CN103411956A - Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method - Google Patents

Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method Download PDF

Info

Publication number
CN103411956A
CN103411956A CN2013103694946A CN201310369494A CN103411956A CN 103411956 A CN103411956 A CN 103411956A CN 2013103694946 A CN2013103694946 A CN 2013103694946A CN 201310369494 A CN201310369494 A CN 201310369494A CN 103411956 A CN103411956 A CN 103411956A
Authority
CN
China
Prior art keywords
iodate
add
reagent
paranitroanilinum
azanol
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN2013103694946A
Other languages
Chinese (zh)
Inventor
李攻科
张凯歌
胡玉玲
田中群
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sun Yat Sen University
Original Assignee
Sun Yat Sen University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Sun Yat Sen University filed Critical Sun Yat Sen University
Priority to CN2013103694946A priority Critical patent/CN103411956A/en
Publication of CN103411956A publication Critical patent/CN103411956A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Investigating, Analyzing Materials By Fluorescence Or Luminescence (AREA)

Abstract

The invention relates to a method for rapidly detecting iodate by surface enhanced Raman spectroscopy and an application of the method. A Raman signal of the iodate is very weak, an SERS (Surface Enhanced Raman Scattering) signal of iodate is also weak, hydroxylamine is oxidated into nitrite by the iodate, coupling dye is generated from nitrite ions and a diazo-coupling reagent under an acidic or alkalescent condition, the SERS signal of the coupling dye is strong, and qualitative and quantitative detection of the iodate is indirectly carried out by measuring the dosage of the coupling dye through SERS. According to the method and the application thereof, Au/SiO2 is used as an SERS substrate material, the stability of particles is improved by means of a silicon dioxide shell, so that the result repeatability is better. The method is suitable for rapid detection of the iodate in complex samples, such as tablet salt, drinking water and environment water and has the advantages of simpleness and rapidness (about 2 minutes), suitability for field detection and benefits for popularization and use and the like.

Description

Method and the application thereof of Surface enhanced raman spectroscopy fast detecting iodate
Technical field
The present invention relates to the method for Surface enhanced raman spectroscopy fast detecting iodate, relate in particular to method and the application thereof of Surface enhanced raman spectroscopy fast detecting iodate, be applicable to the mensuration of iodate in the complex samples such as salt, potable water and environment.
Background technology
Iodine is a kind of important trace element, and iodine deficiency is the important public health problem in the whole world, particularly for child and conceived women.Address this problem at present the best way and in salt, add exactly iodate.Therefore the content of studying the Iodine Content In Iodized Salt acid group has very important significance for the quality and the quality control that guarantee salt.
The traditional detection method of iodate has multiple, and the detection method of recent domestic report mainly contains titrimetry, gas chromatography, high performance liquid chromatography, chromatography of ions, spectrum and mass spectrum etc.But these methods exist process loaded down with trivial details, consuming time, be not easy to the deficiencies such as Site Detection.Therefore foundation simply, the iodate detection method has important meaning fast.
Summary of the invention
Loaded down with trivial details, consuming time and be not easy to the deficiencies such as Site Detection in order to solve conventional iodine acid group detection method process.The invention provides the method for a kind of Surface enhanced raman spectroscopy (SERS) fast detecting iodate, and the application in iodate mensuration in the complex samples such as salt, potable water and environment.
Principle of the present invention: the Raman signal of iodate self is very weak, and the SERS signal is also very weak, therefore can not directly measure iodate by SERS.Iodate is oxidized to nitrite anions by azanol, nitrite anions generates diazonium-coupling product with diazonium-coupling reagent under acid condition, this product self Raman signal is stronger, and the SERS of this product is enhanced, using this coupling product as the probe of iodate, iodate is carried out to indirectly quantitative and qualitative analysis measure by measuring coupling product.
In order to realize the foregoing invention purpose, the present invention has adopted following Surface enhanced raman spectroscopy fast detecting iodate method, it is characterized in that: Surface enhanced raman spectroscopy fast detecting iodate method, it is characterized in that: make iodate in testing sample that azanol is oxidized to nitrite anions, nitrite anions and diazo reagent and azo reagent generate diazonium-para-dye under acid condition, using this diazonium-para-dye as probe molecule, indirectly iodate is carried out to quantitative and qualitative analysis mensuration by measuring diazonium-para-dye.
As preferred version, the iodate ion in said method in testing sample is converted into nitrite anions by azanol, is that nitrite anions and paranitroanilinum and hydrochloride naphthodiamide generate red diazonium-para-dye under acid condition.
Specifically, above-mentioned quilitative method comprises the following steps:
A, get the iodate solution of variable concentrations in centrifuge tube, add azanol to generate nitrite anions, add again diazo reagent, be mixed evenly and make it that diazo-reaction occur, after add and the azo reagent of diazo reagent with equimolar ratio, be mixed evenly and make it that coupling reaction occur, reactant liquor is placed 1min, obtains diazonium-para-dye;
B, get certain volume a step gained reactant liquor in sample hose, then add the enhancing mix particles of equal volume even, directly with the portable Raman instrument of DeltaNu, detect;
C, measure and draw out the corresponding Surface enhanced raman spectroscopy figure of different content iodate solution;
D, measure testing sample, add azanol to generate nitrite anions, add again diazo reagent, be mixed evenly and make it that diazo-reaction occur, after add and the azo reagent of diazo reagent with equimolar ratio, be mixed evenly and make it that coupling reaction occur, reactant liquor is placed 1min, obtains diazonium-para-dye; Add the enhancing mix particles of equal volume even, directly with the Raman instrument, detect the Surface enhanced raman spectroscopy of this sample, to sample, carry out qualitative according to the Raman shift in step c gained Raman spectrogram.
As further quilitative method, described diazo reagent is the paranitroanilinum hydrochloric acid solution; Described azo reagent is the hydrochloride naphthodiamide aqueous solution; Described step c also comprises and draws out 1138cm -1The peak area of Raman shift place-iodate ion content standard curve; Described steps d also comprises according to 1138cm -1The peak area of Raman shift place-iodate ion content standard opisometer is calculated the content of iodate in sample.
Specifically, described concentration of hydrochloric acid solution is 0.1-3.0mol L -1Described azanol concentration is 0.001-3.0mol L -1The concentration of hydrochloric acid solution of described paranitroanilinum is 0.001-1.0mol L -1The concentration of aqueous solution of described hydrochloride naphthodiamide is 0.001-1.0mol L -1.
Described centrifuge tube volume is 1mL.
Described sample hose is the 1mL glass tube.
It is 100:(0.1~3.0 that described iodate solution adds volume and the ratio that adds volume of the hydrochloric acid solution of azanol and paranitroanilinum): (0.1~3.0); It is 100:(0.1~3.0 that described testing sample adds the hydrochloric acid solution of volume and azanol and paranitroanilinum to add the ratio of volume): (0.1~3.0).
Described iodate solution can be selected potassium iodate solution.
As possibility, diazo reagent can be paranitroanilinum, sulfanilamide (SN) and sulfanilic acid etc., and azo reagent can be diphenylamine and hydrochloride naphthodiamide etc.
Described enhancing particle is Au/SiO 2Nano sol, wherein Au/SiO 2For the Au nanoparticle surface, be coated with the core-shell type structure of silica shell, described enhancing particle can be also A g Nano sol or Au Nano sol etc.
Described Raman instrument excitation wavelength is 785nm; Laser power: 60mv; Sweep time: 1s.
Be respectively 1098,1138 for Raman shift qualitatively, 1381 and 1426cm -1For quantitative Raman shift, be 1138cm -1, wherein 1098 is C-NO 2Stretching vibration, 1138cm -1For C-N=N stretching vibration, 1381cm -1C-C stretching vibration in phenyl ring, 1426cm -1For the N=N stretching vibration.
The present invention also provides the application of Surface enhanced raman spectroscopy fast detecting iodate method iodate content in measuring salt, potable water or environment.
By above-mentioned steps, can find, method and the application thereof of surface-enhanced Raman fast detecting iodate of the present invention, have the advantages such as simple, quick, is applicable to Site Detection, is conducive to promote the use of etc.And the degree of depth that color is produced in coupling becomes positive correlation with the concentration of iodate ion, namely iodate ion concentration is larger, and color is darker, can to iodate content in sample, estimate by the change color of visual inspection reaction system.
The accompanying drawing explanation:
Below in conjunction with the drawings and specific embodiments, this experiment is elaborated:
Fig. 1 is Raman and the SERS figure of iodate and diazonium-coupling product,
Wherein, a is 0.05mg L -1Iodate coupling product SERS; B is 1000mg L -1Iodate coupling product Raman figure; C is 1000mg L -1Iodate SERS; D is 1000mg L -1Iodate Raman figure;
Fig. 2 is the SERS figure of the corresponding coupling product of variable concentrations iodate, wherein, and iodate concentration (a-g): 0,0.010,0.030,0.050,0.075,0.10and0.13mg L -1
Fig. 3 is 1138cm -1The peak area of Raman shift place-iodate content standard curve.
Embodiment
The method of SERS fast detecting iodate of the present invention and application thereof are based on following chemical reaction:
2IO 3 -+3NH 2OH→3NO 2 -+3H ++2I -+3H 2O
The final color that generates azo dyes be redness, and the degree of depth of its color becomes positive correlation with the concentration of iodate ion, and namely iodate ion concentration is larger, and color is darker.This azo dyes very easily is adsorbed on the enhancing particle surface, obtains Surface enhanced raman spectroscopy, the content of the amount indirect determination iodate by measuring azo dyes.
The embodiment of SERS fast detecting iodate method of the present invention and application thereof is as follows, but content of the present invention is not limited to this fully.
Iodate in embodiment 1SERS fast detecting salt
1.1 key instrument and reagent:
The portable Raman instrument of DeltaNu Inspector, electronic balance;
The iodate standard solution: precision takes the Potassiumiodate of 0.0122g dry 24h in baking oven, with ultrapure water, dissolves and moves in the 100mL volumetric flask, and be diluted to scale, and being mixed with concentration is 100mg L -1The Potassiumiodate storing solution, 4 ℃ of preservations, be diluted to desired concn before use; Azanol (0.02mol L -1) take the 0.1389g azanol, be dissolved in the 100mL aqueous solution, put in brown bottle and mix, 4 ℃ of preservations; Paranitroanilinum (0.02mol L -1): take the 0.2762g paranitroanilinum, be dissolved in 100mL hydrochloric acid solution (1mol L -1) in, after mixing, put in brown bottle 4 ℃ of preservations; Hydrochloride naphthodiamide (0.02mol L -1): take the 0.5183g hydrochloride naphthodiamide, be dissolved in the 100mL aqueous solution, put in brown bottle and mix, 4 ℃ of preservations; Au/SiO 2: Au NPs radius 55nm, SiO 2Shell thickness 1-2nm.Experimental water is ultrapure water.
1.2 sample preparation:
Take 0.25g iodized salt (being accurate to 0.0001g) in the 25mL volumetric flask, add the 15-20mL ultrapure water, shake up, be settled to 25mL.For the mark-on salt sample, analyzing, is 100mg L by 25 μ L concentration -1Iodate join in the 10mL salt sample, mix, mark-on concentration is 25 μ g g -1.
1.3 the drafting of typical curve
Compound concentration is 0.0075,0.010,0.030,0.050,0.075,0.10and0.13mg L respectively -1Iodate solution, get above-mentioned solution 200 μ L successively in the 2mL centrifuge tube, adds hydroxylamine solution 2 μ L, after mixing, adds paranitroanilinum hydrochloric acid solution 2 μ L, after mixing, continues to add hydrochloride naphthodiamide solution 2 μ L, after standing 1min.Get isopyknic above-mentioned reactant liquor and Au/SiO 2In sample hose, mix, with DeltaNu Raman instrument direct-detection, excitation wavelength 785nm, sweep time: 1s; Drawn 1138cm -1Raman shift place peak area-iodate ion content standard curve, be shown in Fig. 3.
1.4 the mensuration of interfering ion
The effects multiple common kation and negative ion to 0.1mg L -1The interference that iodate is measured, result is as shown in table 1.As add peak area (1138cm after interfering ion -1) RSD in ± 10%, be considered as the mensuration that this ion does not disturb iodate.As can be seen here, this method has good practicality to the mensuration of iodate.
Table 1
Figure BDA0000370349780000051
1.5 the mensuration of salt sample:
Measure the above-mentioned salt solution of 200 μ L, add hydroxylamine solution 2 μ L, after mixing, add the paranitroanilinum of 2 μ L and the hydrochloride naphthodiamide of 2 μ L, after mixing, after standing 1min.Get isopyknic above-mentioned reactant liquor and Au/SiO 2In sample hose, mix, with DeltaNu Raman instrument, detect, excitation wavelength: 785nm, sweep time: 1s, read 1138cm -1The peak area of Raman shift place, substitution 1138cm -1The peak area of Raman shift place-iodate content standard curve, calculate the content of Iodine in Table Salt acid group.The content that calculates the Iodine in Table Salt acid group is 39.33 ± 1.69 μ g g -1, after mark-on, the content of iodate is 66.12 ± 2.31 μ g g -1, recovery of standard addition is 107.1%.
Iodate in embodiment 2SERS fast detecting bottled water
In this application, the key instrument of using and reagent, the drafting of typical curve and the mensuration of interfering ion are identical with embodiment 1.
2.1 the processing of bottled water sample:
Measure the bottled water of certain volume, obtain the bottled water sample.Then by this bottled water sample preparation mark-on concentration, be 0.020mg L -1Mark-on bottled water sample.
2.2 the mensuration of bottled water sample:
Get bottled water sample and the mark-on bottled water sample of 200 μ L, add 2 μ L hydroxylamine solutions, after mixing, add the paranitroanilinum of 2 μ L and the hydrochloride naphthodiamide of 2 μ L, after mixing, after standing 1min.Get isopyknic above-mentioned reactant liquor and Au/SiO 2In sample hose, mix, with DeltaNu Raman instrument, detect, excitation wavelength: 785nm, sweep time: 1s, read 1138cm -1The peak area of Raman shift place, substitution 1138cm -1The peak area of Raman shift place-iodate content standard curve, calculate the content of iodate in bottled water.This method does not detect the existence of iodate in the bottled water sample, and after mark-on, the content of iodate is 0.022 ± 0.001mg L -1, recovery of standard addition is 109.1%.
Iodate in embodiment 3SERS fast detecting seawater
In this application, the key instrument of using and reagent, the drafting of typical curve and the mensuration of interfering ion are identical with embodiment 1.
3.1 the processing of seawater sample:
Measure the seawater of certain volume, after filtration, obtain seawater sample.Then by this seawater sample preparation mark-on concentration, be 0.020mg L -1The mark-on seawater sample.
3.2 the mensuration of seawater sample:
Get seawater sample and the mark-on seawater sample of 200 μ L,, add 2 μ L hydroxylamine solutions, after mixing, add the paranitroanilinum of 2 μ L and the hydrochloride naphthodiamide of 2 μ L, after mixing, after standing 1min.Get isopyknic above-mentioned reactant liquor and Au/SiO 2In sample hose, mix, with DeltaNu Raman instrument, detect, excitation wavelength: 785nm, sweep time: 1s, read 1138cm -1The peak area of Raman shift place, substitution 1138cm -1The peak area of Raman shift place-iodate content standard curve, calculate the content of iodate in seawater.This method does not detect the existence of iodate in seawater sample, and after mark-on, the content of iodate is 0.017 ± 0.001mg L -1, recovery of standard addition is 86.2%.
Be more than the application of SERS fast detecting iodate of the present invention in salt, bottled water and seawater moderate sample, can find out from embodiment, the method for this mensuration iodate of the present invention has the advantages such as simple, quick.
Those skilled in the art will be appreciated that, above embodiment illustrates the present invention, not as the restriction to invention, as long as in connotation scope of the present invention, all will drop in claim scope of the present invention variation, the sex change of the above embodiment.

Claims (10)

1. Surface enhanced raman spectroscopy fast detecting iodate method, it is characterized in that: iodate is oxidized to nitrite anions by azanol, nitrite ion and diazo reagent and azo reagent reacting generate diazonium-para-dye under acid condition, using this diazonium-para-dye as probe molecule, indirectly the iodate root is carried out to quantitative and qualitative analysis mensuration by measuring diazonium-para-dye.
2. method according to claim 1, it is characterized in that: at first iodate is oxidized to nitrite anions by azanol, and nitrite ion and paranitroanilinum and hydrochloride naphthodiamide generate red diazonium-para-dye under acid condition.
3. method according to claim 1 is characterized in that comprising the following steps:
A, get the iodate solution of variable concentrations in centrifuge tube, add azanol, after mixing, add diazo reagent, be mixed evenly and make it that diazo-reaction occur, after add and the azo reagent of diazo reagent with equimolar ratio, be mixed evenly and make it that coupling reaction occur, reactant liquor is placed 1min, obtains diazonium-para-dye;
B, get certain volume a step gained reactant liquor in sample hose, then add the enhancing mix particles of equal volume even, directly with the portable Raman instrument of DeltaNu, detect;
C, measure and draw out the corresponding Surface enhanced raman spectroscopy figure of different content iodate solution;
D, measure testing sample, add azanol to generate nitrite anions, add again diazo reagent, be mixed evenly and make it that diazo-reaction occur, after add and the azo reagent of diazo reagent with equimolar ratio, be mixed evenly and make it that coupling reaction occur, reactant liquor is placed 1min, obtains diazonium-para-dye; Add the enhancing mix particles of equal volume even, directly with the Raman instrument, detect the Surface enhanced raman spectroscopy of this sample, to sample, carry out qualitative according to the Raman shift in step c gained Raman spectrogram.
4. method according to claim 3, it is characterized in that: described diazo reagent is the paranitroanilinum hydrochloric acid solution; Described azo reagent is the aqueous solution of hydrochloride naphthodiamide; Described step c also comprises and draws out 1138cm -1The peak area of Raman shift place-iodate ion content standard curve; Described steps d also comprises according to 1138cm -1The peak area of Raman shift place-iodate ion content standard opisometer is calculated the content of iodate in sample.
5. method according to claim 4, is characterized in that: be 0.1-3.0mol L be used to the concentration of hydrochloric acid solution of preparing the paranitroanilinum hydrochloric acid solution -1Azanol concentration is 0.001-3.0mol L -1The concentration of hydrochloric acid solution of paranitroanilinum is 0.001-1.0mol L -1The concentration of aqueous solution of described hydrochloride naphthodiamide is 0.001-1.0mol L -1.
6. method according to claim 5, it is characterized in that: it is 100:(0.1~3.0 that described iodate solution adds volume and the ratio that adds volume of the hydrochloric acid solution of azanol and paranitroanilinum): (0.1~3.0); It is 100:(0.1~3.0 that described testing sample adds the hydrochloric acid solution of volume and azanol and paranitroanilinum to add the ratio of volume): (0.1~3.0).
7. method according to claim 1, diazo reagent can be paranitroanilinum, sulfanilamide (SN) and sulfanilic acid etc., azo reagent can be diphenylamine and hydrochloride naphthodiamide etc.
8. detection method according to claim 2, it is characterized in that: described enhancing particle is Au/SiO 2Nano sol, wherein Au/SiO 2For the Au nanoparticle surface, be coated with the core-shell type structure of silica shell, described enhancing particle can be also the Nano sols such as Ag Nano sol or Au etc.
9. detection method according to claim 4 is characterized in that: for Raman shift qualitatively, be respectively 1098,1138,1381 and 1426cm -1For quantitative Raman shift, be 1138cm -1, wherein 1098 is C-NO 2Stretching vibration, 1138cm -1For C-N=N stretching vibration, 1381cm -1C-C stretching vibration in phenyl ring, 1426cm -1For the N=N stretching vibration.
10. the application of the arbitrary described Surface enhanced raman spectroscopy fast detecting iodate method of claim 1~9 iodate content in measuring salt, potable water or environment.
CN2013103694946A 2013-08-22 2013-08-22 Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method Pending CN103411956A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2013103694946A CN103411956A (en) 2013-08-22 2013-08-22 Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2013103694946A CN103411956A (en) 2013-08-22 2013-08-22 Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method

Publications (1)

Publication Number Publication Date
CN103411956A true CN103411956A (en) 2013-11-27

Family

ID=49604983

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2013103694946A Pending CN103411956A (en) 2013-08-22 2013-08-22 Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method

Country Status (1)

Country Link
CN (1) CN103411956A (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103868907A (en) * 2014-01-24 2014-06-18 中国科学院长春光学精密机械与物理研究所 Method for preparing silica-coated surface-enhanced raman marker nanoparticles
CN104165881A (en) * 2014-08-25 2014-11-26 广西师范大学 Method for measuring IO3<-> by utilizing surface-enhanced Raman scattering spectrums
CN104777148A (en) * 2015-04-17 2015-07-15 华东理工大学 Method for rapidly detecting total protein in milk
CN105259158A (en) * 2015-11-13 2016-01-20 暨南大学 Surface enhanced Raman scattering immunochromatography test paper strip and preparation method and application
CN105372222A (en) * 2014-08-22 2016-03-02 中国科学院生态环境研究中心 Detection method of divalent heavy metal
CN108279228A (en) * 2018-05-04 2018-07-13 山东理工大学 A method of utilizing acetate ion concentration in the Raman spectroscopy acid solution of the silica dioxide granule containing methylene blue
CN111175241A (en) * 2020-03-09 2020-05-19 薛原 High-precision urine iodine detection method
CN114685311A (en) * 2020-12-29 2022-07-01 华中师范大学 Azo aromatic compound, application thereof and reagent for enhancing Raman scattering signals
CN116148410A (en) * 2022-12-23 2023-05-23 苏州大学 SERS substrate material for continuous TLC detection and preparation method and application thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102998298A (en) * 2012-12-13 2013-03-27 中山大学 Method for rapidly detecting nitrite by using surface enhanced Raman spectrum and application thereof

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102998298A (en) * 2012-12-13 2013-03-27 中山大学 Method for rapidly detecting nitrite by using surface enhanced Raman spectrum and application thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
李咏梅等: "对硝基苯胺— α-萘胺测定微量碘(V)", 《淮海工学院学报》 *

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103868907A (en) * 2014-01-24 2014-06-18 中国科学院长春光学精密机械与物理研究所 Method for preparing silica-coated surface-enhanced raman marker nanoparticles
CN105372222A (en) * 2014-08-22 2016-03-02 中国科学院生态环境研究中心 Detection method of divalent heavy metal
CN104165881A (en) * 2014-08-25 2014-11-26 广西师范大学 Method for measuring IO3<-> by utilizing surface-enhanced Raman scattering spectrums
CN104165881B (en) * 2014-08-25 2017-01-18 广西师范大学 Method for measuring IO3 by utilizing surface-enhanced Raman scattering spectrums
CN104777148A (en) * 2015-04-17 2015-07-15 华东理工大学 Method for rapidly detecting total protein in milk
CN105259158A (en) * 2015-11-13 2016-01-20 暨南大学 Surface enhanced Raman scattering immunochromatography test paper strip and preparation method and application
CN108279228A (en) * 2018-05-04 2018-07-13 山东理工大学 A method of utilizing acetate ion concentration in the Raman spectroscopy acid solution of the silica dioxide granule containing methylene blue
CN108279228B (en) * 2018-05-04 2020-12-08 山东理工大学 Method for measuring concentration of acetate ions in acidic solution by utilizing Raman spectrum of silica particles containing methylene blue
CN111175241A (en) * 2020-03-09 2020-05-19 薛原 High-precision urine iodine detection method
CN111175241B (en) * 2020-03-09 2020-09-18 刘宇娜 High-precision urine iodine detection method
CN114685311A (en) * 2020-12-29 2022-07-01 华中师范大学 Azo aromatic compound, application thereof and reagent for enhancing Raman scattering signals
CN114685311B (en) * 2020-12-29 2024-06-04 华中师范大学 Azo aromatic compound, application thereof and reagent for enhancing Raman scattering signal
CN116148410A (en) * 2022-12-23 2023-05-23 苏州大学 SERS substrate material for continuous TLC detection and preparation method and application thereof

Similar Documents

Publication Publication Date Title
CN103411956A (en) Method for rapidly detecting iodate by surface enhanced Raman spectroscopy and application of method
Chi et al. A simple, reliable and sensitive colorimetric visualization of melamine in milk by unmodified gold nanoparticles
Liu et al. Quantitative remote and on-site Hg2+ detection using the handheld smartphone based optical fiber fluorescence sensor (SOFFS)
CN102998298B (en) Surface enhanced raman spectroscopy detects nitrite anions method and application thereof fast
Jin et al. Determination of malachite green in environmental water using cloud point extraction coupled with surface-enhanced Raman scattering
CN103884669B (en) Detect preparation method and the application thereof of mercury ion nanometer silver probe
Zhang et al. Determination of cysteine, homocysteine, cystine, and homocystine in biological fluids by HPLC using fluorosurfactant‐capped gold nanoparticles as postcolumn colorimetric reagents
CN103837519A (en) A method of measuring a plurality of polychlorinated biphenyls by surface enhanced Raman spectroscopy
Cao et al. Highly sensitive ‘naked-eye’colorimetric detection of thiourea using gold nanoparticles
CN103926232A (en) Method for rapidly detecting formaldehyde through surface-enhanced Raman scattering, and its application
Xia et al. Improving the quantitative accuracy of surface-enhanced Raman spectroscopy by the combination of microfluidics with a multiplicative effects model
Zhang et al. Ultrasensitive detection of lead (II) ion by dark-field spectroscopy and glutathione modified gold nanoparticles
Chen et al. A homogeneous capillary fluorescence imprinted nanozyme intelligent sensing platform for high sensitivity and visual detection of triclocarban
CN108250133A (en) It is a kind of to be used to detect double probe materials of fluorescence-Raman of zinc ion and preparation method thereof
Páscoa et al. Spectrophotometric determination of zinc and copper in a multi-syringe flow injection analysis system using a liquid waveguide capillary cell: Application to natural waters
CN103487430B (en) A kind of trivalent aluminium ion detection reagent and detection method
Firdaus et al. Quantitative analysis of Cr (III) and Cr (VI) using gold nanoparticles with UV-vis spectrometry and smartphone colorimetric-sensing
CN109060768A (en) A method of based on Surface enhanced Raman spectroscopy trace detection erythrosine concentration
CN108982465A (en) Sulfur dioxide high throughput SERS online test method in wine
CN102890078B (en) Method for detecting phenanthroline by using surface-enhanced Raman spectroscopy
Chen et al. A novel and rapid approach to fluorescent automated Lab-In-Syringe sensing of ammonium
CN104165852A (en) Resonance Rayleigh scattering energy transfer spectroscopy method for determining fluorinion simply and rapidly
Guo et al. Real-time analysis of multicomponent dissolved inorganic carbon in the air-sea exchanging process using gas-liquid Raman spectroscopy
KR102613289B1 (en) Acetate complex and acetate quantification method
CN109001289A (en) The method of bipyridyl ruthenium system electrogenerated chemiluminescence method measurement nefopam hydrochloride

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20131127