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    宁夏输变电塔基植被恢复区土壤微生物残体碳累积及其对有机碳的贡献

    Soil microbial necromass carbon accumulation and its contribution to organic carbon in vegetation restoration area of power transmission and transformation tower in Ningxia

    • 摘要: 输电线路工程塔基架设会严重破坏周围植被和土壤,造成土壤肥力下降。在该区域进行植被恢复是改善区域生态环境的重要措施。探究土壤微生物残体碳累积情况,可有效评估塔基处的植被恢复生态效益。设置塔基建设干扰后的植被恢复区、干扰后未进行植被恢复的裸地区域以及未被干扰的区域3种样地,采用生物标志物法,测定植被恢复区域土壤氨基糖质量分数,计算微生物残体碳对有机碳的贡献,并分析微生物残体碳质量分数与土壤理化性质和微生物量的关系。结果表明:1)塔基处植被恢复后,土壤微生物残体碳质量分数(11.2 ± 0.1 mg/g)显著高于干扰区域土壤(3.9 ± 0.6 mg/g),并恢复到未干扰土壤水平(8.84 ± 1.3 mg/g)。2)微生物残体碳对土壤有机碳库的贡献从21.9%恢复到50.8%,甚至高于未干扰土壤水平30.0%。3)土壤微生物残体碳主要由真菌贡献,真菌残体碳对土壤有机碳贡献的范围为18.3%~29.8%,细菌残体碳的贡献范围为13.6%~20.9%。4)土壤性质和微生物量共同解释微生物残体碳质量分数的48.3%。其中,土壤性质解释35.5%,微生物量解释变异的27.4%。Mantel分析显示,土壤碳氮质量分数和微生物量碳与微生物残体碳质量分数呈显著正相关关系。本结果揭示植被恢复对塔基干扰土壤有机碳质量分数及其稳定性具有重要作用。

       

      Abstract:
      Background The construction of transmission towers in arid ecosystems has significantly disrupted ecological balance, triggering soil fertility degradation through altered microbial-mediated nutrient cycling. While vegetation restoration serves as a critical intervention for combating desertification and modulating soil microbial communities, its long-term impacts on microbial necromass carbon, a key determinant of soil organic carbon (SOC) persistence and ecosystem stability, remain poorly quantified.
      Methods This study was carried out in the anthropogenic disturbance zone of the power transmission infrastructure within the Mu Us Sandy Land ecosystem. Standardized field sampling protocols coupled with gas chromatography-mass spectrometry (GC-MS) analytical techniques were implemented to evaluate the effects of engineered vegetation restoration on soil carbon. We employed amino sugar biomarkers to analyze microbial necromass dynamics in revegetated soils. By quantitative assessment of microbial residue carbon contributions to SOC, we established relationships between necromass carbon, soil properties, and microbial biomass using variance partitioning and Mantel tests.
      Results 1) The results indicated that the microbial necromass carbon content (11.2 ± 0.1 mg/g) in vegetation restoration soil was significantly higher than that in disturbed soil (3.9 ± 0.6 mg/g), and restored to the level of undisturbed soil (8.84 ± 1.3 mg/g). 2) The contribution of microbial necromass carbon to soil organic carbon recovered from (21.9%± 3.1%) to (50.8% ± 4.0%), even higher than the undisturbed soil level of (30.0% ± 5.2%). 3) Soil microbial necromass carbon was mainly contributed by fungi, and the contribution of fungal residue carbon to soil organic carbon ranged from 18.3% to 29.8%, and that of bacterial residue carbon ranged from 13.6% to 20.9%. 4) The variance decomposition results showed that soil properties and microbial biomass jointly explained 48.3% of the variation in microbial necromass carbon content, in which soil properties explained 35.5% of the variation and microbial biomass explained 27.4% of the variation. Mantel analysis further showed that soil carbon and nitrogen content and microbial biomass carbon were significantly positively correlated with microbial necromass carbon content.
      Conclusions Our findings demonstrate that vegetation restoration not only rehabilitates SOC pools but critically enhances their stability through fungal-dominated microbial necromass accumulation. This mechanistic understanding advances restoration strategies for arid land recovery by highlighting microbial-derived carbon as a fundamental indicator of soil health resilience.

       

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