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使用与电感耦合等离子体质谱联用的流场流分级分离技术(FlFFF-ICP-MS)对受贫铀污染土壤进行化学形态分析研究。

Chemical speciation studies on DU contaminated soils using flow field flow fractionation linked to inductively coupled plasma mass spectrometry (FlFFF-ICP-MS).

作者信息

Brittain S R, Cox A G, Tomos A D, Paterson E, Siripinyanond A, McLeod C W

机构信息

Centre for Analytical Sciences, Department of Chemistry, University of Sheffield, Sheffield S3 7HF, UK.

出版信息

J Environ Monit. 2012 Mar;14(3):782-90. doi: 10.1039/c2em10716c. Epub 2012 Jan 11.

DOI:10.1039/c2em10716c
PMID:22237634
Abstract

Flow field flow fractionation (FlFFF) in combination with inductively coupled plasma mass spectrometry (ICP-MS) was used to study the chemical speciation of U and trace metals in depleted uranium (DU) contaminated soils. A chemical extraction procedure using sodium pyrophosphate, followed by isolation of humic and fulvic substances was applied to two dissimilar DU contaminated sample types (a sandy soil and a clay-rich soil), in addition to a control soil. The sodium pyrophosphate fractions of the firing range soils (Eskmeals and Kirkcudbright) were found to contain over 50% of the total U (measured after aqua regia digestion), compared to approximately 10% for the control soil. This implies that the soils from the contaminated sites contained a large proportion of the U within more easily mobile soil fractions. Humic and fulvic acid fractions each gave characteristic peak maxima for analytes of interest (Mn, Fe, Cu, Zn, Pb and U), with the fulvic acid fraction eluting at a smaller diameter (approximately 2.1 nm on average) than the humic fraction (approximately 2.4 nm on average). DU in the fulvic acid fraction gave a bimodal peak, not apparent for other trace elements investigated, including natural U. This implies that DU interacts with the fulvic acid fraction in a different way to all other elements studied.

摘要

采用流场流分级法(FlFFF)结合电感耦合等离子体质谱法(ICP-MS)研究贫铀(DU)污染土壤中铀和痕量金属的化学形态。除对照土壤外,对两种不同类型的DU污染土壤样品(一种砂土和一种富粘土土壤)采用焦磷酸钠化学萃取程序,随后分离腐殖质和富里酸物质。发现靶场土壤(埃斯克米尔和柯克库布里奇)的焦磷酸钠组分中总铀含量(王水消解后测定)超过50%,而对照土壤约为10%。这意味着受污染场地的土壤中大部分铀存在于更易迁移的土壤组分中。腐殖酸和富里酸组分对感兴趣的分析物(锰、铁、铜、锌、铅和铀)均给出了特征性的峰值最大值,富里酸组分的洗脱直径(平均约2.1 nm)小于腐殖酸组分(平均约2.4 nm)。富里酸组分中的DU呈现双峰峰形,这在包括天然铀在内的其他所研究痕量元素中并不明显。这意味着DU与富里酸组分的相互作用方式与所研究的所有其他元素不同。

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