首页> 外文期刊>Fresenius Environmental Bulletin >LEAD DISTRIBUTION BETWEEN SOIL GEOCHEMICAL PHASES AND ITS FRACTIONATION IN PB-TREATED SOILS
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LEAD DISTRIBUTION BETWEEN SOIL GEOCHEMICAL PHASES AND ITS FRACTIONATION IN PB-TREATED SOILS

机译:PB处理过的土壤地球化学相中的铅分布及其分馏

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摘要

Eight horizons from four natural soils (Umbric Ac-risol (UA), Dystric Fluvisol (DF), Mollic Umbrisol (MU) and Tionic Fluvisol (TF) were treated with an acidic dissolution of Pb~(2+) with the aim of determining its sorption capacity and the distribution of Pb in the different geo-chemical phases of soil. The amount of Pb sorbed was determined, and fractioning was carried out by sequential extraction. XDR and FE-SEM techniques were also used to determine the mineralogy of the soils and the changes that occurred after treatment. The Pb content that was sorbed was found to be greater in the surface horizons rather than in the subsurface horizons, except in the Mollic Umbrisol. The majority of the Pb was sorbed in an exchangeable form (between 56.24 % in DF.A and 85.17 % in TF.G). Organic matter and amorphous Mn and Fe oxides were the soil components with greatest influence in Pb sorption. The crystalline Fe oxides and the residual fraction sorbed the least Pb (<1%). By means of XRD and FE-SEM we verified that the acid treatment produced alteration in the soil minerals, leading to an increase in the content of amorphous and the formation of new crystalline phases such as nitratine. We also observed the Pb sorption on hydroxy compounds of Fe, which interacted with albite, muscovite and gibbsite, and the fixing of this metal in associations between organic material and gibbsite. We identified the presence of spherical and curved particles of aluminous clays with a low level of crystallinity with the ability to sorb Pb.
机译:用酸性溶解的Pb〜(2+)处理来自四种天然土壤(Ubric Ac-risol(UA),Dystric Fluvisol(DF),Mollic Umbrisol(MU)和Tionic Fluvisol(TF))的八个层在土壤的不同地球化学相中其吸附能力和Pb的分布,测定Pb的吸附量,并通过顺序萃取进行分级分离,还使用XDR和FE-SEM技术确定了Pb的矿物学。在土壤和处理后发生的变化中,发现吸附的Pb含量在表层而不是在地下表层中要高,但在软体动物中除外。大多数Pb以可交换的形式吸附(在两者之间)。在DF.A中为56.24%,在TF.G中为85.17%),有机物和无定形Mn和Fe氧化物是对Pb吸附影响最大的土壤成分,结晶的Fe氧化物和残留分数对Pb的吸附最少(<1% )。通过XRD和FE- SEM我们证实,酸处理会改变土壤中的矿物质,从而导致非晶质含量增加,并形成新的结晶相(如硝胺)。我们还观察到了铁的羟基化合物对铅的吸附,铁与钠长石,白云母和三水铝石相互作用,并且这种金属在有机物质和三水铝石之间的结合中固定。我们确定了球形粘土和弯曲粘土颗粒的存在,这些颗粒具有较低的结晶度并具有吸附Pb的能力。

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