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通过柱浸试验探索电解锰渣中重金属和氨氮向农业土壤中的迁移转化行为。

Exploring the migration and transformation behaviors of heavy metals and ammonia nitrogen from electrolytic manganese residue to agricultural soils through column leaching test.

机构信息

State Key Laboratory of Geomechanics and Geotechnical Engineering, Institute of Rock and Soil Mechanics, Chinese Academy of Sciences, Wuhan, 430071, China.

School of Urban Construction, Wuhan University of Science and Technology, Wuhan, 430065, China.

出版信息

Environ Sci Pollut Res Int. 2023 Aug;30(40):93199-93212. doi: 10.1007/s11356-023-28820-2. Epub 2023 Jul 28.

Abstract

Heavy metals (HMs) and ammonia nitrogen (AN) leaching from electrolytic manganese residue (EMR) result in the contamination of agricultural soils and water bodies. Batch and column leaching tests were conducted to simulate the release of HMs and AN in EMR during precipitation, as well as their migration and transformation in agricultural soils. The results show that Mn, AN, Cd, Ni, and Zn present in the EMR had high acid soluble fraction (un-fixed AN) content, and the leachability of Mn and AN was significantly higher than that of other hazardous elements. The cumulative release of hazardous elements in the EMR stockpile was well-fitted (R > 0.95) by the HILL model. Significant HMs and AN accumulated in the agricultural soils after contamination from the EMR leachate. The pollution degree of HMs in agricultural soils was ranked as Mn > Ni > Pb ≈ Zn ≈ Cr > Cd. The acid soluble fraction (un-fixed AN) content of Mn, Ni, Zn, and AN in agricultural soils increased significantly. The risk assessment code shows that the risk level of Mn in agricultural soils changed from medium to high; Ni and Zn in surface soils changed from low to medium. These results indicated that the leaching from EMR would significantly increase the ecological risk of HMs in surrounding agricultural soils, and the large release of AN would pose a great threat to aquatic systems if not properly addressed.

摘要

重金属(HMs)和氨氮(AN)从电解锰渣(EMR)浸出导致农业土壤和水体受到污染。通过批量和柱浸出试验模拟了 EMR 在沉淀过程中 HMs 和 AN 的释放以及它们在农业土壤中的迁移和转化。结果表明,EMR 中存在的 Mn、AN、Cd、Ni 和 Zn 具有高酸可溶分数(未固定 AN)含量,Mn 和 AN 的浸出率明显高于其他有害元素。EMR 堆存量中有害元素的累积释放通过 HILL 模型得到很好的拟合(R > 0.95)。EMR 浸出液污染后,大量的 HMs 和 AN 会在农业土壤中积累。农业土壤中 HMs 的污染程度依次为 Mn > Ni > Pb ≈ Zn ≈ Cr > Cd。农业土壤中 Mn、Ni、Zn 和 AN 的酸可溶分数(未固定 AN)含量显著增加。风险评估代码显示,农业土壤中 Mn 的风险水平从中等变为高;表层土壤中的 Ni 和 Zn 从低变为中。这些结果表明,EMR 的浸出会显著增加周围农业土壤中 HMs 的生态风险,如果不加以适当处理,大量释放的 AN 将对水系统构成巨大威胁。

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