WO2005096359A1 - Method of ozone water supply and ozone water supply apparatus - Google Patents

Method of ozone water supply and ozone water supply apparatus Download PDF

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Publication number
WO2005096359A1
WO2005096359A1 PCT/JP2005/005632 JP2005005632W WO2005096359A1 WO 2005096359 A1 WO2005096359 A1 WO 2005096359A1 JP 2005005632 W JP2005005632 W JP 2005005632W WO 2005096359 A1 WO2005096359 A1 WO 2005096359A1
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WO
WIPO (PCT)
Prior art keywords
ozone
ozone water
water
concentration
gas
Prior art date
Application number
PCT/JP2005/005632
Other languages
French (fr)
Japanese (ja)
Inventor
Takeo Fukui
Junichi Ida
Hiroshi Morita
Original Assignee
Kurita Water Industries Ltd.
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Filing date
Publication date
Application filed by Kurita Water Industries Ltd. filed Critical Kurita Water Industries Ltd.
Priority to KR1020067021257A priority Critical patent/KR101161904B1/en
Publication of WO2005096359A1 publication Critical patent/WO2005096359A1/en

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B08CLEANING
    • B08BCLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
    • B08B3/00Cleaning by methods involving the use or presence of liquid or steam
    • B08B3/04Cleaning involving contact with liquid
    • B08B3/08Cleaning involving contact with liquid the liquid having chemical or dissolving effect
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B13/00Oxygen; Ozone; Oxides or hydroxides in general
    • C01B13/10Preparation of ozone
    • CCHEMISTRY; METALLURGY
    • C03GLASS; MINERAL OR SLAG WOOL
    • C03CCHEMICAL COMPOSITION OF GLASSES, GLAZES OR VITREOUS ENAMELS; SURFACE TREATMENT OF GLASS; SURFACE TREATMENT OF FIBRES OR FILAMENTS MADE FROM GLASS, MINERALS OR SLAGS; JOINING GLASS TO GLASS OR OTHER MATERIALS
    • C03C23/00Other surface treatment of glass not in the form of fibres or filaments
    • C03C23/0075Cleaning of glass
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B08CLEANING
    • B08BCLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
    • B08B2203/00Details of cleaning machines or methods involving the use or presence of liquid or steam
    • B08B2203/005Details of cleaning machines or methods involving the use or presence of liquid or steam the liquid being ozonated
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/34Treatment of water, waste water, or sewage with mechanical oscillations
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/34Treatment of water, waste water, or sewage with mechanical oscillations
    • C02F1/36Treatment of water, waste water, or sewage with mechanical oscillations ultrasonic vibrations
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/78Details relating to ozone treatment devices
    • C02F2201/782Ozone generators
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/23O3

Definitions

  • the present invention relates to an ozone water supply method and an ozone water supply device. More specifically, the present invention relates to an ozone solution capable of stably supplying ozone water having a predetermined ozone concentration to a use point in an etching process, a surface treatment process, or the like of an electronic material such as a body or a liquid crystal. Water supply and ozone water supply. Background scythe
  • Ozone water with ozone dissolved in fek exhibits extremely strong and oxidizing power even though the amount of fertilizer is a few mg / L, and impurities such as organic substances and metals attached to the electronic material surface
  • the process has been shifted to the process of removing contamination due to oxidization and the process of uniformly oxidizing the surface of silicon II to form an oxidized surface. Since the concentration of the supplied ozone water affects the m-plane »power and the control of acidity, it is very important to control the concentration.
  • an ozone dissolving device that dissolves ozone in the water to be dissolved
  • a water supply pipe that supplies the water to be dissolved to the dissolving device
  • a fast-acting device In the water supply device having a delivery pipe for delivering water, a water supply pipe is provided at an arbitrary position from the yarn ⁇ K pipe to the delivery pipe, asatsu, asia M ⁇ , carbonic acid, charcoal, ⁇ ,
  • One or more ozone components selected from the group consisting of sulfurous acid, sulfurous acid, and hydrazine an ozone-dissolved water supply device provided with a supply device that excites the inhibitor (Patent Document 2).
  • the concentration of ozone water in which ozone is dissolved in ii ⁇ is used as the concentration of ozone water that can easily provide the required concentration of ozone water.
  • ⁇ Kffi length, calorie temperature, ultrasonic wave, ultraviolet light or turbulence promotes ozone decomposition, and the ozone water concentration adjustment method to haze ozone water concentration is $ ⁇ Patent Document 3)
  • ozone-containing water is woven with glass, and the ozone-containing water having a desired concentration is mixed with ozone-containing water.
  • Patent Document 4 The fS & ⁇ method of the degree of oscillosis has been tested (Patent Document 4).
  • Patent Document 3 Japanese Patent Application Laid-Open No. 2000-1808043 (pages 2-3)
  • Patent Document 4 Japanese Patent Application Laid-Open No. 2000-330334 (page 2)
  • the present invention provides an ozone water supply system that can stably supply ozone water having a predetermined ozone concentration to a use point in an ejection process and a surface treatment process of an electronic material such as a liquid crystal and a liquid crystal.
  • the purpose is to remove and supply ozone water. Disclosure of the invention
  • the inventors of the present invention have made intensive efforts to solve the above, and as a result, transferred highly concentrated ozone water in which an ozone suppressing substance was present to a use point, and returned to the use point by a concentration adjusting means.
  • the present inventors have found that by reducing the ozone concentration to a predetermined value, it is possible to stably supply ozone water of a predetermined ozone level to a youth bottle, and based on this finding, completed the present invention.
  • Ozone water supplied with ozone-suppressed substances is transported to youth bottles, placed near the youth bottles, and ii. ,
  • the anti-drought substance is derived from a water-soluble arizide compound, maleic acid or its: ⁇ 3 ⁇ 4 ⁇ hydrazine
  • Oranj ⁇ is ozone water supply according to (2),
  • the amount of dissolved ozone is selected from the group consisting of ultrasonic irradiation, ultraviolet irradiation, tongue generation, « ⁇ , warming, alkali addition, and peroxygen b ⁇ element addition.
  • Ozone water supply method of 53 ⁇ 4 is selected from the group consisting of ultrasonic irradiation, ultraviolet irradiation, tongue generation, « ⁇ , warming, alkali addition, and peroxygen b ⁇ element addition.
  • Ozone dissolving device for dissolving ozone gas in yarn fcR to prepare ozone water, means for supplying an ozone dissolution inhibiting substance to ttft3 ⁇ 43 ⁇ 47_k or tiff self-ozone water, ozone water prepared using a self-contained zon dissolution device Ozone water transfer pipe for sending the ozone water to the point of use, and a concentration concession means for reducing the ozone water transferred by the ozone 7pipe suitable pipe to a predetermined ozone concentration.
  • Ozone water supply device for supplying an ozone dissolution inhibiting substance to ttft3 ⁇ 43 ⁇ 47_k or tiff self-ozone water, ozone water prepared using a self-contained zon dissolution device Ozone water transfer pipe for sending the ozone water to the point of use, and a concentration concession means for reducing the ozone water transferred by the ozone 7pipe suitable pipe to a predetermined ozone concentration.
  • ⁇ «x is a salt of, sulfuric acid, carbonic acid, charcoal «, charcoal ⁇ salt, zinc, mm salt, ⁇ -acid, is a sulfurous acid ⁇ / salt (9) ⁇ Place,
  • Dissolved ozone is selected from the group consisting of ultrasonic irradiation, ultraviolet irradiation, tongue generation, m heating, heating, and peroxidation.
  • Ozone water supply weaving device according to (11),
  • Ozone water supply arrangement according to (8), wherein the concentration adjusting means is ozone water, and (14) transfer of the ozone water to the point of use is performed by gas-liquid mixing of ozone water and ozone gas. Ozone water supply according to any one of (8) to (13)
  • FIG. 1 is a process flow diagram of one embodiment of the ozone water supply apparatus of the present invention
  • FIG. 2 is low
  • Fig. 3 is a graph showing the relationship between ififfik silver lamp output and ozone concentration
  • Fig. 4 is a diagram showing concentration means with a lifetime and cool-off time.
  • FIG. 5 is a graph showing the relationship between the silver lamp output and the fertilizer yield.
  • reference numeral 1 denotes an oxygen gas container
  • 2 denotes a nitrogen gas container
  • 3 denotes a leaching generator
  • 4 denotes a leaching device
  • 5 denotes an ozone-reducing substance and a co-joining means
  • 6 denotes ozone water transfer.
  • the ozone water covered with the ozone-suppressing substance is transferred to a use point through a use point, and is lowered to a predetermined ozone concentration by a concentration adjusting means near the use point.
  • the ozone water supply device of the present invention is an ozone dissolving device for preparing ozone water by dissolving ozone gas in IfeK, a means for supplying an ozone-suppressing substance to tfif self-fek or unfavorable ozone water.
  • the ozone water transfer pipe for transferring the ozone water prepared by the self-disciplined zoning apparatus to the use point, and the ozone water transfer pipe installed in the vicinity of the use point, and the ozone water transferred by the three ozone water transfer pipes are used for the specified ozone. It has a density adjusting means for reducing the temperature.
  • FIG. 1 is a process diagram of one fiber of the ozone water supply / separation device of the present invention.
  • Oxygen gas 1 and nitrogen gas container 2 The ozone generator 3 with no power is supplied with a mixed gas of gas and a small amount of nitrogen gas to produce ozone-containing gas.
  • the ozone water is produced preferably by dissolving ozone in the previously degassed fibrils.
  • the device shown in this figure is a means for supplying an ozone decomposition inhibiting substance to the pure water or flit self-ozone water 5, an ozone water transfer device for transferring ozone water produced by an ozone dissolution device to a use point, a self-management pipe 6, a use device.
  • concentration haze means 8 provided near the point 7 for reducing the ozone water transferred by the ozone feed pipe to a predetermined ozone concentration.
  • ozone water not used at the point of use is converted into ozone ⁇ 9 filled with active acid and the like, and is recovered as ozone-free water.
  • the ozone water is allowed to contain an ozone-suppressing substance, so that the ozone water can be removed without drastically reducing the agrochemical level of the ozone water Mt produced by the ozone M digester. Since it can be transferred to the use point, even if the concentration is reduced by the concentration adjusting means near the use point, it is still required at the use point.
  • the concentration can be i3 ⁇ 4.
  • ffck is added with an ozone-suppressing substance, and then is allowed to generate an ozone-water containing ozone-suppressing substance.
  • Ozonated water containing ozone-suppressing substances can be produced by exciting willow materials. It is preferable that the free agriculture of the aquatic water having the inhibitory substance be present is 1 to L 0 mg / L higher than the predetermined ozone in the youth bottle.
  • the presence of ozone decomposition inhibiting agent of the ozone water forces S preferably 0. 1 ⁇ 5 0 0 m g / / L, more preferably 1 ⁇ 4 0 Om gZL, 1 0 More preferably, it is ⁇ 300 mg / L. If the amount of the ozone-suppressing substance is less than 0.1 lm gZL, the ozone-suppressing effect is fully exhibited.3 ⁇ 4-f, ozone in the ozone water may be advanced during transfer to the point of use. There is.
  • the ozone-suppressing substance may have an adverse effect on the substance as an impurity.
  • the ozone-suppressing substance reacts with hydroxyl radical, which promotes the ⁇ - It is presumed to stop the ozone ⁇ ⁇ run.
  • the ozone decomposition inhibitor is preferably at least two kinds of 1SX selected from the group consisting of zk-soluble anionic compounds, inorganic acids or salts thereof, and hydrazine.
  • the water-soluble aridani used in the present invention include alcohols such as methanol, ethanol, propanol and isopropyl alcohol, ketones such as acetone, methyl ethyl ketone and methyl isopropyl / leketone, and ethylene.
  • Glycols such as glycol and propylene glycol, alcohols such as monoethanolamine and diethanolamine, fatty acids such as acetic acid and propionic acid, benzyl alcohol, phenol, hydroquinone, benzoic acid, isophthalic acid, etc.
  • Aromatic rudder compounds and the like can be mentioned.
  • alcohols such as isopyl pill alcohol can be suitably used because they do not have a possibility of adversely affecting the coating upon jfe ⁇ such as silicon-a-chamber glass anticoagulation. . 7 Solubility (The conjugate works as a scavenger to withdraw the hydroxyl radical that promotes ozone ⁇ , suppresses ozone self-depletion, and can prevent a sharp decrease in agricultural yield.
  • Examples of the salt used in the present invention as X include, for example, hydrochloric acid, sulfuric acid, carbonic acid, carbonic acid, hydrogencarbonate, nitrous acid, sulfuric acid, ⁇ » ffi « 7, hydrofluoric acid and the like. Can do. Among them, carbonic acid can be suitably used because it can be volatilized as carbon dioxide gas after using ozone water. Inorganic te: ha salt can be added to fck or ozone water as an intense night of water, and can be pumped in gaseous form such as carbon dioxide gas, sub-gas, etc.
  • HC 0 3 - cowpea to Rohm Anion ⁇ fat forms can be added.
  • the amount of hydroxyl radical that promotes ozone ⁇ is reduced by suppressing the pH to 2 to 6 by exciting the acid, and the ozone self ⁇ is suppressed. Can be prevented.
  • anions such as carbonate ions and nitrite ions that form salts have a function of reducing hydroxyl radicals, thereby preventing a sharp decrease in the concentration of dilute zon.
  • examples of the Ozofuji Jtfi adjusting means include a ⁇ of ozone water, ozone water, and the like.
  • the means of ozone ⁇ ⁇ , for example, ultrasonic irradiation, ultraviolet irradiation, tongue generation, ⁇ , warming, alkali addition, exothermic toK element outlet, etc. it can.
  • the concentration of the ozone water obtained by the concentration adjusting means is preferably 5 mg / L or more. If the concentration of free ozone is less than 5 mg / L, the effect of ozone water and surface treatment may be insufficient at the point of use.
  • the irradiation of the ultrasonic wave to the ozone water can be performed by, for example, irradiating the ultrasonic wave to the ozone water with ultrasonic waves.
  • irradiating the ozone water with ultrasonic waves By irradiating the ozone water with ultrasonic waves, ultrasonic cavitation is generated in the ozone, and hydroxyl radicals are generated.
  • the frequency of the ultrasonic waves to be illuminated is preferably 10 kHz to 3 MHz. It is preferable to use the filter in combination with a filter because there is a possibility that fine particles may be generated in the ultrasonic wave
  • the ultrasonic amplitude, frequency, output, etc. it is possible to achieve a predetermined ozone concentration.
  • the ultraviolet irradiation of the water can be performed by, for example, providing an ultraviolet irradiation device at the ifek of the ozone water and irradiating the ozone water with the ultraviolet light.
  • an ultraviolet irradiation device at the ifek of the ozone water and irradiating the ozone water with the ultraviolet light.
  • the wavelength of the ultraviolet light to be illuminated can be changed, and among them, a high-mercury lamp with a high ultraviolet irradiation efficiency having a main wavelength of 253.7 nm can be used for S7k «ultraviolet irradiation.
  • a cell made of an ultraviolet! ⁇ ! Material such as quartz glass, transparent polytetrafluoroethylene etc.
  • the line can be effectively illuminated tf ".
  • Ultraviolet illumination can be controlled by blurring the lamp output, and some lasers can be controlled by blocking the lamp surface.
  • UV irradiation generates hydroxyl radicals and promotes ozone self-radiation UV irradiation can be used favorably because it is easy to handle as a concentration adjusting means and does not cause ozone water contamination.
  • the output of the ultraviolet lamp can be adjusted by adjusting the lamp primary side mm value, primary side separation value, secondary side ⁇ E value, secondary side temporary value, and the like.
  • the power consumption on the secondary side of the lamp is preferably 0.5 to 15 W.
  • the secondary consumption of the ffi mercury lamp is in the range of 0.5 to 15 w, the reproducible gradual force between the secondary consumption of the lamp and the amount of ozone ⁇
  • the zoning water can be easily reduced to the specified azo level.
  • a high-pressure mercury lamp is used as a lamp for irradiating ultraviolet rays, it is preferable that the secondary consumption of the lamp is 5 to 1,500 W.
  • the relationship between the secondary consumption of the lamp and the ozone ⁇ It can be easily made to ozone water at a given ozone it degree.
  • the reciprocal of the residence time of the ozone water in the lamp irradiating ultraviolet rays, that is, the space velocity (SV) is preferably 100 to 5,000 h- 1 .
  • turbulence can be generated, for example, by providing a turbulent flow generating device in ifek ⁇ of ozone water and oxidizing ozone water.
  • a turbulent flow generator 4 there are no particular restrictions on the location of the turbulent flow generator 4 on the shelf, and examples thereof include, for example, a static mixer without an image portion, an ultrasonic device that emits fine fibers, and a pipeline mixer that incorporates a turbine and a stator. be able to.
  • the static mixer is easy to control, and there is no risk of contaminating ozone water due to foreign matter, so that it can be used appropriately.
  • the energy of the dissolved ozone is changed to St, and the drought of ozone is increased.
  • ozone water can be drained by providing a ⁇ step on a crane.
  • the means for passing water fibers include stirring blades such as paddle blades, discta single bin blades, curved blades, and the like, a magnetic stirrer, and a stationary machine.
  • the static mixer can be used for females because there is no risk of polluting the ozone water by dust generation.
  • the ozone water can be heated by, for example, providing heat exchange to the ozone water 3 ⁇ 4k ⁇ .
  • the heat exchange woman provided in the above can use the foreign matter force and contaminate the ozone water, so that it can be suitably used.
  • Heating the ozone water gives energy to the dissolved ozone, which promotes o ozone water whose free ozone has been reduced to a predetermined concentration by heating. It is important to cool the product to the specified temperature required for youth points by using a heater. Heating and cooling of the ozone water can use the recovered heat to increase the leakage rate.
  • the ozone can be promoted by adding the calorie to the fresh water.
  • the alkali to be pumped into the ozone water and examples thereof include ammonia, zk sodium oxide, lithium hydroxide, and calcium hydroxide. Among them, ammonia can be suitably used because it does not volatilize to leave foreign substances.
  • the pH rises and the ozone water becomes individual the ozone power becomes unstable, and the speed increases.
  • the irradiation amount of the ultraviolet ray to the ozone water the irradiation amount of the ultrasonic wave, the intensity of the generated tongue, the intensity of the tongue, the intensity and the time, the upper skirt by the temperature of the caro, Since a clear quantitative relationship is established with good alertness between the amount of guidance and the decrease in the amount of free ozone W ozone due to ⁇ , it is necessary to determine the quantitative relationship in advance.
  • the ozone concentration of ozone water can be set to a predetermined value.
  • ozone water can be used as a means for concentrating ozone water near the use point.
  • Ozone water may be used for the production of ozone water, or may have the same qualities as ffek.
  • acid [ ⁇ raw ffok, or fifek, which has organic acid, especially organic acid.
  • the transfer of the ozone water to the use point can be performed in a gas-liquid mixed state in which ozone_k and ozone gas coexist.
  • Ozone water and ozone gas »gas-liquid mixed state For example, the shape can be changed by injecting k into the ejector, blowing out the injected feK to the center of the bench lily nozzle, and sucking and ozone-containing gas by E generated around the nozzle.
  • the ozone contained in the ozone-containing gas absorbed into the ejector dissolves to form ozone water, and the ozone-containing gas [!] Becomes a gas-liquid mixture of ozone water and natural gas, «Expansion
  • the pressure increases as the flow velocity decreases in the section, and is discharged to the ozone tube X.
  • the ozone water in a gas-liquid mixed state with ozone gas contains ozone while it is transferred through the ozone water supply line.
  • the ozone water and ozone gas at the outlet of the ejector can be used to compensate for the ozone lost by ⁇ and ozone loss.
  • the power S is preferably higher than ⁇ , and the pressure is more preferably 200 kPa or more.
  • the pressure of the gas-liquid mixed fluid of ozone water and ozone gas is increased by more than In particular, the effect of suppressing the rapid decrease in ozone concentration due to the ozone-suppressing substances and the use of ozone water and ozone gas to maintain the ozone concentration.
  • the ozone water and the ozone gas are sent to the use point in a gas-liquid mixed state to the use point immediately before the use point.
  • the gas-liquid separator can be provided after the concentration haze means, that is, the gas-liquid separator can be provided before, after, or both before and after the ozone concentration adjusting means.
  • Fig. 1 shows the process diagram of the ozone generator [Sumitomo Seimitsu Kogyo Co., Ltd., silent ⁇ Ozone generator SG-01 CHU] 3, ozone Solver [Janongo-Tex Co., Ltd., Ozo ⁇ ! ⁇
  • high oxygen gas and high nitrogen gas were supplied from the oxygen gas container 1 and the nitrogen gas container 2, respectively.
  • ⁇ J's Sai Zong water was decomposed after passing water through an ozone decomposition tower 9 filled with live [Kurita Kogyo Co., Ltd., Clicor WG 160].
  • an S ⁇ 3 ⁇ 4k silver lamp with a dominant stabilizer 10 with a dominant wavelength of 253.7 nm as shown in Fig. 2 [Chiyoda Sales Co., Ltd., GL-4, GL-10 and GL The test was carried out using a water flow cell 11 equipped with The dissolved ozone concentration of the ozone water at the outlet of the flow cell was measured using an ozone meter 12.
  • Example 2 The same operation as in Example 1 was performed, except that ozone water having a synthetic ozone concentration of 25.9 mg / L was prepared without dissolving carbon dioxide in the 3 ⁇ 43 ⁇ 4zK supplied to the pit mouth plant.
  • Example 1 in which carbonic acid was present as an ozone- ⁇ 1 control substance in super fcK, the ozone concentration prepared by the ozone dissolving apparatus was 25. 9 mg ZL of ozone water poison concentration S is transferred to youth point without lowering.
  • the output of the silver lamp of the water passage cell is increased, ozone is drastically reduced.
  • the ozone concentration power S decreases, and the relationship between the output and the free ozone concentration becomes a gentle curve, so ⁇ ⁇ ⁇
  • the desired water can be obtained in a stable manner.
  • This ozone water was heated to 25 ° C with calo, and it was allowed to flow out at 25 ° C for
  • the ozone concentration of ozone water at the outlet of the cooler was 14. lmgZL. Heating with a heater at 30 ° C, 40 ° C, and 50 ° C, and when cooling to 25 ° C in the cool-off period, the free fertilizer at the outlet of the cooler is 12.8 mg /: L each. 10. Omg / L and 6.4 mg / L.
  • ozone concentration As a means of adjusting ozone concentration, it has a dimmer chamber with a dominant wavelength of 253.7 nm as shown in Fig. 2.
  • ⁇ 3 ⁇ 4k silver lamp [Chiyoda Corporation, GL-4, GL-10 and GL-40] The test was performed using an ifek cell with! /.
  • Carbon dioxide is supplied to ultra ffek supplied to the pilot plant-
  • the same operation as in Example 4 was performed, except that the prepared ozone water having the ozone concentration of 36.5 mg ZL was prepared.
  • f ⁇ ⁇ The relationship between the output of the mercury lamp and the ozone water ozone concentration at the cell outlet is 31.8 mg / L at 1.5 W, 25.7 mg / L at 3.6 W, 18.8 mg / L at 5.5 W, 9.8 W At that time, it was 14. lmgZL, and at OW, it was 10. OmgZL.
  • Example 4 The results of Example 4 and Comparative Example 3 are shown in Table 4 and FIG.
  • «j contains ozone ⁇ ⁇ and carbonic acid as a suppressor ⁇ 3 ⁇ 4
  • the space velocity (SV) is 6,000 h- 1. Residence time in water cell Even if it is short, when the output of the iz ⁇ ⁇ silver lamp of the iizk cell is increased, ozone is ⁇ and the ozone concentration is reduced, and the relationship between output and free ozone is a smooth curve, so iS3 ⁇ 4k silver By controlling the output of the lamp, it is possible to stably obtain ozone water having a desired level of water.
  • the test was performed using a cell equipped with an ultrasonic generator ⁇ [ ⁇ ⁇ 005 JIA] manufactured by Pretec Co., Ltd. as a means of ozone concentration haze.
  • the ozone concentration at the cell outlet was 19mg / L at 30W output, 17mgZL at 4OW, 15mgZL at 5OW, and 14mgZL at 6OW. Comparative Example 4
  • Example 5 Without dissolving carbon dioxide gas into the 3 ⁇ 47 supplied to the Neulot plant, without? The same operation as in Example 5 was performed except that ozone water having a concentration of 25.9 mg / L was prepared.
  • the ozone concentration of ozone water at the outlet of the flow cell was 5 mg / L at an output of 3 OW, 40 W (6 mgZL at 5 OW, 6 mgZL at 5 OW, and 3 mg / L at 6 OW).
  • Table 5 shows the results of Example 5 and Comparative Tree 4.
  • fiber was turned on using a glass cell with a turntable for magnetic stirrer [Az-One Co., Ltd., HS-3B].
  • Example 2 In the same manner as flame Example 1 was C 0 2 concentration 3 mg ZL, the O zone down water Yu ozone concentration 25. 9m g / L was prepared. The ozone water was applied to a glass cell, and was applied at 100 rpm, 500 rpm, 1,000 rpm or 1,500 rpm each time.
  • the dissolved ozone concentration of the ozone water at the glass cell outlet is determined by the rotation of the rotor! 3 ⁇ 4Female 100 rpm, 500 rpm, l, 000 rpm, 1,500 rpm, 19 mgZL, 15 mg / L, respectively , 13 mg ZL and 1 Smg / L.
  • Example 6 The same operation as in Example 6 was carried out, except that ozone water having a free ozone concentration of 25.9 mg / L was prepared without dissolving carbon dioxide in the 3 ⁇ 4ifek supplied to the neurot plant.
  • Ozone water at the outlet of the glass cell At 100 rpm, 500 rpm, l, 000 rpm, and 1,500 rpm, the rotation was 5 mgZL, 7 mg / L, 4 mgZL, and 5 mg / L, respectively.
  • Table 6 shows the results of Example 6 and comparative tree sequence 5.
  • the ozone concentration of ozone water at the glass cell outlet is 18 mgZ when the hydrogen peroxide concentration in the ozone water is 5 mg / L, 7 mg / L, 15 mg / L, 22 mg / L s 32 mg / L, and 50 mgZL.
  • Example 7 The same operation as in Example 7 was performed except that ozone water with an ozone concentration of 25.9 mg / L was prepared without introducing carbon dioxide into the pilot plant [7] without injecting carbon dioxide.
  • Dissolved ozone concentration of ozone water glass cell outlet can the Kasani ⁇ iodine concentration of ozone in water 5m g / L 7mg / L, 15mg / L, 22mg / L, 32mg / / L, and was SOMG / L
  • the results were 5 mg / L, 4 mgZL, 5 mgZL, 3 mg / L, 4 mgZL, and 3 mgZ, respectively.
  • Table 7 shows the results of Example 7 and Comparative Example 6.
  • IPA isopropyl alcohol
  • decomposition of ozone is suppressed, ozone agriculture is high, ozone water is transported to a use point, and the ozone agriculture is arranged near a use point.
  • Ozone water of a predetermined concentration can be stably supplied to the use point by lowering the ozone concentration to a predetermined value by using means.

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Abstract

A method of ozone water supply, characterized in that ozone water wherein an ozonolysis inhibiting substance is present is transferred to use point (7) and that the ozone concentration is lowered to a given level by concentration regulation means in the vicinity of the use point. Further, there is provided an ozone water supply apparatus characterized by including ozone dissolution unit (4) for dissolving ozone gas in pure water to thereby prepare ozone water; means for feeding an ozonolysis inhibiting substance into the pure water or ozone water; ozone water transfer piping (6) for transferring the ozone water prepared by the ozone dissolution unit to a use point; and disposed in the vicinity of the use point, concentration regulation means (8) for lowering the ozone concentration of ozone water having been transferred through the ozone water transfer piping to a given level. In the use of this apparatus, the ozone water of given ozone concentration can be stably supplied to the use point so as to be available in, for example, the wet cleaning and surface treatment steps for electronic materials, such as semiconductors and liquid crystals.

Description

明細書 オゾン水供給;^法及ぴ才ゾン水供^ ¾置  Description ozone water supply;
鎌分野 Sickle field
本発明は、 オゾン水供給方法及びオゾン水供給装置に関する。 さらに詳しくは、 本発明 は、 体、 液晶などの電子材料のゥエツト赚工程、 表面処理工程などにおいて、 ユー スポイントに所定のオゾン濃度のオゾン水を安定して供^ 1~ることができるオゾン水供給 去及びオゾン水供^ g置に関する。 背景鎌  The present invention relates to an ozone water supply method and an ozone water supply device. More specifically, the present invention relates to an ozone solution capable of stably supplying ozone water having a predetermined ozone concentration to a use point in an etching process, a surface treatment process, or the like of an electronic material such as a body or a liquid crystal. Water supply and ozone water supply. Background scythe
半導体用シリコン基板、 液晶用ガラス ¾¾、 フォトマスク用 ¾¾¾などの電子ネオ料の 表面から、 物、條などを除去することは、 製品の品質と歩留まりを確保する上で極 めて觀である。 fekにオゾンを溶解したオゾン水は、 雜ォゾ ^農度が数 m g/L鍵 の でありながら、 極めて強レ、酸化力を発揮し、 電子材 面に付着した有機物や金 属などの不純物による汚染を除去する工程や、 シリコン¾¾の表面を均一に酸化して酸化 月 を形成する工程に翻されている。 この^、 供給されるオゾン水の濃度は、 m 面の »力や、 酸ィ 鎮さの制御などに影響するために、 その濃度管理は非常に重要であ る。  It is very important to remove objects and conditions from the surface of electronic neo-materials such as silicon substrates for semiconductors, glass for liquid crystal, and photomasks for securing product quality and yield. Ozone water with ozone dissolved in fek exhibits extremely strong and oxidizing power even though the amount of fertilizer is a few mg / L, and impurities such as organic substances and metals attached to the electronic material surface The process has been shifted to the process of removing contamination due to oxidization and the process of uniformly oxidizing the surface of silicon II to form an oxidized surface. Since the concentration of the supplied ozone water affects the m-plane »power and the control of acidity, it is very important to control the concentration.
水中に^ する才ゾンは自己分解が非常に激しく、 オゾン水の^ #才ゾン濃度が低下し やすいという問題がある。 オゾン水を長 ¾|勝送じても、 移送中におけるオゾ^度の低 下が少なく、 ユースポイントに一定した濃度のオゾン水を供給することができるオゾン水 供糸幾置として、 糸 ΐ7_κにオゾンを溶解させてオゾン水を生^ るオゾン水溶解装置と、 生 成したオゾン水を移送するオゾン水供糸 己管を有するオゾン水供^置であって、 糸 ifeK又 はオゾン水に炭酸ガス又は有衞匕合物を溶解させる勸ロ手段を設けてなるオゾン水供糸幾 置が提案されている (特許文献 1 )。 同様な効果を有するォゾ W容解水の供糸幾置として、 オゾンを被溶解水に溶解するオゾン溶解装置、 溶解装置に被溶解水を供給する給水管及び 容角早装置から才ゾン?容角军水を送出する送出管を有する才ゾン溶角爭水の供給装置において、 糸^ K管から送出管までの任意の位置に、 亜薩、 亜 M^、 炭酸、 炭謹、 赚、 亜 硫酸、 亜 ≤¾硫«¾びヒドラジンからなる群から選ばれる 1又は 2以上のォゾ ン分媚:卬制剤を翻口する 供給装置を設けてなるオゾン溶解水の供給装置が されて いる (特許文献 2)。 There is a problem that ^^^^^^^^^^^^^^^^^^^^^^^^^^^^^^^^^ ^^^^^^^^^^^^^ 自己 が 。i 自己 In to all. Even if the ozone water is sent for a long time, the ozone water drops little during the transfer and can supply the ozone water at a certain concentration to the point of use. An ozone water dissolving device that dissolves ozone to generate ozone water, and an ozone water supply device that transports the generated ozone water. There has been proposed an ozone water supply device provided with an admission means for dissolving a gas or an arrested compound (Patent Document 1). The same effect can be achieved by using an ozone dissolving device that dissolves ozone in the water to be dissolved, a water supply pipe that supplies the water to be dissolved to the dissolving device, and a fast-acting device. In the water supply device having a delivery pipe for delivering water, a water supply pipe is provided at an arbitrary position from the yarn ^ K pipe to the delivery pipe, asatsu, asia M ^, carbonic acid, charcoal, 赚, One or more ozone components selected from the group consisting of sulfurous acid, sulfurous acid, and hydrazine: an ozone-dissolved water supply device provided with a supply device that excites the inhibitor (Patent Document 2).
又、 オゾン水を棚箇所に供^ るに際して、 所要の濃度のオゾン水を容易に供 "る ことができるオゾン水の濃度 として、 ii^にオゾンを溶解させたオゾン水の濃度 調 ¾¾¾であって、 ¾Kffiの長さ、カロ温、超音波、 紫外線又は乱流化によりオゾンの分 解を促進して、 オゾン水の濃度を霞するオゾン水の濃度調勤法が $^されている (特 許文献 3 )。 ユースポイントに所望の^ オゾン濃度のオゾン含有水を容易に供給するこ とができるォゾ の調 去として、 オゾン含有水をガラスと織虫させ、 所望濃度の オゾン含有水とするオゾ^度の fS&^法が驗されている (特許文献 4)。  In addition, when supplying ozone water to a shelf location, the concentration of ozone water in which ozone is dissolved in ii ^ is used as the concentration of ozone water that can easily provide the required concentration of ozone water. ^ Kffi length, calorie temperature, ultrasonic wave, ultraviolet light or turbulence promotes ozone decomposition, and the ozone water concentration adjustment method to haze ozone water concentration is $ ^ Patent Document 3) As a control of ozone that can easily supply ozone-containing water having a desired ozone concentration to a point of use, ozone-containing water is woven with glass, and the ozone-containing water having a desired concentration is mixed with ozone-containing water. The fS & ^ method of the degree of oscillosis has been tested (Patent Document 4).
しかし、 従来のオゾン水供給方法及びオゾン水供糸織置では、 安定した濃度のオゾン水 を供糸^ ること力 s難しく、 又ユースポイントで所定の オゾン濃度に制御することも非 常に難しいという問題があった。  However, with the conventional ozone water supply method and the ozone water supply weaving apparatus, it is difficult to supply a stable concentration of ozone water, and it is also very difficult to control the ozone concentration to a predetermined level at the point of use. was there.
[輔午文献 1 ] 特開 2 0 0 0 - 3 7 6 9 5号公報 (第 2頁)  [Memorial Document 1] Japanese Patent Application Laid-Open No. 2000-370695 (page 2)
圈午文献 2] 欄 2 0 0 2 - 1 8 4 5 4号公報 (第 2頁)  Reference 2] Column 2 0 0 2-1 8 4 5 4 Publication (page 2)
[特許文献 3 ] 特開 2 0 0 0 - 1 8 0 4 3 3号公報 (第 2— 3頁)  [Patent Document 3] Japanese Patent Application Laid-Open No. 2000-1808043 (pages 2-3)
[特許文献 4] 特開 2 0 0 0— 3 3 4 4 6 8号公報 (第 2頁)  [Patent Document 4] Japanese Patent Application Laid-Open No. 2000-330334 (page 2)
本発明は、 ^体、 液晶などの電子材料のゥエツト 工程、 表面処 S 程などにおい て、 ユースポィントに所定のオゾン濃度のオゾン水を安定して供給することができるォゾ ン水供糸合方?去及びオゾン水供^置を することを目的としてなされたものである。 発明の開示  The present invention provides an ozone water supply system that can stably supply ozone water having a predetermined ozone concentration to a use point in an ejection process and a surface treatment process of an electronic material such as a liquid crystal and a liquid crystal. The purpose is to remove and supply ozone water. Disclosure of the invention
本発明者らは、 上記の,を解決すべく鋭意 w¾を重ねた結果、 オゾン 抑制物質を 存在させた濃度の高いオゾン水をユースボイントに移送し、 ユースボイントにおレヽて濃度 調整手段により所定のオゾン濃度に低下させることにより、 所定のオゾ^農度のオゾン水 を安定してユースボイントに供給し得ることを見いだし、 この知見に基づいて本発明を完 るに至った。  The inventors of the present invention have made intensive efforts to solve the above, and as a result, transferred highly concentrated ozone water in which an ozone suppressing substance was present to a use point, and returned to the use point by a concentration adjusting means. The present inventors have found that by reducing the ozone concentration to a predetermined value, it is possible to stably supply ozone water of a predetermined ozone level to a youth bottle, and based on this finding, completed the present invention.
すなわち、 本発明は、  That is, the present invention
( 1 ) オゾン^^抑制物質を させたオゾン水をユースボイントに移送し、 ユースボイ ント近傍にぉレ、て ii¾謹手段により所定のオゾン濃度に低下させることを樹敫とするォ ゾン水供給雄、  (1) Ozone water supplied with ozone-suppressed substances is transported to youth bottles, placed near the youth bottles, and ii. ,
( 2) オゾン 旱抑制物質が、水溶性有樹匕合物、 雄酸又はその:^ ¾ぴヒドラジンから なる群から選ばれる 1種又は 2種以上である( 1 )記載のオゾン水供給方法、 o)纖^ Xはその塩が、 敏 敵 炭酸、 炭赚、 炭 素塩、 亜硝酸、
Figure imgf000005_0001
(2) Ozone The anti-drought substance is derived from a water-soluble arizide compound, maleic acid or its: ^ ¾ ぴ hydrazine The ozone water supply method according to (1), wherein the ozone water supply method is one or more kinds selected from the group consisting of: o) Fiber ^ X is a salt of carbon dioxide, charcoal, carbon salt, nitrite,
Figure imgf000005_0001
、 ¾«、 亜蘭叙は 素塩である(2)記載のオゾン水供給^去、 , ¾ «, Oranj 叙 is ozone water supply according to (2),
(4) 濃 整手段が、 游ォゾンの である(1)記載のオゾン水供給; ^去、  (4) The ozone water supply according to (1), wherein the concentration means is a yuzozon;
(5) 溶存オゾンの 军を、 超音波照射、 紫外線照射、 舌 発生、 «≥、加温、 アルカリ 添 Π及び過酸ィ b ^素添 からなる群から選ばれる 1@Xは 2種以上の手段により行う(4) 言 5¾のオゾン水供給方法、  (5) The amount of dissolved ozone is selected from the group consisting of ultrasonic irradiation, ultraviolet irradiation, tongue generation, «≥, warming, alkali addition, and peroxygen b ^ element addition. (4) Ozone water supply method of 5¾,
(6) 濃 β¾手段が、 オゾン水の ^である(1)言 のオゾン水供給方法、  (6) The ozone water supply method according to (1), wherein the concentrated β¾ means is ozone water ^
(7) 才ゾン水のユースポイントへの移送を、 オゾン水とオゾンガスが する気液混合 状態で行う( 1 )乃至( 6 )のレヽずれか 1項に雄のオゾン水働合;^去、  (7) The transfer of the water to the point of use is carried out in a gas-liquid mixture of ozone water and ozone gas. (1) to (6)
(8) 糸 fcRにオゾンガスを溶解させてオゾン水を調製するォゾ 容解装置、 ttft¾¾7_k又は tiff己オゾン水にオゾン 解抑制物質を供給する手段、 己才ゾン溶解装置で調製したォゾ ン水をユースポイント 送するオゾン水移送配管、 ユースポイント近傍に設けられ、 ォ ゾン 7嫩適己管で移送されたオゾン水を所定のオゾン濃度に低下させる濃度譲手段を有 することを樹敫とするオゾン水供給装置、  (8) Ozone dissolving device for dissolving ozone gas in yarn fcR to prepare ozone water, means for supplying an ozone dissolution inhibiting substance to ttft¾¾7_k or tiff self-ozone water, ozone water prepared using a self-contained zon dissolution device Ozone water transfer pipe for sending the ozone water to the point of use, and a concentration concession means for reducing the ozone water transferred by the ozone 7pipe suitable pipe to a predetermined ozone concentration. Ozone water supply device,
(9) オゾン^^抑制物質が、 水溶性有觀匕^)、 道酸又はその ぴヒドラジンから なる群から選ばれる 1 ¾Xは 2種以上である( 8 )記載のオゾン水供糸幾置、  (9) The ozone water supply system according to (8), wherein the ozone-suppressing substance is selected from the group consisting of water-soluble soluble thiol, oxalic acid and ぴ hydrazine, and 1 ¾X is two or more.
d o) ^«xはその塩が、 ,硫酸、 炭酸、 炭 «、 炭^^素塩、 亜 、 mm 塩、 β酸、 は亜硫^ /素塩である(9)言 2¾のオゾン水供^ ¾置、  do) ^ «x is a salt of, sulfuric acid, carbonic acid, charcoal«, charcoal ^^ salt, zinc, mm salt, β-acid, is a sulfurous acid ^ / salt (9) ^ Place,
(11) 濃度霞手段が、 游オゾンの である(8)記載のオゾン水供^ ¾置、 (11) The ozone water supply apparatus according to (8), wherein the concentration haze means is free ozone.
(12) 溶存オゾンの を、 超音波照射、 紫外線照射、 舌 発生、 m加温、 アル力 リ励 Π及び過酸ィは素勸口からなる群から選ばれる 1 ¾Xは 2種以上の手段により行う( 11)記載のオゾン水供糸織置、 (12) Dissolved ozone is selected from the group consisting of ultrasonic irradiation, ultraviolet irradiation, tongue generation, m heating, heating, and peroxidation. Ozone water supply weaving device according to (11),
(13) 濃度調整手段が、 オゾン水の である(8)記載のオゾン水供糸幾置、 及び、 (14) オゾン水のユースポイントへの移送を、 オゾン水とオゾンガスが共存する気液混 合状態で行う( 8 )乃至( 13 )のレヽずれか 1項に記載のオゾン水供給施、  (13) Ozone water supply arrangement according to (8), wherein the concentration adjusting means is ozone water, and (14) transfer of the ozone water to the point of use is performed by gas-liquid mixing of ozone water and ozone gas. Ozone water supply according to any one of (8) to (13)
を するものである。 図面の簡単な説明 It is what you do. Brief Description of Drawings
F i g. 1は本発明のオゾン水供給装置の一態様の工程系統図、 F i g. 2は低 |¾K銀 ランプを備えた濃度 手段の説明図、 F i g . 3は ififfi k銀ランプ出力と? オゾン濃 度の関係を示すグラフ、 F i g . 4 口涯と冷去暇を備えた濃度漏手段の説明図、 F i g . 5は ί©¾Κ銀ランプ出力と?雜ォゾ f農度の関係を示すグラフである。 図中符号 1 は酸素ガス容器、 2は窒素ガス容器、 3は才ゾン発生器、 4は才ゾン溶解装置、 5はォゾ ン^ 卬制物質ィ共糸合手段、 6はオゾン水移] ϋ己管、 7はユースポイント、 8は 手 段、 9はオゾン分角? t荅、 1 0は調光機能つき安定器、 1 1は通 7kセル、 1 2は溶存オゾン 計、 1 3は加顯、 1 4は 表す。 発明を実施するための最良の形態 FIG. 1 is a process flow diagram of one embodiment of the ozone water supply apparatus of the present invention, and FIG. 2 is low | ¾K silver. Fig. 3 is a graph showing the relationship between ififfik silver lamp output and ozone concentration, Fig. 4 is a diagram showing concentration means with a lifetime and cool-off time. FIG. 5 is a graph showing the relationship between the silver lamp output and the fertilizer yield. In the figure, reference numeral 1 denotes an oxygen gas container, 2 denotes a nitrogen gas container, 3 denotes a leaching generator, 4 denotes a leaching device, 5 denotes an ozone-reducing substance and a co-joining means, and 6 denotes ozone water transfer. Self-management, 7 is use point, 8 is means, 9 is ozone angle angle? t water, 10 is ballast with dimming function, 11 is 7k cell, 12 is dissolved ozone meter, 13 is dissolved ozone meter Kahen, 14 represents. BEST MODE FOR CARRYING OUT THE INVENTION
本発明のオゾン水供給方法においては、 オゾン^^抑制物質を被させたオゾン水をュ ースボイント ίこ移送し、 ユースボイント近傍にぉレ、て濃度調整手段により所定のオゾン濃 度に低下させる。 本発明のオゾン水の供糸幾置は、 IfeKにオゾンガスを溶解させてオゾン 水を調製するォゾ 解装置、 tfif己 fek又は嫌己オゾン水にオゾン^^抑制物質を供糸 B ~ る手段、 ΙϋΙ己才ゾン溶解装置で調製したオゾン水をユースボイントへ移送するオゾン水移 送配管、 ユースポイント近傍に設けられ、 オゾン水移避 3管で移送されたォゾ を所定 のォゾ ^農度に低下させる濃度調整手段を有する。  In the ozone water supply method of the present invention, the ozone water covered with the ozone-suppressing substance is transferred to a use point through a use point, and is lowered to a predetermined ozone concentration by a concentration adjusting means near the use point. The ozone water supply device of the present invention is an ozone dissolving device for preparing ozone water by dissolving ozone gas in IfeK, a means for supplying an ozone-suppressing substance to tfif self-fek or unfavorable ozone water. The ozone water transfer pipe for transferring the ozone water prepared by the self-disciplined zoning apparatus to the use point, and the ozone water transfer pipe installed in the vicinity of the use point, and the ozone water transferred by the three ozone water transfer pipes are used for the specified ozone. It has a density adjusting means for reducing the temperature.
F i g . 1は、 本発明のオゾン水供離置の一纖の工程系統図である。 酸素ガス 1と窒素ガス容器 2力 、 無^ ¾^¾;のオゾン発生器 3に、 ガスと微量の窒素ガス の混合ガスを供給して、 オゾン含有ガスを製造し、 ォゾ: 容解装置 4において、 好ましく はあらかじめ脱気された糸脉にオゾンを溶解させてオゾン水を製造する。 本図に示す装置 は、 前記純水又は flit己オゾン水にオゾン分解抑制物質を供給する手段 5、 オゾン溶解装置 で製造されたオゾン水をユースボイントに移送するオゾン水移 ¾S己管 6、 ユースボイント 7近傍に設けられ、 オゾンフ^送配管で移送されたたオゾン水を、 所定の オゾン濃度 に低下させる濃度霞手段 8を有する。 本纖の装置においては、 ユースポイントで使用 されなかったオゾン水は、 活酸などを充填したオゾン ^碟 9に され、 オゾンを含 有しない水として回収される。  FIG. 1 is a process diagram of one fiber of the ozone water supply / separation device of the present invention. Oxygen gas 1 and nitrogen gas container 2 The ozone generator 3 with no power is supplied with a mixed gas of gas and a small amount of nitrogen gas to produce ozone-containing gas. In 4, the ozone water is produced preferably by dissolving ozone in the previously degassed fibrils. The device shown in this figure is a means for supplying an ozone decomposition inhibiting substance to the pure water or flit self-ozone water 5, an ozone water transfer device for transferring ozone water produced by an ozone dissolution device to a use point, a self-management pipe 6, a use device. There is provided a concentration haze means 8 provided near the point 7 for reducing the ozone water transferred by the ozone feed pipe to a predetermined ozone concentration. In the device of the present fiber, ozone water not used at the point of use is converted into ozone ^ 9 filled with active acid and the like, and is recovered as ozone-free water.
本発明にぉレヽては、 オゾン水にオゾン^军抑制物質を させることにより、 ォゾ M容 解装置で Mtされたオゾン水の游ォゾ 農度を大幅に低下させることなく、 オゾン水を ユースボイントに移送することができるので、 ユースボイント近傍にぉレヽて濃度調整手段 によりォゾ を低下させても、 なおユースボイントにおレヽて必要とされる^ ォゾン 濃度を i¾ することができる。 本発明にぉレヽては、 ffckにオゾン 锊卬制物質を添 した のち才ゾンを^ させることにより、 オゾン^抑制物質を させたオゾン水とするこ とができ、 あるいは、 オゾン水にオゾン^柳制物質を励口することにより、 オゾン^军 抑制物質を させたオゾン水とすることもできる。 才ゾン^^抑制物質を存在させた才 ゾン水の游ォゾ 農度は、 ユースボイントにおける所定のォゾ ϋ度より 1〜: L 0 0 m g/L高いこと力 S好ましい。 In the present invention, the ozone water is allowed to contain an ozone-suppressing substance, so that the ozone water can be removed without drastically reducing the agrochemical level of the ozone water Mt produced by the ozone M digester. Since it can be transferred to the use point, even if the concentration is reduced by the concentration adjusting means near the use point, it is still required at the use point. The concentration can be i¾. According to the present invention, ffck is added with an ozone-suppressing substance, and then is allowed to generate an ozone-water containing ozone-suppressing substance. Ozonated water containing ozone-suppressing substances can be produced by exciting willow materials. It is preferable that the free agriculture of the aquatic water having the inhibitory substance be present is 1 to L 0 mg / L higher than the predetermined ozone in the youth bottle.
本発明において、 オゾン水中のオゾン分解抑制物質の存在量は、 0. 1〜 5 0 0 m g // Lであること力 S好ましく、 1〜4 0 Om gZLであることがより好ましく、 1 0〜3 0 0 m g/Lであることがさらに好ましい。 オゾン^^抑制物質の 量が 0. l m gZL未 満であると、 オゾン^^抑制効果が十分に発現 ¾~f、 ユースポイントへの移送中にオゾン 水中のオゾンの ^^が に進行するおそれがある。 オゾン^军抑制物質の被量が 5 0 O m g/Lを超えると、 オゾン^军抑制物質が被 に対して不純物としての悪 を 及ぼすおそれがある。 オゾン^^抑制物質の ¾¾¾により、 オゾンの 早が抑制される詳細 な樹冓は明ら力ではないが、 オゾン^^抑制物質が^ 才ゾンの^^を促進するヒドロキ シルラジカノレと ®Sし、 オゾン^军の連 を停止するためと推定される。 In the present invention, the presence of ozone decomposition inhibiting agent of the ozone water, it forces S preferably 0. 1~ 5 0 0 m g / / L, more preferably 1~4 0 Om gZL, 1 0 More preferably, it is 〜300 mg / L. If the amount of the ozone-suppressing substance is less than 0.1 lm gZL, the ozone-suppressing effect is fully exhibited.¾-f, ozone in the ozone water may be advanced during transfer to the point of use. There is. If the amount of the ozone-suppressing substance exceeds 50 O mg / L, the ozone-suppressing substance may have an adverse effect on the substance as an impurity. The details of the ozone-suppressing substance が, which suppresses the premature ozone generation, are not obvious. However, the ozone-suppressing substance reacts with hydroxyl radical, which promotes the ^^- It is presumed to stop the ozone ^ 军 run.
本発明においては、 オゾン分解抑制物質が、 zk溶性有謝匕合物、 無機酸又はその塩及び ヒドラジンからなる群から選ばれる 1SXは 2種以上であること力 S好ましい。 本発明に用 レ、る水溶性有衞匕^/としては、 例えば、 メタノーノレ、 エタノール、 プロパノール、 イソ プロピルアルコールなどのアルコール類、 アセトン、 メチルェチルケトン、 メチルイソプ ロピ/レケトンなどのケトン類、 エチレングリコール、 プロピレングリコ一ルなどのグリコ ール類、 モノエタノールァミン、 ジエタノールァミンなどのアル力ノールアミ^、酢酸 、 プロピオン酸などの脂肪酸、 ベンジルアルコール、 フエノール、 ヒドロキノン、 安息香 酸、 イソフタル酸などの芳香腐匕合物などを挙げることができる。 これらの中で、 イソプ 口ピルアルコールなどのアルコール類は、 シリコンゥエーハゃガラス凝反などの? jfe ^に際 して、 被 ¾ ^に悪影響を与えるおそれがないので、 好適に用いることができる。 7溶性 (匕合物は、 オゾンの^^を促進するヒドロキシルラジカルを撤足するスカベンジャー としてはたらき、 オゾンの自己 军を抑制し、 ォゾ: 農度の急激な低下を防ぐことができ る。  In the present invention, the ozone decomposition inhibitor is preferably at least two kinds of 1SX selected from the group consisting of zk-soluble anionic compounds, inorganic acids or salts thereof, and hydrazine. Examples of the water-soluble aridani used in the present invention include alcohols such as methanol, ethanol, propanol and isopropyl alcohol, ketones such as acetone, methyl ethyl ketone and methyl isopropyl / leketone, and ethylene. Glycols such as glycol and propylene glycol, alcohols such as monoethanolamine and diethanolamine, fatty acids such as acetic acid and propionic acid, benzyl alcohol, phenol, hydroquinone, benzoic acid, isophthalic acid, etc. Aromatic rudder compounds and the like can be mentioned. Of these, alcohols such as isopyl pill alcohol can be suitably used because they do not have a possibility of adversely affecting the coating upon jfe ^ such as silicon-a-chamber glass anticoagulation. . 7 Solubility (The conjugate works as a scavenger to withdraw the hydroxyl radical that promotes ozone ^^, suppresses ozone self-depletion, and can prevent a sharp decrease in agricultural yield.
本発明に用いる解 «Xはその塩としては、 例えば、塩酸、 硫酸、 炭酸、 炭赚、 炭酸 水素塩、 亜 «、 ¾酸、 β»、 ffi«7素塩、 フッ酸などを挙げること ができる。 これらの中で、 炭酸は、 オゾン水使用後に炭酸ガスとして揮散させることがで きるので、好適に用いることができる。 無機 te:はその塩は、 fck又はオゾン水に水激夜 として添カロすることができ、 炭酸ガス、 亜«ガスなどのガス状で励口することもでき、Examples of the salt used in the present invention as X include, for example, hydrochloric acid, sulfuric acid, carbonic acid, carbonic acid, hydrogencarbonate, nitrous acid, sulfuric acid, β », ffi« 7, hydrofluoric acid and the like. Can do. Among them, carbonic acid can be suitably used because it can be volatilized as carbon dioxide gas after using ozone water. Inorganic te: ha salt can be added to fck or ozone water as an intense night of water, and can be pumped in gaseous form such as carbon dioxide gas, sub-gas, etc.
HC 03—形のァニオン交麵脂に通水することによつても添加することができる。 酸を 励口して p Hを 2〜6とすることにより、 オゾンの^^を促進するヒドロキシルラジカル の 量を減少し、 オゾンの自己^^を抑制し、 ォゾ f農度の急激な低下を防ぐことがで きる。 又、塩を形财る炭酸イオン、 亜硝酸イオン等のァニオンもヒドロキシルラジカル を?咸少、させるィ乍用を有し、 才ゾン濃度の急激な低下を防止する。 HC 0 3 - be cowpea to Rohm Anion交麵fat forms can be added. The amount of hydroxyl radical that promotes ozone ^^ is reduced by suppressing the pH to 2 to 6 by exciting the acid, and the ozone self ^^ is suppressed. Can be prevented. Also, anions such as carbonate ions and nitrite ions that form salts have a function of reducing hydroxyl radicals, thereby preventing a sharp decrease in the concentration of dilute zon.
本発明において、 オゾ^農 Jtfi整手段としては、 オゾン水中の^ 才ゾンの^军、 ォゾ ン水の などを挙げることができる。 オゾン水中の? オゾンを: ^军する手段に特に制 限はなく、 例えば、 超音波照射、 紫外線照射、 舌 発生、辦、加温、 アルカリ添 Π、 過 謝 toK素励口などを挙げることができる。 濃度調整手段より讓されるオゾン水の?雜ォ ゾ> ^農度は、 5 m g/L以上であること力 S好ましい。 游ォゾン濃度が 5 m g /L未満で あると、 ユースポイントにおけるイ^に際して、 オゾン水の旨効果、 表面処»果など が不十分となるおそれがある。  In the present invention, examples of the Ozofuji Jtfi adjusting means include a ^^^ of ozone water, ozone water, and the like. There is no particular limitation on the means of ozone: ^ 军, for example, ultrasonic irradiation, ultraviolet irradiation, tongue generation, 辦, warming, alkali addition, exothermic toK element outlet, etc. it can. The concentration of the ozone water obtained by the concentration adjusting means is preferably 5 mg / L or more. If the concentration of free ozone is less than 5 mg / L, the effect of ozone water and surface treatment may be insufficient at the point of use.
本発明において、 オゾン水への超音波の照 itは、 例えば、 オゾン水の ^に超音波 発婦をネ繊的に赚することにより、 オゾン水に超音波を照 J ることができる。 ォゾ ン水に超音波を照射ることにより、 ォゾ 中に超音波キヤビテーションが^^し、 ヒ ドロキシルラジカルが発生して、 オゾンの 早が ί足進される。 照 J る超音波の周波数は 、 1 0 k H z〜3MH zであること力 S好ましレヽ。 超音波の発驗 |5で微立子などが発生する おそれがあるために、 フィルターと組み合わせて用レヽることが好ましレヽ。 超音波の振幅、 周波数、 出力などの選択により、 所定のオゾン濃度に I ^することができる。  In the present invention, the irradiation of the ultrasonic wave to the ozone water can be performed by, for example, irradiating the ultrasonic wave to the ozone water with ultrasonic waves. By irradiating the ozone water with ultrasonic waves, ultrasonic cavitation is generated in the ozone, and hydroxyl radicals are generated. The frequency of the ultrasonic waves to be illuminated is preferably 10 kHz to 3 MHz. It is preferable to use the filter in combination with a filter because there is a possibility that fine particles may be generated in the ultrasonic wave | 5. By selecting the ultrasonic amplitude, frequency, output, etc., it is possible to achieve a predetermined ozone concentration.
本発明において、 才ゾン水への紫外 IIの照 は、 ί列えば、 オゾン水の ifek«に紫外線 照射装置を設け、 オゾン水に紫外線を照 J "ることができる。 紫外線の照 に用いる駕 に特に制限はなく、 例えば、 ίδΕτΚ銀ランプ、 中 ffi _K銀ランプ、 高 ffi k銀ランプ、 キセノ ンランプ、 素ランプ、 メタル/、ライドランプなどを挙げることができる。 ランプの種 類を変えることにより、 照 It る紫外線の波長を変化させることができる。 これらの中で 、 2 5 3. 7 n mに主波長を有する紫外線照射効率の高レ 水銀ランプを に用いる ことができる。 S7k«の紫外線照射部の配管には、 石英ガラス、透明ポリテトラフルォ 口エチレンなどの紫外!^!性の材料からなるセルを設けることにより、 オゾン水に紫外 線を効果的に照 tf"ることができる。 紫外線の照 は、 ランプの出力を霞することに より制御することができ、 あるレヽは、 ランプの表面を遮蔽することにより制御することも できる。 紫外線照射によりヒドロキシルラジかルが発生し、 オゾンの自己 ^军が促進され る。 紫外線照射は、 濃度調整手段として扱いやすく、 オゾン水の汚染も生じないので、 好 適に用いることができる。 In the present invention, the ultraviolet irradiation of the water can be performed by, for example, providing an ultraviolet irradiation device at the ifek of the ozone water and irradiating the ozone water with the ultraviolet light. There is no particular limitation on the type of lamp, for example, ίδΕτΚ silver lamp, medium ffi_K silver lamp, high ffik silver lamp, xenon lamp, elemental lamp, metal / ride lamp, etc. The wavelength of the ultraviolet light to be illuminated can be changed, and among them, a high-mercury lamp with a high ultraviolet irradiation efficiency having a main wavelength of 253.7 nm can be used for S7k «ultraviolet irradiation. In the piping of the section, a cell made of an ultraviolet! ^! Material such as quartz glass, transparent polytetrafluoroethylene etc. The line can be effectively illuminated tf ". Ultraviolet illumination can be controlled by blurring the lamp output, and some lasers can be controlled by blocking the lamp surface. UV irradiation generates hydroxyl radicals and promotes ozone self-radiation UV irradiation can be used favorably because it is easy to handle as a concentration adjusting means and does not cause ozone water contamination.
本発明において、 紫外線ランプの出力の調整は、 ランプ一次側 mm値、 一次側離値、 二次側 ¾E値、 二次側暫巟値などの調整により行うことができる。 紫外線を照 i^rるラン プとして慨 ZR銀ランプを用いる は、 ランプ二次側消費電力が 0. 5〜1 5 Wである こと力 子ましい。 ffi水銀ランプの二次側消費 ¾Λが 0. 5〜1 5 wの範囲では、 ランプ 二次側消 とオゾン^^量の間に再現性のよいなだら力 ^曲線関係カ铖り立ち、 ォゾ ン水を所定のォゾ 農度に容易に難することができる。 紫外線を照射るランプとして 高圧水銀ランプを用いる は、 ランプ二次側消費 ¾Λが 5〜 1 , 5 0 0 Wであることが 好ましレヽ。高圧水銀ランプの二次側消費電力が 5〜: 1 , 5 0 0 Wの範囲では、 ランプ二次 側消費 ¾Λとオゾン^^量の間に再現性のよいなだらカゝな曲線関係力 S成り立ち、 オゾン水 を所定のォゾ it度に容易に誰することができる。 紫外線を照 るランプの^ ϋ内で のオゾン水の滞留時間の逆数すなわち空間速度( S V)は、 1 0 0〜 5, 0 0 0 h— 1である こと力 S好ましい。 In the present invention, the output of the ultraviolet lamp can be adjusted by adjusting the lamp primary side mm value, primary side separation value, secondary side ΔE value, secondary side temporary value, and the like. When using a ZR silver lamp as a lamp for irradiating ultraviolet rays, the power consumption on the secondary side of the lamp is preferably 0.5 to 15 W. When the secondary consumption of the ffi mercury lamp is in the range of 0.5 to 15 w, the reproducible gradual force between the secondary consumption of the lamp and the amount of ozone ^^ The zoning water can be easily reduced to the specified azo level. When a high-pressure mercury lamp is used as a lamp for irradiating ultraviolet rays, it is preferable that the secondary consumption of the lamp is 5 to 1,500 W. When the power consumption on the secondary side of the high-pressure mercury lamp is in the range of 5 to 1,500 W, the relationship between the secondary consumption of the lamp and the ozone ^^ It can be easily made to ozone water at a given ozone it degree. The reciprocal of the residence time of the ozone water in the lamp irradiating ultraviolet rays, that is, the space velocity (SV) is preferably 100 to 5,000 h- 1 .
本発明において、 乱流発生は、 例えば、 オゾン水の ifek^に乱流発雜置を設け、 ォ ゾン水の ¾Τιを舌 ϋίΕ化することができる。 棚する乱流発 4¾置に特に制限はなく、 例え ば、 ,画部分を有しないスタチックミキサー、 f繊発賦のウルトラソニック、 タービン とステーターを糸且み込んだパイプラインミキサ一などを挙げることができる。 これらの中 で、 スタチックミキサーは、麟管理が容易であり、 異物カ 駄してオゾン水を汚染する おそれがなレヽので、 子適に用レヽることができる。 才ゾン水の流れを舌し流ィ匕することにより In the present invention, turbulence can be generated, for example, by providing a turbulent flow generating device in ifek ^ of ozone water and oxidizing ozone water. There are no particular restrictions on the location of the turbulent flow generator 4 on the shelf, and examples thereof include, for example, a static mixer without an image portion, an ultrasonic device that emits fine fibers, and a pipeline mixer that incorporates a turbine and a stator. be able to. Among these, the static mixer is easy to control, and there is no risk of contaminating ozone water due to foreign matter, so that it can be used appropriately. By tongue the flow of water
、 溶解しているオゾンにエネルギー力 Stされ、 オゾンの^旱が f足進される。 The energy of the dissolved ozone is changed to St, and the drought of ozone is increased.
本発明において、 勝は、 例えば、 :«,鶴に^^段を設けることにより、 オゾン水 を することができる。 通水繊の辦手段と'しては、 例えば、 パドル翼、 ディスクタ 一ビン翼、湾曲翼などの攪拌翼や、 式のマグネチックスターラー、静止猶賠機 などを挙げることができる。 これらの中で、 静止型混合機は、 発塵によりオゾン水を汚染 するおそれがないので、 女 ¾1に用いることができる。 オゾン水を ることにより、 溶 解しているオゾンにエネルギーがィ¾§され、 オゾンの^^が促進される。 本発明において、 オゾン水の加温は、 例えば、 オゾン水の ¾k^^に熱交 »などを設 けることにより、 オゾン水を加温することができる。 に設けた熱交婦は、 異物 力 駄してオゾン水を汚染するおそれがなレ、ので、 好適に用レ、ることができる。 オゾン水 を加温することにより、 溶解しているオゾンにエネルギーが与えられ、 が促進される o加温により所定の濃度まで游オゾ^度が低下したオゾン水は、 ¾Κ繊に設けた冷 却器などにより、 ユースボイントにおレ、て要求される所定の-? まで冷却すること力 子ま しい。 オゾン水の加温と冷却には、 回収熱 を用いて漏率を高めることができる。 本発明にぉレヽては、 才ゾン水にァノレ力リを添カロすることにより、 オゾンの^^を促進す ることができる。 オゾン水に励口するアルカリに特に制限はなく、 ί列えば、 アンモニア、 zk酸化ナトリゥム、水酸化力リウム、 水酸化カルシウムなどを挙げることができる。 これ らの中で、 アンモニアは、 揮散して異物を残さないので好適に用いることができる。 アル 力リの^ ¾口により、 p Hが上昇してオゾン水がアル力リ个生になると、 オゾン力不安定にな り、 ^早が ί足進される。 In the present invention, for example, ozone water can be drained by providing a ^^ step on a crane. Examples of the means for passing water fibers include stirring blades such as paddle blades, discta single bin blades, curved blades, and the like, a magnetic stirrer, and a stationary machine. Among these, the static mixer can be used for females because there is no risk of polluting the ozone water by dust generation. By using ozone water, energy is dissipated in the dissolved ozone, and the ozone is promoted. In the present invention, the ozone water can be heated by, for example, providing heat exchange to the ozone water ¾k ^^. The heat exchange woman provided in the above can use the foreign matter force and contaminate the ozone water, so that it can be suitably used. Heating the ozone water gives energy to the dissolved ozone, which promotes o ozone water whose free ozone has been reduced to a predetermined concentration by heating. It is important to cool the product to the specified temperature required for youth points by using a heater. Heating and cooling of the ozone water can use the recovered heat to increase the leakage rate. According to the present invention, the ozone can be promoted by adding the calorie to the fresh water. There is no particular limitation on the alkali to be pumped into the ozone water, and examples thereof include ammonia, zk sodium oxide, lithium hydroxide, and calcium hydroxide. Among them, ammonia can be suitably used because it does not volatilize to leave foreign substances. When the pH rises and the ozone water becomes individual, the ozone power becomes unstable, and the speed increases.
本努明にぉレヽては、 オゾン水に過酸ィ te素を^)口することにより、 才ゾンの^牟をィ足進 することができる。 過酸ィ 素が水中でヒドロキシルラジカルを^ ¾し、 ヒドロキシルラ ジカルがオゾンを分解する。  In this effort, by adding oxyperoxide to ozone water, it is possible to increase the age of the child. Peroxygen generates hydroxyl radicals in water, and hydroxyl radicals decompose ozone.
本発明において、 オゾン水に财る紫外線の照射量、 超音波の照射量、発生する舌 l荒の 強さ、 勝の強さと時間、 カロ温による上裙踏、 アルカリ勸ロ は過酸ィ tok素勸口量と 、 ^^によるオゾン水の游ォゾ W農度の低下量の間には、 明確な量的関係が醒性よく 成立するので、 あらかじめその量的関係を求めておくことにより、 オゾン水の^ ォゾン 濃度を所定の値に することができる。 ,  In the present invention, the irradiation amount of the ultraviolet ray to the ozone water, the irradiation amount of the ultrasonic wave, the intensity of the generated tongue, the intensity of the tongue, the intensity and the time, the upper skirt by the temperature of the caro, Since a clear quantitative relationship is established with good alertness between the amount of guidance and the decrease in the amount of free ozone W ozone due to ^^, it is necessary to determine the quantitative relationship in advance. The ozone concentration of ozone water can be set to a predetermined value. ,
本発明においては、 ユースポイント近傍におけるオゾン水の濃度譲手段として、 ォゾ ン水を # ^することができる。 オゾン水の には、 該ォゾン水の製造に用レ、た ffekと同 の «を有する を用レ、ること力 子ましレ、。 オゾンの^旱による濃度低下を防ぐた めに、 酸 [·生の ffokや、 有衞匕合物、 特に有機酸を励口した fifekで職することもできる。 オゾン水を職して所定の^ オゾン濃度を有するオゾン水とすることにより、 ユースポ イントに移送されたオゾン水に溶解してレヽるオゾンを、 無駄なく完全〖 幌することがで きる。  In the present invention, ozone water can be used as a means for concentrating ozone water near the use point. Ozone water may be used for the production of ozone water, or may have the same qualities as ffek. In order to prevent the concentration of ozone from dropping due to the drought, you can also work with acid [· raw ffok, or fifek, which has organic acid, especially organic acid. By using the ozone water to form ozone water having a predetermined ozone concentration, ozone dissolved in the ozone water transferred to the use point can be completely and completely removed without waste.
本発明においては、 オゾン水のユースポイントへの移送を、 ォゾ _kとオゾンガスが共 存する気液混合状態で行うことができる。 オゾン水とオゾンガスが »する気液混合状態 は、 例えば、 ェジェクタ一に kを圧入し、 圧入された feKをベンチユリ一ノズルの中心 に吹き出し、 その周辺に生ずる Eによりオゾン含有ガスを吸レヽ込むことにより、 形^ 1" ることができる。 ェジェクタ一に吸レヽ込まれたオゾン含有ガス中のオゾンが ¾7_ こ溶解し てオゾン水が するとともに、 !]のオゾン含有ガスがオゾン水と才ゾンガスの気液混 合状態となって、 «拡大部において流速の減少とともに圧力力 曽大し、 オゾンフ X 送配 管に排出される。 オゾンガスと気液混合状態となっているオゾン水には、 オゾン水供給配 管で移送されている間にオゾンが溶け込み、 ^^により失われるオゾンを補うので、 、赫 ォゾ 農度の低下を防ぐことができる。 ェジェクタ一の出口におけるオゾン水とオゾンガ スの気液齢流体の圧力は、 大^ ΐよりも高いこと力 S好ましく、 2 0 0 k P a以上である ことがより好ましい。 オゾン水とオゾンガスの気液混合流体の圧力を大^ 1£よりも高くす ることにより、 オゾン水の長鹏麟送が可能になる。 特に、 オゾン^ ^抑制物質の被に よるオゾンの急激な濃度低下抑制作用と、 オゾン水、 オゾンガス 状態によるォゾ ϋ 度維樹乍用とカ湘まって、 ォゾ ^農度を高く維持したまま移送することができ、好ましい 本発明 去及び装置によれば、 オゾン水とオゾンガスが する気液混合状態でユース ボイントに長 麟送し、 ユースボイントの直前で所定の濃度に霞することができるの で、 一つのオゾン水製 置から、 多くのユースポイントにそれぞれに必要な濃度のォゾ ン水を自由に供糸^ rることができる。 気液混合状態で移送する齢、 ユースボイント直前 の気夜分 βで余剰ガスを除き、 次レ、で濃度調整手段によりオゾン濃度を低下させること が好ましい。 濃度 USの際にオゾンが^旱して «する酸素力 S過飽和状態になる ¾ ^は、 濃度霞手段の後に気液分离離を設けることもできる。 すなわち、 気液分離器は、 オゾン の濃度調整手段の前段、 後後又は前段と後段の両方に設けることができる。 実施例 In the present invention, the transfer of the ozone water to the use point can be performed in a gas-liquid mixed state in which ozone_k and ozone gas coexist. Ozone water and ozone gas »gas-liquid mixed state For example, the shape can be changed by injecting k into the ejector, blowing out the injected feK to the center of the bench lily nozzle, and sucking and ozone-containing gas by E generated around the nozzle. The ozone contained in the ozone-containing gas absorbed into the ejector dissolves to form ozone water, and the ozone-containing gas [!] Becomes a gas-liquid mixture of ozone water and natural gas, «Expansion The pressure increases as the flow velocity decreases in the section, and is discharged to the ozone tube X. The ozone water in a gas-liquid mixed state with ozone gas contains ozone while it is transferred through the ozone water supply line. The ozone water and ozone gas at the outlet of the ejector can be used to compensate for the ozone lost by ^^ and ozone loss. ^ The power S is preferably higher than ^, and the pressure is more preferably 200 kPa or more.The pressure of the gas-liquid mixed fluid of ozone water and ozone gas is increased by more than In particular, the effect of suppressing the rapid decrease in ozone concentration due to the ozone-suppressing substances and the use of ozone water and ozone gas to maintain the ozone concentration. According to the preferred embodiment of the present invention, the ozone water and the ozone gas are sent to the use point in a gas-liquid mixed state to the use point immediately before the use point. Since it is possible to mist to a predetermined concentration by using the ozone water device, it is possible to freely supply the ozone water having a required concentration to each of many use points from one ozone water device. Age of transfer in a mixed state, youth boin It is preferable to reduce the ozone concentration by the concentration adjusting means in the next step, excluding the excess gas in the immediately preceding air and nighttime β. The gas-liquid separator can be provided after the concentration haze means, that is, the gas-liquid separator can be provided before, after, or both before and after the ozone concentration adjusting means.
以下に、 例を挙げて本発明をさらに詳細に説明するが、 本発明はこれらの実施例に よりなんら限定されるものではなレ、。  Hereinafter, the present invention will be described in more detail by way of examples, but the present invention is not limited to these examples.
なお、 戴 ¾例及び比 列においては、 F i g . 1に工程系統図を示すオゾン発生器 [住 友精密工業 (株)、 無声 ^オゾン発生器 S G— 0 1 CHU] 3、 ォゾ ^容解装置 [ジャ ノ ンゴァテックス (株)、 オゾ^!容角勒莫モジユー/レ] 4、炭酸ガス、添口手段 5、 オゾ^^ 趨己管 6、 ユースポイント 7への分嚇己管及びオゾ^ 度薩手段 8を有するノ ィロット プラントを使用した。 オゾン発继置には、 酸素ガス容器 1と窒素ガス鄉 2よりそれぞ れ高 »酸素ガスと高!^窒素ガスを供給した。 ^ Jの才ゾン水は、 活 [栗田工業( 株)、 クリコール WG 160] を充填したオゾン分解塔 9に通水してオゾンを分解したの ち腿した。 オゾン発生器には、 酸素ガス 1L (標準状態) Zmi nと窒素ガス 4mL (標 準状態 J /m i nを供給し、 オゾン発生器の電流を 0 · 6 Aとして、 ォゾ 農度 200 g / m3 (標準状態)のオゾン含有ガスを製造した。 ォゾ 容解装置 4には 7_Rを 20 L/m i n供給し、 オゾンガスを溶解して 10m离 た濃度調整手段 8に供給した。 In the examples and comparative examples, Fig. 1 shows the process diagram of the ozone generator [Sumitomo Seimitsu Kogyo Co., Ltd., silent ^ Ozone generator SG-01 CHU] 3, ozone Solver [Janongo-Tex Co., Ltd., Ozo ^! ^ A pilot with 8 means The plant was used. For the ozone generation, high oxygen gas and high nitrogen gas were supplied from the oxygen gas container 1 and the nitrogen gas container 2, respectively. ^ J's Sai Zong water was decomposed after passing water through an ozone decomposition tower 9 filled with live [Kurita Kogyo Co., Ltd., Clicor WG 160]. To the ozone generator, supply 1 L of oxygen gas (standard condition) Zmin and 4 mL of nitrogen gas (standard condition J / min, and set the ozone generator current to 0.6 A, and the ozone yield 200 g / m An ozone-containing gas of 3 (standard state) was produced.7_R was supplied at 20 L / min to the ozone dissolving apparatus 4, and the ozone gas was dissolved and supplied to a concentration adjusting means 8 of 10 m2.
実施例 1 Example 1
オゾン濃度調整手段として、 F i g. 2に示す主波長 253.7 nmで調雄能つき安 定器 10を有する S≡¾k銀ランプ [千代田ェ販 (株)、 GL— 4、 GL-10および G L― 40] を備えた通水セル 11を用いて試験を行った。 通水セル出口のオゾン水の溶存ォゾ ン濃度を、 ^オゾン計 12を用いて測定した。  As a means for adjusting ozone concentration, an S≡¾k silver lamp with a dominant stabilizer 10 with a dominant wavelength of 253.7 nm as shown in Fig. 2 [Chiyoda Sales Co., Ltd., GL-4, GL-10 and GL The test was carried out using a water flow cell 11 equipped with The dissolved ozone concentration of the ozone water at the outlet of the flow cell was measured using an ozone meter 12.
パイ口ットプラントに纏 ifekを供給し、 炭酸ガス勵ロ手段としての炭酸ガスボンベから 、 C02濃度 3mg/Lになるように、 炭酸ガスを超 fekに添ロ溶解し、 ォゾ 容解装置 で炭酸ガス溶解超純水にオゾンを溶解して^ ォゾン濃度 25.9mg/Lのオゾン水を 調製した。 この才ゾン水を {gffi*銀ランプを点火丁することなく、 セルに «したところ、 ォゾン水の^ ォゾン濃度は、 セル入口、 セル出口ともに 25.9mgZLであった。 次 いで、 ffizk銀ランプを出力 1.5 Wで点灯したところ、 セル出口の^ ォゾ^ I度は 2 0. lmg/Lとなった。 ffi水銀ランプの出力を逐次上昇すると、 出力とセル出口の溶 存ォゾ 農度の関係は、 2 Wのとき 18.0mgZL、 3.5 WOとき 13 · 7 m g/L, 5Wのとき 11.6mgZL、 1 OWのとき 8. Omg/L、 15Wのとき 5.7mgZL であった。 Supplying fireman's standard ifek pie port Ttopuranto, from carbon dioxide gas cylinder as carbon dioxide勵Ro means, so that the C0 2 concentration 3 mg / L, and添Ro dissolved carbon dioxide in the super-fek, carbonate O zone Yokai device Ozone was dissolved in gas-dissolved ultrapure water to prepare ozone water with a ^ ozone concentration of 25.9 mg / L. When this water was applied to the cell without firing the {gffi * silver lamp, the ozone concentration of ozone water was 25.9 mgZL at both the cell inlet and cell outlet. Next, when the ffizk silver lamp was turned on with an output of 1.5 W, the zo ^ I degree at the cell outlet was 20. lmg / L. When the output of the ffi mercury lamp is increased sequentially, the relationship between the output and the dissolved azo fertility at the cell outlet is 18.0 mg ZL at 2 W, 13.7 mg / L at 3.5 WO, 11.6 mg ZL at 5 W, 11.6 mg ZL, 1 OW At that time, it was 8. Omg / L and at 15W it was 5.7 mgZL.
比較例 1 Comparative Example 1
パイ口ットプラントに供給した ¾¾zKに炭酸ガスを 口溶解することなく、 ί雜オゾン 濃度 25.9 m g /Lのオゾン水を調製した以外は、 戴例 1と同じ操作を行つた。  The same operation as in Example 1 was performed, except that ozone water having a synthetic ozone concentration of 25.9 mg / L was prepared without dissolving carbon dioxide in the ¾¾zK supplied to the pit mouth plant.
オゾン水を ίδΕτΚ銀ランプを点灯することなく、 セルに ifekしたところ、 オゾン水の溶 存ォゾン濃度は、 セル入口、 セル出口ともに 8.2mg/Lであった。 次いで、 ィ©¾銀 ランプを出力 1.5Wで点灯したところ、 セル出口の^ ォゾ^度は 5.9mg//Lとな つた。 ί©¾Κ銀ランプの出力を逐? ifc±昇すると、 出力とセノレ出口の^ ォゾ 農度の関係 は、 2Wのとき 5. Omg/L、 3.5Wのとき 4. lmg/L、 5 Wのとき 2.1 m g L 、 1 OWのとき 2. 6 m gZLであった。 When ozone water was applied to the cell without turning on the ίδΕτΚ silver lamp, the dissolved ozone concentration of the ozone water was 8.2 mg / L at both the cell inlet and cell outlet. Next, the silver lamp was turned on with an output of 1.5 W, and the cell outlet had a zonal temperature of 5.9 mg / L. ί © ¾Κ The output of the silver lamp? When ifc ± rises, the relationship between the output and the yield at the senore outlet is 5. Omg / L at 2 W, 4. lmg / L at 3.5 W, 2.1 mg L at 5 W At 1 OW, it was 2.6 mg gZL.
• 雄例 1及び比較例 1の結果を、 第 1表及び F i g . 3に示す。  • The results of Male Example 1 and Comparative Example 1 are shown in Table 1 and FIG.
第 1表  Table 1
Figure imgf000013_0001
第 1表及ぴ F i . g . 3に見られるように、 超 fcKにオゾン^^ 1卬制物質として炭酸を存 在させた 例 1では、 オゾン溶解装置で調製された オゾン濃度 2 5. 9 m gZLの オゾン水の贿ォゾン濃度力 S低下することなく、 ユースボイントまで移送されてレ、る。 又 、 通水セルの 銀ランプの出力を上昇すると、 オゾンが駕して?雜ォゾン濃度力 S低 下し、 出力と游オゾン濃度の関係はなだらカゝな曲線となるので、 ί©ϊτΚ銀ランプの出力 を制御することにより、 所望の^ 才ゾ 農度の才ゾン水を安定して得ることができるこ と力分かる。 これに対して、 ^ fcKにオゾン^^ =卬制物質としての炭酸を させない比 較例 1では、 ユースポィントまで移送されたオゾン水の游ォゾ >t農度は 8. 2 m g /L まで低下しており、 iS¾k銀ランプの出力と ォゾ 農度の関係にばらつき力大きい。 細列 2 オゾンt^i ^手段として、 F i g. 4に示^口 «13と冷去暇 14を用いて を 行った。 冷去暇出口のオゾン水の游ォゾ^?農度を、 ォゾ 2を用いて測定した 実施例 1と同様にして、 じ02濃度31118// 、 オゾン濃度 25, 9mg/Lのォゾ ン水を調製した。 このオゾン水を、カロ で 25°Cに加熱し、 冷去 |¾|では 25°Cのまま流 出させた。 冷却器出口のオゾン水の^ ォゾン濃度は、 14. lmgZLであった。 加熱 器による加熱 を 30 °C、 40 °C、 50 °Cとし、 冷去暇で 25 °Cに冷却したとき、 冷却 器出口のォゾ の游ォゾ 農度は、 それぞれ 12.8mg/:L、 10. Omg/L, 6 .4mgノ Lであった。
Figure imgf000013_0001
As can be seen in Table 1 and Fi.g.3, in Example 1 in which carbonic acid was present as an ozone- ^ 1 control substance in super fcK, the ozone concentration prepared by the ozone dissolving apparatus was 25. 9 mg ZL of ozone water poison concentration S is transferred to youth point without lowering. In addition, when the output of the silver lamp of the water passage cell is increased, ozone is drastically reduced. The ozone concentration power S decreases, and the relationship between the output and the free ozone concentration becomes a gentle curve, so ί © ϊτΚ By controlling the output of the silver lamp, it can be seen that the desired water can be obtained in a stable manner. On the other hand, in Comparative Example 1, where ^ fcK is not carbonized as ozone ^^ = a control substance, the free water of ozone water transferred to the use point> t is up to 8.2 mg / L. There is a great deal of variation in the relationship between the output of the iS k silver lamp and the azo crop. Row 2 As an ozone t ^ i means, a test was performed using the mouth 13 shown in FIG. The Yu O zo ^? Concentration of ozone water cold Sahima outlet of in the same manner as in Example 1 was measured using a O zone 2, Ji 0 2 concentration 31118 / /, ozone concentration 25, 9 mg / L O A zonal water was prepared. This ozone water was heated to 25 ° C with calo, and it was allowed to flow out at 25 ° C for | 去 | The ozone concentration of ozone water at the outlet of the cooler was 14. lmgZL. Heating with a heater at 30 ° C, 40 ° C, and 50 ° C, and when cooling to 25 ° C in the cool-off period, the free fertilizer at the outlet of the cooler is 12.8 mg /: L each. 10. Omg / L and 6.4 mg / L.
比較例 2 Comparative Example 2
パイロットプラントに供給した ^fokに炭酸ガスを添口溶解することなく、 赫オゾン 濃度 25.9mgZLのオゾン水を調製した以外は、 難例 2と同じ操作を行った。  The same operation as in Difficult Example 2 was performed, except that ozone water having a concentration of 25.9 mg ZL was prepared without dissolving carbon dioxide gas into the ^ fok supplied to the pilot plant.
オゾン水を、カロ で 25°Cに加熱し、 ί ^離では 25 °Cのまま流出させたとき、 !] 器出口のオゾン水の?雜オゾン濃度は、 6.0mgZLであった。 カロ «によるカロ熱 を 30°C、 40°C、 50°Cとし、 冷去暇で 25 °Cに冷却したとき、 出口のオゾン水 の游オゾ 濃度は、 それぞれ 2. Omg/L、 0.6mgZL、 0.6mg/Lであった m 2及び比較例 2の結果を、 第 2表に示す。  When ozone water is heated to 25 ° C with calo and discharged at 25 ° C for ί ^ separation,!? The concentration of ozone was 6.0 mgZL. When the caloric heat due to caro is 30 ° C, 40 ° C, and 50 ° C, and the air is cooled to 25 ° C during the cool-off period, the free ozone concentration of the ozone water at the outlet is 2.Omg / L and 0.6mgZL, respectively. Table 2 shows the results of m 2, which was 0.6 mg / L, and Comparative Example 2.
Figure imgf000014_0001
第 2表に見られるように、超辛 fckにオゾン 柳制物質として炭酸を させた雄例 W
Figure imgf000014_0001
As can be seen in Table 2, a male example of carbonation of super hot fck as ozone willow substance W
2では、力ロ»によるカロ熱 を上昇すると、 オゾンが^军してきオゾ^度が低下し 、力 P熱離と ί雜ォゾ f農度の M系はなだらカゝな曲線となるので、カロ騰によるカロ辦 を制御することにより、 所望の? 才ゾ 農度のオゾン水を安定して得ることができる。 これに対して、 ¾Kにオゾン^^抑制物質としての炭酸を させな 、比較例 2では、 カロ βで加熱することにより、 オゾン水の? オゾン濃度力 S急激に低下している。 In (2), when the calorie heat due to the power is increased, ozone is released and the ozone is reduced, and the M system of the power P heat release and the 農 ォ f f is a smooth curve. By controlling the calorie due to the rise in calories, it is possible to stably obtain ozone water of a desired degree. In contrast, in Comparative Example 2, the carbon dioxide as the ozone-suppressing substance was not allowed to be applied to ¾K, and the ozone-water concentration power S sharply decreased by heating with caro β.
麵列 3 Row 3
オゾン濃度調整手段として、 F i g. 2に示す主波長 253.7 nmで調光機倉を有す る ©¾k銀ランプ [千代田ェ販 (株)、 GL— 4、 GL— 10および GL— 40] を備えた ifekセルを用!/、て試験を行つた。  As a means of adjusting ozone concentration, it has a dimmer chamber with a dominant wavelength of 253.7 nm as shown in Fig. 2. © ¾k silver lamp [Chiyoda Corporation, GL-4, GL-10 and GL-40] The test was performed using an ifek cell with! /.
雄例 1と同様にして、 C〇2濃度 3mg/L、 游オゾン濃度 25.9mg/Lのォゾ ン水を調製し、 通水セルに空間 (S V) 2, 000 h— 1で通水し、 観k銀ランプの出 力を 1.6 Wから 40Wまで変化させた。 ί©Ϊ7_Κ銀ランプの出力とセル出口のオゾン水の ^#才ゾ; 農度の関係は、 1.6Wのとき 20. Omg/L, 3.6Wのとき 13.9mgZ L、 5.6Wのとき 11. lmg/L、 9.9Wのとき 8.1 mg/L、 15.0Wのとき 7. 7mgZL、 20. OWのとき 3.8mgZL、 31.8Wのとき 3.4mg/L、 40.0 Wのとき 2.7mgZLであった。 Prepare ozone water with a concentration of C ォ2 of 3 mg / L and a free ozone concentration of 25.9 mg / L in the same manner as in Male Example 1, and let the water flow through the cell with a space (SV) of 2,000 h- 1. The output of the silver lamp was changed from 1.6 W to 40 W. ί © Ϊ7_Κ The output of the silver lamp and the ozone water at the outlet of the cell ^ # years old; The relationship between the agricultural degree is 20. Omg / L at 1.6W, 13.9mgZL at 3.6W, 11. lmg at 5.6W It was 8.1 mg / L at / L, 9.9W, 7.7mgZL at 15.0W, 3.8mgZL at 20.OW, 3.4mg / L at 31.8W, and 2.7mgZL at 40.0W.
例 3の結果を、 第 3表に示す。  Table 3 shows the results of Example 3.
第 3表に見られるように、 ¾*fekにオゾン^^抑制物質として炭酸を させた 例 As shown in Table 3, ¾ * fek is carbonated as an ozone-suppressing substance
3では、 ¾kセルの teffiTk銀ランプの出力を上昇すると、 オゾンが^^して^ ォゾン濃 度が低下し、 出力と游ォゾ 農度の関係はなだらカゝな曲線となるので、 iS¾k銀ランプ の出力を制御することにより、 所望の? »才ゾ^農度のオゾン水を安定して得ることがで きる。 特に、 ランプ出力 20 W以下の齢が、 ランプ出力と游ォゾン濃度の遍カ S安定 している。 In Fig. 3, when the output of the teffiTk silver lamp in the ¾k cell is increased, ozone is reduced and the ozone concentration is reduced, and the relationship between the output and the free fertility is a smooth curve. By controlling the output of the silver lamp, it is possible to stably obtain ozone water of a desired level. In particular, the lamp output and the age of less than 20 W are stable in the lamp output and the concentration of free ozone.
《表 "table
Figure imgf000016_0001
難例 4
Figure imgf000016_0001
Difficult case 4
オゾン濃度調整手段として、 F i g. 2に示す主波長 253. 7 nmで調光機能を有す る iS¾K銀ランプ [千代田ェ販 (株)、 GL— 4、 GL— 10および GL— 40] を備えた As an ozone concentration adjusting means, an iS¾K silver lamp with a dimming function at the main wavelength of 253.7 nm as shown in Fig. 2 [Chiyoda Sales, GL-4, GL-10 and GL-40] With
¾kセルを用レヽて纖を行つた。 Using the k-cell, we made fiber.
ノ ィ口ットプラントに超術 Jを供給し、 炭酸ガス添口手段としての炭酸ガスボンベから 、 C02濃度 3mgノ Lになるように、 炭酸ガスを超 l¾jに勸ロ溶解し、 ォゾ 容解装置 で炭酸ガス溶解 钝水にオゾンを溶解して、 オゾン濃度 36. 5m g/Lのオゾン水 を調製し、 通水セルに空間速度(SV) 6, 000 h—1で通水し、 ί©£水銀ランプの出力を 1.5Wから 17. OWまで変化させた。 ©¾銀ランプの出力とセル出口のオゾン水の溶 存才ゾ^ の関係は、 1.5Wのとき 20. Omg/L、 3.6Wのとき 13.9mg/L 、 5.5Wのとき 10.9mg/L、 9.8 のとぎ 8.3mg/L、 17.0"Wのとき 5.0 mgZLであつに。 In Bruno I port Ttopuranto supplying super operator J, the carbon dioxide gas cylinder as carbon dioxide添口means, so that the C0 2 concentration 3mg Bruno L, and勸Ro dissolved carbon dioxide in the super L¾j, O zo Yokai device Dissolve ozone in water to prepare ozone water with an ozone concentration of 36.5 mg / L, and pass water through the water flow cell at a space velocity (SV) of 6,000 h— 1. £ mercury lamp output It was changed from 1.5W to 17.OW. © The relationship between the output of the silver lamp and the dissolving capacity of ozone water at the cell outlet is 20. Omg / L at 1.5W, 13.9mg / L at 3.6W, 10.9mg / L at 5.5W, 9.8 togi 8.3mg / L, 17.0 "W, 5.0mgZL.
比較例 3 Comparative Example 3
ノ ィロットプラントに供給した超 ffekに炭酸ガスを-励口溶角することなく、 ?雜オゾン 濃度 36.5 m g Z Lの才ゾン水を調製した以外は、 実施例 4と同じ操作を行つた。 f©± 水銀ランプの出力とセル出口のオゾン水の オゾン濃度の関係は、 1.5Wのとき 31. 8mg/L、 3.6Wのとき 25.7mg/L、 5.5Wのとき 18.8mg/L、 9.8W のとき 14. lmgZL、 17. OWのとき 10. OmgZLであった。  Carbon dioxide is supplied to ultra ffek supplied to the pilot plant- The same operation as in Example 4 was performed, except that the prepared ozone water having the ozone concentration of 36.5 mg ZL was prepared. f © ± The relationship between the output of the mercury lamp and the ozone water ozone concentration at the cell outlet is 31.8 mg / L at 1.5 W, 25.7 mg / L at 3.6 W, 18.8 mg / L at 5.5 W, 9.8 W At that time, it was 14. lmgZL, and at OW, it was 10. OmgZL.
実施例 4及び比較例 3の結果を、 第 4表及ぴ F i g. 5に示す。  The results of Example 4 and Comparative Example 3 are shown in Table 4 and FIG.
第 4表  Table 4
Figure imgf000017_0001
第 4表及び F i g. 5に見られるように、 «jにオゾン 军抑制物質として炭酸を存 在させた^ ¾例 4では、 空間速度(S V) 6, 000 h— 1のように通水セルでの滞留時間が 短くても、 iizkセルの ί©ΕτΚ銀ランプの出力を上昇すると、 オゾンが ^^して^ オゾン 濃度が低下し、 出力と游ォゾン の関係はなだらカゝな曲線となるので、 iS¾k銀ラン プの出力を制御することにより、 所望の赫ォゾ W農度のオゾン水を安定して得ることが できる。 これに対して、 超 ffeRにオゾン^军抑制物質としての炭酸を させない比較例 3では、 空間速度(SV) 6, 0001T1のように通水セルでの滞留時間が短レヽと、 游ォ ゾ 農度は低下が少なく、 teffiTk銀ランプの出力と^ オゾン濃度の関係のばらつきが大 きい。
Figure imgf000017_0001
As can be seen in Table 4 and Fig. 5, «j contains ozone 炭 酸 and carbonic acid as a suppressor ^ ¾ In Example 4, the space velocity (SV) is 6,000 h- 1. Residence time in water cell Even if it is short, when the output of the iz © ΕτΚ silver lamp of the iizk cell is increased, ozone is ^^ and the ozone concentration is reduced, and the relationship between output and free ozone is a smooth curve, so iS¾k silver By controlling the output of the lamp, it is possible to stably obtain ozone water having a desired level of water. In contrast, in Comparative Example 3 Ultra ffeR not cause a carbonate as ozone ^军抑system material, residence time in the water flow cell as a space velocity (SV) 6, 0001T 1 and the short Rere, Yuo zone The degree of decline in the agricultural level is small and the relationship between the output of the teffiTk silver lamp and the ozone concentration is large.
麵列 5 Row 5
オゾン濃度霞手段として、超音波発 β [(株)プレテック製、 ΡΤ005 J IA] を '取り付けた セルを用レ、て試験を行つた。  The test was performed using a cell equipped with an ultrasonic generator β [セ ル 005 JIA] manufactured by Pretec Co., Ltd. as a means of ozone concentration haze.
1と同様にして、 C 02濃度 3mg/L, オゾン濃度 25. 9mg/Lのォゾ ン水を調製した。 このオゾン水をセルに し、 出力 30W、 40W、 50W:¾ 60W で周波数 39kHzの超音波を発振し、 オゾン水に照 した。 1 in the same manner as was C 0 2 concentration 3 mg / L, the O zone down water ozone concentration 25. 9 mg / L was prepared. This ozone water was made into a cell, and ultrasonic waves with a frequency of 39 kHz were oscillated at an output of 30 W, 40 W, and 50 W: ¾60 W, and illuminated with the ozone water.
¾ セル出口のオゾン水の オゾン濃度は、 出力 30Wのとき 19mg/L、 4 OW のとき 17mgZL、 5 OWのとき 15mgZL、 6 OWのとき 14m gZLであった。 比較例 4  オ ゾ ン The ozone concentration at the cell outlet was 19mg / L at 30W output, 17mgZL at 4OW, 15mgZL at 5OW, and 14mgZL at 6OW. Comparative Example 4
ノイロットプラントに供給した ¾ 7に炭酸ガスを^)口溶解することなく、 ?雜オゾン 濃度 25. 9mg/Lのオゾン水を調製した以外は、 実施例 5と同じ操作を行った。  Without dissolving carbon dioxide gas into the ¾7 supplied to the Neulot plant, without? The same operation as in Example 5 was performed except that ozone water having a concentration of 25.9 mg / L was prepared.
通水セル出口のオゾン水の^ オゾン濃度は、 出力 3 OWのとき 5mg/L、 40 W( とき 6mgZL、 5 OWのとき 6mgZL、 6 OWのとき 3mg/Lであった。  The ozone concentration of ozone water at the outlet of the flow cell was 5 mg / L at an output of 3 OW, 40 W (6 mgZL at 5 OW, 6 mgZL at 5 OW, and 3 mg / L at 6 OW).
実施例 5及び比樹列 4の結果を、 第 5表に示す。  Table 5 shows the results of Example 5 and Comparative Tree 4.
第 5表  Table 5
Figure imgf000018_0001
第 5表に見られるように、 趣脉にオゾン 柳制物質として炭酸を雜させた 例 5では、 ¾kセルの超音波斜言器の出力を上昇すると、 オゾンカ^^して^ ォゾ ^農度 力 s低下し、 出力と游ォゾ zi gの関係はなだら力な曲線となるので、 .超音波発露の出 力を制御することにより、.所望の オゾ^農度のオゾン水を安定して得ることができる
Figure imgf000018_0001
As shown in Table 5, an example of carbon dioxide as an ozone willow substance in the vein In Fig. 5, when the output of the ultrasonic oblique device in the ¾k cell is increased, the ozone intensity is reduced and the fertilizer power is decreased, and the relationship between the output and the free zig becomes a gentle curve. Therefore, by controlling the output of ultrasonic dew, it is possible to stably obtain ozone water of the desired ozone level.
。 これに対して、 懇 こオゾン^^抑制物質としての炭酸を^ &させない比樹列 4では 、 超音波発 βの出力と? ^ ォゾ 農度の間に一定の^^がなく、 しかもオゾンの が 多く、 游オゾン濃度の低下の驗が大きレヽ。 . On the other hand, in the specific tree sequence 4 that does not cause carbon dioxide as a suppressive ozone ^^ inhibitory substance, there is no fixed ^^ between the output of ultrasonic wave β and? The decrease in free ozone concentration was significant.
鐘列 6 Bell column 6
ォゾ f農度 手段として、 マグネチックスターラー [ァズワン (株)、 HS-3B] に よる を行うための回車好を A bたガラスセルを用レ、て纖を行った。  As a means of farming, fiber was turned on using a glass cell with a turntable for magnetic stirrer [Az-One Co., Ltd., HS-3B].
難例 1と同様にして、 C 02濃度 3 m g ZL、 游オゾ 濃度 25. 9m g /Lのォゾ ン水を調製した。 このオゾン水をガラスセルに »し、 回 の回 100 r pm、 5 00 r pm、 1, 000 r p m又は 1, 500 r p mで した。 In the same manner as flame Example 1 was C 0 2 concentration 3 mg ZL, the O zone down water Yu ozone concentration 25. 9m g / L was prepared. The ozone water was applied to a glass cell, and was applied at 100 rpm, 500 rpm, 1,000 rpm or 1,500 rpm each time.
ガラスセル出口のオゾン水の溶存オゾン濃度は、 回転子の回! ¾女 100 r pm、 500 r pm、 l, 000 r pm、 1, 500 r pmのとき、 それぞ、れ 19mgZL、 15mg/ L、 13mgZL、 1 Smg/Lであった。  The dissolved ozone concentration of the ozone water at the glass cell outlet is determined by the rotation of the rotor! ¾Female 100 rpm, 500 rpm, l, 000 rpm, 1,500 rpm, 19 mgZL, 15 mg / L, respectively , 13 mg ZL and 1 Smg / L.
比較例 5 Comparative Example 5
ノィロットプラントに供給した ¾ifekに炭酸ガスを勸 P溶解することなく、 游オゾン 濃度 25.9 mg/Lのオゾン水を調製した以外は、 雄例 6と同じ操作を行った。  The same operation as in Example 6 was carried out, except that ozone water having a free ozone concentration of 25.9 mg / L was prepared without dissolving carbon dioxide in the ¾ifek supplied to the neurot plant.
ガラスセル出口のオゾン水の游ォゾ f農度は、 回事^? "の回車激 100 r pm、 500 r pm、 l, 000 r pm、 1, 500 r pmのとき、 それぞれ 5mgZL、 7mg/L, 4mgZL、 5mg/Lであった。  Ozone water at the outlet of the glass cell At 100 rpm, 500 rpm, l, 000 rpm, and 1,500 rpm, the rotation was 5 mgZL, 7 mg / L, 4 mgZL, and 5 mg / L, respectively.
例 6及び比樹列 5の結果を、 第 6表に示す。  Table 6 shows the results of Example 6 and comparative tree sequence 5.
第 6表  Table 6
雜ォゾン濃度 (mg/L)  Maleozone concentration (mg / L)
回車激( r pm)  Round car (rpm)
実施例 6 比較例 5  Example 6 Comparative Example 5
100 19 5  100 19 5
500 15 7  500 15 7
1000 13 4  1000 13 4
1500 12 5 第 6表に見られるように、 超¾7にオゾン^^抑制物質として炭酸を被させた難例 6では、 回 の回車 を上昇すると、 オゾンが 军して雜オゾン濃度が低下し、 回転 数と游ォゾ f農度の関係はなだらカゝな曲線となるので、 回車好の回歸女で辦の強さを 制御することにより、 所望の ォゾ 農度のオゾン水を安定して得ることができる。 こ れに対して、 超 ¾Rにオゾン^^抑制物質としての炭酸を させない比較例 4では、 回 ^の回皐逾と^ #オゾン濃度の間に一定の関係がなく、 しかもオゾンの ^^が多 溶 存ォゾ ^の低下の键が大きレ、。 1500 12 5 As can be seen in Table 6, in Difficult Example 6, where carbon dioxide was applied as an ozone-suppressing substance to super ¾7, when the number of rotations was increased, ozone was released and the ozone concentration decreased, and the rotation speed was reduced. Since the relationship between と and 游 ゾ 農 農 農 農 農 農 度 度 f 農 農 度 と と だ ら な だ ら な だ ら 曲線 、 、 、 、 、 、 Obtainable. On the other hand, in Comparative Example 4 in which carbon dioxide as an ozone-suppressing substance was not added to the super-R, there was no fixed relationship between the repetition time and the ozone concentration, and the ozone concentration was low. The large decrease in the amount of poly-dissolved ozone is large.
麵列 麵 row
オゾン濃度 手段として、過酸ィ bk素を添口して試験を行った。 As a means of ozone concentration, a test was conducted with peroxyperoxide.
m 6と同じ装置のガラスセルの入口側に過酸ィ 素水 ¾λ口を付け、 マグネチック スターラーにより回転子を回! ¾女 100 r p mで回転させて »し、 1重量0 /0過酸 ffek素 水を注入して、 オゾン水中の過酸化水素濃度を 5m gZL、 7mgZL、 15mgZL、 22mgZL、 32mgZし、 5 Omg/Lとした。 Attach a peroxygen solution ¾λ port to the inlet side of the glass cell of the same device as m6, and turn the rotor with a magnetic stirrer! It rotated at ¾ woman 100 rpm and », 1 weight 0/0 by injecting peracid ffek oxygen water, a hydrogen peroxide concentration of the ozone water 5m gZL, 7mgZL, 15mgZL, 22mgZL , and 32mgZ, 5 Omg / L And
ガラスセル出口のオゾン水の オゾン濃度は、 オゾン水中の過酸ィ匕水素濃度を 5 m g /L、 7mg/L、 15mg/L、 22mg/Ls 32mg/L、 50mgZLとしたと き、 それぞれ 18mgZレ 16mg/L, 8mg/L, 6mg/L, 5mg/L, 4m gZLであった。 The ozone concentration of ozone water at the glass cell outlet is 18 mgZ when the hydrogen peroxide concentration in the ozone water is 5 mg / L, 7 mg / L, 15 mg / L, 22 mg / L s 32 mg / L, and 50 mgZL. Re: 16mg / L, 8mg / L, 6mg / L, 5mg / L, 4mgZL.
比較例 6 Comparative Example 6
パイロットプラントに供給した «7]に炭酸ガスを^)口?容角することなく、 オゾン 濃度 25.9 m g/Lのオゾン水を調製した以外は、 «例 7と同じ操作を行った。  The same operation as in Example 7 was performed except that ozone water with an ozone concentration of 25.9 mg / L was prepared without introducing carbon dioxide into the pilot plant [7] without injecting carbon dioxide.
ガラスセル出口のオゾン水の溶存オゾン濃度は、 オゾン水中の過酸ィ匕水素濃度を 5m g /L 7mg/L、 15mg/L, 22mg/L, 32mg//L, SOmg/Lとしたと き、 それぞれ 5mg/L、 4mgZL、 5mgZL、 3mg/L、 4mgZL、 3mgZ であった。 Dissolved ozone concentration of ozone water glass cell outlet, can the Kasani匕水iodine concentration of ozone in water 5m g / L 7mg / L, 15mg / L, 22mg / L, 32mg / / L, and was SOMG / L The results were 5 mg / L, 4 mgZL, 5 mgZL, 3 mg / L, 4 mgZL, and 3 mgZ, respectively.
例 7及び比較例 6の結果を、 第 7表に示す。 第 7表 Table 7 shows the results of Example 7 and Comparative Example 6. Table 7
Figure imgf000021_0001
第 7表に見られるように、 ¾kにオゾン^ 卬制物質として炭酸を被させた雄例
Figure imgf000021_0001
As can be seen in Table 7, a male example of carbonation of オ ゾ ン k with ozone ^ 卬
7では、 '励口する過酸ィ tok素の量を増すと、 オゾンが して游オゾン濃度力 下し、 過酸ィは素の添口量と游オゾン濃度の関係はなだらカゝな曲線となるので、過酸ィ 素の 添加量を制御することにより、 所望の^ ォゾ^農度のオゾン水を安定して得ることがで きる。 これに対して、 ¾ feKにオゾン 军抑制物質としての炭酸を ¾させない比較例 6 では、 過酸ィ匕水素の添加量と ^^オゾン濃度の間に一定の関係がなく、 しかもオゾンの分 解が多く、游ォゾ W農度の低下の @gが大きい。 In Figure 7, when the amount of peroxygen to be stimulated is increased, ozone is released and the concentration of free ozone is reduced, and the relationship between the amount of added peroxygen and the free ozone concentration is rather poor. Since the curve becomes a curve, it is possible to stably obtain ozone water having a desired degree of agriculture by controlling the amount of added silicon peroxide. On the other hand, in Comparative Example 6 in which ¾ feK did not emit carbonic acid as an ozone-suppressing substance, there was no fixed relationship between the amount of hydrogen peroxide added and the ^^ ozone concentration. , And the @g of the decline in Yuzo W farming is large.
鐘列 8 Bell column 8
オゾン ^抑制物質としてィソプロピルアルコール (以下、 I P Aという)を用 ヽて試験 を行 た。  The test was performed using isopropyl alcohol (hereinafter referred to as IPA) as an ozone-suppressing substance.
¾¾ 列 1の炭酸ガスの代わりに、 I PA濃度 5 0 μ g/Lになるように I P Aを超 に励口溶解した以外は、 魏例 1と同様にして、 ffiffiTk銀ランプの出力を変化させて纖 を行った。  出力 The output of the ffiffiTk silver lamp was changed in the same manner as in Wei Example 1, except that the IPA concentration was increased to 50 μg / L in place of the carbon dioxide gas in column 1, except that the IPA was melted. I did fiber.
その結果、 セル出口の游ォゾ f農度は第 8表に示す通りであった。 第 8表 As a result, the Yuzo f agriculture at the cell outlet was as shown in Table 8. Table 8
Figure imgf000022_0001
この結果から、 オゾン^^抑制物質として I P Aを用いたときも、 ランプ (紫外線)出力 に応じてォゾ 農度を fi¾できること力 s分かる。 産業上の利用可能性
Figure imgf000022_0001
From these results, it can be seen that even when IPA is used as the ozone-suppressing substance, the ozone fertility can be adjusted according to the lamp (ultraviolet) output. Industrial applicability
本発明のオゾン水供給方法及 Ό 置によれば、 オゾンの分解を抑制してオゾン農度の高 レ、オゾン水をユースポィントまで移送し、 ユースポィント近傍にぉレヽて、 ォゾ 農i 整 手段を用いて所定のオゾン濃度に低下させ、 ユースポイントに所定濃度のオゾン水を安定 して供^ることができる。  ADVANTAGE OF THE INVENTION According to the ozone water supply method and apparatus of this invention, decomposition | decomposition of ozone is suppressed, ozone agriculture is high, ozone water is transported to a use point, and the ozone agriculture is arranged near a use point. Ozone water of a predetermined concentration can be stably supplied to the use point by lowering the ozone concentration to a predetermined value by using means.

Claims

し — 求の範囲 Shi — the scope of the request
1. オゾン ^^抑制物質を させたオゾン水をユースポィントに移送し、 ユースボイン ト近傍にぉレ、て濃度言纖手段により所定のォゾ f農度に低下させることを擀敫とするォゾ ン水觸合^去。 1. The ozone water containing the ozone-suppressed substance is transferred to the use point, and is brought close to the use point to reduce the concentration to a predetermined level by a fiber means. The water zone is gone.
2. オゾン^抑制物質が、 水溶性 匕合物、 はその ぴヒドラジンからな る群から選ばれる 1 は 2種以上である請求の範囲 1記載のォゾ 供給方法。  2. The ozone supply method according to claim 1, wherein the ozone-suppressing substance is selected from the group consisting of a water-soluble conjugate, and hydrazine.
3. 解«¾はその塩が、 塩酸、 «、 炭酸、 炭^^、 炭^ K素塩、 亜硝酸、 亜 5¾ 、 亜硫酸、 は 素塩である請求の範囲 2記載の才ゾン水供合;^去。  3. The salt solution according to claim 2, wherein the salt is hydrochloric acid, «, carbonic acid, charcoal ^^, charcoal ^ K salt, nitrous acid, nitrous acid, sulfuric acid, sulfurous acid, is a salt. ; ^ Leave.
4. 濃度 手段が、 才ゾンの分解である請求の範囲 1記載のオゾン水供給方法。4. The method for supplying ozone water according to claim 1, wherein the concentration means is a decomposition of genzo.
5. 游ォゾンの ^率を、 超音波照射、 紫外線照射、 舌 発生、 m カロ温、 アルカリ添 力 Π及び過酸ィ! i7j素添カロからなる群から選ばれる 1¾Xは 2種以上の手段により行う請求の 範囲 4記載のオゾン水供給紘 5. The 率 ozone ratio is determined by ultrasonic irradiation, ultraviolet irradiation, tongue generation, m-calo temperature, alkali addition Π and peroxy acid! The ozone water supply described in claim 4.
6. 濃度調整手段が、 オゾン水の希 である請求の範囲 1言 のオゾン水供給;^去。  6. Supply of ozone water according to claim 1, wherein the concentration adjusting means is a rare ozone water;
7. オゾン水のユースポイントへの移送を、 オゾン水とオゾンガスが する気液混合状 態で行う請求の範囲 1乃至 6のレヽ かに記載のオゾン水供給; ^去。 7. The supply of ozone water according to any one of claims 1 to 6, wherein the transfer of the ozone water to the use point is performed in a gas-liquid mixture of the ozone water and the ozone gas.
8. 純水にオゾンガスを溶解させてオゾン水を調製するオゾン溶解装置、 tiit¾feK又は前 記才ゾン水にオゾン分解抑制物質を供給する手段、 己才ゾン容角翠装置で調製した才ゾン 水をユースポイントへ移送するオゾン水移避己管、 ユースポイント近傍に設けられ、 ォゾ ン 7 送配管で移送されたオゾン水を所定のオゾン濃度に低下させる濃翻整手段を有す ることを ί敷とするオゾン水供^ ¾  8. An ozone dissolving device that dissolves ozone gas in pure water to prepare ozone water, tiit¾feK or a means for supplying an ozone decomposition inhibitor to the above-mentioned genius zonal water, Ozone water transfer evacuation pipe for transferring to the point of use, provided near the point of use, and a means for concentrating and regulating the ozone water transferred by the ozone 7 transmission pipe to a predetermined ozone concentration. Ozone water supply to be laid ^ ^
9. オゾン ^^抑制物質が、 水溶性有衞匕合物、 嫌 ¾Xはその ぴヒドラジンからな る群から選ばれる 1 @Xは 2種以上である請求の範囲 8記載のオゾン水供給装 So 9. The ozone water supply apparatus according to claim 8, wherein the ozone-suppressing substance is a water-soluble arid compound, and X is selected from the group consisting of hydrazine.
1 0. はその塩が、 «、 、 炭酸、 炭^^、 炭^素塩、 亜硝酸、 亜«¾ 、 亜 ¾¾、
Figure imgf000023_0001
10 0. The salt is «,, carbonic acid, charcoal ^^, charcoal salt, nitrous acid, nitrous acid, nitrous acid, nitrous acid,
Figure imgf000023_0001
1 1. 濃 J P整手段が、 ^^オゾンの^^である請求の範囲 8記載のオゾン水供;^^ 1 1. The ozone water supply according to claim 8, wherein the concentrated JP adjusting means is ^^ of ozone.
1 2. オゾンの ^军を、 超音波照射、 紫外! ¾ ^射、 乱流発生、 mカロ温、 アルカリ 勸吸ぴ過酸ィ (^R素 ¾¾JPからなる群から選ばれる 1@Xは 2種以上の手段により行う請求 の範囲 1 1記載のオゾン水供糸 1 2. Ultrasonic irradiation and ultraviolet irradiation of ozone ^ 军! The ozone water according to claim 11, wherein 1 @ X selected from the group consisting of 射 ^ radiation, turbulent flow generation, m-caloric temperature, alkali Service
1 3· 濃度 手段が、 オゾン水の希釈である請求の範囲 8記載のオゾン水供給装 13. The ozone water supply device according to claim 8, wherein the concentration means is ozone water dilution.
1 4. オゾン水のユースポイントへの移送を、 オゾン水とオゾンガスが^ する気液混合 状態で行う請求の範囲 8乃至 1 3のレ、f¾かに言識のオゾン水供給 ^去。 1 4. The transfer of ozone water to the point of use is performed in a gas-liquid mixture of ozone water and ozone gas.
PCT/JP2005/005632 2004-03-31 2005-03-18 Method of ozone water supply and ozone water supply apparatus WO2005096359A1 (en)

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