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    鄂尔多斯矿区排土场苜蓿恢复地土壤种子库的演变特征

    Evolution characteristics of soil seed bank during Medicago sativa restoration in the dump of a mining area in Ordos, China

    • 摘要: 苜蓿种植模式在鄂尔多斯矿区排土场生态重建与土地复垦方面具有众多优势, 为掌握其恢复效益及时效性, 以排土场种植年限分别为2年、4年、6年和10年的苜蓿种植地为研究对象(分别表示为M2、M4、M6、M10), 采用空间代替时间法, 研究苜蓿恢复过程中土壤种子库的变化特征。结果表明:苜蓿恢复过程中土壤种子库共8种植物, 分属禾本科、菊科、藜科、豆科4科8属, 以豆科和一年生植物为主; 土壤种子库的物种多样性、丰富度和均匀度指数均表现为M4阶段最优; 土壤种子库密度变化在459.68~3 900.72粒/m2, 在M4阶段显著高于在M10阶段; 不同苜蓿种植年限间土壤种子库相似性系数较高, 在0.44~0.80之间。研究区排土场苜蓿恢复模式下具有一定规模的土壤种子库, 可为植被恢复提供种源, 但物种较贫乏。苜蓿恢复4年后, 群落开始发生衰退, 可考虑通过人工引进区域稳定生态系统优势种种子, 增加群落多样性与稳定性; 亦可考虑进行更新、改造及利用, 确保排土场恢复生态系统的效益与可持续性。

       

      Abstract:
      Background Mine waste and soil-like materials lack nutrients such as nitrogen and phosphorus, while Medicago sativa as a leguminous plant, has strong nitrogen-fixing characteristics, and its root tumors can fix more nitrogen and carbon. Its rhizomes, leaf residues, and root secretions are released into the soil with many organic substances, and they can be used as green fertilizers for flip pressure and decomposition, and have a good fertilization effect and improve soil microbial properties, thereby improving soil quality.
      Methods To master its restoration efficiency and timeliness, M. sativa sites with different plantation ages, respectively, for 2 years, 4 years, 6 years and 10 years in Ordos Wujiata dump were selected as the research objects (respectively expressed as for M2, M4, M6, and M10). Replacing time with space was used to study the changing characteristics of soil seed bank during alfalfa restoration.
      Results There were 8 species plants in the soil seed bank during the recovery of M. sativa, which were mainly leguminous and annual plants, belonging to 8 genera and 4 families of Gramineae, Compositae, Chenopodiaceae and Leguminosae. The index of species diversity, richness and evenness in the soil seed bank were the best in the M4 stage. The density of soil seed bank changed at 459.68-3 900.72 seeds/m2, which was significantly higher in M4 stage than in M10 stage. The similarity coefficient of soil seed bank between different planting years of M. sativa was between 0.44-0.80. Under the M. sativa restoration mode of dumping site, there was a certain scale of soil seed bank, which provided seed source for vegetation restoration. However, the species was relatively poor, thus it increased the community diversity and stability by artificially introducing the dominant seeds of regional stable ecosystem. With the increase of the recovery period, the ecological characteristics of the soil seed bank were reduced. It is possible to consider introducing artificially dominant seeds of regionally stable ecosystems to increase the diversity and stability of the community. Renewal, transformation, and utilization may also be considered to ensure the efficiency and sustainability of the restoration of ecological systems at the dump.
      Conclusions Under the condition of no intensive operation and management in the study area, combined with field observation and investigation, the community restoration and soil improvement benefits are better when the planting of M. sativa is restored at 4 years, its community restoration and soil improvement benefits are both good, and it can be considered for reclamation and utilization, or it can be renewed or artificially introduced in time before it declines, which is conducive to ensuring the ecological restoration benefits of the mining area and land reclamation.

       

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