施用水溶性有机肥条件下水稻对稻田土壤砷镉的提取效能

Efficiency of Arsenic and Cadmium Extraction by Rice Plant from Paddy Soil with Soluble Organic Fertilizer Application

  • 摘要: 为了对砷(As)、镉(Cd)复合污染稻田土壤进行清洁修复,开展了田间试验,在施用水溶性有机肥强化As、Cd溶出条件下利用水稻作为修复稻进行提取. 为了评估水溶性有机肥的作用以及水稻的提取效能,分别在水稻分蘖期、抽穗扬花期和灌浆成熟期,利用扩散梯度薄膜技术(DGT)原位监测土壤剖面有效态As、Cd浓度的变化;收获时利用分级提取方法揭示土壤As、Cd赋存形态的变化,并分析植株各部位As、Cd的积累量;为了阐明去除根系的重要性,对比分析了保留和去除根系处理间土壤As、Cd浓度的差异. 结果表明,施用水溶性有机肥(OF)促进了土壤As、Cd的溶出释放,例如,OF处理39 d后土壤DGT-As (扩散梯度薄膜提取态As)和DGT-Cd (扩散梯度薄膜提取态Cd)平均浓度分别较空白对照升高了34.2%、54.9%. 水稻单株提取As、Cd总量分别为12.63、1.18 mg,其中根系As、Cd积累量占比分别为97.6%、81.3%. 与保留根系处理相比,移除根系使土壤As、Cd总量分别降低了5%、10%,土壤剖面DGT提取态的As、Cd平均浓度分别降低了41.9%、56.4%,作物易利用态As(F1+F2)和Cd(F1+F2)浓度分别降低了9.8%、6.1%. 研究显示,水溶性有机肥可促进土壤As、Cd的溶出,可作为利用水稻生长及根系移除来降低稻田土壤作物有效态As、Cd的强化策略,为As、Cd复合污染稻田土壤清洁与安全利用提供了一条有益路径.

     

    Abstract: In order to achieve cleanup and remediation of arsenic (As) and cadmium (Cd) co-contaminated paddies, field experiments were carried out to extract As and Cd with rice plants under the application of soluble organic fertilizer. In order to evaluate the effect of soluble organic fertilizer and the extraction efficiency with rice plants, the diffusion gradient in thin film technology (DGT) was used to in situ monitor the dynamic profile As and Cd at tillering, heading and flowering, and grain filling stages. At harvest, the changes in soil As and Cd fractions were revealed by sequential extraction, and As and Cd accumulation in rice tissues were determined. To highlight the importance of root removal, the differences in soil As and Cd concentrations between treatments with rice roots retained and removed were analyzed. The results showed that the application of soluble organic fertilizer (OF) promoted soil As and Cd dissolution and release. For example, relative to the control, the average concentration of soil DGT-As and DGT-Cd increased by 34.2% and 54.9%, respectively, after 39 days of treatment. The total As and Cd extracted by each single rice plant were 12.63 and 1.18 mg, respectively, with 97.6% and 81.3% of total As and Cd sequestered in the roots. Removal of rice roots at harvest reduced total soil As and Cd concentration by 5% and 10%, and soil profile of DGT-As and Cd showed 41.9% and 56.4% decrease on average compared with the treatment with roots retained in soils. In addition, the readily available As (F1+F2) and Cd (F1+F2) in the post-treated soils with rice root removed decreased by 9.8% and 6.1%, respectively. Based on the present results, the application of soluble organic fertilizer can promote soil As and Cd dissolution, which could enhance bioavailable As and Cd depletion by rice extraction and root removal from paddy soils. This provides a useful way for cleanup and safe utilization of paddy soils with As and Cd co-contamination.

     

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