汤子衿, 祝明亮, 罗浩祥, 刘敏, 丁园. 钙铁磷材料对Cd、Cu污染土壤的协同钝化及抗逆机制[J]. 南昌航空大学学报(自然科学版), 2025, 39(5): 72-78, 86. DOI: 10.3969/j.issn.2096-8566.2025.05.009
引用本文: 汤子衿, 祝明亮, 罗浩祥, 刘敏, 丁园. 钙铁磷材料对Cd、Cu污染土壤的协同钝化及抗逆机制[J]. 南昌航空大学学报(自然科学版), 2025, 39(5): 72-78, 86. DOI: 10.3969/j.issn.2096-8566.2025.05.009
Zijin TANG, Mingliang ZHU, Haoxiang LUO, Min LIU, Yuan DING. Synergistic Passivation and Resistance Mechanism of Calcium-iron-phosphorus Materials on Cd and Cu Contaminated Soil[J]. Journal of nanchang hangkong university(Natural science edition), 2025, 39(5): 72-78, 86. DOI: 10.3969/j.issn.2096-8566.2025.05.009
Citation: Zijin TANG, Mingliang ZHU, Haoxiang LUO, Min LIU, Yuan DING. Synergistic Passivation and Resistance Mechanism of Calcium-iron-phosphorus Materials on Cd and Cu Contaminated Soil[J]. Journal of nanchang hangkong university(Natural science edition), 2025, 39(5): 72-78, 86. DOI: 10.3969/j.issn.2096-8566.2025.05.009

钙铁磷材料对Cd、Cu污染土壤的协同钝化及抗逆机制

Synergistic Passivation and Resistance Mechanism of Calcium-iron-phosphorus Materials on Cd and Cu Contaminated Soil

  • 摘要: 针对我国南方土壤存在的重金属污染和土壤酸化双重胁迫问题,本文探究含钙碱性材料与磷、铁材料组合配施对污染土壤重金属的协同钝化效果及抗逆机制。选用Cd、Cu污染土壤,碳酸钙(Ca)、磷酸氢二钠(P)、零价铁(Fe)材料组配为供试土壤和钝化剂,进行土壤培养试验和酸雨淋洗试验。结果表明,钙、铁、磷材料均能显著降低土壤Cd、Cu的生物活性,其中Ca-P-Fe组配效果最佳。Ca-P-Fe材料通过提高污染土壤pH和增加 Fea含量使Cd、Cu的活性含量显著降低。极差分析显示,Ca-P-Fe组配材料中Fe对ECA-Cd活性钝化效果最佳,Ca对ECA-Cu钝化效果最好。模拟酸雨长期胁迫条件(25~100 a),Ca-P-Fe材料仍能有效钝化土壤Cd、Cu的生物活性,表现为土壤pH提高2.58,ECA-Cd和ECA-Cu分别下降25.65%和14.78%。Ca-P-Fe组配材料对Cd、Cu污染土壤具有显著的协同钝化效果,且在长期酸雨胁迫下仍能保持稳定的钝化性能。

     

    Abstract: To address the dual challenges of heavy metal pollution and soil acidification prevalent in southern China, this study investigates the synergistic immobilization effects and resistance mechanisms of combined applications of calcium-based alkaline materials with phosphorus and iron-based materials on heavy metals in contaminated soils. Cd and Cu contaminated soils were targeted, with calcium carbonate (Ca), disodium hydrogen phosphate (P), and zero-valent iron (Fe) used as amendments. Soil incubation experiments and acid rain leaching experiments were conducted. Results show that the Ca, Fe, and P contained materials significantly reduced the bioavailability of Cd and Cu in the soil, with the Ca-P-Fe combination exhibiting the optimal performance. This combination significantly minimized the active fractions of Cd and Cu by increasing the soil pH and Fea content. Range analysis indicated that Fe in Ca-P-Fe combination was most effective in controlling ECA-Cd activity, while Ca was most effective for ECA-Cu. Under long-term acid rain stress (simulating 25~100 years), the Ca-P-Fe combination remiained effective in immobilizing the bioavailability of Cd and Cu, with ECA-Cd and ECA-Cu decreasing by 25.65% and 14.78%, and soil pH increasing by 2.58. These findings validiate that the Ca-P-Fe combination exerts significant synergistic immobilization effects on Cd and Cu contaminated soils and maintains stable immobilization performance under long-term acid rain stress.

     

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