植酸改性生物质炭通过调控pH和团聚体结构降低土壤Cd释放
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中国林业科学研究院亚热带林业研究所

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国家自然科学基金项目(32071736,32101370)资助


Phytic Acid-modified Biochar Reduces Soil Cd Release by Regulating pH and Aggregates Structure
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Research Institute of Subtropical Forestry, Chinese Academy of Forestry

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Supported by the National Natural Science Foundation of China (Nos. 32071736 and 32101370)

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    摘要:

    植酸改性生物质炭对水溶液中镉(Cd)具有良好的吸附性能,但其对重度Cd污染土壤的修复效果和影响机制尚不清楚。通过180 d的土壤培养试验,系统评估了竹质生物质炭(BBC)、植酸改性竹炭(PABC)和植酸钠改性竹炭(SPBC)在Cd污染土壤中的动态修复过程。结果表明,在前期和中期(0~120 d),3种生物质炭显著降低了土壤溶液中的Cd浓度(降幅为24.60%~99.35%),并表现出明显的剂量效应,植酸改性生物质炭尤其是SPBC效果最佳。除自身的吸附机制外,生物质炭还通过影响土壤和土壤溶液的化学(pH、全磷、全碳)、物理(团聚体结构)和生物性质(脲酶、酸性磷酸酶)间接抑制Cd释放,其中,土壤pH和微团聚体含量是影响Cd释放的关键因子。后期(120~180 d),土壤团聚体稳定性增强,生物质炭通过提高脲酶和酸性磷酸酶活性进一步促进该过程。植酸改性生物质炭对重度Cd污染土壤具有较强的修复及土壤改良潜力,具有较大的应用价值。

    Abstract:

    【Objective】Phytic acid-modified biochar exhibits excellent adsorption capacity for cadmium (Cd) in aqueous solution; However, its effectiveness and mechanisms in remediating Cd-contaminated soils remain unclear. This study systematically analyzes the dynamic impact of phytic acid-modified biochar on soil properties, investigates its effect on Cd release in soil, and reveals the key mechanisms underlying biochar regulation of Cd movement in soil. 【Method】 Soil incubation experiments were conducted to systematically evaluate the remediation and amelioration effects of bamboo biochar (BBC), phytic acid-modified bamboo biochar (PABC), and sodium phytate-modified bamboo biochar (SPBC) on Cd-contaminated soils over various incubation periods (0, 10, 20, 60, 120, and 180 days). 【Result】The addition of biochar significantly altered the pH of both soil and soil solution and increased the electrical conductivity (EC). SPBC exhibited the highest EC and total carbon concentration in the soil solution, while PABC showed a distinct advantage in supplying total phosphorus, particularly in the short term. During the early and mid-phases (0-120 days), biochar treatment significantly reduced the Cd concentration in soil solution (24.60%-99.35%), with a significant dose-response effect, and SPBC exhibited the most effective remediation. In addition to their inherent adsorption mechanisms, biochar also inhibited Cd release indirectly by affecting the chemical (pH, total phosphorus, and total carbon), physical (aggregate structure), and biological properties (urease and acid phosphatase) of the soil and soil solution, with soil pH and micro-aggregate content identified as key factors influencing Cd release. In the later phase (120-180 days), enhanced soil aggregate stability further facilitated the remediation process, as biochar increased the activity of urease and acid phosphatase. 【Conclusion】 Phytic acid-modified biochar demonstrates strong potential for both Cd remediation and soil improvement in heavily contaminated soils, offering significant application value.

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邸东柳,肖江,盖旭,李璞君,陈光才.植酸改性生物质炭通过调控pH和团聚体结构降低土壤Cd释放[J].土壤学报,DOI:10.11766/trxb202507010321,[待发表]
DI Dongliu, XIAO Jiang, GAI Xu, LI Pujun, CHEN Guangcai. Phytic Acid-modified Biochar Reduces Soil Cd Release by Regulating pH and Aggregates Structure[J]. Acta Pedologica Sinica, DOI:10.11766/trxb202507010321,[In Press]

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  • 收稿日期:2025-07-01
  • 最后修改日期:2025-10-14
  • 录用日期:2025-10-27
  • 在线发布日期: 2025-11-03
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