HPLC-ICP-MS Determination of Iodate and Iodide in Drinking Water
摘 要
提出了高效液相色谱-电感耦合等离子体质谱法测定饮用水中碘酸根和碘离子的方法。饮用水样品通过Dionex IonPac AS14阴离子交换柱及AG14保护柱分离碘酸根和碘离子,用50 mmol·L-1碳酸铵溶液(用氨水调至pH 9.9)作流动相进行淋洗。于洗脱液中用电感耦合等离子体质谱法分别测定碘酸根和碘离子的含量,两者的线性范围均为0.20~300 μg·L-1,检出限(3S/N)依次为0.09 μg·L-1和0.13 μg·L-1。以饮用水为基体加入两个不同浓度水平的标准溶液按方法分析后,求得方法的回收率及精密度为① 碘酸根回收率在100.5%~113.0%,相对标准偏差(n=8)在1.2%~2.8%之间;② 碘离子回收率在101.9%~110.7%,相对标准偏差(n=8)在1.3%~2.0%之间。
Abstract
A method of HPLC-ICP-MS for the determination of iodate and iodide in drinking water was proposed. Dionex IonPac AS14 anion chromagraphic column and AG14 guard column and 50 mmol·L-1 ammonium carbonate (adjusted to pH 9.9 with aq. ammonia) as mobile phase were used for separation of iodate and iodide. The eluates were used for ICP-MS determination, with linearity ranges between 0.20 to 300 μg·L-1 for both iodate and iodide. Values of detection limit (3S/N) found were 0.09 μg·L-1 for iodate and 0.13 μg·L-1 for iodide. Tests for recovery and precision were made by standard addition method at 2 different concentration levels, the results obtained were as follows: ① for iodate, recovery: 100.5% to 113.0%, RSD′s (n=8): 1.2% to 2.8%; ② for iodide, recovery: 101.9% to 110.7%, RSD′s (n=8): 1.3% to 2.0%.
中图分类号 O657.63
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收稿日期 2011/1/19
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备注侯艳霞(1985-),女,内蒙古包头人,硕士研究生,研究方向为元素分析及形态研究。
引用该论文: HOU Yan-xia,LIU Li-ping,DU Zhen-xia. HPLC-ICP-MS Determination of Iodate and Iodide in Drinking Water[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2011, 47(11): 1262~1265
侯艳霞,刘丽萍,杜振霞. 高效液相色谱-电感耦合等离子体质谱法测定饮用水中碘酸根和碘离子[J]. 理化检验-化学分册, 2011, 47(11): 1262~1265
被引情况:
【1】戴兴德,张爱菊,张小林, "石墨烯修饰玻碳电极循环伏安法测定碘盐中的碘酸根",理化检验-化学分册 52, 351-353(2016)
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参考文献
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【9】YAMANAKA M, SAKAI T, KUMAGAI H, et al. Specific determination of bromate and iodate in ozonized water by ion chromatography with postcolumn derivatization and inductively coupled plasma mass spectrometry[J]. Journal of Chromatography A, 1997,789:259-265.
【2】BURGI H, SCHAFFNER T H, SEILER J P. The toxicology of iodate: A review of the literature[J]. Thyroid, 2001,11(5):449-456.
【3】GILFEDDER B S, PETRI M, WESSELS M, et al. An iodine mass-balance for Lake constance, germany: insights into iodine speciation changes and fluxes[J]. Geochimica et Cosmochimica Acta, 2010,74:3090-3111.
【4】SCHWEHR K A, SANTSCCHI P H. Sensitive determination of iodine species,including organic-iodine for freshwater and seawater samples using high performance liquid chromatography and spectrophotometric detection[J]. Anal Chim Acta, 2003,482:59-71.
【5】HONGLAN S, CRAIG A. Rapid IC-ICP-MS method for simultaneous analysis of iodoacetic acids, bromoacetic acids, bromate, and other related halogenated compounds in water[J]. Talanta, 2009,79:523-527.
【6】张翼,徐子刚,姚琪,等.离子色谱-电感耦合等离子体质谱联用测定不同形态碘元素[J].浙江大学学报, 2009,36(4):439-441.
【7】SHAH M, WUILLUID R G, KANNAMKUMARATH S S, et al. Iodine speciation studies in commercially available seaweed by coupling different chromatographic techniques with UV and ICP-MS detection[J]. JAAS, 2005,20:176-182.
【8】CHEN Zu-liang, MEGHARAJ M, NAILDU R. Sepciation of iodate and iodide in seawater by non-suppressed ion chromatography with inductively coupled plasma mass spectrometry[J]. Talanta, 2007,72:1842-1846.
【9】YAMANAKA M, SAKAI T, KUMAGAI H, et al. Specific determination of bromate and iodate in ozonized water by ion chromatography with postcolumn derivatization and inductively coupled plasma mass spectrometry[J]. Journal of Chromatography A, 1997,789:259-265.
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