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一种新方法可同时测定环境样品中 127I 和 129I 的碘化物、碘酸盐和有机碘,采用气相色谱-质谱法。

A novel approach for the simultaneous determination of iodide, iodate and organo-iodide for 127I and 129I in environmental samples using gas chromatography-mass spectrometry.

机构信息

Department of Oceanography and Marine Science, Texas A&M University, Galveston, Texas 77551, United States.

出版信息

Environ Sci Technol. 2010 Dec 1;44(23):9042-8. doi: 10.1021/es102047y. Epub 2010 Nov 11.

DOI:10.1021/es102047y
PMID:21069952
Abstract

In aquatic environments, iodine mainly exists as iodide, iodate, and organic iodine. The high mobility of iodine in aquatic systems has led to (129)I contamination problems at sites where nuclear fuel has been reprocessed, such as the F-area of Savannah River Site. In order to assess the distribution of (129)I and stable (127)I in environmental systems, a sensitive and rapid method was developed which enables determination of isotopic ratios of speciated iodine. Iodide concentrations were quantified using gas chromatography-mass spectrometry (GC-MS) after derivatization to 4-iodo-N,N-dimethylaniline. Iodate concentrations were quantified by measuring the difference of iodide concentrations in the solution before and after reduction by Na(2)S(2)O(5). Total iodine, including inorganic and organic iodine, was determined after conversion to iodate by combustion at 900 °C. Organo-iodine was calculated as the difference between the total iodine and total inorganic iodine (iodide and iodate). The detection limits of iodide-127 and iodate-127 were 0.34 nM and 1.11 nM, respectively, whereas the detection limits for both iodide-129 and iodate-129 was 0.08 nM (i.e., 2pCi (129)I/L). This method was successfully applied to water samples from the contaminated Savannah River Site, South Carolina, and more pristine Galveston Bay, Texas.

摘要

在水生环境中,碘主要以碘化物、碘酸盐和有机碘的形式存在。碘在水生系统中的高迁移性导致了核燃料再处理地点(如萨凡纳河站点的 F 区)的 (129)I 污染问题。为了评估环境系统中 (129)I 和稳定 (127)I 的分布,开发了一种灵敏快速的方法,能够确定碘形态的同位素比值。将溶液中的碘化物浓度用气相色谱-质谱法(GC-MS)进行衍生化,转化为 4-碘-N,N-二甲基苯胺后进行定量。将溶液中的碘化物浓度用亚硫酸钠(Na2S2O5)还原前后的差值来定量碘酸盐浓度。总碘,包括无机碘和有机碘,在 900°C 下燃烧转化为碘酸盐后进行测定。有机碘是总碘与总无机碘(碘化物和碘酸盐)之间的差值。碘化物-127 和碘酸盐-127 的检测限分别为 0.34 nM 和 1.11 nM,而碘化物-129 和碘酸盐-129 的检测限均为 0.08 nM(即 2pCi (129)I/L)。该方法成功应用于来自南卡罗来纳州受污染的萨凡纳河站点和德克萨斯州更原始的加尔维斯顿湾的水样。

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