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抗坏血酸-磺胺增效氢化物发生-原子荧光光谱法测定土壤中镉 被引量:21

Determination of Cadmium in Soil Samples with Ascorbic Acid and Sulfanilamide as Enhanced Reagent Using Hydride Generation Atomic Fluorescence Spectrometry
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摘要 建立了一种用抗坏血酸-磺胺双络合体系进行氢化物原子荧光光谱法测定土壤中镉的新方法。研究了抗坏血酸-磺胺双络合体系对方法的增效作用,以及Ni2+对测定的显著增感作用;探讨了氢化物发生的反应机理,并应用核磁共振仪对机理进行实验验证。该方法测镉的最佳条件为:以3%HCl为载流,20g/LKBH4溶液为还原剂,在0.05%抗坏血酸+0.05%磺胺双络合试剂+0.1mg/LNi2+体系中,镉的线性范围为2~40μg/L,相关系数(r)0.9993,检出限为0.08μg/L,RSD<4.8%(n=14)。应用本方法测定了4种国家土壤标准物质中镉的含量,结果与标准值吻合。 A novel system was developed for the determination of Cd in soil samples using hydride generation atomic fluoresce spectroscopy.Some complexing reagents and transition metal ions were tested as enhancement reagents respectively.The results showed that an appropriate amount of ascorbic acid and sulfanilamide added simultaneously could effectively improve the vapor generation efficiency of Cd.The volatile species was generated noticeably when nickel ion was added.The principle of hydride generation of cadmium was discussed,and verified by nuclear magnetic resonance method.The optimal detective conditions were that the double complexing reagent concentrations of ascorbic acid and sulfanilamide were all in 0.05%,and Ni2+was 0.1 mg/L when the instrument condition was in 3%HCl as a carrier flow,and 20 g/L of KBH 4 as a reductant.The limit of detection(LOD,3σ) was 0.08μg/L and the linear range was 2-40μg/L.The relative standard deviation(RSD) was less than 4.8%(n=14) .The method was successfully applied for the determination of trace Cd in the four national standard reference materials(GBW07428,GBW07402,GBW07404 and GBW07408) and the results analyzed were in good agreement with the certified values.
出处 《分析化学》 SCIE EI CAS CSCD 北大核心 2010年第4期542-546,共5页 Chinese Journal of Analytical Chemistry
基金 国家自然科学基金(No.40573044) 教育部留学回国人员基金(No.2004527)资助项目
关键词 增效剂 氢化物发生 原子荧光光谱 土壤 Cadmium Enhancement regent Chemical vapor generation atomic fluorescence spectrometry Soil
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参考文献13

  • 1Deng T L,Chen Y W,Belzile N.Anal.Chim.Acta,2001,432(2):293-302.
  • 2Liao M X,Deng T L.Journal of Environmental Sciences,2006,18(5):995-999.
  • 3Aranda P R,Gil R A,Moyano S,De Vito I,Martinez L D.Journal of Hazardous Materials,2009,161(2-3):1399-1403.
  • 4CHENYuan(陈媛) ZENGYing(曾英) WUHong-Ji(吴虹霁) WANGQin-Er(王琴儿).光谱学与光谱分析,2004,513:417-423.
  • 5Li Z X,Yang X M,Guo Y A,Li H T,Feng Y H.Talanta,2008,74(4):915-921.
  • 6Mazej D,Falnoga I,Veber M,Stibilj V.Talanta,2006,68(3):558-568.
  • 7Feng Y L,Lam J W,Sturgeon R E.Spectrochimica Acta B,2004,59(5):667-675.
  • 8李岩,袁爱萍.碱熔-氢化物发生原子荧光光谱法连续测定锑精矿中的砷、铋、硒、锡[J].分析化学,2008,36(9):1273-1276. 被引量:24
  • 9Cacho J,Beltran I,Nerin C.J.Anal.At.Spectro.,1989,4(7):661-663.
  • 10Guo X W,Guo X M.Anal.Chim.Acta,1995,310:377-385.

二级参考文献23

  • 1袁爱萍,唐艳霞,黄玉龙,汪静玲,覃然,吴健玲,蒙文飞.氢化物-原子荧光法测定锑精矿中痕量砷、汞的研究[J].光谱学与光谱分析,2006,26(8):1553-1556. 被引量:61
  • 2宋雪洁,郭鹏然,陈杭亭,段太成.氢化物发生原子荧光光谱法测定铅基合金中砷[J].分析化学,2007,35(8):1183-1186. 被引量:18
  • 3Wang J H, Yu Y L, Du Z , Fang Z L. J. Anal. At. Spectrom. ,2004, 19 :1559 -1563.
  • 4Mesko M F , Pozebon D , Flores E M M , Dressier V L. Anal. Chim. Acta, 2004, 517:195 -200.
  • 5Ye Q Y, Li Y Y, Yan X P. J. Agric, Food Chem. ,2003,51:2111-2114.
  • 6Edwin A, Caraballo H, Burguera M, Burguera J L, Talanta, 2004, 63:419-424.
  • 7Wang y, Wang J H, Fang Z L. Anal. Chem, , 2005, 77:5396 -5401.
  • 8Wan Z, Xu Z R, Wang J H. Analyst, 2006, 131 : 141-147.
  • 9Duan T C, Song X J, Jin D , Li H F , Xu J W, Chen H T. Talanta, 2005, 67 : 968 -974.
  • 10Li An-Mo(李安模),Wei Ji-Zhong(魏继中).Spectral analysis of Atomic Adsorption and Atomic Fluorescence Spectrometry(原子吸收及原子荧光光谱分析).Beijing(北京):Science Press(科学出版社),2002:215-232.

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