WO2008056513A1 - Élément de détection d'ozone - Google Patents
Élément de détection d'ozone Download PDFInfo
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- WO2008056513A1 WO2008056513A1 PCT/JP2007/070260 JP2007070260W WO2008056513A1 WO 2008056513 A1 WO2008056513 A1 WO 2008056513A1 JP 2007070260 W JP2007070260 W JP 2007070260W WO 2008056513 A1 WO2008056513 A1 WO 2008056513A1
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- ozone
- dye
- detection element
- detection
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N31/00—Investigating or analysing non-biological materials by the use of the chemical methods specified in the subgroup; Apparatus specially adapted for such methods
- G01N31/22—Investigating or analysing non-biological materials by the use of the chemical methods specified in the subgroup; Apparatus specially adapted for such methods using chemical indicators
- G01N31/223—Investigating or analysing non-biological materials by the use of the chemical methods specified in the subgroup; Apparatus specially adapted for such methods using chemical indicators for investigating presence of specific gases or aerosols
- G01N31/224—Investigating or analysing non-biological materials by the use of the chemical methods specified in the subgroup; Apparatus specially adapted for such methods using chemical indicators for investigating presence of specific gases or aerosols for investigating presence of dangerous gases
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N21/00—Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
- G01N21/75—Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
- G01N21/77—Systems 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
- G01N21/78—Systems 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
- G01N21/783—Systems 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
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10T—TECHNICAL SUBJECTS COVERED BY FORMER US CLASSIFICATION
- Y10T436/00—Chemistry: analytical and immunological testing
- Y10T436/20—Oxygen containing
- Y10T436/206664—Ozone or peroxide
Definitions
- the present invention relates to an ozone sensing device (device) that detects ozone present in a gas such as the atmosphere.
- photochemical oxidants are mainly composed of strong and / or oxidizing substances such as ozone, and pollutants such as NO and hydrocarbons emitted from factories, offices, and automobiles are exposed to sunlight and exposed to photochemistry. It is produced by the reaction and causes photochemical smog.
- ozone has been attracting attention for its strong bactericidal power (oxidizing power) and the advantage that it does not produce harmful substances after being decomposed into oxygen, and is used in various industries such as water treatment, food sterilization, and paper bleaching.
- oxidizing power bactericidal power
- Use in the field is expanding.
- the standard value for lOOppb, 8 hours is set for the ozone concentration as the working environment standard.
- factories that use ozone It is necessary to manage the situation where each worker is working within the limits of labor standards, and this requires a measuring instrument that can be carried by the worker. Become.
- ozone gas measurement technologies such as a semiconductor gas sensor, a solid electrolyte gas sensor, an electrochemical gas sensor, and a quartz oscillation type gas sensor has been widely developed.
- these were developed to evaluate the response in a short time, and few were developed for monitoring that required accumulation of measurement data. Therefore, when it is necessary to accumulate measurement data, it is necessary to keep it operating at all times. For example, in the case of a semiconductor sensor, it is necessary to keep the detection unit at several hundreds of degrees Celsius, and a lot of electric power is always required to operate constantly.
- the above-described sensor since the above-described sensor has a detection sensitivity of about sub ppm, it cannot cope with the concentration in the actual environment, for example, measurement of lOppb ozone. Some semiconductor sensors react to the ozone of lOppb. The force detection output is non-linear with respect to the concentration, and the output value varies greatly from sensor to sensor. Is not easy. In many cases, the influence of other gases cannot be ignored.
- an ozone detection paper carrying starch and potassium iodide has been proposed as a simple and highly sensitive ozone analysis technique! (Reference 1: Japanese Patent No. 3257622).
- the technique according to Document 1 requires a pump for forcibly sucking the gas to be detected, a light source for measurement, and electric power for driving a detector composed of these.
- a special sheet-like carrier is required, and it is necessary to update the sheet for each measurement, so that cumulative measurement is not easy.
- the measurement using the detection paper has a problem of detecting all photochemical oxidants that are not ozone.
- the technique of Document 1 requires a pump and an optical system and is expensive, and the techniques of Document 2 and Document 3 have a problem in outdoor use under sunlight.
- the conventional technologies in References 2 and 3 enable measurement of the accumulated concentration of ozone gas by changing the color of the ozone detection paper or detection element.
- the technique of Document 1 has a problem that the cost of the apparatus is high, and the techniques of Documents 2 and 3 are limited to measuring ozone gas indoors, and outdoors such as detecting ozone by photochemical smog. The force that is not easy to measure.
- even when ozone is generated using ultraviolet rays! / It is not easy to measure the generated ozone gas.
- the present invention has been made to solve the above-described problems.
- the integrated amount from the start of measurement of ozone in the gas to be measured is easily detected and irradiated with ultraviolet rays.
- the ozone detection element includes a carrier composed of fibers, a detection component containing a pigment that is supported on the carrier and changes color when reacted with ozone gas, and a hydrophilic group supported on the carrier. And an ultraviolet absorber having The UV power applied to the carrier carrying the dye is carried simultaneously! And absorbed by the UV absorber. I will become.
- the ultraviolet absorber is carried on the carrier together with the detection component, the ultraviolet ray irradiated to the carrier carrying the dye is simultaneously carried on the ultraviolet ray. It will be absorbed by the absorbent.
- the present invention it is possible to easily detect the integrated amount of ozone in the gas to be measured and to detect ozone more accurately even in a state where ultraviolet rays are irradiated! If a sensing element can be provided! /, An excellent effect can be obtained.
- FIG. 1A to FIG. 1E are process diagrams for explaining an example of a method for manufacturing an ozone detecting element in an embodiment of the present invention.
- FIG. 2 is an explanatory diagram for explaining the action of the ultraviolet absorber.
- Fig. 3 shows that each ozone detector A to G is irradiated with ultraviolet rays in 1 minute increments for 1 to 5 minutes, and the reflected light of the ozone detector is measured with a spectrophotometer for each irradiation.
- the state of the influence of ultraviolet rays was evaluated using the change in the absorbance of the sample as an index. It is a characteristic view which shows this result.
- FIG. 4A is a characteristic diagram showing changes in absorbance when a predetermined amount of ozone gas is exposed to detection sheet B.
- FIG. 4B is a characteristic diagram showing the change in absorbance when a predetermined amount of ozone gas is exposed to detection sheet B.
- FIG. 5A is a characteristic diagram showing a change in absorbance when ozone detection sheet C is exposed to a predetermined amount of ozone gas.
- FIG. 5B is a characteristic diagram showing changes in absorbance when ozone detection sheet C is exposed to a predetermined amount of ozone gas.
- FIG. 6A is a characteristic diagram showing changes in absorbance when ozone detection sheet D is exposed to a predetermined amount of ozone gas.
- FIG. 6B is a characteristic diagram showing changes in absorbance when ozone detection sheet D is exposed to a predetermined amount of ozone gas.
- FIG. 1A to 1E are process diagrams for explaining an example of a method for manufacturing an ozone detection element in an embodiment of the present invention.
- the detection solution 101 is an aqueous solution in which a detection component including a dye that changes color (light absorption spectrum) by reacting with ozone gas, a moisturizing agent, and an ultraviolet absorber having a hydrophilic group are dissolved.
- Examples of the dye include indigo carmine (C H N Na O S) and indigo.
- the detection component is composed of the pigment and the acidic substance.
- the color (hue) changes and fades.
- the acidic substance does not react directly with ozone gas, but here it is assumed that it is included in the detection component as a component involved in the reaction between the dye and ozone gas.
- Azo dyes such as O S
- methyl orange C H N NaO S
- any anthraquinone dye having a hydroxy group is also applicable.
- this dye it is used as alkaline by an alkaline substance such as sodium hydroxide. Therefore, when using alizarin or the like as the dye, the detection component is composed of the dye and the alkaline substance.
- a dye having a polyene structure such as bixin such as an anato dye and norbixin is also applicable.
- bixin such as an anato dye and norbixin
- humectants include glycerin H 2 O), ethylene glycol (C H 2 O 3), and
- UV absorbers having a hydrophilic group include 2-hydroxy-4-methoxybenzophenone-15 sulfonic acid, 2-hydroxy-4-methoxybenzophenone-5 sodium sulfonate, and ferulic acid (4-hydroxy-3-methoxy). Cinnamic acid) is applicable. These ultraviolet absorbers are common in that they have a benzene ring in the skeleton.
- ferulic acid as described later, first, an ozone detecting element not containing an ultraviolet absorber is prepared, and then the ozone detecting element is dissolved in ferulic acid! Therefore, it is difficult to manufacture as compared with a water-soluble ultraviolet absorber.
- ferulic acid is a substance contained in rice bran and the like, as is well known, so it is highly safe.
- the detection solution 101 was indigo carmine 0.045g, 2 hydroxy mono 4-methoxy benzophenone 5 sulfonic acid trihydrate 0.8g, glycerin 12.5g and pure water was added to make a total of 50ml.
- Indigo carmine is a pigment having an indigo ring, and the detection solution 101 made acidic is in a blue state. Since indigo carmine is used as an acid, generally it can be used by adding citrate, acetic acid, etc. In the case of the above-mentioned configuration, it is acidic because 2 hydroxy-4-methoxybenzophenone-15 sulfonic acid is used. Therefore, other acidic substances such as citrate are not added.
- a carrier 103 having a predetermined size is prepared.
- the carrier 103 is formed into a sheet from fibers such as cell mouth, and is, for example, cellulose filter paper (No. 2) manufactured by Advantech (Toyo Filter Paper Co., Ltd.).
- the carrier 103 may be white, for example.
- the carrier 103 is not limited to a sheet shape, and may have other shapes.
- the carrier 103 may have a plate shape. As shown below, If the liquid 103 is impregnated and the dye and UV absorber are supported so as to be in contact with the gas to be detected.
- the prepared carrier 103 is immersed in the detection solution 101, for example, for 30 seconds.
- the impregnated carrier 104 is pulled up from the detection solution 101 and air-dried. After being air-dried to some extent, the impregnated carrier 104 is dried in dry nitrogen to evaporate a solvent (medium) such as moisture impregnated in the impregnated carrier 104 and dry it. For example, as shown in FIG. 1D, it is placed in a nitrogen gas stream inside a predetermined container 106 filled with circulating nitrogen gas, and this state is maintained for 24 hours or more to dry, so that sheet-like ozone Assume that the detection element 105 is formed.
- a solvent medium
- the ozone detecting element 105 formed in this way is in a state where a dye 111, an ultraviolet absorber 112 and a humectant 113 are supported.
- indigo carmine is used as the dye 111
- the obtained ozone detecting element 105 is in a state of exhibiting a color by the dye 111, and this color can be easily visually confirmed.
- the above-mentioned support means a state in which substances such as dyes, ultraviolet absorbers, and humectants are chemically, physically, or electrically bound to a carrier (base material), such as cellulose. It shows a state in which a dye is coated and / or impregnated on a sheet made of this fiber!
- the ozone detecting element 105 manufactured in this way is exposed to an environment where ozone exists, the color density of the dye gradually decreases with the exposure time, and finally the white state is obtained.
- the ozone detection element 105 is exposed to an environment where the ozone concentration is 0.04 ppm and 24 hours elapses, it becomes a slightly white state with a slight yellowishness S.
- other pigments there is a case where the color is almost lost and the color of the original filter paper (white) is obtained.
- the ozone detection element 105 it is possible to detect ozone by a color change, and it is possible to perform cumulative detection, in other words, to measure the integrated amount from the start of measurement. .
- This color change is thought to be due to fading according to the decomposition of dye 111 by ozone.
- the force that makes the carrier 103 white is not limited to this, and the carrier 103 is used. Any color that does not overlap the absorption wavelength in the visible region with the dye may be used.
- a yellow colored carrier filter paper
- the detection element is produced in a green state and changes to yellow by reacting with ozone.
- the ozone detection element 105 is formed by impregnating the detection solution 101 containing the humectant whose weight% is about 20, the humectant 113 is supported, Color change due to the presence of ozone (ozone detection ability) 1S is more effective.
- the humectant 113 it is considered that the reaction of fading due to ozone of the pigment in the ozone detecting element 105 is promoted.
- the concentration of the humectant in the detection solution is too high, for example, exceeding 50%, the time required for drying becomes enormous, making it difficult to produce a reproducible detection element.
- the ozone detection element 105 includes the ultraviolet absorber 112
- the influence of ultraviolet irradiation is suppressed.
- an ultraviolet absorber when an ultraviolet absorber is not used, exposure to solar light changes the color of the ozone detection element even when ozone is not present. This phenomenon is particularly noticeable when the ozone detection element is made using a moisturizing agent. In this case, even if ozone is not present, the irradiation of sunlight takes about 10 to several tens of minutes. When exposed, the color change can be visually confirmed. In this way, using an ultraviolet absorber, the ozone detector cannot detect ozone in an environment where ultraviolet rays are irradiated.
- ozone detection element 105 even if it is exposed to sunlight irradiation for about 10 minutes to several tens of minutes, fading is not confirmed at the visual level! Therefore, ozone can be detected even in an environment where ultraviolet rays are irradiated.
- the ozone detection element 105 carrying the ultraviolet absorber 112 is irradiated with ultraviolet rays and ozone acts.
- a water layer 105a is formed on the surface of the fiber 103a constituting the simple substance by the effect of the moisturizing agent 113, and the UV absorber 112 is present together with the pigment 111 in the water layer 105a.
- UV ultraviolet rays
- the ultraviolet absorber 112. oxygen that contributes to decomposition of the dye 111 Generation of radicals and direct dye degradation by ultraviolet rays are significantly reduced.
- ozone (O 2) is a gas, it is dissolved and diffused in the moisture layer 105a even if the ultraviolet absorber 112 is present. In addition, ozone is hardly consumed in reactions such as oxidative decomposition of the ultraviolet absorber 112. For this reason, most of ozone is dissolved and diffused in the moisture layer 105a, and is considered to act on the pigment 111 and decompose it as described above. Therefore, by allowing a predetermined amount of the ultraviolet absorber 112 to be present on the surface of the moisture layer 105a, it is possible to suppress the invasion of ultraviolet rays and to suppress the decomposition of the pigment 111 by ultraviolet rays in a state where ozone can enter. Become.
- sensing solution A was prepared by dissolving 0.05 g of indigo carmine, 3. Og of citrate, 12.5 g of glycerin and 12.5 g of glycerin in water to make the total volume 50 ml, and this sensing solution A was used to detect ozone sensing element A as described above. Is produced. This is a sample containing no UV absorber. The ozone detection element A is formed in a blue state.
- Og, quenic acid 3.5 g, and glycerin 12.5 g were dissolved in water to make detection solution C with a total volume of 50 ml.
- This detection solution C was used to install ozone detection element C as described above. Make it.
- the ozone detection element C is formed in a blue state.
- sodium 2-hydroxy-4-methoxybenzophenone-5 sodium sulfonate was prepared by dissolving an equimolar amount of 2-hydroxy 4-methoxybenzophenone 5-sulfonic acid.trihydrate and sodium hydroxide. It is obtained by drying this aqueous solution.
- a detection solution with a total solution volume of 50 ml was prepared by adding water and indigo strength noremin 0 ⁇ 045 g, quenate 3 ⁇ Og, and glycerin 1 ⁇ 5 g to a total volume of 50 ml.
- an ozone detector is manufactured. This detection solution is the same as the detection solution A described above, and the produced ozone detection element is the same as the ozone detection element A.
- an ultraviolet absorber solution in which 3.5 g of ferulic acid was dissolved in 50 ml of acetone was prepared. The ozone detector was immersed in the ultraviolet absorber solution for 10 seconds to impregnate the ozone detector with the ultraviolet absorber solution. The ozone detection element D impregnated with the wire absorbent solution is formed.
- the ozone detecting element D is pulled up from the ultraviolet absorbent solution and air-dried. After being air-dried to some extent, the ozone detection element D is dried in dry nitrogen to evaporate a solvent (medium) such as moisture impregnated in the ozone detection element D and dry it.
- a solvent medium
- FIG. 1 (d) it may be placed in a nitrogen gas stream inside a predetermined container 106 filled with circulating nitrogen gas, and this state may be kept for 24 hours or more and dried.
- an ultraviolet absorber solution in which 0.5 g of 4 dodecyloxy-2-hydroxybenzophenone was dissolved in 50 ml of acetone was produced, and the ozone detector element was immersed in the ultraviolet absorber solution for 10 seconds. And impregnated with an ultraviolet absorbent solution to form an ozone sensing element E impregnated with the ultraviolet absorbent solution. After this, the ozone detection element Lift child E from the UV absorber solution and dry as before.
- a detection solution with a total solution volume of 50 ml was prepared by adding water and indigo strength noremin 0 ⁇ 045 g, quenate 3 ⁇ Og, and glycerol 1 ⁇ 5 g to a total volume of 50 ml.
- an ozone detector is manufactured. This detection solution is the same as the detection solution A described above, and the produced ozone detection element is the same as the ozone detection element A.
- 2- (3,5 di-t-pentylene 2-hydroxyphenyl) 2H Benzotriazole 0.5 ⁇ 5 g of an ultraviolet absorber solution prepared in acetone 50 ml was prepared, and the ozone detecting element 1 was added to the ultraviolet absorber solution. Immerse for 0 seconds to impregnate the ozone detector element with the ultraviolet absorber solution, and then lift it from the ultraviolet absorber solution and dry it as described above to obtain the ozone detector element F.
- a detection solution with a total solution volume of 50 ml was prepared by adding water and indigo strength noremin 0 ⁇ 045g, quenate 3 ⁇ Og, and glycerin 1 ⁇ 5g to a total volume of 50 ml.
- an ozone detector is manufactured. This detection solution is the same as the detection solution A described above, and the produced ozone detection element is the same as the ozone detection element A.
- 2- (2-hydroxy-5- 1-butylphenyl) 2H Benzotriazole 0.5 g dissolved in 50 ml of acetone was prepared, and the ozone detector was immersed in this UV absorber solution for 10 seconds. Then, the ozone detecting element is impregnated with the ultraviolet absorbent solution, and then the ozone detecting element is pulled up from the ultraviolet absorbent solution and dried in the same manner as described above to obtain the ozone detecting element G.
- an ultraviolet exposure test for irradiating the ozone detection elements A to G described above with ultraviolet rays is performed.
- an artificial solar light XC-100AF manufactured by Celic Corporation was used with the UV filter removed.
- the incident angle of illumination light to each ozone detection element A to G is 20 °, and the distance from the lower end of the illuminating lamp to each ozone detection element A to G is 110 cm, and each ozone detection is in the strongest central part of the illumination light Elements A to G are arranged.
- Each of the ozone detection elements A to G described above was irradiated with ultraviolet rays in 1 minute increments for 1 to 5 minutes, and the reflected light of the ozone detection element was measured with a spectrophotometer for each irradiation, and the absorbance at a wavelength near 618 nm was measured. The state of the influence of ultraviolet rays was evaluated using the change as an index. The results are shown in Fig. 3.
- the result of ozone detection element A is indicated only by a solid line
- the result of ozone detection element B is indicated by a white circle
- the result of ozone detection element C is indicated by a white triangle
- the result of ozone detection element D is indicated by a white square
- the black circle indicates the result of the ozone detection element E
- the black triangle indicates the result of the ozone detection element F
- the black square indicates the result of the ozone detection element G.
- the irradiation amount of ultraviolet rays is assumed to be about 300 to 500 W'h / day at maximum on a fine weather day.
- the absorbance at a wavelength near 618 nm changes in proportion to the amount of UV exposure, and the absorbance is increased by 200 Wh UV irradiation.
- the absorbance at the wavelength of 618 nm of ozone detector A changes in proportion to the amount of ozone gas exposure, and the absorbance decreases by about 0.7 by exposure to ozone gas 640 ppb'h (humidity 60%).
- the absorbance change of ozone detector ⁇ ⁇ (no UV absorber) is 0.586, and absorbance of ozone detector B The change is 0.057, the absorbance change of the ozone detection element C is 0.047, and the absorbance change of the ozone detection element D is 0.057, both of which are 10% or less of the ozone detection element A.
- the ozone detection elements B to D exhibit a sufficient ultraviolet absorbing ability.
- the ozone detection element E, the ozone detection element F, and the ozone detection element G for comparison can reduce the influence of ultraviolet rays only by about 50%, and the necessary ultraviolet absorbing ability can be obtained.
- water-soluble ultraviolet rays having a hydrophilic group such as ozone detection elements B to D, are used. It is necessary to use a line absorber.
- 2Hydroxy-4-methoxybenzophenone 5 Sodium sulfonate and ferulic acid, when dissolved in a solvent and analyzed for the spectrum of transmitted light, are compared to those using other UV absorbers that are not water-soluble as described above. UV absorption is so high! For example, for 2-hydroxy-4-methoxybenzophenone 5 sulfonic acid 'trihydrate and 4-dodecyloxy-2-hydroxybenzophenone, 4-dodecyloxy-2-hydroxybenzophenone has a wavelength of 300-400 nm when equal amounts are added. In the region, the UV absorption capacity is high by an average of 1.25 times.
- 2-hydroxy-4-methoxybenzophenone 5 sulfonic acid 'trihydrate is 9.0 g for 50 ml of water
- 2 hydroxy-4-methoxybenzophenone-5 sodium sulfonate is 1.0 g for 50 ml of water
- Ferulic acid is added in an amount of 3.5 g per 50 ml of acetone, and even if it is used to make a sensing element, it precipitates in powder form I never did.
- the UV absorbent that is insoluble in water aggregates when the carrier is dried after impregnating the solution, and the UV absorbent collects on the surface where the solvent is volatilized and precipitates in a powder form. It is considered that the agent is not uniformly distributed and the ultraviolet absorption effect is not sufficiently exhibited. In addition, even when the UV absorber is not deposited in powder form on the surface of the carrier, the concentration becomes uneven, the concentration is low, and the UV absorbing ability of the site is sufficiently obtained! /, I think!
- the ultraviolet absorber having a certain degree of water solubility, it is held on the carrier! /, Glycerin or glycerin is held! /, Moisture, and the ultraviolet absorber.
- the hydrophilic group of the molecule binds.
- the carrier is cellulose, the hydroxyl group of cellulose and the hydrophilic group of the ultraviolet absorber molecule are bonded. For this reason, it is considered that the ultraviolet absorber aggregates when dried, and the ultraviolet absorber is uniformly held (supported) on the carrier, so that a sufficient ultraviolet absorption ability is exhibited.
- Ferulic acid is soluble in water to about 0.05 wt% and is also soluble in acetone.
- a method of dissolving in acetone and dispersing in ozone detection element D was used in order to add more ferulic acid than dissolved in water.
- Ultraviolet absorbing ability was obtained. Therefore, even when an amount of UV-absorbing agent that is soluble in water or more is added by the method for manufacturing the ozone detector D described above, it is uniform during drying as long as it has a water solubility of at least 0.05 wt% at 25 ° C. It can be seen that it is possible to hold the UV absorber.
- the ozone absorber is dissolved in the ozone detection element!
- the solvent that dissolves the UV absorber does not contain the UV absorber.
- the constituent elements of the zon detecting element may be a solvent in which the ultraviolet absorber is soluble without being eluted in a short time.
- ethyl acetate is also preferably used.
- ultraviolet absorbers are added to paints and resins, or dissolved in a liquid such as oil as in cosmetics, so once dissolved or uniformly dispersed in a solvent. From this point onward, the hydrophilic group contained in the UV absorber molecule is not important.
- a lyophilic group is essential. It becomes a component of Such a method of use is very different from a general method of using a UV absorber, and the present invention cannot be easily analogized.
- water-soluble UV absorbers include p-aminobenzoic acid (water-soluble 0.4 wt%), salicylate phenyl (water-soluble 0.05 wt%), and the like. It can be easily inferred that even if these are used, it will be possible to retain the UV absorber uniformly. These ultraviolet absorbers also have a benzene ring in the skeleton. As a measure of water solubility, 0.05 wt% or more of ferulic acid is a measure.
- the ultraviolet absorber having a hydrophilic group since the ultraviolet absorber having a hydrophilic group is used, it is uniformly distributed on the carrier without aggregating and absorbs ultraviolet rays. The effect of ultraviolet irradiation on the selected dye is suppressed, and the change in color due to ultraviolet light is very small compared to the change in dye (absorbance change) caused by ozone gas. As a result, according to the ozone detecting element according to the present embodiment, it is possible to detect ozone gas even in a situation where it is exposed to ultraviolet rays.
- the ozone detection element according to the present invention can be suitably used for detecting ozone generated from an apparatus that generates ozone by irradiating ultraviolet rays. Further, the ozone detecting element according to the present invention does not use electric power and can be easily carried by an individual.
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Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US12/444,845 US8084003B2 (en) | 2006-11-07 | 2007-10-17 | Ozone detecting device |
| CN200780039394XA CN101529244B (zh) | 2006-11-07 | 2007-10-17 | 臭氧检测装置 |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2006-301353 | 2006-11-07 | ||
| JP2006301353A JP4880425B2 (ja) | 2006-11-07 | 2006-11-07 | オゾン検知素子 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2008056513A1 true WO2008056513A1 (fr) | 2008-05-15 |
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/JP2007/070260 Ceased WO2008056513A1 (fr) | 2006-11-07 | 2007-10-17 | Élément de détection d'ozone |
Country Status (4)
| Country | Link |
|---|---|
| US (1) | US8084003B2 (ja) |
| JP (1) | JP4880425B2 (ja) |
| CN (1) | CN101529244B (ja) |
| WO (1) | WO2008056513A1 (ja) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2018007772A1 (fr) | 2016-07-08 | 2018-01-11 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Matrice nanoporeuse et son utilisation |
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| CN102156127A (zh) * | 2011-05-24 | 2011-08-17 | 南昌航空大学 | 基于碱性碘化钾比色法的高浓度臭氧分析方法 |
| US9244013B2 (en) * | 2012-06-29 | 2016-01-26 | Johnson & Johnson Vision Care, Inc. | Method of quantifying UV disinfecting doses applied to an ophthalmic lens using indicators |
| US9415126B2 (en) * | 2013-05-23 | 2016-08-16 | Sensor Electronic Technology, Inc. | Reflective transparent optical chamber |
| US10725002B2 (en) | 2016-11-03 | 2020-07-28 | Microsoft Technology Licensing, Llc | Chemical sensors for detection and display of environmental hazards |
| CN111751304B (zh) * | 2020-05-19 | 2023-04-14 | 北京交运通达环境科技有限公司 | 一种臭氧检测方法 |
| CN117074395A (zh) * | 2023-07-24 | 2023-11-17 | 郑州航空工业管理学院 | 一种臭氧浓度测量方法 |
| CN120177162A (zh) * | 2025-05-22 | 2025-06-20 | 北京海岸鸿蒙标准物质技术有限责任公司 | 一种臭氧检测用标准物质及其制备方法与应用 |
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| US20030165404A1 (en) * | 2000-06-05 | 2003-09-04 | Takeshi Omatsu | Ozone indicator and method of measuring ozone concentration |
| US6852281B2 (en) * | 2000-06-30 | 2005-02-08 | Sakura Color Products Corporation | Gas indicator and gas sensor sheet |
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- 2007-10-17 CN CN200780039394XA patent/CN101529244B/zh not_active Expired - Fee Related
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
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| WO2018007772A1 (fr) | 2016-07-08 | 2018-01-11 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Matrice nanoporeuse et son utilisation |
| FR3053602A1 (fr) * | 2016-07-08 | 2018-01-12 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Matrice nanoporeuse et son utilisation |
Also Published As
| Publication number | Publication date |
|---|---|
| US8084003B2 (en) | 2011-12-27 |
| CN101529244B (zh) | 2011-12-07 |
| JP2008116387A (ja) | 2008-05-22 |
| CN101529244A (zh) | 2009-09-09 |
| JP4880425B2 (ja) | 2012-02-22 |
| US20100074800A1 (en) | 2010-03-25 |
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