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Sulfur controlled cadmium dissolution in pore water of cadmium- contaminated soil as affected by DOC under waterlogging

机译:淹水条件下DOC对镉污染土壤孔隙水中硫控制的镉溶解

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Cadmium (Cd) precipitation and dissolution in pore water is associated with dissolved organic carbon (DOC)-induced reduction-oxidation of sulfur (S) under waterlogging and is vital for controlling the bioavailability in paddy soil. A 120-day soil incubation experiment, including application of sulfur (5, 30 mg kg(-1)) and wheat straw (W, 1.0%) alone or in combination (W + S) into Cd-contaminated paddy soil under waterlogging, was conducted to investigate the dynamic of dissolved Cd and its relationship with DOC, S-2-, Fe2+, pH, Eh and pe + pH in soil pore water. The results showed that the lowest dissolved Cd concentration was observed in the W + S-treated soil pore water among all treatments when the soil Eh remained at lower values during the period of 15-60 days of incubation, which could be attributed to CdS precipitation and/or co-precipitation of Cd absorbed by FeS2 because of the reduction in sulfur. The application of S resulted in a Cd rebound in the pore water irrespective of W addition when the Eh began to increase from its lowest values during the period of 45-75 days of incubation, and SOB genera were observed in the S added soil. This could be attributed to re-dissolution of the precipitated Cd in soils under the SOB-driven oxidation of sulfide such as CdS and FeS2. In conclusion, DOC-driven reduction-oxidation of sulfur controls Cd dissolution in the pore water of Cd-contaminated paddy soil under waterlogging conditions. Further studies are required to investigate the interaction of sulfur and SOM-induced DOC on Cd bioavailability in rice-planted paddy soils. (C) 2019 Elsevier Ltd. All rights reserved.
机译:镉(Cd)的沉淀和在孔隙水中的溶解与涝渍下溶解的有机碳(DOC)诱导的硫(S)的还原氧化有关,对于控制稻田土壤的生物利用度至关重要。一个为期120天的土壤培养实验,包括在渍水条件下将硫(5,30 mg kg(-1))和麦秸(W,1.0%)单独或组合(W + S)施用到受Cd污染的稻田中,旨在研究土壤孔隙水中溶解镉的动态及其与DOC,S-2-,Fe2 +,pH,Eh和pe + pH的关系。结果表明,在孵育15-60天的过程中,当土壤Eh保持较低值时,在所有处理中,用W + S处理的土壤孔隙水中的Cd浓度最低,这可能归因于CdS沉淀和/或由于硫的减少而被FeS2吸收的Cd共沉淀。当Eh在孵化45-75天期间从最低值开始增加时,施用S会导致孔隙水中Cd反弹,而与加入W无关,并且在添加S的土壤中观察到SOB属。这可能归因于在SOB驱动的硫化物如CdS和FeS2的氧化作用下,沉淀的Cd在土壤中的重新溶解。总之,在淹水条件下,DOC驱动的硫还原氧化控制了Cd在受Cd污染的稻田土壤孔隙水中的溶解。需要进一步的研究以调查硫和SOM诱导的DOC对水稻种植的水稻土中Cd生物利用度的相互作用。 (C)2019 Elsevier Ltd.保留所有权利。

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