  不同修复年限研究区灌木植物重要值雷达图

    Figure  3.  Radar map of important values of shrub plants in the study area with different recovery years

    图  4  甘珠尔沙地不同修复年限植被盖度、地上生物量比较

    注:不同小写字母表示组间差异显著(P<0.05),全文同。

    Figure  4.  Comparison of vegetation coverage and aboveground biomass in different restoration years in Ganzhuer sandy land

    图  5  甘珠尔沙地不同修复年限植被多样性指数比较

    Figure  5.  Comparison of diversity index of different restoration years in Ganzhuer sandy land

    图  6  环境因子与草本植物多样性指数随机森林模型重要性排序

    注:R2为全部变量对多样性指数解释的方差的百分比;MSE为均方误差;因子的重要性由均方误差增加率表示;*、**分别表示在0.05、0.01水平下差异显著。

    Figure  6.  Importance ranking chart of random forest model of environmental factors and herb diversity index

    图  7  环境因子与草本植物多样性指数部分依赖图

    Figure  7.  Partial dependence of environmental factors on herb diversity index

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  • 收稿日期:  2022-09-01
  • 录用日期:  2023-04-21
  • 修回日期:  2022-10-31
  • 网络出版日期:  2023-05-15

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