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在有机肥施用条件下,同时最小化土壤中生物可利用镉和砷含量的最适 pH 值和 Eh 值。

The optimum pH and Eh for simultaneously minimizing bioavailable cadmium and arsenic contents in soils under the organic fertilizer application.

机构信息

Beijing Key Laboratory of Resource-oriented Treatment of Industrial Pollution, School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China.

Beijing Key Laboratory of Resource-oriented Treatment of Industrial Pollution, School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China; Beijing Municipal Key Laboratory of Resource Environment and GIS, College of Resource Environment and Tourism, Capital Normal University, Beijing 100048, China.

出版信息

Sci Total Environ. 2020 Apr 1;711:135229. doi: 10.1016/j.scitotenv.2019.135229. Epub 2019 Nov 22.

Abstract

Cadmium (Cd) and arsenic (As) are usually found in contaminated soils. Their bioavailabilities are often related to pH and Eh, which indicate a generally contrasting or antagonistic effect. In this paper, the pH and Eh of soil samples were altered by adding organic fertilizer, and Tessier sequential extraction procedures were used to extract heavy metal speciation. With increasing pH and decreasing Eh, the content of the exchangeable, carbonate-bound, Fe-Mn oxide-bound, and organic-bound forms of the Cd decreased. The content of the residual form of Cd increased. The content of water-soluble Cd also increased. In terms of As, the content of the water-soluble, exchangeable, carbonate-bound, and organic-bound forms increased, and the content of the residual form decreased. Bioavailable forms contained water-soluble and exchangeable forms. With increasing pH or decreasing Eh, bioavailable Cd content linearly decreased, whereas bioavailable As content exponentially increased. The fitting curve showed that compared with 200 mV, the bioavailable Cd content decreased by 52.4%, and the bioavailable As content increased by 3.2 times at -400 mV. Finally, using the indicator of trade-off value, optimum pH = 7.31, and Eh = -130 mV, the bioavailable Cd and As contents were simultaneously maintained at a relatively low level. The novelty of this paper is studying the effects of different soil pH and Eh values changed by organic fertilizer on the speciation of Cd and As rather than the direct quantitative effects between organic fertilizer and the speciation of Cd and As, which can better explain the mechanism underlying the effect of organic fertilizer on the speciation of Cd and As.

摘要

镉(Cd)和砷(As)通常存在于污染土壤中。它们的生物可利用性通常与 pH 值和 Eh 值有关,这表明它们通常具有相反或拮抗的作用。在本文中,通过添加有机肥来改变土壤样品的 pH 值和 Eh 值,并采用 Tessier 连续提取程序来提取重金属形态。随着 pH 值的升高和 Eh 值的降低,可交换态、碳酸盐结合态、铁锰氧化物结合态和有机结合态 Cd 的含量减少,残渣态 Cd 的含量增加,水溶性 Cd 的含量也增加。对于 As,水溶性、可交换态、碳酸盐结合态和有机结合态的含量增加,而残渣态的含量减少。生物有效态包含水溶性和可交换态。随着 pH 值的升高或 Eh 值的降低,生物有效态 Cd 的含量呈线性下降,而生物有效态 As 的含量呈指数增加。拟合曲线表明,与 200 mV 相比,在-400 mV 时,生物有效态 Cd 的含量下降了 52.4%,生物有效态 As 的含量增加了 3.2 倍。最后,使用权衡值指标,最优 pH 值为 7.31,Eh 值为-130 mV,同时将生物有效态 Cd 和 As 的含量维持在相对较低的水平。本文的新颖之处在于研究了有机肥改变不同土壤 pH 值和 Eh 值对 Cd 和 As 形态的影响,而不是直接研究有机肥与 Cd 和 As 形态之间的定量关系,这可以更好地解释有机肥对 Cd 和 As 形态影响的机制。

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