CN105675599B - A kind of photochemical method of recyclable detection nitrogen oxides - Google Patents

A kind of photochemical method of recyclable detection nitrogen oxides Download PDF

Info

Publication number
CN105675599B
CN105675599B CN201610041298.XA CN201610041298A CN105675599B CN 105675599 B CN105675599 B CN 105675599B CN 201610041298 A CN201610041298 A CN 201610041298A CN 105675599 B CN105675599 B CN 105675599B
Authority
CN
China
Prior art keywords
solution
concentration
nitrogen oxides
colourless
detection
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.)
Active
Application number
CN201610041298.XA
Other languages
Chinese (zh)
Other versions
CN105675599A (en
Inventor
李红波
李静
方海林
王伟
张喜标
潘志文
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.)
Yangcheng Institute of Technology
Original Assignee
Yangcheng Institute of Technology
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 Yangcheng Institute of Technology filed Critical Yangcheng Institute of Technology
Priority to CN201610041298.XA priority Critical patent/CN105675599B/en
Publication of CN105675599A publication Critical patent/CN105675599A/en
Application granted granted Critical
Publication of CN105675599B publication Critical patent/CN105675599B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N21/78Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator producing a change of colour
    • G01N21/783Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator producing a change of colour for analysing gases
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry

Landscapes

  • Physics & Mathematics (AREA)
  • Chemical & Material Sciences (AREA)
  • Pathology (AREA)
  • General Health & Medical Sciences (AREA)
  • Spectroscopy & Molecular Physics (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • Immunology (AREA)
  • General Physics & Mathematics (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Plasma & Fusion (AREA)
  • Investigating Or Analysing Materials By The Use Of Chemical Reactions (AREA)
  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)

Abstract

The present invention discloses a kind of photochemical method of recyclable detection nitrogen oxides, barium doping titanium dioxide nano crystalline substance solution is added in methylene blue solution and is sufficiently mixed and obtains mixed solution with water constant volume, then the optical filter of irradiation and use≤365nm wavelength filters under mercury lamp, it reacts under agitation, mixed solution takes off into colourless, obtains colourless light-catalyzed reaction system solution;The sodium nitrite standard solution of various concentration is added dropwise in above-mentioned colourless photocatalytic system solution;System becomes blue, is fitted concentration absorbance quantitative relationship equation;According to the concentration absorbance quantitative relationship equation drafted, the concentration of nitrogen oxides in sample to be tested is calculated.The detection method of the present invention has the characteristics that simple, easy to operate, at low cost;Acid photocatalytic system is constructed, detection sensitivity is high;The colourless retention time that light-catalyzed reaction system solution is placed in air is 15~30min, and accuracy is high;Recycle number >=45 time.

Description

A kind of photochemical method of recyclable detection nitrogen oxides
Technical field
The invention belongs to chemical analysis test fields, and in particular to a kind of photochemistry side of recyclable detection nitrogen oxides Method.
Background technology
Nitrogen oxides based on nitric oxide and nitrogen dioxide is the important original to form photochemical fog and acid rain Cause.Nitrogen oxides in vehicle exhaust irradiates the react toxic smog to be formed, referred to as light with hydrocarbon through ultraviolet light Chemical fumes.Photochemical fog has special odor, stimulates eyes, injures plant, and can reduce atmospheric visibility.In addition, Nitrogen oxides reacts the nitric acid of generation with the water in air and nitrous acid is the ingredient of acid rain.The main source of nitrogen oxides in air The conversion of nitrogenous compound in the burning of fossil fuel and the burning of plant and agricultural land soil and animal excrements.Greatly Gas is precious resources for the survival of mankind, and the destruction of Atmosphere environment resource is a kind of irreversible procedure, restores good air Quality pays more costs than Air Pollution prevention and control.It prevents and remedies pollution it is necessary to understand pollution first, correctly to understand dirt Contaminate object from where, what ingredient is, pollutant load how many, careful, conscientious and extensive investigations are made to everything After research, method and the measure of prevention can be just made, extensive environment measuring or monitoring will be carried out thus.With science skill The progress of art and the tremendous development of all kinds of subjects, substance detection means are also greatly enriched and are developed, accuracy of detection and There has also been qualitative leaps for reliability.At present, many gas detection methods have been derived according to the chemically and physically characteristic of gas.Such as Colorimetric method:It is much like that the measuring method and chemical test paper measure liquid pH value method.Gas is passed through during measurement and has solution examination In the colorimetric cylinder of agent, then it is tested gas and is chemically reacted with solution, solution colour can change in reaction process, different Gas concentration solution different colors can be presented, control color table can roughly estimate the concentration and type of gas.It should Measuring method applicability is very wide, but precision is relatively low, is suitable for some gas detections without particular instrument detection method;It is based on Semiconductor technology sensor:The operation principle of the sensor is the chemistry based on semi-conducting material, biology and physical characteristic.So It can be classified as chemical-sensitive semiconductor transducer, bio-sensing semiconductor transducer and physics sensitive semiconductor sensor.Its Available for the detection of imflammable gas, for certain pernicious gases, detection limit is up to ppm stratification levels;Electrochemical sensor:Electricity The principle of chemical sensor is based on tested gas generation oxidation or reduction reaction and generates the electricity directly proportional to gas concentration Signal.Electrochemical sensor mensuration be at present be applied to portable gas detector in detection pernicious gas it is most common and most into Ripe detection technique, its main feature is that it is small, power consumption is small, it is linear and reproducible, last a long time, but there are cross jamming disadvantages End;Non-dispersion infrared absorption process:According to tested gas to the absorption characteristic of infrared light, absorbed amount of infrared light is detected, i.e., The parameters such as the concentration of tested gas can be calculated.This method measuring range is big, and precision is high, and can measure multiple gases simultaneously, And there is no cross jamming effect, but involve great expense;The surface acoustic wave method and gas chromatography-mass spectrum that also latest developments are got up Combination method, quartz resonance gas sensor mensuration etc., above-mentioned measuring method all achieves certain effect.But due to quilt Survey gaseous species are various, and chemical property difference is very big, and a kind of instrument can be not only accurate, economical but also be quickly solved currently not yet The test problems of specific gas, it is desirable that have the higher response sensitivity even more extremely difficult to multiple gases.
Invention content
Goal of the invention:Present invention aims in view of the deficiencies of the prior art, provide a kind of structure simplicity, quick, Gao Ling The photochemical method of sensitivity, high specific and environmentally friendly recyclable detection nitrogen oxides.
Technical solution:A kind of photochemical method of recyclable detection nitrogen oxides of the present invention, it is characterised in that packet Include following steps:
(1) light-catalyzed reaction system solution is prepared:The barium doping titanium dioxide nano crystalline substance of a concentration of 18~40mg/mL is molten Liquid by volume 8~12:1 is added to and is sufficiently mixed in the methylene blue solution of 0.05mol/L~0.015mol/L and is determined with water Hold to 15mL~35mL and obtain mixed solution, above-mentioned mixed solution is then transferred to photocatalytic system, is irradiated simultaneously under mercury lamp It is filtered, reacted under agitation, mixed solution takes off into colourless after 3~10s, obtains colourless with the optical filter of≤365nm wavelength Light-catalyzed reaction system solution;
(2) oxides of nitrogen gas is passed through sodium hydroxide solution, generates the sodium nitrite standard solution of various concentration, and adjusted PH value is saved to neutrality, the salting liquid of the normal concentration is added dropwise in above-mentioned colourless light-catalyzed reaction system solution, the system Moment becomes au bleu, and the absorption spectrum change curve of solution, is then fitted concentration-absorbance quantitative relationship after detection each group becomes basket Equation;
(3) according to the concentration-absorbance quantitative relationship equation drafted, the concentration of nitrogen oxides in sample to be tested is calculated.
Further, the volume of barium doping titanium dioxide nano crystalline substance solution described in step (1) is 300~700 μ L.
Further, the power of mercury lamp described in step (1) is 300~500W.
In this method, the colourless retention time that step (1) the light-catalyzed reaction system solution is placed in air is 15 ~30min.
Further, a concentration of 0.8~1.2mmol L of sodium hydroxide described in step (2)-1
Further, to avoid interference of the dissolved oxygen to test system, before detection to the colourless light-catalyzed reaction System solution and the salting liquid of the neutrality advertise method using nitrogen and remove dissolved oxygen.
Further, for gas is avoided to flow through havoc light-catalyzed reaction system solution and prevents letting nitrogen in and deoxidizing overlong time Solution becomes blue again, influences testing result, and the air velocity that the nitrogen advertises nitrogen in method is controlled in 300~700ml min-1 In the range of.
In this method, the light-catalyzed reaction system solution recycles number >=45 time.
Advantageous effect:(1) present invention is, selection nanocrystalline based on ultraviolet excitation functional form barium doped nano titanium dioxide Property real estate third contact of a total solar or lunar eclipse electronics, is quickly restored to colourless reduced form methylene blue by blue methylene blue solution, is added dropwise in this system The sodium hydroxide neutral salt solution of nitrogen oxides, colourless reduced form methylene blue solution momentary recovery blue, nitrogen oxides Concentration is bigger, and blue is deeper, measures the concentration of nitrogen oxides accordingly, which has the spies such as simple, easy to operate, at low cost Point;(2) this method, which constructs acid photocatalytic system, is beneficial to the raising of nitrogen oxides, and further improve photochemical The detection sensitivity of method;(3) the colourless retention time that light-catalyzed reaction system solution is placed in air in this method is 15 ~30min, time period carry out the measure of nitrous oxides concentration enough, avoid detecting caused by system self-recovery blue Error, it is ensured that the accuracy of detection;(4) this method using the methylene blue that is easy to switch between oxidation state and reduction-state as Probe and beacon, this detection architecture can be recycled, coloration can 100% recovery, recycle number >=45 time, improve light and urge The recycling number of agent reduces testing cost.
Description of the drawings
Fig. 1 is the structure schematic diagram that nitrogen oxides photochemical method detects in the present invention;
Fig. 2 is the abosrption spectrogram before and after light-catalyzed reaction system solution light color in embodiment 1;Wherein a is ultraviolet Abosrption spectrogram before illumination, b are the abosrption spectrogram after ultraviolet lighting;
Fig. 3 is that reduction-state methylene blue colourless in embodiment 1 restores to absorb light to the time change of the oxidation state of blue Spectrogram;
Fig. 4 is the absorption spectrum change curve changed in embodiment 1 with sodium nitrite concentration of standard solution;Illustration is fitting Concentration afterwards-absorbance quantitative relationship curve, the concentration of Sodium Nitrite standard solution are followed successively by 0.05,0.1,0.5,1,5, 25,50 μm of ol L-1
Fig. 5 is common gas in embodiment 1 to the interference block diagram of detection architecture;Wherein, interference gas is 10 times of oxygen Gas, 100 times of sulfur dioxide, 1000 times of carbon monoxide, carbon dioxide, nitrogen, hydrogen sulfide;
Fig. 6 is cycle-index-absorbance figure of light-catalyzed reaction detection architecture in embodiment 1.
Specific embodiment
Technical solution of the present invention is described in detail below by attached drawing, but protection scope of the present invention is not limited to The embodiment, method is conventional method unless otherwise specified in embodiment, and the reagent used is normal unless otherwise specified It advises commercially available.
Embodiment 1:
(1) light-catalyzed reaction system solution is prepared:By 500 μ L, the barium doping titanium dioxide nano crystalline substance solution of 28.5mg/mL It is added in the methylene blue solution of 50 μ L, 0.01mol/L to be sufficiently mixed and be settled to 25mL with water and obtains mixed solution, then Above-mentioned mixed solution is transferred to photocatalytic system, irradiated under 300W mercury lamps and is filtered with the optical filter of 365nm wavelength, is being stirred It is reacted under the conditions of mixing, mixed solution takes off into colourless after 5s, obtains colourless light-catalyzed reaction system solution;Take the light that part is colourless Catalystic converter system solution observes its color-recovering time, and timing measures the change curve of m- trap at that time;
(2) oxides of nitrogen gas is passed through 1mmol L-1Sodium hydroxide solution, generate the sodium nitrite mark of various concentration Quasi- solution, and pH value is adjusted to neutrality, the concentration of sodium nitrite standard solution is respectively 0.05,0.1,0.5,1,5,25,50 μ mol L-1, first progress nitrogen is advertised respectively for salting liquid and colourless light-catalyzed reaction system solution to the neutrality, removes solution Interior dissolved oxygen, nitrogen flow rate is 500ml min during nitrogen is advertised-1, then salting liquid is added dropwise to colourless photocatalysis In reaction system solution, which becomes au bleu, and the absorption spectrum change curve of solution, then intends after detection each group becomes basket Close concentration-absorbance quantitative relationship equation;
(3) according to the concentration-absorbance quantitative relationship equation drafted, the concentration of nitrogen oxides in sample to be tested is calculated.
Fig. 1 is the structure schematic diagram that nitrogen oxides photochemical method detects in the present invention, and this method is based on ultraviolet excitation Functional form barium doped nano titanium dioxide is nanocrystalline, selectively generates photoelectron, quickly restores blue methylene blue solution To colourless reduced form methylene blue, using being not easy to restore after colour fading to the principle of former blue, we construct photochemical method detection The sodium hydroxide neutral salt solution of nitrogen oxides, colourless reduced form methylene is added dropwise in the new method of nitrogen oxides in this system Blue solution momentary recovery blue, the concentration of nitrogen oxides is bigger, and blue is deeper, measures the concentration of nitrogen oxides accordingly;
Fig. 2 is the abosrption spectrogram before and after light-catalyzed reaction system solution light color in the present embodiment;Wherein a is ultraviolet Abosrption spectrogram before illumination, b are the abosrption spectrogram after ultraviolet lighting;As can be seen from Figure, it is penetrated by outer illumination Before catalysis, the light absorption to 400~700nm wave bands of mixed solution is apparent, with significantly absorption peak, solution show as indigo plant Color;By after ultraviolet light is catalyzed, mixed solution becomes colorless, the mixed solution pair after illumination it can be seen from curve b The light of 400~700nm wave bands does not absorb substantially, thus proves, and after ultraviolet catalytic irradiates, mixed solution do not absorb 400~ The light of 700nm wave bands, becomes colorless;
Fig. 3 is that reduction-state methylene blue colourless in the present embodiment restores to absorb light to the time change of the oxidation state of blue Spectrogram;Reduction in Air state methylene blue need to can just be fully returned to primitive color through 480min as can be seen from Figure, preceding 20min does not see its color change visually, and nitrogen oxides can fully be reacted with reduction-state methylene blue very much in 20 minutes, So as to avoid influence of the oxygen to test system in air;
Fig. 4 is the absorption spectrum change curve changed in the present embodiment with sodium nitrite concentration of standard solution;Illustration is intends Concentration-absorbance quantitative relationship curve after conjunction, the concentration of Sodium Nitrite standard solution are followed successively by 0.05,0.1,0.5,1, 5,25,50 μm of ol L-1;By test result, the raising of solution absorbance sodium nitrite concentration of standard solution linearly improves, according to Each test point can be fitted concentration-absorbance quantitative relationship equation.
Fig. 5 is common gas in the present embodiment to the interference block diagram of detection architecture;In order to prove the selectivity of this method, We have investigated interference of the component common in flue gas to the detection architecture, the results showed that, 10 times of oxygen, 100 times of dioxy Change sulphur, 1000 times of carbon monoxide, carbon dioxide, nitrogen, hydrogen sulfide do not form this detection architecture interference, and this method is with excellent Good selectivity.
Fig. 6 is cycle-index-absorbance figure of light-catalyzed reaction detection architecture in embodiment 1, the results showed that 45 cycles Still close to 100%, this method has excellent stability for the recovery of methylene blue absorbance afterwards.
Embodiment 2:
(1) light-catalyzed reaction system solution is prepared:By 300 μ L, the barium doping titanium dioxide nano crystalline substance solution of 18.5mg/mL It is added in the methylene blue solution of 40 μ L, 0.005mol/L to be sufficiently mixed and be settled to 15mL with water and obtains mixed solution, so Above-mentioned mixed solution is transferred to photocatalytic system afterwards, irradiated under 350W mercury lamps and is filtered with the optical filter of 254nm wavelength, It is reacted under stirring condition, mixed solution takes off into colourless after 8s, obtains colourless light-catalyzed reaction system solution;Take part colourless Light-catalyzed reaction system solution observes its color-recovering time, and timing measures the change curve of m- trap at that time;
(2) oxides of nitrogen gas is passed through 0.8mmol L-1Sodium hydroxide solution, generate the sodium nitrite of various concentration Standard solution, and pH value is adjusted to neutrality, the concentration of sodium nitrite standard solution is respectively 0.05,0.1,0.5,1,5,25,50 μ mol L-1, first progress nitrogen is advertised respectively for salting liquid and colourless light-catalyzed reaction system solution to the neutrality, removes solution Interior dissolved oxygen, nitrogen flow rate is 300ml min during nitrogen is advertised-1, then salting liquid is added dropwise to colourless photocatalysis In reaction system solution, which becomes au bleu, and the absorption spectrum change curve of solution, then intends after detection each group becomes basket Close concentration-absorbance quantitative relationship equation;
(3) according to the concentration-absorbance quantitative relationship equation drafted, the concentration of nitrogen oxides in sample to be tested is calculated.
Obtained colourless light-catalyzed reaction system solution is after air is placed 25 minutes in the present embodiment, solution colour Ability and sagacity becomes micro- blue, needs just can completely to become for 510 minutes former blue, and methylene blue absorbance after cycle detection 46 times Recovery still close to 100%.
Embodiment 3:
(1) light-catalyzed reaction system solution is prepared:By 700 μ L, the barium doping titanium dioxide nano crystalline substance solution of 38.5mg/mL It is added in the methylene blue solution of 60 μ L, 0.015mol/L to be sufficiently mixed and be settled to 35mL with water and obtains mixed solution, so Above-mentioned mixed solution is transferred to photocatalytic system afterwards, irradiated under 500W mercury lamps and is filtered with the optical filter of 365nm wavelength, It is reacted under stirring condition, mixed solution takes off into colourless after 10s, obtains colourless light-catalyzed reaction system solution;Take part colourless Light-catalyzed reaction system solution observe its color-recovering time, and timing measures the change curve of m- trap at that time;
(2) oxides of nitrogen gas is passed through 1.2mmol L-1Sodium hydroxide solution, generate the sodium nitrite of various concentration Standard solution, and pH value is adjusted to neutrality, the concentration of sodium nitrite standard solution is respectively 0.05,0.1,0.5,1,5,25,50 μ mol L-1, first progress nitrogen is advertised respectively for salting liquid and colourless light-catalyzed reaction system solution to the neutrality, removes solution Interior dissolved oxygen, nitrogen flow rate is 700ml min during nitrogen is advertised-1, then salting liquid is added dropwise to colourless photocatalysis In reaction system solution, which becomes au bleu, and the absorption spectrum change curve of solution, then intends after detection each group becomes basket Close concentration-absorbance quantitative relationship equation;;
(3) according to the concentration-absorbance quantitative relationship equation drafted, the concentration of nitrogen oxides in sample to be tested is calculated.
Obtained colourless light-catalyzed reaction system solution is after air is placed 15 minutes in the present embodiment, solution colour Ability and sagacity becomes micro- blue, needs just can completely to become for 460 minutes former blue, and methylene blue absorbance after cycle detection 45 times Recovery still close to 100%.
As described above, although the present invention has been represented and described with reference to specific preferred embodiment, must not explain For to the limitation of itself of the invention.It, can be right under the premise of the spirit and scope of the present invention that appended claims define are not departed from Various changes can be made in the form and details for it.

Claims (7)

1. a kind of photochemical method of recyclable detection nitrogen oxides, it is characterised in that include the following steps:
(1) by the barium doping titanium dioxide nano crystalline substance solution of a concentration of 18~40mg/mL by volume 8~12:1 is added to Be sufficiently mixed in the methylene blue solution of 0.05mol/L~0.015mol/L and with water be settled to 15mL~35mL obtain mixing it is molten Then above-mentioned mixed solution is transferred to photocatalytic system by liquid, the optical filter of the irradiation and use≤365nm wavelength filter under mercury lamp Light reacts under agitation, and mixed solution takes off into colourless after 3~10s, obtains colourless light-catalyzed reaction system solution;
(2) oxides of nitrogen gas is passed through sodium hydroxide solution, generates the sodium nitrite standard solution of various concentration, and adjust pH The salting liquid of the normal concentration is added dropwise in above-mentioned colourless light-catalyzed reaction system solution, the system moment by value to neutrality Become au bleu, the absorption spectrum change curve of solution, is then fitted concentration-absorbance quantitative relationship side after detection each group becomes basket Journey;
(3) according to the concentration of fitting-absorbance quantitative relationship equation, the concentration of nitrogen oxides in sample to be tested is calculated.
2. the photochemical method of recyclable detection nitrogen oxides according to claim 1, it is characterised in that:In step (1) The volume of the barium doping titanium dioxide nano crystalline substance solution is 300~700 μ L.
3. the photochemical method of recyclable detection nitrogen oxides according to claim 1, it is characterised in that:In step (1) The power of the mercury lamp is 300~500W.
4. the photochemical method of recyclable detection nitrogen oxides according to claim 1, it is characterised in that:In step (2) A concentration of 0.8~1.2mmol L of the sodium hydroxide-1
5. the photochemical method of recyclable detection nitrogen oxides according to claim 1, it is characterised in that:It is right before detection The colourless light-catalyzed reaction system solution and the salting liquid of the neutrality advertise method using nitrogen and remove dissolved oxygen.
6. the photochemical method of recyclable detection nitrogen oxides according to claim 5, it is characterised in that:The nitrogen drum The air velocity for blowing nitrogen in method is 300~700ml min-1
7. the photochemical method of recyclable detection nitrogen oxides according to claim 1, it is characterised in that:Step (1) institute That states light-catalyzed reaction system solution recycles number >=45 time.
CN201610041298.XA 2016-01-21 2016-01-21 A kind of photochemical method of recyclable detection nitrogen oxides Active CN105675599B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610041298.XA CN105675599B (en) 2016-01-21 2016-01-21 A kind of photochemical method of recyclable detection nitrogen oxides

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610041298.XA CN105675599B (en) 2016-01-21 2016-01-21 A kind of photochemical method of recyclable detection nitrogen oxides

Publications (2)

Publication Number Publication Date
CN105675599A CN105675599A (en) 2016-06-15
CN105675599B true CN105675599B (en) 2018-07-03

Family

ID=56301956

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610041298.XA Active CN105675599B (en) 2016-01-21 2016-01-21 A kind of photochemical method of recyclable detection nitrogen oxides

Country Status (1)

Country Link
CN (1) CN105675599B (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101655449A (en) * 2008-08-20 2010-02-24 鸿富锦精密工业(深圳)有限公司 Device for measuring catalytic performance of photocatalyst
CN102295310A (en) * 2010-06-28 2011-12-28 中国科学院理化技术研究所 Preparation method of metal-ion-doped titanium dioxide transparent aqueous sol
CN102519926A (en) * 2011-12-09 2012-06-27 厦门大学 Application of rhodamine B derivative in nitrite ion detection
US8951722B1 (en) * 2013-11-04 2015-02-10 Allied Innovative Systems Llc Methods for improving analyte detection using photochemical reactions

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101655449A (en) * 2008-08-20 2010-02-24 鸿富锦精密工业(深圳)有限公司 Device for measuring catalytic performance of photocatalyst
CN102295310A (en) * 2010-06-28 2011-12-28 中国科学院理化技术研究所 Preparation method of metal-ion-doped titanium dioxide transparent aqueous sol
CN102519926A (en) * 2011-12-09 2012-06-27 厦门大学 Application of rhodamine B derivative in nitrite ion detection
US8951722B1 (en) * 2013-11-04 2015-02-10 Allied Innovative Systems Llc Methods for improving analyte detection using photochemical reactions

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
亚甲基蓝催化光度法测定亚硝酸盐;王海燕 等;《食品与机械》;20080531;第24卷(第3期);第94-95页 *
催化光度法测定痕量亚硝酸根的研究及在食品中的应用;严小平 等;《食品科学》;20051231;第26卷(第12期);第189-190页 *
基于TiO2异质结在光电化学传感领域的应用;薛延 等;《盐城工学院学报(自然科学版)》;20140630;第27卷(第2期);第73-78页 *
磁载光催化剂Ba2+-TiO2/SiO2-NiFe2O4的制备及光催化性能;夏淑梅 等;《化工环保》;20091231;第29卷(第3期);第274-278页 *
纳米TiO2光催化降解亚甲基蓝;邱克辉 等;《矿物盐岩石》;20071231;第27卷(第4期);第13-16页 *

Also Published As

Publication number Publication date
CN105675599A (en) 2016-06-15

Similar Documents

Publication Publication Date Title
Mikuška et al. Simultaneous determination of nitrite and nitrate in water by chemiluminescent flow-injection analysis
Randviir et al. The latest developments in quantifying cyanide and hydrogen cyanide
Zhang et al. A highly selective chemiluminescent H2S sensor
Petruci et al. Portable and disposable paper-based fluorescent sensor for in situ gaseous hydrogen sulfide determination in near real-time
Freiberg Effects of relative humidity and temperature on iron-catalyzed oxidation of sulfur dioxide in atmospheric aerosols
CN105928914B (en) The qualitative checking method of sulfurated hydrogen detection sensor and preparation method thereof, the quantitative detecting method of hydrogen sulfide and intracellular hydrogen sulfide
Lu et al. Flow-injection chemiluminescent determination of nitrite in water based on the formation of peroxynitrite from the reaction of nitrite and hydrogen peroxide
Pungjunun et al. Electrochemical detection of NOx gas based on disposable paper-based analytical device using a copper nanoparticles-modified screen-printed graphene electrode
Felix et al. A new fluorescence method for determination of ozone in ambient air
CN110987843B (en) Phosphate radical colorimetric detection method based on bimetallic MOF nano-oxidase
CN104267026A (en) Mercury-ion detection method simulating peroxidase based on nano platinum and kit
Yan et al. Carbon dots for ratiometric fluorescence detection of morin
Ma et al. A turn-on fluorescent probe for selective and sensitive detection of hydrogen sulfide
Yavarinasab et al. A selective polypyrrole-based sub-ppm impedimetric sensor for the detection of dissolved hydrogen sulfide and ammonia in a mixture
Chen et al. A poly (thymine)-templated fluorescent copper nanoparticle hydrogel-based visual and portable strategy for an organophosphorus pesticide assay
Nejad et al. Wide color-varying visualization of sulfide with a dual emissive ratiometric fluorescence assay using carbon dots and gold nanoclusters
Wang et al. Fluorescent detection of S2− based on ZnMOF-74 and CuMOF-74
Yin et al. Determination of sulfite in water samples by flow injection analysis with fluorescence detection
CN109520946A (en) Sub- cerium ion measuring method based on nanogold Mimetic enzyme
CN105675599B (en) A kind of photochemical method of recyclable detection nitrogen oxides
Bartelmess et al. Development of a “Turn-on” Fluorescent Probe-Based Sensing System for Hydrogen Sulfide in Liquid and Gas Phase
JP2812745B2 (en) Chemiluminescence determination of ammonia and its device
CN106525806A (en) Method for detecting ethrel by using fluorescent nitrogen doped carbon quantum dot
Toda et al. Gas analyzer for continuous monitoring of trace level methanethiol by microchannel collection and fluorescence detection
CN110128389A (en) It is a kind of detect sulfur dioxide reversible fluorescence probe and its application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant