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Effects of nearly four decades of long-term fertilization on the availability, fraction and environmental risk of cadmium and arsenic in red soils

文献类型： 外文期刊

作者： Gao, Peng 1 ; Huang, Jing 2 ; Wang, Yu 3 ; Li, Lijuan 4 ; Sun, Yuanyuan 5 ; Zhang, Tuo 3 ; Peng, Fuyuan 1 ;

作者机构： 1.Hunan Acad Agr Sci, Inst Agroenvironm & Ecol, Changsha 410125, Hunan, Peoples R China

2.Agroecosyst Natl Field Expt Stn, Qiyang 426182, Hunan, Peoples R China

3.China West Normal Univ, Coll Environm Sci & Engn, Nanchong 637009, Sichuan, Peoples R China

4.Chinese Acad Agr Sci, Inst Agr Environm & Sustainable Dev, Beijing 100081, Peoples R China

5.Guizhou Normal Univ, Key Lab Plant Physiol & Dev Regulat, Guiyang 550025, Guizhou, Peoples R China

关键词： Long-term fertilization; Cadmium; Arsenic; Environmental risk

期刊名称：JOURNAL OF ENVIRONMENTAL MANAGEMENT （ 影响因子：6.789； 五年影响因子：6.914 ）

ISSN： 0301-4797

年卷期： 2021 年 295 卷

页码：

收录情况： SCI

摘要： Fertilizers are important for agricultural production because they can effectively promote crop productivity. However, long-term fertilization can cause heavy metal accumulation in soils and crops. This study utilized sequential extraction, the diffusive gradient in the thin films (DGT) technique and risk assessment models to estimate the effects of the longest long-term fertilization (38 years) in China on cadmium (Cd) and arsenic (As) accumulation in soils. The treatments included no fertilization (CK); inorganic nitrogen, phosphorus, and potassium fertilization (NPK); manure fertilization (M); and NPK plus M cofertilization (NPKM). The results indicated that the soils treated with NPKM, M and NPK had significantly increased total and available concentrations of Cd and As after 38 years of long-term fertilization. Cd mainly originates from cattle manure, while As originates from phosphate fertilizer. Sequential extraction results indicated that the application of manure increased the acid/exchangeable fraction (F1) and organic matter-bound fraction (F3) of Cd and As. The risk assessment results showed that the environmental risks of both Cd and As increased during long-term fertilization, and Cd contamination in the soil was at a moderate-high level, while As remained at a relatively low level. According to the calculations of the maximum numbers of years of soil productivity and rice production, Cd was labile and accumulated in the soils, and As was more labile than Cd in terms of accumulating in rice, indicating that the true risk from As in rice is higher than that from Cd. Controlling the heavy metals in fertilizers, mitigating effective amendments, and identifying plant types that accumulate low amounts of contaminants may be good choices for cleaner crop production.

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