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WO2010058607A1 - Dispositif de stérilisation aux ultraviolets pour eau extérieure - Google Patents

Dispositif de stérilisation aux ultraviolets pour eau extérieure Download PDF

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Publication number
WO2010058607A1
WO2010058607A1 PCT/JP2009/006295 JP2009006295W WO2010058607A1 WO 2010058607 A1 WO2010058607 A1 WO 2010058607A1 JP 2009006295 W JP2009006295 W JP 2009006295W WO 2010058607 A1 WO2010058607 A1 WO 2010058607A1
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WO
WIPO (PCT)
Prior art keywords
ultraviolet
outdoor water
uvc
sterilizer
uva
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/JP2009/006295
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English (en)
Japanese (ja)
Inventor
高橋章
木内陽介
芥川正武
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
SILVER MAKING CO Ltd
University of Tokushima NUC
Original Assignee
SILVER MAKING CO Ltd
University of Tokushima NUC
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by SILVER MAKING CO Ltd, University of Tokushima NUC filed Critical SILVER MAKING CO Ltd
Priority to EP09827388.1A priority Critical patent/EP2394963B1/fr
Priority to JP2010539163A priority patent/JPWO2010058607A1/ja
Priority to US13/130,574 priority patent/US8324595B2/en
Publication of WO2010058607A1 publication Critical patent/WO2010058607A1/fr
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K63/00Receptacles for live fish, e.g. aquaria; Terraria
    • A01K63/04Arrangements for treating water specially adapted to receptacles for live fish
    • 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
    • C02F1/325Irradiation devices or lamp constructions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • 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
    • C02F2201/32Details relating to UV-irradiation devices
    • C02F2201/322Lamp arrangement
    • C02F2201/3221Lamps suspended above a water surface or pipe
    • 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
    • C02F2201/32Details relating to UV-irradiation devices
    • C02F2201/322Lamp arrangement
    • C02F2201/3222Units using UV-light emitting diodes [LED]
    • 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
    • C02F2201/32Details relating to UV-irradiation devices
    • C02F2201/322Lamp arrangement
    • C02F2201/3225Lamps immersed in an open channel, containing the liquid to be treated
    • 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
    • C02F2201/32Details relating to UV-irradiation devices
    • C02F2201/322Lamp arrangement
    • C02F2201/3227Units with two or more lamps
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Definitions

  • the present invention relates to an apparatus for sterilizing outdoor water, such as sewage, pool water, fish culture pond water, etc., which is drained outdoors and irradiated with sunlight.
  • Sterilization is indispensable not only in our daily life but also in industry.
  • chemical sterilization methods such as chlorine, heat sterilization, ultraviolet sterilization, and ozone sterilization are known as sterilization methods.
  • Higher quality sterilization techniques are required from the standpoint of no residue and environmental friendliness. From such a background, a sterilization method using ultraviolet rays (UV), that is, ultraviolet sterilization has been widely used.
  • UV ultraviolet rays
  • UV sterilization unlike sterilization with chemicals, has no residue and is excellent in safety. In addition, since it destroys bacterial DNA, it has the advantage of not creating resistant bacteria unlike drug sterilization.
  • the sterilization mechanism by UV is generally explained as follows. Nucleic acids (DNA) that control genetic information exist in cells of organisms, including bacteria, and when UV is irradiated, the nucleic acids absorb the light, and some pyrimidines (mainly thymines) are pyrimidine dimers. It is said that the transcriptional control from the gene is delayed and the metabolism is disturbed, resulting in death.
  • DNA Nucleic acids
  • pyrimidines mainly thymines
  • Patent Document 1 An apparatus for sterilizing water using ultraviolet rays has been developed.
  • the apparatus described in this publication sterilizes the treated water flowing in the tube with an ultraviolet light source provided outside the tube.
  • the ultraviolet light source is a lamp or a light emitting diode, and sterilizes the treated water of the tube by irradiating it with ultraviolet light.
  • This device can sterilize water without the use of chemicals.
  • UV sterilization inactivates microorganisms by causing damage to intracellular DNA, but when irradiated with sunlight, microorganisms deactivated by UV irradiation are included in the sunlight. In other words, it regains its activity with near-ultraviolet rays or visible rays, and grows.
  • the sterilizing power is reduced due to the light recovery phenomenon.
  • the light recovery phenomenon occurs when light near 400 nm activates a gene repair enzyme (photolyase) to repair the formation of a pyrimidine dimer. Sterilization by ultraviolet light is due to chromosomal damage caused by directly damaging microbial DNA to form pyrimidine dimers. However, when the microorganisms inactivated by ultraviolet rays are irradiated with light of around 400 nm, the gene repair enzyme (photolyase) is activated and the formation of the pyrimidine dimer is repaired, and the microorganisms due to the light recovery phenomenon are recovered. Activation occurs.
  • FIG. 1 is a graph showing that microorganisms sterilized by a light recovery phenomenon grow.
  • the horizontal axis represents time (minutes), and the vertical axis represents the number of E. coli bacteria decreased by sterilization with the number of bacteria before sterilization being 1.
  • This figure shows that UVC ultraviolet light having a main emission peak of 254 nm is irradiated with an intensity of 0.01 mW / cm 2 for about 30 minutes to reduce the number of bacteria to 1/2500, and then the main emission peak is 365 nm.
  • the present invention was developed for the purpose of eliminating the above-mentioned adverse effects, and an important object of the present invention is to prevent an increase in the number of bacteria after sterilization due to a light recovery phenomenon and effectively sterilize with ultraviolet rays. It is to provide an ultraviolet sterilizer for outdoor water that can be used.
  • the ultraviolet sterilizer of the present invention sterilizes the outdoor water 9 by irradiating it with ultraviolet rays.
  • the ultraviolet sterilizer includes an ultraviolet light emitting diode 1 for irradiating UVA ultraviolet light having a main emission peak of 320 nm to 400 nm, and the outdoor water 9 is sterilized by sterilizing the outdoor water 9 with the UVA ultraviolet light emitted by the ultraviolet light emitting diode 1. Bacteria growth due to the light recovery phenomenon of the outdoor water 9 is prevented.
  • the ultraviolet sterilization apparatus described above has the feature that it prevents the increase in the number of bacteria after sterilization due to the light recovery phenomenon, and can effectively sterilize outdoor water irradiated with sunlight with ultraviolet rays.
  • FIG. 2 shows that the ultraviolet sterilization apparatus of the present invention can maintain an effective sterilization state even in a state where it is irradiated with sunlight by suppressing the light recovery phenomenon.
  • This figure shows that UVA ultraviolet light having a main emission peak of 365 nm is irradiated with an ultraviolet light emitting diode at an intensity of 70 mW / cm 2 for 30 minutes to reduce the bacterial count of E.
  • Curves A, B, and C indicate that the number of bacteria changes after sterilizing the number of bacteria to 1/800, and then irradiating with UV intensity of 0.01 mW / cm 2 , 0.09 mW / cm 2 , and 0.30 mW / cm 2. It shows the state to do.
  • the chain line in this figure shows a state in which light is not irradiated after sterilization to 1/800.
  • UVA ultraviolet rays are irradiated to sterilize the E. coli bacteria count to 1/800, and then UVA rays contained in solar rays are irradiated. Proliferation does not occur.
  • the number of bacteria may be further reduced by irradiation with UVA light.
  • FIG. 3 is a graph showing the sterilized state of Vibrio parahaemolyticus. This figure shows that UVC ultraviolet light with a main emission peak of 254 nm is irradiated and sterilized until the number of Vibrio parahaemolyticus bacteria is reduced to about 1/700, and then UVA light of 405 nm contained in sunlight is irradiated.
  • the UVA contained in sunlight It shows a state in which Vibrio parahaemolyticus is increased by irradiation with 405 nm light.
  • Curve A shows the number of bacteria of Vibrio parahaemolyticus sterilized with UVC
  • curve B shows the number of bacteria of Vibrio parahaemolyticus sterilized with UVA UV light.
  • the chain line C is in a state in which the number of bacteria is sterilized to 1/700 with UVC and is not irradiated with light
  • the chain line D is in a state in which the number of bacteria is sterilized with UVA to 1/700 and is not irradiated with light.
  • the number of bacteria in Vibrio parahaemolyticus sterilized with UVC ultraviolet rays increases to 1/50 after 180 minutes due to the light recovery phenomenon. That is, the number of bacteria grows about 10 times or more by the light recovery phenomenon.
  • Vibrio parahaemolyticus sterilized with UVA ultraviolet rays hardly grows after 180 minutes and does not increase bacteria due to the light recovery phenomenon, as in the case where light is not irradiated after sterilization.
  • the above sterilization apparatus also realizes the following incidental features. Since the sterilizer uses UVA ultraviolet light emitting diodes that are close to visible light as ultraviolet rays, effective sterilization can be realized while preventing adverse effects on human eyes. Although conventional UV sterilization uses invisible UV rays, it is necessary to turn off the UV irradiation and stop the UV irradiation when a person is in the area. While checking the sterilization state, it is not necessary to turn on / off even when a person is present, and the sterilization effect can be exhibited by continuously lighting for 24 hours. Moreover, it can be installed without providing a special shielding material even in a place such as a wall that is visible to the human eye.
  • the outdoor water 9 can be any one of sewage, outdoor pool water, and fish culture pond water.
  • the above ultraviolet sterilizers are characterized in that they can be effectively sterilized even when they are exposed to sunlight by draining sewage, outdoor pool water, and fish culture pond water outdoors.
  • an apparatus for sterilizing sewage with ultraviolet rays has an excellent feature that the sterilized sewage is drained into a natural river or sea and does not adversely affect the natural environment like a medicine.
  • outdoor pool water can be effectively sterilized without adding chemicals such as chlorine, and therefore has no phytotoxicity to swimmers and can be used safely and safely.
  • fish farming in order to prevent fish death, a huge amount of antibiotics is added to the feed. Fish cultivated in this state is not preferable for food because antibiotics remain.
  • the sterilization apparatus of the present invention can effectively sterilize fish culture pond water, it can effectively prevent killing caused by fish bacteria. For this reason, the amount of antibiotics added to the bait can be significantly reduced, and the remaining amount of antibiotics can be limited. For this reason, it is possible to cultivate fish that can be eaten safely and safely.
  • the main light emission peak of the ultraviolet light-emitting diode 1 can be 350 nm to 380 nm.
  • the outdoor water ultraviolet sterilizer of the present invention can have a UVC light source 2 that emits UVC ultraviolet light.
  • FIGS. 4 to 6 are graphs showing a state in which the number of bacteria is changed by a light recovery phenomenon after sterilizing sewage with ultraviolet rays. These figures show the state in which the number of bacteria changes by irradiating with 365-nm UVA rays contained in sunlight with an intensity of 0.30 mW / cm 2 after sterilizing with ultraviolet rays, and irradiating the rays after sterilizing. The number of bacteria in the absence is shown by a chain line.
  • FIG. 4 shows a state where the number of bacteria is changed by irradiating UVC ultraviolet light having a main emission peak of 254 nm with an intensity of 0.02 mW / cm 2 by a solid line.
  • the bacteria sterilized with UVC ultraviolet rays are irradiated with sunlight and the number of bacteria rapidly increases. That is, the number of bacteria increases remarkably by the light recovery phenomenon.
  • FIG. 5 irradiates the UVA rays contained in the sun rays after sterilization by irradiating UVA ultraviolet rays having a main emission peak of 365 nm with an intensity of 70 mW / cm 2 . Proliferation due to the light recovery phenomenon of sterilized bacteria does not occur.
  • FIG. 6 the main emission peak and 254 nm, along with ultraviolet UVC to 0.02 mW / cm 2 intensity, the main emission peak and 365 nm, both UVA ultraviolet to strength and 70 mW / cm 2 This shows a state in which the number of bacteria is increased by sterilizing sewage by irradiating with water.
  • the ultraviolet sterilizer for outdoor water of the present invention can make the output of the UVC light source 2 smaller than the output of the ultraviolet light emitting diode 1.
  • the above sterilizer can effectively sterilize the UVC light source by making the output of the UVC light source smaller than the output of the UV light emitting diode, and can effectively sterilize by synergistic effect of the UVC light source and the ultraviolet light emitting diode.
  • the UV sterilizer shown in FIGS. 7 to 10 sterilizes the outdoor water of any one of sewage, outdoor pool water, and fish pond water by irradiating UVA ultraviolet rays.
  • 7 and FIG. 8 is set above the surface of the outdoor water 9 stored in the water tank 10 and irradiates UVA ultraviolet rays toward the outdoor water 9.
  • the ultraviolet sterilizer of FIG. 9 and FIG. 10 has a waterproof structure and is disposed in the liquid of the outdoor water 9 to irradiate the outdoor water 9 with ultraviolet rays.
  • an ultraviolet light emitting diode 1 that irradiates UVA ultraviolet rays is provided on the outer case 3.
  • 8 and 10 includes a UVC light source 2 that emits UVC ultraviolet light in addition to the ultraviolet light-emitting diode 1 in the exterior case 3.
  • the outer case 3 is provided with a reflective layer 4 that reflects ultraviolet rays on the inner surface.
  • the exterior case 3 shown in these figures is provided with a peripheral wall 5 around it, and effectively reflects the ultraviolet rays emitted from the ultraviolet light emitting diode 1 and the UVC light source 2 to irradiate the outdoor water 9.
  • the outer case 3 containing the UVC light source 2 prevents UVC ultraviolet rays from leaking outside through the peripheral wall 5.
  • the exterior case 3 incorporates a circuit board 6, and a plurality of ultraviolet light emitting diodes 1 are fixed to the circuit board 6.
  • the circuit board 6 shown in the figure has an elongated plate shape, and a plurality of ultraviolet light-emitting diodes 1 are arranged and fixed on the circuit board 6 in a plurality of rows.
  • the circuit boards 6 are arranged in a plurality of rows to increase the irradiation area of the ultraviolet light emitting diode 1.
  • the exterior case can incorporate a single circuit board, and a plurality of ultraviolet light emitting diodes can be fixed to the circuit board. Further, as shown in the perspective view of FIG. 11, the outer case 3 of FIGS.
  • FIG. 8 and 10 is an elongated plate-like circuit board 6 to which a plurality of ultraviolet light emitting diodes 1 are fixed, and a cylindrical elongated ultraviolet lamp.
  • a certain UVC light source 2 is alternately arranged and incorporated.
  • This structure has a feature that it can irradiate ultraviolet rays uniformly over a wide range from the plurality of ultraviolet light emitting diodes 1 and the UVC light source 2 fixed to the circuit board 6.
  • the opening of the outer case 3 is closed with a light-transmitting plate 7 in order to have a waterproof structure.
  • the translucent plate 7 is fixed to the outer case 3 with a waterproof member (not shown) such as packing interposed at the boundary with the end surface of the peripheral wall 5 in order to close the opening edge of the outer case 3 in a watertight manner.
  • the translucent plate 7 transmits the ultraviolet rays emitted from the ultraviolet light emitting diode 1 and the UVC light source 2 built in the outer case 3 and irradiates the outside. Therefore, quartz glass excellent in ultraviolet transmittance is used for the translucent plate 7.
  • quartz glass excellent in ultraviolet transmittance is used for the translucent plate 7.
  • calcium fluoride, magnesium fluoride, or the like can be used for the translucent plate.
  • the outer case 3 described above has a box-like container shape as a whole, and a circuit board 6 to which a plurality of ultraviolet light-emitting diodes 1 are fixed is disposed, or a plurality of ultraviolet light-emitting diodes 1 are fixed.
  • the circuit board 6 and the UVC light source 2 are arranged.
  • the ultraviolet sterilizer of the present invention does not specify the shape of the outer case or the arrangement of the ultraviolet light emitting diode and the UVC light source as the above structure.
  • the ultraviolet sterilization apparatus attaches a plurality of ultraviolet light emitting diodes side by side to the surface and / or the back surface of an attachment member having a flat shape, a rod shape, a cylinder shape, a box shape, a spherical shape, or an arbitrary shape.
  • ultraviolet rays emitted from the ultraviolet light-emitting diode can be emitted to the surroundings according to the shape of the mounting member, and can be irradiated to outdoor water.
  • the ultraviolet sterilizer of FIGS. 12 and 13 has a cylindrical outer case 23 coaxially piped with a translucent transfer tube 25 and a plurality of ultraviolet light emitting diodes 1 built in the outer case 23.
  • the UV light of UVA is irradiated from these ultraviolet light emitting diodes 1 to the transfer tube 25 to sterilize the outdoor water 9 transferred by the transfer tube 25.
  • this ultraviolet sterilizer transfers outdoor water 9 to a transfer pipe 25 through a circulator 28 such as a pump, and irradiates the outdoor water 9 passing through the transfer pipe 25 with ultraviolet rays. Sterilize the water 9.
  • the cylindrical outer case 23 is provided with a reflective layer 24 on the inner surface.
  • the transfer tube 25 is a cylindrical pipe and is made of quartz glass so that it can efficiently transmit ultraviolet rays emitted from the ultraviolet light emitting diode 1.
  • the plurality of ultraviolet light emitting diodes 1 are fixed to a circuit board 26 as an attachment member, and the circuit board 26 is fixed to the inside of a cylindrical outer case 23 at equal intervals.
  • the ultraviolet sterilization apparatus shown in the drawing is disposed inside the outer case 23, and the UVC light source 2 is disposed between the plurality of circuit boards 6. This ultraviolet sterilizer can irradiate UVA ultraviolet rays from the ultraviolet light emitting diode 1 and UVC ultraviolet rays simultaneously from the UVC light source 2 and sterilize the outdoor water 9 transferred by the transfer pipe 25 more effectively.
  • the ultraviolet sterilizer shown in FIGS. 14 and 15 has a plurality of ultraviolet light emitting diodes in a transparent container 33 that has a hermetic and waterproof property against water and transmits ultraviolet rays emitted from the ultraviolet light emitting diodes 1. 1 is built-in. As shown in FIG. 14, this ultraviolet sterilizer is disposed in a solution of outdoor water 9 and sterilizes by irradiating the outdoor water 9 with ultraviolet rays.
  • the container 33 has a cylindrical shape whose bottom is closed, and its upper opening is water-tightly closed with a lid 35.
  • the container 33 is made of quartz glass so that the ultraviolet rays emitted from the ultraviolet light emitting diode 1 can be efficiently transmitted.
  • the plurality of ultraviolet light emitting diodes 1 are arranged in the container 33 in a posture in which the irradiation direction is the outside, and have a structure that radiates ultraviolet rays emitted from the ultraviolet light emitting diodes 1 in all directions.
  • the ultraviolet sterilizer of FIG. 15 fixes a plurality of ultraviolet light emitting diodes 1 to the outer peripheral surface of a fixed cylinder 36 as an attachment member at a predetermined interval, and the fixed cylinder 36 is coaxial with the inside of a cylindrical container 33. Is arranged.
  • the illustrated fixed cylinder 36 is provided with a reflective layer 34 on the outer peripheral surface, and effectively reflects ultraviolet rays to irradiate the outdoor water 9.
  • the ultraviolet sterilization apparatus having this structure is small and has a feature that a sterilization effect can be realized in a wide range. Further, as shown by the chain line in the figure, the ultraviolet sterilizer disposes the UVC light source 2 on the outside of the fixed cylinder 36 and irradiates the UVA ultraviolet rays and the UVC ultraviolet rays, so that the outdoor water 9 is more effectively used. It can also be sterilized.
  • the ultraviolet light emitting diode 1 emits UVA ultraviolet light having a main light emission peak in a wavelength range of 320 nm to 400 nm. More preferably, the main emission peak of ultraviolet rays emitted from the ultraviolet light emitting diode 1 is 350 to 380 nm, which is an even narrower wavelength range.
  • the ultraviolet light emitting diode 1 having the main light emission peak in these wavelength regions is realized by a gallium nitride compound semiconductor light emitting element.
  • the ultraviolet light emitting diode 1 irradiates light including a boundary region between visible light and near ultraviolet light. This is because visible light is in a wavelength region of 380 nm or more.
  • the output of the ultraviolet light-emitting diode 1, the radiation intensity on the center line away 1cm from the tip for example 10 mW / cm 2 or more, preferably 50 mW / cm 2 or more, further preferably 60 mW / cm 2 or more.
  • the UVC light source 2 is an ultraviolet lamp that emits UVC ultraviolet light in a wavelength range of less than 280 nm.
  • the UVC light source 2 shown in the drawing uses a cylindrical elongated lamp as the most general ultraviolet lamp.
  • the ultraviolet sterilization apparatus provided with the UVC light source 2 has a synergistic effect by irradiating UVC ultraviolet rays from the UVC light source 2 in addition to sterilization by irradiating UVA ultraviolet rays from the ultraviolet light emitting diodes 1.
  • UVC ultraviolet rays are effectively applied to UVC and UVA while suppressing the light recovery phenomenon by irradiating the ultraviolet light emitting diode 1 with UVA ultraviolet rays, thereby realizing more effective sterilization.
  • the output of the UVC light source 2 can be made smaller than the output of the ultraviolet light emitting diode 1.
  • the output of the UVC light source 2 is, for example, 1 ⁇ W / cm 2 or more, preferably 5 ⁇ W / cm 2 or more, and more preferably 10 ⁇ W / cm 2 or more.
  • UV light-emitting diodes and UVC light sources can be reflected and indirectly irradiated to the outdoor water without directly irradiating the ultraviolet light toward the outdoor water.
  • the photocatalyst can be irradiated with a part of the ultraviolet rays emitted from the ultraviolet light emitting diode or the UVC light source, and sterilized by a synergistic effect with the photocatalyst.
  • a wavelength conversion material such as a phosphor can be irradiated with a part of the ultraviolet rays, and the wavelength of the ultraviolet rays can be converted with the wavelength conversion material.
  • the ultraviolet sterilizer of the present invention can activate a photocatalyst with ultraviolet rays emitted from an ultraviolet light-emitting diode or a UVC light source, and can use a synergistic effect of ultraviolet rays and active oxygen when used together with the photocatalyst.
  • a photocatalyst when used in combination, the dispersion and deterioration of the catalyst performance, as well as material costs and processing costs increase. Therefore, effective sterilization can be realized by irradiating the outdoor water with the ultraviolet rays emitted from the ultraviolet light emitting diode or the UVC light source as efficiently as possible without using a photocatalyst or a wavelength conversion material.
  • FIG. 16 shows the survival rate by single or combined irradiation using UVA and UVC.
  • this figure shows the state in which the viability of Vibrio parahaemolyticus changes when UVA and UVC are irradiated, that is, the Vibrio parahaemolyticus is sterilized by UVA and UVC irradiation against the number of Vibrio parahaemolyticus that are not irradiated with UVA and UVC.
  • the ratio at which the number of bacteria is reduced is shown as the survival rate.
  • UVA is irradiated for 6 minutes and the integrated light amount is 36 J / cm 2
  • UVC is irradiated for 6 minutes and the integrated light amount is 0.024 J / cm 2 .
  • the Vibrio parahaemolyticus is sterilized to about 1/5 with respect to the state not irradiated with UVA alone.
  • Vibrio parahaemolyticus is sterilized to about 1/10 with respect to irradiation that is not irradiated.
  • the state of irradiating UVC after irradiating UVA it is sterilized to about 1/46 with respect to the state not irradiated, and sterilized to about 1/21 in the state of irradiating UVA after irradiating UVC.
  • the germicidal effect is synergistically enhanced by irradiating UVA and UVC at the same time by sterilizing to about 1/130 of the state not irradiating. Becomes clear.
  • FIG. 17 is a graph showing that the sterilizing effect of Vibrio parahaemolyticus is improved by increasing the integrated amount of light irradiated with UVA.
  • UVC is irradiated for 6 minutes
  • the integrated light quantity is set to a constant 0.024 J / cm 2
  • the UVA irradiation intensity is set to 100 mW / cm 2
  • the irradiation time is changed to change the integrated light quantity from 0 to It shows the survival rate in which the Vibrio parahaemolyticus is sterilized and the number of bacteria is reduced in a state of changing to 100 J / cm 2 .
  • This figure shows the ratio at which the number of bacteria is reduced by sterilizing Vibrio parahaemolyticus by irradiating UVA and UVC with respect to the number of bacteria of Vibrio parahaemolyticus not irradiated with UVA and UVC.
  • the bactericidal effect by UVA and UVC simultaneous irradiation is remarkably enhanced by increasing the cumulative amount of UVA.
  • the survival rate in the state that the survival rates of about 1 / 10,36J / cm 2 in a state that the integrated light amount of UVA and 25 J / cm 2 is in a state to be about 1 / 100,90J / cm 2 The survival rate is about 1 / 50,000 and the bactericidal effect is extremely strong.
  • the integrated light quantity of UVC and 0.024J / cm 2 in the state in which the 25 J / cm 2 the integrated light quantity of UVA UVA / UVC is about 1000 times, the integrated light quantity of UVA 36J / cm
  • the UVA / UVC in the state of 2 is 1500 times
  • the UVA / UVC in the state of 90 J / cm 2 in the state where the UVA integrated light amount is 3750 times the UVA integrated light amount is 500 times or more of the UVC integrated light amount.
  • the sterilization effect can be remarkably improved by irradiating both UVA and UVC by setting it to 1000 times or more, more preferably 1500 times or more.
  • the ratio of the integrated light quantity of UVA / UVC is the ratio of the irradiation intensity of UVA / UVC in an apparatus that irradiates UVA and UVC simultaneously.
  • FIG. 18 shows the bactericidal effect using titanium oxide as a photocatalyst and UVA in combination.
  • this figure shows the rate at which the number of Vibrio parahaemolyticus decreases when 200 ⁇ l of Vibrio parahaemolyticus is placed in a 96-well plate at a concentration of 10 6 / ml, that is, the survival rate. .
  • the bottom of the well is coated with 0.5 cm 2 of titanium oxide.
  • the survival rate of irradiation with only UVA is about 1/5
  • the survival rate of only titanium oxide is about 1/2
  • the survival rate when UVA is irradiated to titanium oxide is about 1/6. From this figure, it is clear that the synergistic effect of sterilization of titanium oxide and UVA is very weak.
  • a plurality of ultraviolet light emitting diodes 1 are arranged in a predetermined arrangement in the outer case 3.
  • the plurality of ultraviolet light emitting diodes 1 are fixed to the inside of the outer case 3 through the circuit board 6 so as to face downward.
  • the ultraviolet light-emitting diode 1 (manufactured by Nichia Corporation) has a main emission peak wavelength of 365 nm, an emission spectrum half-width of 10 nm, and an optical output of 100 mW.
  • the plurality of ultraviolet light emitting diodes 1 are connected in series and in parallel to a power source (PAS40-9 manufactured by Kikusui Electronics Co., Ltd.).
  • the power source is a DC stabilized power source that stabilizes the output.
  • This power supply is used in a constant current mode in which a current is applied at a rated current of 500 mA where the light output of the ultraviolet light emitting diode 1 is 100 mW.
  • LB medium is used for culture of bacteria.
  • a method for preparing a liquid medium and an agar medium (LB plate) will be described below.
  • -Composition of LB medium tryptone 1% 10 g / l yeast extract 0.5% 5g / l NaCl 1% 10g / l
  • agar is added to this so that it may become 1.5% (W / V).
  • LB medium is dissolved in deionized water and then sterilized (121 ° C., 20 minutes) in an autoclave.
  • a stirrer bar For the agar medium, add a stirrer bar, stir uniformly with a stirrer after autoclaving, and cool to about 65 ° C. Dispense an appropriate amount into a 10 cm disposable plastic petri dish (Eiken Equipment Co., Ltd.) Set to solidify.
  • a non-pathogenic Escherichia coli DH5 ⁇ strain is used as an indicator for outdoor water to be sterilized.
  • the Escherichia coli is cultured for 16 hours in a 37 ° C. shaking incubator using 5 ml of LB medium.
  • Method for adjusting the number of bacteria In the experiment, a plate culture method is used to measure the number of bacteria. This is to count the number of colonies produced by smearing and culturing a certain amount of bacterial solution on an agar medium. A colony is a group of the same bacteria, and one cell cannot be seen with the naked eye, but the colony can be confirmed with the naked eye. To adjust the number of bacteria, first measure the approximate number of bacteria with a spectrophotometer, and then perform serial dilution.
  • Spectrophotometer Assume that the intensity of light having a certain wavelength changes from I 0 (intensity of incident light) to I (intensity of transmitted light) while passing through a solution layer of a substance. In this case, the ratio of I to I 0 (I / I 0) the permeability; says (t Transmittance), those representing the permeability in percentage transmittance; say (T percent transmittance). Optical density (OD) is the common logarithm of the inverse of transmission.
  • 100 ⁇ l of the sample stock solution is mixed with 900 ⁇ l of PBS to make a 10-fold diluted solution, and further 100 ⁇ l of 10-fold diluted solution is mixed with 900 ⁇ l of PBS to make a 100-fold diluted solution.
  • dilution was carried out sequentially to adjust up to 6 levels.
  • the bacterial solution diluted 10 5 times or 10 6 times is suitable for the measurement of the number of bacteria before UV irradiation, so 100 ⁇ l of each was dropped onto the LB plate, smeared evenly with a large stick, and 37 ° C. Incubate for 16 hours. Thereafter, the number of colonies appearing on the LB agar medium is measured. To count the number of colonies, count all colonies with the naked eye from the back of the petri dish. The number of bacteria is obtained by multiplying the number of colonies of each dilution factor by the dilution factor and averaging. The number of bacteria in the bacterial solution is adjusted to be, for example, 5 ⁇ 10 9 cells / ml.
  • Sterilization step 200 ⁇ l of the bacterial solution prepared by the above-described adjustment method is placed in a sterilized well plate (Becton Dickinson Labware). There are about 10 9 E. coli in 200 ⁇ l of this bacterial solution.
  • the bacterial solution is irradiated with UVA ultraviolet light having a main emission peak of 365 nm with the ultraviolet light emitting diode 1 at an intensity of 70 mW / cm 2 for 30 minutes.
  • the UVA irradiation in this step is performed in order to sterilize Escherichia coli, which is the indicator bacterium. The number of bacteria after UV irradiation is measured.
  • UVA rays contained in solar rays having a main light emission peak of 365 nm were changed to 0.01 mW / cm 2 , 0.09 mW / cm 2 , and 0.30 mW / cm 2 .
  • Irradiate in steps of UV intensity The UVA irradiation in this step is performed to measure the change in the number of bacteria due to the light recovery phenomenon after sterilization. For irradiation at each ultraviolet intensity, the number of bacteria after 30 minutes, 60 minutes, 120 minutes and 180 minutes has been measured.
  • the number of bacteria of E. coli that decreases by ultraviolet irradiation is shown as a ratio, where the number of bacteria before ultraviolet irradiation (before sterilization) is 1.
  • FIG. 1 shows that the bacteria count of E. coli is reduced to about 1/800 by the sterilization process in which UVA ultraviolet light having a main emission peak of 365 nm is irradiated at an intensity of 70 mW / cm 2 for 30 minutes, and then in the light recovery process, A state in which the number of bacteria is changed by irradiating with UVA light contained in sunlight is shown.
  • curves A, B, and C show the state in which the number of bacteria changes with the intensity of ultraviolet rays irradiated after sterilization being 0.01 mW / cm 2 , 0.09 mW / cm 2 , and 0.30 mW / cm 2. Yes.
  • the chain line in the figure shows the change in the number of bacteria in a state where the UVA light contained in the sunlight is not irradiated.
  • UVA ultraviolet rays are irradiated to sterilize the number of E. coli bacteria to 1/800, and then UVA rays contained in sunlight are irradiated with various ultraviolet intensities.
  • curve C the number of bacteria may be further reduced by irradiation with UVA light.
  • Vibrio parahaemolyticus is used in place of non-pathogenic Escherichia coli as an indicator bacterium for outdoor water to be sterilized, and the UV intensity of the UVA light contained in the sunlight irradiated in the light recovery process after the sterilization process is 0.30 mW.
  • the change in the number of bacteria is measured in the same manner as in Example 1 except that / cm 2 is used.
  • FIG. This figure shows that the number of bacteria of Vibrio parahaemolyticus is reduced to about 1/700 by the sterilization process in which UVA ultraviolet light having a main emission peak of 365 nm is irradiated at an intensity of 70 mW / cm 2. It shows a state in which the number of bacteria of Vibrio parahaemolyticus changes by irradiating with 365 nm UVA light contained in the light.
  • the curve B shows a state in which the number of bacteria is changed with the ultraviolet ray intensity irradiated in the light recovery step being 0.30 mW / cm 2
  • the chain line D in the figure does not irradiate the UVA rays contained in the sunlight. It shows the change in the number of bacteria in the state.
  • an exterior case 3 having a plurality of ultraviolet light emitting diodes 1 and a UVC light source 2 is used, and sewage is used as outdoor water to be sterilized.
  • UVA ultraviolet light having a main emission peak of 365 nm is irradiated with the ultraviolet light emitting diode 1 at an intensity of 70 mW / cm 2 for 15 minutes to sterilize.
  • UVA light contained in sunlight with a main emission peak of 365 nm is irradiated at an ultraviolet intensity of 0.30 mW / cm 2 and the number of bacteria after 180 minutes is measured. .
  • FIG. This figure shows a state in which the number of bacteria contained in the sewage is reduced to about 1/20 by the sterilization process, and then the number of bacteria is changed in the light recovery process.
  • the solid line in the figure shows a state in which the number of bacteria is changed by irradiating UVA light contained in sunlight in the light recovery process, and the chain line in the figure shows a state in which UVA light contained in sunlight is not irradiated. It shows changes in the number of bacteria.
  • the main emission peak as 254 nm, the ultraviolet UVC that the strength and 0.02 mW / cm 2 was irradiated from the UVC light source 2, a primary emission peak as 365 nm, UVA ultraviolet to strength and 70 mW / cm 2 Is measured in the same manner as in Example 3, except that both UVC ultraviolet rays and UVA ultraviolet rays are irradiated together for 15 minutes to sterilize the sewage.
  • FIG. This figure shows a state in which the number of bacteria contained in the sewage is reduced to about 1/5000 by the sterilization process, and then the number of bacteria is changed in the light recovery process.
  • the solid line in the figure shows a state in which the number of bacteria is changed by irradiating UVA light contained in sunlight with an ultraviolet intensity of 0.30 mW / cm 2 in the light recovery process. The change of the number of bacteria in the state which does not irradiate the UVA light contained is shown.
  • Example 1 In the sterilization step, the change in the number of bacteria is measured in the same manner as in Example 2 except that UVC ultraviolet light having a main emission peak of 254 nm is irradiated at an intensity of 70 mW / cm 2 .
  • Curve A in FIG. 3 shows a state in which the number of bacteria is changed by irradiating UVA rays contained in sunlight with an ultraviolet intensity of 0.30 mW / cm 2 in the light recovery process after sterilization by UVC ultraviolet rays.
  • the chain line C in the figure shows the change in the number of bacteria in a state where the UVA light contained in the sunlight is not irradiated.
  • UVC ultraviolet rays are irradiated to sterilize Vibrio parahaemolyticus to 1/700
  • UVA rays contained in sunlight are then irradiated.
  • the number of bacteria increases to 1/50 after 180 minutes due to the light recovery phenomenon. That is, it can be seen that the number of bacteria grows about 10 times or more by the light recovery phenomenon.
  • Example 2 In the sterilization step, the change in the number of bacteria is measured in the same manner as in Example 3 except that UVC ultraviolet light having a main emission peak of 254 nm is irradiated at an intensity of 70 mW / cm 2 .
  • the solid line in FIG. 4 shows a state in which the number of bacteria is changed by irradiating UVA light contained in sunlight with an ultraviolet intensity of 0.30 mW / cm 2 in the light recovery process after sterilization by UVC ultraviolet rays.
  • the chain line in the figure shows the change in the number of bacteria in a state where the UVA light contained in the sunlight is not irradiated.
  • UVC ultraviolet rays are irradiated to sterilize until the number of bacteria contained in the sewage is reduced to 1/800, and then UVA rays contained in sunlight are irradiated.
  • the number of bacteria increases to 1/50 after 180 minutes due to the light recovery phenomenon. That is, it can be seen that the number of bacteria grows about 10 times or more by the light recovery phenomenon.
  • the present invention can be used in various fields such as sterilizing outdoor water with ultraviolet rays, such as sewage, pool water, and fish culture pond water.
  • FIG. 8 It is a schematic sectional drawing which shows the use condition of the ultraviolet sterilizer concerning the other Example of this invention. It is a perspective view which shows the internal structure of the ultraviolet sterilizer shown in FIG. 8 and FIG. It is a schematic sectional drawing which shows the use condition of the ultraviolet sterilizer concerning the other Example of this invention. It is an expanded horizontal sectional view which shows the internal structure of the ultraviolet sterilizer shown in FIG. It is a schematic sectional drawing which shows the use condition of the ultraviolet sterilizer concerning the other Example of this invention. It is an expanded cross-sectional view which shows the internal structure of the ultraviolet sterilizer shown in FIG. It is a graph which shows the survival rate of the bacteria by single and combined irradiation using UVA and UVC.

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Abstract

L'invention porte sur un dispositif de stérilisation aux ultraviolets qui peut stériliser efficacement de l'eau extérieure avec de la lumière ultraviolette, par suppression d'une augmentation du nombre de cellules bactériennes due à la photo-réactivation après la stérilisation. Le dispositif de stérilisation aux ultraviolets stérilise de l'eau extérieure (9) par rayonnement de lumière ultraviolette. Le dispositif de stérilisation aux ultraviolets comprend une diode électroluminescente ultraviolette (1) qui émet de la lumière ultraviolette UVA présentant un pic d'émission principale entre 320 et 400 nm. Grâce à la stérilisation de l'eau extérieure (9) avec la lumière ultraviolette UVA émise à partir de la diode électroluminescente ultraviolette (1), une augmentation du nombre de cellules bactériennes due à la photo-réactivation peut être supprimée dans l'eau extérieure stérilisée (9).
PCT/JP2009/006295 2008-11-21 2009-11-21 Dispositif de stérilisation aux ultraviolets pour eau extérieure Ceased WO2010058607A1 (fr)

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EP09827388.1A EP2394963B1 (fr) 2008-11-21 2009-11-21 Dispositif de stérilisation aux ultraviolets pour eau extérieure
JP2010539163A JPWO2010058607A1 (ja) 2008-11-21 2009-11-21 屋外水の紫外線殺菌装置
US13/130,574 US8324595B2 (en) 2008-11-21 2009-11-21 Outdoor water treatment apparatus to kill bacteria with ultraviolet light

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US20110226966A1 (en) 2011-09-22
EP2394963B1 (fr) 2016-02-17

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