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MWNTs与GNPs-CHIT修饰的过氧化氢生物传感器 被引量:1

Hydrogen peroxide biosensor based on MWNTs and GNPs-CHIT
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摘要 在玻碳电极(GCE)上自组装一层多壁碳纳米管(MWNTs),构建负电荷的界面,然后,静电吸附一层阳离子电子媒介体硫堇(Thi),再由共价键作用自组装一层纳米金(GNPs),壳聚糖(CHIT)混合溶液的复合薄膜,通过静电吸附辣根过氧化物酶(HRP)制得过氧化氢(H2O2)生物传感器。采用循环伏安法和计时电流法考察了该生物传感器的电化学性质,并研究了该修饰电极对H2O2的催化还原作用。生物传感器的响应电流与H2O2浓度在8.2×10^-6~1.1×10^-3mol/L范围内呈现线性关系,检出限为5.8×10^-7mol/L,达到95%稳态响应时间约为15s。将此生物传感器用于H2O2的检测,结果令人满意。 Muhi-walled nanotubes(MWNTs) is self-assembled onto the coated glassy carbon elecrtode(GCE) to form a negative-charge surface. Cationic dye-thionine (Thi) is linked by electrostatic adsorption as an electron transfer mediator. Next the mixture of gold nanoparticles ( GNPs ) and chitosan (CHIT) is assembled on the electrode by covalent bond. The positively charged horseradish peroxidase is successfully immobilized on the GNPs surface. The electrocataltyic behavior of the modified electrode to H2O2 is investigated by cyclic vohammetry and chronoamperometry. The experiments show that the modified electrode has excellent electrocatalytic activity for the detection of H2O2. The linear range of this biosensor is 8.2×10^-6~1.1×10^-3mol/L with a detection limit of 5.8×10^-7mol/L. The response time achieved 95 % steady state is about 15 s. The biosensor is applied for deteetion of H2O2, and the results are satisfied.
出处 《传感器与微系统》 CSCD 北大核心 2009年第10期79-81,84,共4页 Transducer and Microsystem Technologies
关键词 多壁碳纳米管 纳米金 壳聚糖 过氧化氢 mtdti-walled nanotubes (MWNTs) gold nanoparticles (GNPs) chitosan (CHIT) hydrogen peroxide ( H2O2 )
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  • 1Li Jun, Alan Cassell, Lance Delzeit. Novel three-dimensional electrodes: Electrochemical properties of carbon nanotube ensembles[ J]. J Phys Chem B ,2002 ( 106 ) :9299 -9305.
  • 2Wei Choongpoh, Klan Pingloh. Biosensing porperties of diamond and carbon nanotubes [ J ]. Langmuir,2004 (20) :5484 -5492.
  • 3Moore R R, Banks C E, Compton R G. Basal plane pyrolytic graphite modified electrodes : Comparison of carbon nanotubes and graphite powder as electrocatalysts [ J ]. Anal Chem, 2004 ( 76 ) : 2677 -2682.
  • 4Thanh N T K, Rosenzweig Z. Development of an aggregationbased immunoassay for anti-protein a using gold nanoparticles [ J ]. Anal Chem,2002 (74) : 1624 -1628.
  • 5Lei C X,Gong F C, Shen G L, et al. Amperometric for Schistosoma japonicum antigen using antibodies loaded on a nano-Au monolayer modified chitosan-entrapped carbon paste electrode [ J ]. Sens Actuators B ,2003 (96) :582 -588.
  • 6陈贤光,钱莹,张素娟,邹小勇.基于纳米金和硫堇固定酶的过氧化氢生物传感器[J].化学学报,2007,65(4):337-343. 被引量:16
  • 7麦智彬,谭学才,邹小勇.一种基于碳纳米管的安培型过氧化氢生物传感器[J].分析化学,2006,34(6):801-804. 被引量:16
  • 8Frens G. Controlled nucleation for the regulation of the particlesize in monodisperse gold suspension[ J]. Nature Phy Sci, 1973 (241) : 20 -22.
  • 9Ou Chaofeng, Yuan Ruo, Chai Yaqin, et al. A novel amperometric immunosensor based on layer-by-layer assembly of gold nanoparticles-multi-walled carbon nanotubes-thionine multilayer films on polyelectrolyte surface[ J]. Anal Chim Acta,2007, 603 (2) : 205 -213.

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  • 1Whitenett G,Stewart G,Atherton K,et al.Optical fibre instrumentation for environmental monitoring applications[J].J Opt A:Pure Appl Op 2003,23 (7):140-145.
  • 2Lupold S E,Hicke B J,Lin Y,et al.Identification and characterization of nuclease-stabilized RNA molecules that bind human prostate cancer cells via the prostate-specific membrane antigen[J].Cancer Res,2002,62:4029-4033.
  • 3Bourgeois W.The use of sensor arrays for environmental monitoring:Interests and limitations[J].J Environ Monit,2003,17 (5):452-560.
  • 4崔明超,陈繁忠,傅家谟,盛国英.固定化微生物技术在废水处理中的研究进展[J].化工环保,2003,23(5):261-264. 被引量:33
  • 5闫志明,普红平,阳立平.生物固定化技术研究及应用评述[J].四川化工,2004,7(1):12-15. 被引量:31

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