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硝酸根(NO₃⁻)和磷酸根(PO₄³⁻)对农业湿地土壤中地质成因砷和锑释放的影响:田间与实验室研究方法

Effects of NO3 (-) and PO4 (3-) on the release of geogenic arsenic and antimony in agricultural wetland soil: a field and laboratory approach.

作者信息

Rouwane Asmaa, Rabiet Marion, Grybos Malgorzata, Bernard Guillaume, Guibaud Gilles

机构信息

Groupement de Recherche Eau Sol Environnement (GRESE), Université de Limoges, 123 Avenue Albert Thomas, 87060, Limoges, France.

出版信息

Environ Sci Pollut Res Int. 2016 Mar;23(5):4714-28. doi: 10.1007/s11356-015-5699-5. Epub 2015 Nov 3.

Abstract

The dynamics of arsenic (As) and antimony (Sb) in wetland soil periodically submitted to agricultural pressure as well as the impact of soil enrichment with NO3 (-) (50 mg L(-1)) and PO4 (3-) (20 mg L(-1)) on As and Sb release were evaluated at both field and laboratory scales. The results showed that As and Sb exhibited different temporal behaviors, depending on the study scale. At field scale, As release (up to 93 μg L(-1)) occurred under Fe-reducing conditions, whereas Sb release was favored under oxidizing conditions (up to 5 μg L(-1)) and particularity when dissolved organic carbon (DOC) increased in soil pore water (up to 92.8 mg L(-1)). At laboratory scale, As and Sb release was much higher under reducing conditions (up to 138 and 1 μg L(-1), respectively) compared to oxic conditions (up to 6 and 0.5 μg L(-1), respectively) and was enhanced by NO3 (-) and PO4 (3-) addition (increased by a factor of 2.3 for As and 1.6 for Sb). The higher release of As and Sb in the enriched reduced soil compared to the non-enriched soil was probably induced by the combined effect of PO4 (3-) and HCO3 (-) which compete for the same binding sites of soil surfaces. Modeling results using Visual Minteq were in accordance with experimental results regarding As but failed in simulating the effects of PO4 (3-) and HCO3 (-) on Sb release.

摘要

对周期性承受农业压力的湿地土壤中砷(As)和锑(Sb)的动态变化,以及用NO3 (-)(50 mg L(-1))和PO4 (3-)(20 mg L(-1))对土壤进行富集处理对As和Sb释放的影响,在田间和实验室尺度上进行了评估。结果表明,As和Sb表现出不同的时间行为,这取决于研究尺度。在田间尺度上,As的释放(高达93 μg L(-1))发生在铁还原条件下,而Sb的释放在氧化条件下更有利(高达5 μg L(-1)),特别是当土壤孔隙水中溶解有机碳(DOC)增加时(高达92.8 mg L(-1))。在实验室尺度上,与有氧条件(分别高达6和0.5 μg L(-1))相比,还原条件下As和Sb的释放要高得多(分别高达138和1 μg L(-1)),并且添加NO3 (-)和PO4 (3-)会增强这种释放(As增加2.3倍,Sb增加1.6倍)。与未富集土壤相比,富集的还原土壤中As和Sb的较高释放可能是由PO4 (3-)和HCO3 (-)的综合作用引起的,它们竞争土壤表面的相同结合位点。使用Visual Minteq的模拟结果与关于As的实验结果一致,但未能模拟PO4 (3-)和HCO3 (-)对Sb释放的影响。

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