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TW201823166A - Hydrogen peroxide removal method and apparatus - Google Patents

Hydrogen peroxide removal method and apparatus Download PDF

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Publication number
TW201823166A
TW201823166A TW106132896A TW106132896A TW201823166A TW 201823166 A TW201823166 A TW 201823166A TW 106132896 A TW106132896 A TW 106132896A TW 106132896 A TW106132896 A TW 106132896A TW 201823166 A TW201823166 A TW 201823166A
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hydrogen peroxide
water
container
platinum
catalyst
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TW106132896A
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Chinese (zh)
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森田博志
港康晴
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日商栗田工業股份有限公司
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/28Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/40Regeneration or reactivation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • B01J38/48Liquid treating or treating in liquid phase, e.g. dissolved or suspended
    • 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
    • C02F1/20Treatment of water, waste water, or sewage by degassing, i.e. liberation of dissolved gases
    • 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
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • 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
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/04Non-contaminated water, e.g. for industrial water supply for obtaining ultra-pure water

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Inorganic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)
  • Catalysts (AREA)
  • Physical Water Treatments (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

In a method and apparatus for degrading and removing hydrogen peroxide by passing hydrogen peroxide-containing water through platinum catalyst-filled columns 21-25, hydrogen peroxide removal performance is restored by stopping water passage through one column at a specified time. During said specified time, nitrogen gas or water with dissolved hydrogen can be flushed through said column in which water passage has been stopped and the volume of water passed through the other columns can be increased.

Description

過氧化氫去除方法及裝置Method and device for removing hydrogen peroxide

[0001] 本發明,是有關於在純水製造過程將水中的過氧化氫去除用的方法及裝置。又,在本發明中,純水是包含超純水。[0001] The present invention relates to a method and an apparatus for removing hydrogen peroxide from water in a pure water production process. In the present invention, pure water includes ultrapure water.

[0002] 半導體、電子材料洗淨用的超純水,是藉由由前處理裝置、一次純水製造裝置、二次純水製造裝置(副系統)所構成的超純水製造設備將原水(工業用水、市水、井水等)處理而被製造。   [0003] 在由凝集、加壓浮上(沈澱)、過濾(膜過濾)裝置等形成的前處理裝置中,進行原水中的懸濁物質和溶膠物質的去除。且,在此過程中也可將高分子系有機物,疏水性有機物等去除。   [0004] 在具備逆滲透膜分離裝置、脫氣裝置及離子交換裝置(混床式或是4床5塔式等)的一次純水製造裝置中,進行原水中的離子和有機成分的去除。又,在逆滲透膜分離裝置中,將鹽類去除,並且將離子性、溶膠性的TOC去除。在離子交換裝置中,進行將鹽類去除並且將藉由離子交換樹脂吸附或是離子交換的TOC成分去除。在脫氣裝置中進行無機系碳(IC)、溶解氧的去除。   [0005] 來自一次純水製造裝置的一次純水,是在副系統,由紫外線(UV)照射裝置、離子交換裝置及限外過濾(UF)膜分離裝置被處理,使超純水被製造。在UV氧化裝置中,藉由由UV燈泡被照射的185nm的UV將TOC有機酸,進一步CO2 分解。藉由分解而生成的有機物及CO2 是由後段的離子交換裝置(通常是混床式離子交換裝置)被去除。在UF膜分離裝置中微粒子被去除,從離子交換裝置流出的離子交換樹脂的碎片等也被去除。如此獲得的超純水被供給至使用點。   [0006] 藉由紫外線氧化裝置中的由紫外線照射所產生的氧化處理,水中的有機物(TOC成分)被分解使有機酸及碳酸發生。此紫外線氧化裝置中的TOC成分的氧化分解機構,是將水氧化分解並生成OH自由基,藉由此OH自由基將TOC成分氧化分解,紫外線照射量是可以將水中的TOC充分地氧化分解地過剩照射。   [0007] 如此紫外線照射量多的情況,由水的分解生成的OH自由基因為成為過剩,所以多餘的OH自由基是藉由會合而生成過氧化氫。生成的過氧化氫,是與後段的混床式離子交換裝置的陰離子交換樹脂接觸並分解,此時,會使離子交換樹脂劣化。隨著此分解,溶解氧也增加。且,由離子交換樹脂的分解而重新生成離子交換樹脂衍生的TOC成分,所獲得的超純水的水質會下降。且,在混床式離子交換裝置通水後也殘留的過氧化氫,會使混床式離子交換裝置的後段的脫氣裝置和UF膜劣化。   [0008] 在專利文獻1中,超純水中的過氧化氫去除方法,是將從超純水製造裝置的紫外線氧化處理裝置被排出的包含過氧化氫的被處理水,與將白金族的金屬奈米溶膠粒子載持在陰離子交換樹脂載體的過氧化氫分解觸媒接觸,將被處理水中的過氧化氫分解至1ppb以下的方法。   [0009] 在專利文獻2中,為了白金系觸媒的劣化抑制,將被處理水由紫外線氧化裝置紫外線氧化處理之後,使用白金系觸媒進行過氧化氫去除處理的純水的製造方法,將朝該紫外線氧化裝置的給水的TOC成為5ppb以下。   [0010]   [專利文獻1]日本特開2007-185587號公報   [專利文獻2]日本特開2015-93226號公報   [0011] 如上述,Pt所代表的白金族觸媒,以往是活用在氧化性物質的分解等。在超純水製造系統中,在將在水中包含微量的有機物的分解為目的紫外線氧化過程中,作為副生成物發生的過氧化氫的去除是成為近年來的課題,而進行由將Pt奈米溶膠載持的離子交換樹脂和Pd載持樹脂等所產生的過氧化氫分解處理。   [0012] 藉由此過氧化氫分解處理,雖可以使被處理水中的過氧化氫濃度減少至低於目標濃度(例如1ppb),但是伴隨長時間的使用,觸媒的性能會漸漸地下降。[0002] Ultra-pure water for cleaning semiconductors and electronic materials is made of raw water (Ultra-pure water) by ultra-pure water production equipment consisting of a pretreatment device, a primary pure water production device, and a secondary pure water production device (sub-system). Industrial water, municipal water, well water, etc.). [0003] In a pretreatment device formed by an agglutination, pressure floating (precipitation), filtration (membrane filtration) device, and the like, removal of suspended substances and sol substances in raw water is performed. In addition, polymer organic substances, hydrophobic organic substances, etc. can be removed in this process. [0004] In a primary pure water production apparatus including a reverse osmosis membrane separation device, a degassing device, and an ion exchange device (such as a mixed bed type or a four-bed five-tower type), ions and organic components in raw water are removed. In the reverse osmosis membrane separation device, salts are removed, and ionic and sol-based TOC are removed. The ion exchange device removes salts and removes TOC components adsorbed or ion-exchanged by an ion-exchange resin. The degassing device removes inorganic carbon (IC) and dissolved oxygen. [0005] The primary pure water from the primary pure water manufacturing device is processed in a sub-system by an ultraviolet (UV) irradiation device, an ion exchange device, and an external filtration (UF) membrane separation device, so that ultrapure water is manufactured. In a UV oxidation apparatus, by UV irradiation by a UV 185nm lamp will be an organic acid TOC, CO 2 is further decomposed. The organic matter and CO 2 generated by the decomposition are removed by an ion exchange device (usually a mixed-bed ion exchange device) in the subsequent stage. In the UF membrane separation device, fine particles are removed, and fragments of the ion exchange resin flowing out of the ion exchange device are also removed. The ultrapure water thus obtained is supplied to the point of use. [0006] By an oxidation treatment by ultraviolet irradiation in an ultraviolet oxidizing device, organic substances (TOC components) in water are decomposed to generate organic acids and carbonic acid. The oxidative decomposition mechanism of the TOC component in this ultraviolet oxidizing device is to oxidize and decompose water to generate OH radicals, thereby oxidizing and decomposing the TOC components by the OH radicals, and the amount of ultraviolet radiation can fully oxidize and decompose TOC in water Excessive exposure. [0007] In such a case where there is a large amount of ultraviolet radiation, since OH radicals generated by the decomposition of water become excessive, the excess OH radicals are combined to generate hydrogen peroxide. The generated hydrogen peroxide is in contact with the anion exchange resin of the mixed-bed ion exchange device in the subsequent stage and decomposes, and at this time, the ion exchange resin is deteriorated. With this decomposition, dissolved oxygen also increases. In addition, the TOC component derived from the ion exchange resin is regenerated by the decomposition of the ion exchange resin, and the quality of the ultrapure water obtained is degraded. In addition, the hydrogen peroxide remaining in the mixed-bed ion exchange device after passing water may deteriorate the degassing device and the UF membrane in the later stage of the mixed-bed ion exchange device. [0008] In Patent Document 1, a method for removing hydrogen peroxide in ultrapure water is to treat water containing hydrogen peroxide discharged from an ultraviolet oxidation treatment device of an ultrapure water production device, and A method in which metal nanosol particles are supported on an anion exchange resin carrier by a hydrogen peroxide decomposition catalyst, and the hydrogen peroxide in the treated water is decomposed to 1 ppb or less. [0009] In Patent Document 2, in order to suppress degradation of a platinum-based catalyst, a method for producing pure water in which treated water is subjected to ultraviolet oxidation treatment by an ultraviolet oxidation device and then subjected to hydrogen peroxide removal treatment using a platinum-based catalyst is described. The TOC of the feed water to the ultraviolet oxidizer is 5 ppb or less. [0010] [Patent Document 1] Japanese Patent Laid-Open No. 2007-185587 [Patent Document 2] Japanese Patent Laid-Open No. 2015-93226 [0011] As described above, the platinum catalyst represented by Pt has been conventionally used for oxidizing Decomposition of matter, etc. In the ultrapure water production system, the removal of hydrogen peroxide generated as a by-product in the ultraviolet oxidation process for the purpose of decomposing trace amounts of organic matter in water has become a problem in recent years. Decomposition treatment of hydrogen peroxide generated by sol-supported ion exchange resin, Pd-supported resin, and the like. [0012] Through this hydrogen peroxide decomposition treatment, although the hydrogen peroxide concentration in the water to be treated can be reduced below a target concentration (for example, 1 ppb), the performance of the catalyst gradually decreases with long-term use.

[0013] 本發明的目的是提供一種過氧化氫去除方法及裝置,可抑制白金系觸媒的性能下降,或是使回復,可以長期保持具有充分的觸媒活性的狀態。   [0014] 一般,藉由將流入白金系觸媒裝置的被處理水中的有機物濃度下降,來抑制白金系觸媒的性能下降,但是本發明人是為了進一步抑制性能下降而專心重疊研究的結果而發現,白金系觸媒的性能下降,觸媒表面的氧化也是一因,藉由抑制此觸媒表面的氧化,就可抑制白金系觸媒的性能下降。   [0015] 本發明,是依據這種知識而完成者。   [0016] 本發明的過氧化氫去除方法,是朝具有被並列設置的白金系觸媒充填容器的過氧化氫去除裝置將含過氧化氫水通水將過氧化氫去除的過氧化氫去除方法,進行將含過氧化氫水朝一部分的容器的通水規定期間停止的過氧化氫去除性能回復操作。   [0017] 在本發明的一態樣中,在前述規定時間,朝前述容器供給氮氣體等的非氧化性氣體。   [0018] 在本發明的一態樣中,在前述規定時間,從前述容器將觸媒取出再充填。   [0019] 在本發明的一態樣中,在前述規定時間,朝前述容器將氫溶解水通水。   [0020] 在本發明的一態樣中,前述過氧化氫去除裝置是被設置在超純水製造裝置,在前述規定時間,使朝前述一部分以外的白金系觸媒充填容器的通水量增加。   [0021] 本發明的過氧化氫去除裝置,是具備:被並列設置的白金系觸媒充填容器、及朝各容器將含過氧化氫水通水的含過氧化氫水通水手段、及朝各容器供給非氧化性氣體或是氫溶解水的供給手段、及將朝各容器的含過氧化氫水通水及非氧化性氣體或是氫溶解水供給切換的切換手段。 [發明的效果]   [0022] 觸媒,原本不是其本身變化而是降低任何的化學性反應的障壁來促進進行的功能,但是藉由長期被曝在氧化條件下,表面會氧化,其會引起性能下降。   [0023] 白金系觸媒,是強力氧化的話,會成為不可逆的氧化物,但是在可逆的表面氧化的階段中,藉由持續地從氧化狀態開放而回復至原條性能。在本發明中,藉由通水停止而將白金系觸媒持續從氧化狀態開放,使觸媒的性能回復。在此通水停止期間將N2 氣體通氣,且將白金系觸媒從容器取出再充填,且在通水停止後,藉由將氫溶解水通水,使過氧化氫分解性能進一步有效地回復。   [0024] 觸媒劣化的原因,是除了由白金族觸媒本身的表面氧化所產生的變質以外,也有由被包含於被處理水中的有機物等的不純物所產生的污染。且,也有基材也就是載體(例如離子交換樹脂)本身的劣化。因此,被處理水中的不純物減少,且過氧化氫濃度是比較高的情況時,因為氧化是成為性能下降的主原因,所以本發明是特別有效。   [0025] 依據本發明的話,不需要將白金系觸媒交換成新品,可以將白金系觸媒的有效期間延長。   [0026] 將白金系觸媒充填容器複數個並列設置,將性能回復處理在一部分的容器實施期間,藉由依序反覆提高朝其他的容器的通水流量的通水切換操作,就可以將所期的處理水質及水量一邊維持一邊長期進行過氧化氫分解處理。[0013] An object of the present invention is to provide a method and a device for removing hydrogen peroxide, which can suppress the degradation of the performance of a platinum-based catalyst, or restore it, and can maintain a state with sufficient catalyst activity for a long time. [0014] Generally, the decrease in the performance of platinum-based catalysts is suppressed by reducing the concentration of organic substances flowing into the treated water of the platinum-based catalyst device. However, the inventors focused on the results of overlapping studies to further suppress the performance degradation. It was found that the performance of the platinum-based catalyst is reduced, and the oxidation of the catalyst surface is also a cause. By suppressing the oxidation of the catalyst surface, the performance of the platinum-based catalyst can be suppressed. [0015] The present invention has been completed based on such knowledge. [0016] The method for removing hydrogen peroxide according to the present invention is a method for removing hydrogen peroxide by passing hydrogen peroxide-containing water through water to a hydrogen peroxide removal device having a platinum catalyst filling container arranged in parallel. Then, the operation of restoring hydrogen peroxide removal performance to stop the passage of hydrogen peroxide-containing water toward a part of the container for a predetermined period of time is performed. [0017] In one aspect of the present invention, a non-oxidizing gas such as a nitrogen gas is supplied to the container at the predetermined time. [0018] In one aspect of the present invention, the catalyst is removed from the container and refilled at the predetermined time. [0019] In one aspect of the present invention, hydrogen-dissolved water is passed through the container at the predetermined time. [0020] In one aspect of the present invention, the hydrogen peroxide removing device is installed in an ultrapure water producing device, and increases a water flow amount to a platinum-based catalyst filling container other than the part at the predetermined time. [0021] A hydrogen peroxide removing device of the present invention includes a platinum catalyst filling container arranged in parallel, a hydrogen peroxide-containing water passing means for passing hydrogen peroxide-containing water to each container, and a Supply means for supplying non-oxidizing gas or hydrogen-dissolved water to each container, and switching means for switching supply of hydrogen peroxide-containing water and non-oxidizing gas or hydrogen-dissolved water to each container. [Effect of the invention] [0022] The catalyst is not a change in itself, but a barrier to reduce any chemical reaction to promote the function, but by long-term exposure to oxidation conditions, the surface will oxidize, which will cause performance decline. [0023] Platinum-based catalysts are irreversible oxides if they are strongly oxidized, but in the stage of reversible surface oxidation, they return to their original properties by continuously opening from the oxidized state. In the present invention, the platinum-based catalyst is continuously opened from the oxidized state by stopping the water flow to restore the performance of the catalyst. During this stoppage of water flow, aerate N 2 gas, and remove the platinum catalyst from the container and fill it. After the stoppage of water flow, hydrogen peroxide dissolves water to pass through the water to further restore the hydrogen peroxide decomposition performance. . [0024] The cause of the catalyst deterioration is contamination caused by impurities such as organic substances contained in the water to be treated, in addition to the deterioration caused by the surface oxidation of the platinum group catalyst itself. In addition, there is also degradation of the substrate, that is, the carrier (for example, an ion exchange resin) itself. Therefore, when the impurities in the water to be treated are reduced and the hydrogen peroxide concentration is relatively high, the present invention is particularly effective because oxidation is the main cause of performance degradation. [0025] According to the present invention, there is no need to exchange platinum catalysts for new products, and the validity period of platinum catalysts can be extended. [0026] A plurality of platinum-type catalyst filling containers are arranged in parallel, and performance recovery processing is performed during a part of the container implementation. By sequentially increasing the water flow switching operation to other containers, the desired water flow can be changed. The long-term hydrogen peroxide decomposition treatment is performed while maintaining the quality and quantity of the treated water.

[0028] 以下,對於本發明進一步詳細說明。   [0029] 本發明的過氧化氫去除方法及裝置,是使用在超純水製造過程最佳。在超純水製造過程中,如前述,來自一次純水製造裝置的一次純水是由副系統被處理使超純水被製造。在副系統中,將一次純水由紫外線氧化裝置處理之後,由具有白金系觸媒的過氧化氫去除裝置進行過氧化氫去除處理,接著朝非再生離子交換裝置、膜式脫氣裝置、UF膜裝置通水。   [0030] TOC成分是藉由紫外線氧化裝置中的紫外線氧化處理被氧化分解,生成有機酸及碳酸,並且發生過氧化氫。在本發明中,將來自紫外線氧化裝置的流出水朝過氧化氫去除裝置通水將過氧化氫去除。此過氧化氫去除裝置,是採用將白金系觸媒充填在容器者。白金系觸媒,是白金系金屬的溶膠粒子,特別是將奈米溶膠粒子載持在載體者較佳。   [0031] 白金系金屬,可以舉例釕、銠、鈀、鋨、銥及白金。這些的白金族金屬,是可以將1種單獨使用,將2種以上組合使用也可以,作為2種以上的合金使用也可以,或是不將天然產出的混合物的精製品分離成單體地使用也可以。在這些之中,白金、鈀、白金/鈀合金的單獨或是這些的2種以上的混合物,因為觸媒活性強所以可以特別最佳使用。   [0032] 將白金系金屬的奈米溶膠粒子製造的方法沒有特別限制,例如,可以舉例金屬鹽還原反應法、燃燒法等。在這些之中,金屬鹽還原反應法,是製造容易,因為可以獲得穩定的品質的金屬奈米溶膠粒子所以可以最佳使用。   [0033] 白金系金屬的奈米溶膠粒子的平均粒子徑較佳是1~50nm,更佳是1.2~20nm,進一步較佳是1.4~5nm。此粒徑是從電子顯微鏡攝像獲得的值。   [0034] 將白金系金屬奈米溶膠粒子載持的載體,是例如,可以舉例氧化鎂、二氧化鈦、氧化鋁、二氧化矽-氧化鋁、氧化鋯、活性碳、沸石、矽藻土土、離子交換樹脂等。在這些之中,陰離子交換樹脂可以特別最佳使用。白金系金屬奈米溶膠粒子,是具有雙電層,因為負地帶電,所以穩定地被載持在陰離子交換樹脂而不易剝離。被載持在陰離子交換樹脂的白金系金屬奈米溶膠粒子,是顯示對於過氧化氫的分解去除強的觸媒活性。陰離子交換樹脂的交換基,是OH形較佳。OH形陰離子交換樹脂,是樹脂表面成為鹼性,促進過氧化氫的分解。   [0035] 白金系金屬奈米溶膠粒子朝陰離子交換樹脂的載持量,是0.01~0.2重量%較佳,0.04~0.1重量%更佳。   [0036] 水中的過氧化氫,是藉由將含過氧化氫水接觸將白金系金屬奈米溶膠粒子載持在載體的過氧化氫分解觸媒,藉由2H2 O2 →2H2 O+O2 的反應而被分解。   [0037] 朝含過氧化氫水的白金系觸媒充填容器的通水速度,是空間速度SV100~2,000h-1 較佳,300~1,500h-1 更佳。白金系觸媒,因為過氧化氫的分解速度是非常地快,所以SV即使是100h-1 以上,過氧化氫也可充分地被分解。但是,SV是超過2,000h-1 的話,通水的壓力損失過大,並且過氧化氫的分解去除有可能成為不充分。   [0038] 參照第1圖及第2圖說明本發明的過氧化氫去除方法及裝置的具體例。   [0039] 在第1圖中,白金系觸媒被充填的圓柱21~25是複數條(在圖示中為5條)被並列設置。上述紫外線照射裝置流出水等的含過氧化氫水是從配管1透過閥11~15朝圓柱21~25被通水。來自圓柱21~25的流出水,是透過閥31~35及集合配管2被取出。   [0040] 由朝5條圓柱21~25並列通水的要領進行處理。在處理水劣化的徵兆被認定的時點,對於朝如第1圖(b)的1條圓柱(在第1圖(b)中為圓柱21)的通水,藉由將閥11、31關閉而停止,將暫時殘留的4條圓柱22~25的通水量各別增加25%來進行確保處理水量的並列運轉。   [0041] 對於將通水停止的圓柱21,藉由施加:   (1)一定期間靜置。   (2)由N2 氣體等的非氧化性氣體將圓柱內的氣氛置換。   (3)將白金系觸媒一旦拔出,較佳是在超純水中浸漬規定時間(較佳是1日以上,特別是2~10日程度)保管之後,再充填。   (4)將氫溶解水通水。   以上其中任一或二以上的組合的處理使過氧化氫分解性能回復。   [0042] 其後,較佳是朝此圓柱21試驗地通水,確認處理水質是良好之後,將閥11、31打開將朝圓柱21的通水再開。其後,對於其他的圓柱22~25也同樣地依序進行性能回復操作,將性能返回至良好的狀態。   [0043] 對於5條圓柱21~25全部的回復處理完成之後,返回至原本的標準流量的5條並列通水。   [0044] 第2圖是顯示可取代閥11~15而設置三方閥41~45,可取代閥31~35而設置三方閥51~55,朝各圓柱21~25將N2 氣體或是氫溶解水藉由三方閥31~35、51~55的切換操作而可供給的過氧化氫去除裝置。   [0045] 在三方閥41~45的第3通口中,連接有從配管60分岐的配管61~65。三方閥51~55的第3通口,是透過分岐配管71~75與排出用配管70連接。從配管60將N2 氣體或是氫溶解水供給至圓柱21~25的其中任一,將其流出氣體或是氫溶解水從配管70排出。   [0046] 朝具備如第1、2圖並列的5條圓柱21~25的過氧化氫去除裝置的各圓柱21~25均等地使標準的SV由400/h通水的情況,1條是進入回復處理而成為4條並列通水(例如第1圖(b))的話,各圓柱的SV是增大至500/h。這對於處理水質維持的面不佳。但是,白金系樹脂的過氧化氫分解壽命(不施加回復處理的情況)只有數年,對於此,因為回復處理是1條最長為1週間程度,所以在各圓柱增加25%的負擔的話,最長4週間程度。在此,朝陸續地性能回復了的圓柱的通水因為是被再開,所以維持過氧化氫去除裝置整體處理水量(SV500/h)並不困難。   [0047] 在第1、2圖中將5條圓柱並列設置,但是將6條圓柱並列設置,將其中的1條依序停歇(性能回復操作),時常由5條圓柱通水運轉也可以。   [0048] 此情況時,由規定時間(規定的過氧化氫負荷)超過時將1條停止,將未同時使用的1條開始通水的要領,各容器皆整體的5/6的時間是通水,1/6的時間是停止的間歇運轉)依順旋轉的旋轉木馬輪式的運用,就可以充餘地運轉是。   [0049] 依據本發明人的實驗結果的話,認定以下的事。   (1)將被處理水朝白金系觸媒充填容器的通水在規定時間停止之後將通水再開的話,過氧化氫分解性能可回復。停止時間愈長,其回復程度愈高。   (2)在被處理水朝白金系觸媒充填容器的通水停止中加上藉由N2 氣體通氣從該容器內將O2 排除的操作的話,過氧化氫分解性能是比(1)更短時間回復。   (3)在被處理水朝白金系觸媒充填容器的通水停止中一旦將白金系觸媒從容器拔出,規定時間,在超純水中保管之後重新充填並通水再開的話,過氧化氫分解性能是比上述(1)及(2)更短時間回復。   (4)將被處理水朝白金系觸媒充填容器的通水停止之後,將氫溶解水通水的話,過氧化氫分解性能是比上述(1)~(3)更短時間回復。   [0050] 上述實施例是本發明的一例,本發明是上述以外的實施例也可以。例如圓柱不限定於5條。 [實施例]   [0051] [參考例]   超純水製造裝置,是準備第3圖所示者。此超純水製造裝置81,是由前處理裝置82、一次純水製造裝置83、及二次純水製造裝置(副系統)84的3段的裝置所構成。在此超純水製造裝置81的前處理裝置82中,是被施加由原水W的過濾、凝集沈澱、精密過濾膜所產生的前處理。   [0052] 一次純水製造裝置83,是具有:前處理水W1的槽桶85、及逆滲透(RO)膜裝置86、及紫外線(UV)氧化裝置87、及再生型離子交換裝置(混床式或是4床5塔式等)88、及膜式脫氣裝置89。   [0053] 副系統84,是由:將由一次純水製造裝置83被製造的一次純水W2貯留的副槽桶91、及將從此副槽桶91透過無圖示的泵被配送的一次純水W2處理的紫外線氧化裝置92、及白金族金屬觸媒樹脂塔93、及膜式脫氣裝置94、及非再生型混床式離子交換裝置95、及作為膜過濾裝置的限外過濾(UF)膜96所構成。由限外過濾(UF)膜96將微粒子去除而作成超純水W3,將其供給至使用點97,將未使用的超純水朝副槽桶91還流。   [0054] 將平均粒子徑3.5nm的白金奈米溶膠粒子,由0.07重量%的載持量載持在強鹼性凝膠(膠狀物)型陰離子交換樹脂,調製了載持了白金族的金屬奈米粒子的陰離子交換樹脂作為白金族金屬觸媒樹脂。   [0055] 在第3圖所示的裝置構成的超純水製造裝置81中,使用上述的白金族金屬觸媒樹脂將白金族金屬觸媒樹脂塔93構成將超純水W3製造,測量了副系統84的白金族金屬觸媒樹脂塔93的入口水及出口水的過氧化氫濃度(初期)。將結果如表1所示。且,測量了將此超純水製造裝置81的運轉持續長時間(30日)之後的白金族金屬觸媒樹脂塔93的出口水的過氧化氫濃度(末期)。將結果配合表1顯示。   [0056] 為了測量過氧化氫濃度,在酚酞4.8mg、硫酸銅(無水)8mg及氫氧化鈉48mg添加硫酸鈉(無水)成為10g,調製了微量過氧化氫濃度定量用試藥。在試驗水10mL添加該試藥0.5g並溶解,在室溫10分鐘靜置之後,測量552nm中的吸光度,依據此測量值將過氧化氫濃度算出。   [0057] [表1] [0058] 從表1明顯可知,長時間運轉後的超純水W3的過氧化氫濃度的上昇是顯著。   [0059] [比較例1]   在參考例中,將長時間運轉後的白金族金屬觸媒樹脂塔93的樹脂取出,充填至試驗用的圓柱,作成試驗用的白金族金屬觸媒樹脂塔。且,為了比較而將新品的白金族金屬觸媒樹脂同樣地充填至試驗用的圓柱,作成白金族金屬觸媒樹脂塔。   [0060] 朝超純水(過氧化氫1μg/L未滿)將過氧化氫各別添加300μg/L或是1000μg/L將試驗用入口水調製,測量了將此試驗用入口水朝上述的試驗用圓柱由通水速度(SV)300hr-1 下向流通水之後的出口水的過氧化氫濃度。將結果如表2所示。   [0061] [表2] [0062] 從表2明顯可知,將長時間運轉後的白金族金屬觸媒樹脂塔93的樹脂充填至圓柱的比較例1的過氧化氫的濃度是比新品更高。由此可知,過氧化氫分解能下降。   [0063] [實施例1]   在參考例中,將長時間運轉後的白金族金屬觸媒樹脂塔93的樹脂充填至試驗用的圓柱,作成試驗用的白金族金屬觸媒樹脂塔。且,為了比較而將新品的白金族金屬觸媒樹脂同樣地充填至試驗用的圓柱,作成白金族金屬觸媒樹脂塔。   [0064] 朝超純水(過氧化氫1μg/L未滿)將過氧化氫添加30μg/L而調製成入口水,測量了將此入口水朝上述的試驗用圓柱由通水速度(SV)400hr-1 下向流通水之後的出口水的過氧化氫濃度。結果如表3所示。   [0065] 且負荷試驗是朝超純水(過氧化氫1μg/L未滿)添加過氧化氫400μg/L將試驗用入口水調製,將此試驗用入口水朝上述的試驗用圓柱由通水速度(SV)6400hr-1 22小時下向流通水之後將運轉停止之後,將朝超純水(過氧化氫1μg/L未滿)添加了過氧化氫30μg/L的入口水通水,測量了5分鐘後、60分鐘後的出口水的過氧化氫濃度。結果如表3所示。   [0066] 且將各試驗用的白金族金屬觸媒樹脂塔的樹脂取出,在超純水(過氧化氫1μg/L未滿)保管2週之後,再度充填,測量了朝超純水(過氧化氫1μg/L未滿)將過氧化氫添加了30μg/L的入口水通水時的出口水的過氧化氫濃度。將結果如表3所示。   [0067] [表3] [0068] 從表3明顯可知,藉由在超純水中保管2週,白金族金屬觸媒的性能有回復。   [0069] 雖使用特定的態樣詳細說明了本發明,但是本行業者明顯不需遠離本發明的意圖及範圍,就可進行各式各樣的變更。   本案,是援用依據2016年12月28日申請的日本專利申請第2016-255445號的整體。[0028] Hereinafter, the present invention will be described in further detail. [0029] The method and device for removing hydrogen peroxide according to the present invention are optimally used in the manufacturing process of ultrapure water. In the ultrapure water manufacturing process, as described above, the primary pure water from the primary pure water manufacturing device is processed by the sub-system so that the ultrapure water is manufactured. In the sub-system, once the pure water is processed by the ultraviolet oxidation device, the hydrogen peroxide is removed by the hydrogen peroxide removal device with a platinum catalyst, and then the non-renewable ion exchange device, membrane degassing device, and UF are processed. Membrane device is water-permeable. [0030] The TOC component is oxidized and decomposed by the ultraviolet oxidation treatment in the ultraviolet oxidation device to generate organic acid and carbonic acid, and hydrogen peroxide is generated. In the present invention, the effluent water from the ultraviolet oxidation device is passed to a hydrogen peroxide removal device to remove hydrogen peroxide. This hydrogen peroxide removal device uses a platinum catalyst to fill a container. Platinum-based catalysts are sol particles of platinum-based metals, especially those in which nano-sol particles are carried on a carrier. [0031] Platinum-based metals include ruthenium, rhodium, palladium, osmium, iridium, and platinum. These platinum group metals can be used singly or in combination of two or more kinds. They can also be used as two or more kinds of alloys, or the refined products of naturally produced mixtures are not separated into monomers. You can use it. Among these, platinum, palladium, and a platinum / palladium alloy alone or a mixture of two or more of these are particularly preferred because of their strong catalyst activity. [0032] The method for producing nanosol particles of platinum-based metal is not particularly limited, and examples thereof include a metal salt reduction reaction method and a combustion method. Among these, the metal salt reduction reaction method is easy to manufacture and can be used optimally because metal nanosol particles of stable quality can be obtained. [0033] The average particle diameter of the nanosol particles of the platinum-based metal is preferably 1 to 50 nm, more preferably 1.2 to 20 nm, and still more preferably 1.4 to 5 nm. This particle diameter is a value obtained from an electron microscope image. [0034] Examples of the carrier for supporting the platinum-based metal nanosol particles include, for example, magnesium oxide, titanium dioxide, aluminum oxide, silica-alumina, zirconia, activated carbon, zeolite, diatomaceous earth, and ions. Exchange resin, etc. Among these, anion exchange resins can be particularly preferably used. Platinum metal nanosol particles have an electric double layer and are negatively charged, so they are stably supported on an anion exchange resin and are not easily peeled off. Platinum metal nanosol particles supported on an anion exchange resin show strong catalytic activity for the decomposition and removal of hydrogen peroxide. The exchange group of the anion exchange resin is preferably OH. OH-type anion exchange resin is used to make the resin surface alkaline and promote the decomposition of hydrogen peroxide. [0035] The supporting amount of the platinum-based metal nanosol particles toward the anion exchange resin is preferably 0.01 to 0.2% by weight, and more preferably 0.04 to 0.1% by weight. [0036] Hydrogen peroxide in water is a hydrogen peroxide decomposition catalyst supporting platinum-based metal nanosol particles on a carrier by contacting hydrogen peroxide-containing water, and 2H 2 O 2 → 2H 2 O + O 2 is decomposed by reaction. [0037] The water passing through the velocity toward the platinum-containing catalyst based aqueous hydrogen peroxide filled container, the space velocity is preferably SV100 ~ 2,000h -1, 300 ~ 1,500h -1 better. Platinum catalysts, because the decomposition rate of hydrogen peroxide is very fast, even if the SV is 100h -1 or more, the hydrogen peroxide can be fully decomposed. However, if the SV exceeds 2,000 h -1 , the pressure loss due to water flow is too large, and the decomposition and removal of hydrogen peroxide may become insufficient. [0038] Specific examples of the method and apparatus for removing hydrogen peroxide according to the present invention will be described with reference to FIGS. 1 and 2. [0039] In FIG. 1, a plurality of columns 21 to 25 in which platinum-based catalysts are filled are arranged in parallel (five in the figure). The hydrogen peroxide-containing water such as the outflow water of the ultraviolet irradiation device passes through the valves 11 to 15 through the pipes 1 and passes through the cylinders 21 to 25. The outflow water from the cylinders 21 to 25 is taken out through the valves 31 to 35 and the collecting pipe 2. [0040] Treatment is carried out by the method of passing water in parallel to five columns 21 to 25. At the time when the signs of the deterioration of the treated water were recognized, the water flow to a cylinder as shown in Fig. 1 (b) (the cylinder 21 in Fig. 1 (b)) was closed by closing the valves 11, 31 Stop, and increase the water flow of the four remaining cylinders 22 to 25 by 25% each to perform parallel operation to ensure the amount of treated water. [0041] With respect to the cylinder 21 that stops water flow, by applying: (1) standing still for a certain period of time. (2) The atmosphere in the cylinder is replaced with a non-oxidizing gas such as N 2 gas. (3) Once the platinum-based catalyst is pulled out, it is preferably immersed in ultrapure water for a predetermined time (preferably more than 1 day, especially about 2 to 10 days), and then filled. (4) Pass hydrogen-dissolved water through the water. Any one or a combination of two or more of the above treatments restores the hydrogen peroxide decomposition performance. [0042] Thereafter, it is preferable to pass water to the cylinder 21 experimentally, and after confirming that the quality of the treated water is good, the valves 11 and 31 are opened to reopen the water to the cylinder 21. Thereafter, the performance recovery operation is performed on the other columns 22 to 25 in the same order in order to return the performance to a good state. [0043] After the reply processing for all of the five cylinders 21 to 25 is completed, the five parallel water flows of the original standard flow rate are returned. [0044] FIG. 2 shows that three-way valves 41 to 45 can be provided instead of valves 11 to 15, three-way valves 51 to 55 can be provided instead of valves 31 to 35, and N 2 gas or hydrogen can be dissolved toward each of the columns 21 to 25. A hydrogen peroxide removal device that can supply water by switching operations of the three-way valves 31 to 35 and 51 to 55. [0045] The third ports of the three-way valves 41 to 45 are connected to pipes 61 to 65 branched from the pipe 60. The third ports of the three-way valves 51 to 55 are connected to the discharge pipe 70 through the branch pipes 71 to 75. N 2 gas or hydrogen-dissolved water is supplied from the pipe 60 to any of the columns 21 to 25, and the outflow gas or hydrogen-dissolved water is discharged from the pipe 70. [0046] In the case where the standard SV is allowed to pass water at 400 / h equally to each of the columns 21 to 25 provided with the hydrogen peroxide removing device of the five columns 21 to 25 juxtaposed as shown in FIGS. In response to the treatment, four parallel water flows (for example, Fig. 1 (b)) will increase the SV of each cylinder to 500 / h. This is not good for maintaining the quality of treated water. However, the hydrogen peroxide decomposition life of platinum-based resin (when no recovery treatment is applied) is only a few years. For this reason, since the recovery treatment is a maximum of one week, a 25% increase in the load on each column is the longest. Degree in 4 weeks. Here, since the water flow of the cylindrical cylinders whose performance has been restored has been reopened, it is not difficult to maintain the overall water treatment capacity (SV500 / h) of the hydrogen peroxide removal device. [0047] In the first and second figures, five cylinders are arranged side by side, but six cylinders are arranged side by side, and one of them is stopped in order (performance recovery operation), and it is often possible to run the five cylinders through water. [0048] In this case, when the prescribed time (predetermined hydrogen peroxide load) is exceeded, one of them will be stopped, and one of the methods that will not be used at the same time to start the water flow will be 5/6 of the time of each container. Water, 1/6 of the time is the intermittent intermittent operation) According to the rotating merry-go-round application, you can run with plenty of room. [0049] Based on the experimental results of the present inventors, the following are considered. (1) If the water passing through the treated water into the platinum-type catalyst filling container is stopped after a predetermined period of time and the water passing is turned on again, the hydrogen peroxide decomposition performance can be restored. The longer the stop time, the higher the degree of recovery. (2) When the water flow to the platinum-type catalyst filling container from the treated water is stopped, and the operation of removing O 2 from the container by N 2 gas aeration is added, the hydrogen peroxide decomposition performance is better than (1) Reply shortly. (3) Once the water passing through the treated water to the platinum-based catalyst filling container is stopped, once the platinum-based catalyst is pulled out of the container, it will be refilled after being stored in ultrapure water for a predetermined period of time, and then re-opened with water. The hydrogen decomposition performance is recovered in a shorter time than the above (1) and (2). (4) After stopping the water flow from the treated water to the platinum catalyst filling container, and passing hydrogen-dissolved water through the water, the hydrogen peroxide decomposition performance is restored in a shorter time than the above (1) to (3). [0050] The above embodiment is an example of the present invention, and the present invention may be an embodiment other than the above. For example, the number of columns is not limited to five. [Example] [0051] [Reference Example] An ultrapure water production apparatus is prepared as shown in FIG. 3. This ultrapure water production device 81 is composed of a three-stage device of a pretreatment device 82, a primary pure water production device 83, and a secondary pure water production device (sub-system) 84. The pretreatment device 82 of this ultrapure water production device 81 is a pretreatment produced by filtration, agglomeration, and precision filtration of raw water W. [0052] The primary pure water production device 83 includes a tank 85 of pre-treated water W1, a reverse osmosis (RO) membrane device 86, an ultraviolet (UV) oxidation device 87, and a regenerative ion exchange device (mixed bed). Type or 4 bed 5 tower type, etc.) 88, and membrane type degassing device 89. [0053] The sub-system 84 includes a sub-tank bucket 91 that stores the primary pure water W2 produced by the primary pure water production device 83, and primary pure water that is distributed from the sub-tank bucket 91 through a pump (not shown). W2 treated ultraviolet oxidation device 92, platinum group metal catalyst resin tower 93, membrane degassing device 94, non-regenerating mixed bed type ion exchange device 95, and ultra-restricted filtration (UF) as a membrane filtration device The film 96 is formed. The ultrafine water W3 is produced by removing the fine particles by the ultra-limiting filtration (UF) membrane 96, and the ultrapure water W3 is supplied to the use point 97, and the unused ultrapure water is returned to the sub tank 91. [0054] Platinum nano sol particles having an average particle diameter of 3.5 nm were supported on a strongly basic gel (gel) type anion exchange resin with a supporting amount of 0.07 wt% to prepare a platinum-supported Anion exchange resins of metal nano particles serve as platinum group metal catalyst resins. [0055] In the ultrapure water production device 81 having the device configuration shown in FIG. 3, the platinum group metal catalyst resin 93 was used to manufacture the ultrapure water W3 using the platinum group metal catalyst resin described above, and the measurement The hydrogen peroxide concentration (initial stage) of the inlet water and the outlet water of the platinum group metal catalyst resin tower 93 of the system 84. The results are shown in Table 1. Then, the hydrogen peroxide concentration (last stage) of the outlet water of the platinum group metal catalyst resin tower 93 after the operation of this ultrapure water production device 81 was continued for a long time (30 days) was measured. The results are shown in Table 1. [0056] In order to measure the hydrogen peroxide concentration, 4.8 mg of phenolphthalein, 8 mg of copper sulfate (anhydrous) and 48 mg of sodium hydroxide were added with sodium sulfate (anhydrous) to 10 g, and a reagent for quantifying a small amount of hydrogen peroxide concentration was prepared. 0.5 g of the reagent was added to 10 mL of test water and dissolved. After standing at room temperature for 10 minutes, the absorbance at 552 nm was measured, and the hydrogen peroxide concentration was calculated based on the measured value. [Table 1] [0058] As apparent from Table 1, the increase in the hydrogen peroxide concentration of the ultrapure water W3 after a long-term operation is significant. [Comparative Example 1] In the reference example, the resin of the platinum group metal catalyst resin tower 93 after long-time operation was taken out, filled into a test cylinder, and a platinum group metal catalyst resin tower for testing was prepared. In addition, for comparison, a new platinum group metal catalyst resin was similarly filled into a test cylinder to form a platinum group metal catalyst resin tower. [0060] Adding 300 μg / L or 1000 μg / L of hydrogen peroxide to ultrapure water (less than 1 μg / L of hydrogen peroxide), the inlet water for the test was prepared, and the inlet water for the test was measured. The concentration of hydrogen peroxide in the outlet of the test cylinder after the water was passed from the flow velocity (SV) 300hr -1 to the circulating water. The results are shown in Table 2. [Table 2] [0062] It is clear from Table 2 that the concentration of hydrogen peroxide in Comparative Example 1 in which the resin of the platinum group metal catalyst resin tower 93 after a long-time operation was filled into the column was higher than that of the new product. From this, it can be seen that the decomposition energy of hydrogen peroxide decreases. [Example 1] In the reference example, the resin of the platinum group metal catalyst resin tower 93 after being operated for a long time was filled into a test cylinder to form a platinum group metal catalyst resin tower for the test. In addition, for comparison, a new platinum group metal catalyst resin was similarly filled into a test cylinder to form a platinum group metal catalyst resin tower. [0064] 30 μg / L of hydrogen peroxide was added to ultrapure water (less than 1 μg / L of hydrogen peroxide) to prepare inlet water, and the water passing velocity (SV) of the inlet water toward the test cylinder was measured. The concentration of hydrogen peroxide in the outlet water after flowing into the water at 400hr -1 . The results are shown in Table 3. [0065] In the load test, 400 μg / L of hydrogen peroxide was added to ultrapure water (less than 1 μg / L of hydrogen peroxide), and the inlet water for the test was prepared, and the inlet water for this test was passed through the water to the above-mentioned test cylinder. Velocity (SV) 6400hr -1 After 22 hours of flow to the circulating water, the operation was stopped, and 30 μg / L of hydrogen peroxide was added to the ultra pure water (with hydrogen peroxide 1 μg / L under). The hydrogen peroxide concentration of the outlet water after 5 minutes and 60 minutes. The results are shown in Table 3. [0066] The resin of the platinum group metal catalyst resin tower for each test was taken out, and after being stored for 2 weeks in ultrapure water (less than 1 μg / L of hydrogen peroxide), it was refilled, and measurements were made on The hydrogen peroxide is less than 1 μg / L) The hydrogen peroxide concentration of the outlet water when hydrogen peroxide is added to the inlet water at 30 μg / L. The results are shown in Table 3. [Table 3] [0068] As apparent from Table 3, the performance of the platinum group metal catalyst was restored by storage in ultrapure water for 2 weeks. [0069] Although the present invention has been described in detail using specific aspects, those skilled in the art can obviously make various changes without departing from the intention and scope of the present invention. This case refers to the entirety of Japanese Patent Application No. 2016-255445 filed on December 28, 2016.

[0070][0070]

W‧‧‧原水W‧‧‧ raw water

W1‧‧‧前處理水W1‧‧‧ pre-treated water

W2‧‧‧一次純水W2‧‧‧Pure water

W3‧‧‧超純水W3‧‧‧ ultra pure water

1‧‧‧配管1‧‧‧Piping

2‧‧‧集合配管2‧‧‧collection piping

11~15、31~35‧‧‧閥11 ~ 15, 31 ~ 35‧‧‧valve

21~25‧‧‧圓柱21 ~ 25‧‧‧Column

41~45、51~55‧‧‧三方閥41 ~ 45、51 ~ 55‧‧‧Three-way valve

61~65‧‧‧配管61 ~ 65‧‧‧Piping

70‧‧‧排出用配管70‧‧‧ discharge pipe

71~75‧‧‧分岐配管71 ~ 75‧‧‧ branch manifold

81‧‧‧超純水製造裝置81‧‧‧Ultra-pure water manufacturing equipment

82‧‧‧前處理裝置82‧‧‧Pre-treatment device

83‧‧‧一次純水製造裝置83‧‧‧Pure water manufacturing equipment

84‧‧‧副系統84‧‧‧ Subsystem

85‧‧‧槽桶85‧‧‧ tank

86‧‧‧膜裝置86‧‧‧ membrane device

87‧‧‧氧化裝置87‧‧‧oxidation device

89‧‧‧脫氣裝置89‧‧‧ degassing device

91‧‧‧副槽桶91‧‧‧ Deputy tank

92‧‧‧紫外線氧化裝置92‧‧‧ultraviolet oxidation device

93‧‧‧白金族金屬觸媒樹脂塔93‧‧‧Platinum metal catalyst resin tower

94‧‧‧脫氣裝置94‧‧‧ degassing device

95‧‧‧離子交換裝置95‧‧‧ ion exchange device

96‧‧‧限外過濾(UF)膜96‧‧‧External Filter (UF) Membrane

97‧‧‧使用點97‧‧‧points of use

[0027]   [第1圖]本發明方法的說明圖。   [第2圖]本發明裝置的一例的說明圖。   [第3圖]超純水製造裝置的系統圖。[0027] [FIG. 1] An explanatory diagram of the method of the present invention. [Fig. 2] An explanatory diagram of an example of the device of the present invention.第 [Figure 3] System diagram of ultrapure water production equipment.

Claims (7)

一種過氧化氫去除方法,   是朝具有被並列設置的白金系觸媒充填容器的過氧化氫去除裝置將含過氧化氫水通水將過氧化氫去除的過氧化氫去除方法,其特徵為:   進行將含過氧化氫水朝一部分的容器的通水規定期間停止的過氧化氫去除性能回復操作。A method for removing hydrogen peroxide is a method for removing hydrogen peroxide by passing hydrogen peroxide-containing water through water to a hydrogen peroxide removal device having a platinum-type catalyst filling container arranged in parallel, which is characterized by: The operation of restoring hydrogen peroxide removal performance to stop the passage of hydrogen peroxide-containing water toward a part of the container for a predetermined period of time is performed. 如申請專利範圍第1項的過氧化氫去除方法,其中,   在前述規定時間,朝前述容器供給非氧化性氣體。For example, the method for removing hydrogen peroxide according to item 1 of the scope of patent application, wherein: (i) supplying non-oxidizing gas to the container at the aforementioned predetermined time. 如申請專利範圍第2項的過氧化氫去除方法,其中,   非氧化性氣體是氮氣體。For example, the method for removing hydrogen peroxide according to item 2 of the patent application, wherein the non-oxidizing gas is nitrogen gas. 如申請專利範圍第1至3項中任一項的過氧化氫去除方法,其中,   在前述規定時間,從前述容器將觸媒取出再充填。For example, the method for removing hydrogen peroxide according to any one of claims 1 to 3, wherein, at a predetermined time, the catalyst is removed from the container and refilled. 如申請專利範圍第1至4項中任一項的過氧化氫去除方法,其中,   在前述規定時間,朝前述容器將氫溶解水通水。The method for removing hydrogen peroxide according to any one of claims 1 to 4 of the scope of patent application, wherein: passes hydrogen-dissolved water into the container at the predetermined time. 如申請專利範圍第1至5項中任一項的過氧化氫去除方法,其中,   前述過氧化氫去除裝置是被設置在超純水製造裝置,在前述規定時間,使朝前述一部分以外的白金系觸媒充填容器的通水量增加。For example, the hydrogen peroxide removal method according to any one of claims 1 to 5, wherein the aforementioned hydrogen peroxide removal device is provided in an ultrapure water production device, and at a predetermined time, the platinum The water flow of the catalyst filling container increased. 一種過氧化氫去除裝置,其特徵為,具備:   被並列設置的白金系觸媒充填容器、及   朝各容器將含過氧化氫水通水的含過氧化氫水通水手段、及   朝各容器供給非氧化性氣體或是氫溶解水的供給手段、及   將朝各容器的含過氧化氫水通水及非氧化性氣體或是氫溶解水供給切換的切換手段。A hydrogen peroxide removing device, comprising: (1) a platinum-type catalyst filling container arranged in parallel; and a hydrogen peroxide-containing water passing means for passing hydrogen peroxide-containing water toward each container; and a container directed toward each container Supply means for supplying non-oxidizing gas or hydrogen-dissolved water, and switching means for switching supply of hydrogen peroxide-containing water to each container, and supply of non-oxidizing gas or hydrogen-soluble water.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI801307B (en) * 2020-06-23 2023-05-01 日商奧璐佳瑙股份有限公司 Water treatment device, pure water production device, ultrapure water production device, and water treatment method

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA3201871A1 (en) 2020-12-10 2022-06-16 Andreas Kempter Process for the controlled decomposition of peroxo compounds
CN113019362B (en) * 2021-05-31 2021-09-07 江苏欣诺科催化剂有限公司 Metallic ruthenium supported catalyst

Family Cites Families (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2560167Y2 (en) * 1991-05-02 1998-01-21 須賀工業株式会社 Hydrogen peroxide water decomposition equipment
CN1063354C (en) * 1993-12-22 2001-03-21 三菱化学株式会社 The regeneration method of ruthenium series catalyst
JP2780652B2 (en) * 1993-12-22 1998-07-30 三菱化学株式会社 Ruthenium-based regenerated catalyst
JP2003305465A (en) * 2002-04-15 2003-10-28 Mitsubishi Electric Corp Pure water production system and water quality monitoring method
JP4578048B2 (en) * 2002-06-21 2010-11-10 中国電力株式会社 Denitration catalyst regeneration method
JP2007160268A (en) * 2005-12-16 2007-06-28 Tokyo Electric Power Co Inc:The Denitration catalyst regeneration treatment method
JP5124946B2 (en) * 2006-01-12 2013-01-23 栗田工業株式会社 Removal method of hydrogen peroxide in ultrapure water in ultrapure water production equipment
JP5098215B2 (en) * 2006-05-01 2012-12-12 三菱瓦斯化学株式会社 Method for activating hydrogenation catalyst and method for producing hydrogen peroxide containing the same
JP2010017633A (en) 2008-07-09 2010-01-28 Japan Organo Co Ltd Apparatus for producing hydrogen-dissolved water and method for producing hydrogen-dissolved water using the apparatus, and washing device for electronic component or for instrument for manufacturing electronic component
JP5838485B2 (en) * 2012-02-14 2016-01-06 国立大学法人大阪大学 Glycerol hydrocracking catalyst and method for producing 1,3-propanediol using the catalyst
JP2013215679A (en) * 2012-04-09 2013-10-24 Nomura Micro Sci Co Ltd Ultrapure water production apparatus
JP6351589B2 (en) * 2013-06-18 2018-07-04 株式会社ダイセル Method for regenerating catalyst for hydrogenation reaction and method for producing hydride of polyhydric alcohol
JP6423211B2 (en) * 2013-09-25 2018-11-14 オルガノ株式会社 Substrate processing method and substrate processing apparatus
JP2015093226A (en) * 2013-11-11 2015-05-18 栗田工業株式会社 Method and apparatus for manufacturing pure water
JP6290654B2 (en) * 2014-03-04 2018-03-07 オルガノ株式会社 Ultrapure water production equipment
JP6490952B2 (en) * 2014-11-26 2019-03-27 オルガノ株式会社 Reactor and water treatment device
CN104785254B (en) * 2015-03-20 2017-04-12 西安凯立新材料股份有限公司 Catalyst for degrading hydrogen peroxide as well as preparation method and application of catalyst
JP6670047B2 (en) 2015-05-22 2020-03-18 オルガノ株式会社 Ultrapure water production equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI801307B (en) * 2020-06-23 2023-05-01 日商奧璐佳瑙股份有限公司 Water treatment device, pure water production device, ultrapure water production device, and water treatment method

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