TW200936510A - Water purifying device and water purifying method - Google Patents

Water purifying device and water purifying method Download PDF

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Publication number
TW200936510A
TW200936510A TW097141909A TW97141909A TW200936510A TW 200936510 A TW200936510 A TW 200936510A TW 097141909 A TW097141909 A TW 097141909A TW 97141909 A TW97141909 A TW 97141909A TW 200936510 A TW200936510 A TW 200936510A
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Taiwan
Prior art keywords
water
woven fabric
fiber
ultraviolet
phase
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TW097141909A
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Chinese (zh)
Inventor
Hiroyuki Yamaoka
Yoshikatsu Harada
Teruaki Fujii
Shinichirou Otani
Tadashi Matsunaga
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Ube Industries
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Publication of TW200936510A publication Critical patent/TW200936510A/en

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    • B01J35/59
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/06Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
    • B01J21/063Titanium; Oxides or hydroxides thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/06Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
    • B01J21/08Silica
    • B01J35/50
    • 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
    • B01J35/39
    • B01J35/58
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Toxicology (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Physical Water Treatments (AREA)
  • Catalysts (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

A water purifying device and method for purifying water by efficiently decomposing unwanted organic substances present in water. The water purifying device comprises a water flowing tank through which water to be purified is made to flow in one direction, one or more platy nonwoven fabrics permeable to water, placed in the water flowing tank, and composed of fibers having a photocatalytic function, and an ultraviolet radiation irradiating means for irradiating the platy nonwoven fabrics with ultraviolet radiation. The device is characterized in that the ultraviolet irradiating means has a shape extending in the length direction and can radiates ultraviolet radiation having peak wavelengths in the range from 180 to 190 nm and in the range from 250 to 260 nm, and the platy nonwoven fabrics are parallel to the length direction of the ultraviolet irradiating means.

Description

200936510 九、發明說明: 【發明所屬之技術領域】 本發明係關於一種水淨化裝置及水淨化方法,其可藉 由有效率地分解存在於水中之不要的有機物而將水淨化。 【先前技術】 近年來,於電子工業領域技術革新的速度快,於半導 體產業微細化方面也持續進展。伴隨如此之技術的進步,BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water purification apparatus and a water purification method which can purify water by efficiently decomposing unnecessary organic substances present in water. [Prior Art] In recent years, technological innovation in the field of electronics industry has been fast, and progress has been made in the miniaturization of the semiconductor industry. With the advancement of such technology,

例如,於半導體製造所使用之超純水的水質基準也變得非 常嚴格而需要可有效率地分解、淨化水中所含之不要之 微置有機物的水淨化裝置。將水中所含之不要的有機物淨 化之裝置例如於專利文獻丨,揭示一種藉由對水照射紫外線 將存在於水中之不要的有機物氧化分解之水淨化裝置。 又,於專利文獻2記載-種水淨化裝置,其係將254nm之 峰值波長(peak Wavelength)之紫外線照射於不織布所載 之光觸媒’藉由藉此生成之〇H自由基,將水中之不 機物刀解,该水淨化裝置,係將具有光觸媒機能之不織布 作成中空圓錐台形狀,並將具有254nm之降值波長 線燈配置於中心部。 $外 專利文獻1 .日本專利特開平6_198279號公報。 專利文獻2 :日本專利第3436267號公報。 【發明内容】 烈rfn ,為了以照射紫外線分解水中之有機物係 “、。因此’大部分係使用高輪出之紫外線燈 - 數個紫外、線燈。於專利文獻 或使用 号』又馱1中’顯不為了節省分 200936510 之能源’而監控處理水中 變紫外線燈之輸出。2 因應該濃度改 ^ ^ ' 17使如此,其問題在於藉照射 氧化分解仍需要很大之能源。於專利文獻2中, '、種和用一氧化鈦光觸媒而有效率地生成〇H自由基,並 使該OH自由基與水巾之㈣物良好地接觸之構造可得高 刀解效率。但是’其問題在於無法得到滿足現今高水質基 準之足夠的分解效率。 種水淨化裝置及水淨 於水中之不要的有機 因此,本發明之目的在於提供一 化方法,其可藉由有效率地分解存在 物而將水淨化。 為了達成以上之目的,本發明人等,努力研究的結果 發現,由設置成平行於具光觸媒功能之纖維所構成之平板 狀不織布之紫外'線照、射手段,對該平板狀不織布照射於 180〜190nm與250〜26〇nm具有峰值波長之紫外線可有效 率地分解存在於水中之不要的有機物。亦即,本發明係一 種水淨化裝置,其具備: 使欲淨化之水朝一方向流動之流動槽; 設置於該流動槽内且可使該欲淨化之水通過之至少一 個以上之由具光觸媒功能之纖維所構成的平板狀不織布; 與 將紫外線照射於該平板狀不織布之紫外線照射手段. 其特徵在於: 該紫外線照射手段,其構成係具有朝長邊方向延長之 形狀,可照射於180〜190nm與250〜260nm具有峰值、皮長之 200936510 紫外線,且設晋点甘、皇> 又太恭 纟丨長邊方向與該平板狀不織布呈平行。 又’本發明亦為—錄 丁 種尺孕化方法,其特徵在於,使欲 之水於流動之下,通過由 柘贴X述士 项迥由八光觸媒功能之纖維所構成的平 板狀不織布,而由且右朝i泳 ^朝長邊方向延長之形狀且設置成該 古與該平板狀不織布呈平行之紫外線照射手段,對 /平板狀不織布’照射於⑽〜⑽咖與25Q〜細咖具有峰 值波長之紫外線。 ❹ ^如上所述’藉由本發明,可提供一種水淨化裝置及水 淨化方法’其可藉由有效率地分解存在於水中之不要的有 機物而將水淨化。 【實施方式】 接著,使用圖式詳細說明本發明之水淨化裝置之第夏 實施型態。圖卜係第i實施型態之水淨化裝置之概念立體 圖。第1實施型態之水淨化裝置10,具備: 使欲淨化之水由形成於底面之流入口 41朝形成於頂面 之流出口 42流動之流動槽丨i、 收納於流動槽11内且其之面設置成相對於欲淨化之水 之流動方向呈垂直相交之互相平行之三個光觸媒匣2〇、 與配置於該等光觸媒g 20之間之紫外線燈3〇。 構成紫外線燈3 0之外表面之外殼構件係形成為圓柱 狀,由不僅可使250〜260nm透過且亦可使180〜190nm之峰 值波長透過的材質所構成《該外殼構件之材質可舉例如合 成石英。一般之低壓水銀燈’原本係具有185ηιη與254nm 之兩個波長,但由於通常之外殼構件之原料玻璃,不會使 7 200936510 短波長之紫外線透過,故僅照射254nm之波長。於本實施 型態之水淨化裝置中,紫外線燈3〇,如上述藉由以特殊原 料作為外殼構件之原料’而成為可照射於18〇〜19〇nm與 250〜26〇nm具有峰值波長之紫外線的構成。由紫外線燈% 所照射之紫外線,於l80〜19〇nm(較佳為185nm)具有峰值波 長、且於250〜260nm(較佳為254nm)具有峰值波長。各紫外 線燈30,於各光觸媒匣2〇之間各設置2根'共計設置4根, 且係設置成分別平行、且其之軸方向與光觸媒匣2〇平行。 又’於第1實施型態中,紫外線照射燈3G之外殼構件係形 成為圓柱狀,但並不限定於此,只要為朝長邊方向延伸之 形狀即可。紫外線照射燈30之個數係視所需之水質或處理 水中所含之不要的有機物之量等來決定。 各光觸媒S20如圖2所示,係由平板狀不織布 對網22所構成,平板狀不織布2丨 綑”私+从 對不鐵鋼製之 故2所夾持。如此般藉由使用網22作為支持 :’則可容易更換光觸媒功能劣化之平板狀不織布2 由使用框體等將多段的光觸媒£ 2G作成連結構造 使裝卸容易。於第丨實施型態中, 伸可妨“ + 十板狀不織布21為3個, -了視所需求之水質等任意決定其之個數 個。又’於第1實施型態中,係將平板狀不織布。固1〜50 ^動槽U作為光觸隸20,但亦可以其㈣段 疋於 實施型態中,各平板狀不織布21, 。於第 動方向垂直相交之方i π ¥ . 、面係以與水之流 J坐直相父之方式δ又置,但只要 地通過各平板狀不織布21即 :動之水有效率 1 J如亦可傾斜配置。平 200936510 板狀不織布2卜較佳為其之面係以與水之流動方向垂直相 交之方式配置’亦可相對於流動方向前後傾斜10。(較佳為 前後5° )設置。 於第1實施型態之水淨化裝置中,平板狀不織布上之 平均々紫外線強度,較佳為、更佳為2〜8mW/cm2 之範圍右平板狀不織布表面之紫外線強度為 1〜1〇mW/Gm2,則可以2個紫外線成分高效率地進行水處 ο 了達到如此之範® ’可使紫外線照射手段與平板狀 不織t之距離等為適當範圍即可。此處,平均紫外線強度 係測疋由不織布表面之中央部至端部為止之數個部位的紫 外線強度,可將該等之值平均視為平均紫外線強度。” . 冑含不要的有機物之處理水加以淨化,首先,由水淨 化裝置10 4 15之流入口 41流入處理水。所流入之處理水 係通過流動槽11或16内再由流出口 42排出。平板狀不織 布21係纖維-根-根以具有1程度之空隙分散的構造, 〇故水通過之際,與光觸媒之接觸面積非常大。因此,可藉 具先觸媒功能之平板狀残布21有效率地產生自由基,而 分解不要的有機物。又,未達完全分解之不要的 會經0Η自由基等所分解至成為分解中間生成物即有機 酸,故亦可藉由將由流出口 42排出之處理水以離子 除去。 、寺 通常’利用二氧化鈦光觸媒之水淨化裝置中’紫外線 燈係使用波長351_之黑光螢光燈或波i Μ — 燈。此原因在於二氧化鈦光觸媒只要為387nm以下之 200936510 即可激發,且該等燈之製品容易取得。本發明之水淨化裝 置係利用以往未使用之紫外線,且藉由將光觸媒作成既定 之配置構造’可得高分解效率。亦即,於本發明之水淨化 裝置,由於具有具光觸媒功能之平板狀不織布、與設置成 與該平板狀不織布平行且照射出於18〇~19如m與 250〜260nm具有峰值波長之紫外線的紫外線照射手段,故 可維持對該光觸媒之光照射效率和與處自流體之接觸效 率,而180〜190nm之紫外線不會因光觸媒而截斷。因此, 藉由將250〜26〇nm之紫外線照射平板狀不織布以激發光觸 媒’藉由所產生之0H自由基分解有機物,而可藉由 之紫外線直接分解水中之有機物,可維持高分 解效果。 平板狀不織布21,較佳為由以二氧化矽成分為主體之 氧化物相(以下’稱為第1相)與含Ti之金屬氧化物相(以 下,稱為第2相)之複合氧化物即二氧化矽基複合氧化物纖 維所構成。 第1相係以二氧化矽成分為主體之氧化物相可為非 晶質或結晶質’且亦可含有可與二氧化矽形成固熔體或共 熔點化合物之金屬元素或金屬氧化物。可與二氧化矽形成 固熔體之金屬元素(A)可舉例如鈦等。可與二氧切形成共 溶點化合物之金屬元素⑻可舉例如紹、錯、妃、鐘、納、 鋇、鹤、硼、鋅、鎳、錳、鎂及鐵等。 第1相係形成二氧化矽基複合氧化物纖維之内部相, 扮肩肩負力學特性之重要角色。相對於二氧化矽基複合氧 200936510 化物纖維整體,第1相之存在比例較佳為4〇〜98重量%,而 為了充分發揮所要之第2相之功能且亦展現高力學特性, 第1相之存在比例以控制為5〇〜95重量%之範圍内為更佳。For example, the water quality standard for ultrapure water used in semiconductor manufacturing has become very strict, and there is a need for a water purification apparatus that can efficiently decompose and purify unwanted micro-organisms contained in water. An apparatus for purifying an organic substance contained in water, for example, in the patent document, discloses a water purification apparatus which oxidizes and decomposes an organic substance which is present in water by irradiating ultraviolet rays with water. Further, Patent Document 2 discloses a water purification device in which ultraviolet rays having a peak wavelength of 254 nm are irradiated onto a photocatalyst carried by a non-woven fabric to generate a ruthenium H radical, thereby causing a lack of water. In the water purifying device, the non-woven fabric having the photocatalytic function is formed into a hollow truncated cone shape, and a wavelength line lamp having a decreasing value of 254 nm is disposed at the center portion. Japanese Patent Laid-Open Publication No. Hei 6-198279. Patent Document 2: Japanese Patent No. 3436267. [Summary of the Invention] Strong rfn, in order to decompose the organic matter in the water by irradiation with ultraviolet rays, "so most of them use high-intensity ultraviolet lamps - several ultraviolet and linear lamps. In the patent literature or the use number" It is obvious that in order to save the energy of 200936510', the output of the ultraviolet lamp is monitored and treated in the water. 2 Because the concentration should be changed, the problem is that the oxidative decomposition by irradiation still requires a large amount of energy. In Patent Document 2 , ', and the structure of efficiently generating 〇H radicals with a titanium oxide photocatalyst and making the OH radicals in good contact with the water towel (4) can achieve high cleavage efficiency. However, the problem is that Obtaining sufficient decomposition efficiency to meet today's high water quality standards. Seed water purification device and organic water that is not in the water. Therefore, the object of the present invention is to provide a method for efficiently decomposing the presence of water. In order to achieve the above object, the inventors of the present invention have diligently studied and found that a flat plate composed of fibers disposed parallel to a photocatalytic function is used. The ultraviolet non-woven fabric of the non-woven fabric is irradiated with ultraviolet rays having a peak wavelength of 180 to 190 nm and 250 to 26 nm at the flat non-woven fabric, and the organic matter existing in the water can be efficiently decomposed. A water purification device comprising: a flow channel for flowing water to be purified in one direction; and at least one of the fibers having photocatalyst function disposed in the flow channel and allowing the water to be purified to pass through And a UV-ray irradiation means for irradiating ultraviolet rays on the flat-shaped nonwoven fabric. The ultraviolet irradiation means is configured to have a shape extending in the longitudinal direction and can be irradiated at 180 to 190 nm and 250 to 260 nm. The peak, the length of the skin is 200936510, and the setting point is Jin, Huang, and gt; and the direction of the long side is parallel with the flat non-woven fabric. The invention is also a method for the birthing of a stalk. It is to make the water of the desired flow flow through the flat non-woven fabric composed of the fibers of the eight-photocatalyst function. And the right side of the i swimming ^ is extended in the direction of the long side and is set to be an ultraviolet irradiation means in parallel with the flat non-woven fabric, and the pair of flat non-woven fabrics are irradiated with (10) to (10) coffee and 25Q to fine coffee having a peak wavelength.紫外线 ^ As described above, by the present invention, it is possible to provide a water purification device and a water purification method which can purify water by efficiently decomposing organic substances present in water. [Embodiment] The summer embodiment of the water purification device of the present invention will be described in detail with reference to the drawings. Fig. 2 is a conceptual perspective view of the water purification device of the first embodiment. The water purification device 10 of the first embodiment has: The water is flowed into the flow channel 11 by the flow inlet 41 formed in the bottom surface toward the flow outlet 42 formed in the top surface, and the surface thereof is disposed to intersect perpendicularly with respect to the flow direction of the water to be purified. The three photocatalysts 平行2〇 parallel to each other and the ultraviolet lamp 3〇 disposed between the photocatalysts g20. The outer casing member constituting the outer surface of the ultraviolet lamp 30 is formed in a columnar shape, and is made of a material that can transmit not only 250 to 260 nm but also a peak wavelength of 180 to 190 nm. The material of the outer casing member can be, for example, synthesized. quartz. A typical low-pressure mercury lamp has two wavelengths of 185 ηηη and 254 nm. However, since the raw material glass of the usual outer casing member does not transmit the short-wavelength ultraviolet rays of the light of 200936510, only the wavelength of 254 nm is irradiated. In the water purifying apparatus of the present embodiment, the ultraviolet lamp 3 is irradiated at 18 〇 to 19 〇 nm and 250 to 26 〇 nm with a peak wavelength by using a special raw material as a raw material of the outer casing member. The composition of ultraviolet light. The ultraviolet ray irradiated by the ultraviolet lamp % has a peak wavelength at 180 to 19 Å (preferably 185 nm) and a peak wavelength at 250 to 260 nm (preferably 254 nm). Each of the ultraviolet lamps 30 is provided in two "between two photocatalysts", and four of them are provided in total, and are arranged in parallel, and the axial direction thereof is parallel to the photocatalyst. Further, in the first embodiment, the outer casing member of the ultraviolet irradiation lamp 3G is formed in a columnar shape. However, the outer casing member is not limited thereto, and may have a shape extending in the longitudinal direction. The number of the ultraviolet irradiation lamps 30 is determined depending on the required water quality or the amount of unnecessary organic matter contained in the treated water. As shown in Fig. 2, each of the photocatalysts S20 is composed of a flat non-woven fabric pair 22, and a flat non-woven fabric 2 bundles are privately held from the non-ferrous steel. Therefore, by using the net 22 as Support: 'The flat non-woven fabric 2 which can easily replace the photocatalytic function is replaced by a multi-stage photocatalyst £2G by using a frame or the like to facilitate attachment and detachment. In the third embodiment, the extension can be "+ ten-plate non-woven fabric. 21 is 3, - depending on the water quality required, etc. Further, in the first embodiment, a flat non-woven fabric is used. The solid groove 1 to 50 is used as the light contact 20, but it is also possible that the (four) segment is in the embodiment, and each of the flat non-woven fabrics 21 is used. In the direction in which the first direction intersects perpendicularly, i π ¥ . , the surface is placed in a straight line with the flow of water J, but the ground is passed through each flat non-woven fabric 21: the water is efficient 1 J It can also be tilted. Flat 200936510 The slab-shaped non-woven fabric 2 is preferably disposed such that its surface is perpendicularly intersected with the flow direction of water. It may also be inclined 10 forward and backward with respect to the flow direction. (preferably 5° front and rear) settings. In the water purifying apparatus of the first embodiment, the average 々 ultraviolet ray intensity on the flat non-woven fabric is preferably, more preferably, 2 to 8 mW/cm 2 , and the ultraviolet ray intensity of the surface of the right flat woven fabric is 1 to 1 〇 mW. /Gm2, it is possible to efficiently carry out water at two ultraviolet components. To achieve such a standard, 'the distance between the ultraviolet ray irradiation means and the flat non-woven t can be set to an appropriate range. Here, the average ultraviolet ray intensity measures the intensity of the ultraviolet rays from a plurality of portions from the central portion to the end portion of the non-woven fabric surface, and these values can be regarded as an average ultraviolet ray intensity on average. The treated water containing the unnecessary organic matter is purified. First, the treated water flows into the inlet 41 of the water purification device 104. The inflowing treated water is discharged through the flow port 11 or 16 and then discharged from the outlet 42. The flat non-woven fabric 21-fiber-root-root structure has a structure in which a gap of 1 degree is dispersed, so that the contact area with the photocatalyst is very large when the water passes, and therefore, the flat-shaped residual cloth 21 with the first catalyst function can be used. The free radicals are efficiently generated, and the organic matter which is not decomposed is decomposed. Further, if it is not completely decomposed, it is decomposed by a radical or the like to an organic acid which is a decomposition intermediate product, and therefore can be discharged by the outflow port 42. The treated water is removed by ions. The temple is usually used in a water purification device using titanium dioxide photocatalyst. The ultraviolet light system uses a black light fluorescent lamp or a wave light of a wavelength 351. The reason is that the titanium dioxide photocatalyst is only 387 nm or less 200936510. It can be excited, and the products of the lamps are easily obtained. The water purifying device of the present invention utilizes ultraviolet rays which have not been used in the past, and is formed by photocatalyst. The water-purifying device of the present invention has a flat-shaped non-woven fabric having a photocatalytic function, and is disposed in parallel with the flat-shaped non-woven fabric and irradiated with 18 〇 to 19, such as m. With an ultraviolet ray irradiation means having a peak wavelength of 250 to 260 nm, the light irradiation efficiency to the photocatalyst and the contact efficiency with the fluid can be maintained, and the ultraviolet ray of 180 to 190 nm is not interrupted by the photocatalyst. Irradiating the flat non-woven fabric with ultraviolet light of 250 to 26 〇 nm to excite the photocatalyst to decompose the organic substance by the generated OH radical, thereby directly decomposing the organic substance in the water by the ultraviolet ray, thereby maintaining a high decomposition effect. The flat non-woven fabric 21 Preferably, it is a composite oxide of an oxide phase mainly composed of a cerium oxide component (hereinafter referred to as a first phase) and a metal oxide phase containing Ti (hereinafter referred to as a second phase), that is, a cerium oxide group. The composite oxide fiber is composed of the first phase of the oxide phase mainly composed of the ceria component, which may be amorphous or crystalline, and may also contain dioxable The metal element or metal oxide which forms a solid solution or a eutectic compound, and the metal element (A) which can form a solid solution with cerium oxide, for example, titanium, etc., can form a metal of a co-melting point compound with dioxo The element (8) may, for example, be a smear, a samarium, a bell, a nano, a samarium, a crane, a boron, a zinc, a nickel, a manganese, a magnesium, or an iron. The first phase forms an internal phase of the cerium oxide-based composite oxide fiber. The shoulder and shoulder negative mechanical properties play an important role. Compared with the ceria-based composite oxygen 200936510 compound fiber, the first phase is preferably present in a ratio of 4〇 to 98% by weight, and in order to fully exert the function of the desired second phase, The high mechanical properties are exhibited, and the ratio of the presence of the first phase is preferably in the range of 5 Torr to 95% by weight.

另一方面,第2相係含有Ti之金屬氧化物相,於發揮 光觸媒功能上扮演重要的角色。構成金屬氧化物之金屬可 舉例如Ti。其之金屬氧化物可為單體亦可為其之共熔點化 合物或以特定元素形成取代型之固熔體等。第2相係形成 二氧化矽基複合氧化物纖維之表層相,二氧化矽基複合氧 化物纖維之第2相之存在比例視金屬氧化物之種類而異, 但較佳為2〜6G重量% ’而為了充分發揮其之功能且同時展 現高強度’以控制為5〜50重量%之範圍内為更佳。 弟2相所含之金屬氧化物之巧之存在比例係朝二氧化 石夕基複合氧化物纖維之表面傾斜地增大,其組成之傾斜可 明破確認區域之厚度,較佳為控制在從表層開* $〜鳩請 之範圍’但亦可達纖維直徑之約1/3。又,第i相及第2相 之「存在比例」係表示構成帛1相之金屬氧化物及第2相 之金屬氧化物相對於構成第丨相之金屬氧化物與構成第2 =之金屬氧化物整體(亦即,二氧切基複合氧化物纖維整 體)之重量%。 7氧化矽基複合氧化物纖維所構成之平板狀不織布21 可藉以下之製造方法製得。 (炼融訪絲法) 水氧切基複合氧化物纖维可藉由經下述帛1步驟至 第4步驟而傲得,f ’、P,將具有具下述化1所表示之主鏈 11 200936510 骨架且數量平均分子量為200〜10000之聚碳矽烷 (polycarbosilane)以有機金屬化合物修飾之構造的變性聚碳 石夕烷、或變性聚碳矽烷與有機金屬化合物之混合物,進行 ’溶融紡絲,不溶化處理後,於空氣中或氧氣中進行燒成, 藉此’可製造二氧化矽基複合氧化物纖維。On the other hand, the second phase contains a metal oxide phase of Ti and plays an important role in functioning as a photocatalyst. The metal constituting the metal oxide can be exemplified by Ti. The metal oxide thereof may be a monomer or a eutectic compound thereof or a substituted solid solution formed of a specific element. The second phase forms a surface layer of the ceria-based composite oxide fiber, and the ratio of the second phase of the ceria-based composite oxide fiber varies depending on the kind of the metal oxide, but is preferably 2 to 6 G% by weight. It is more preferable to control the thickness to be 5 to 50% by weight in order to fully exert its function and simultaneously exhibit high strength. The proportion of the metal oxide contained in the second phase of the second phase increases obliquely toward the surface of the cerium oxide composite oxide fiber, and the inclination of the composition can clearly indicate the thickness of the confirmed region, preferably controlled from the surface layer. Open * $ ~ 鸠 please range 'but can also reach about 1/3 of the fiber diameter. Further, the "presence ratio" of the i-th phase and the second phase means that the metal oxide constituting the 帛1 phase and the metal oxide of the second phase are oxidized with respect to the metal oxide constituting the second phase and the metal constituting the second = The weight % of the whole material (i.e., the entire dioxin-cut composite oxide fiber). The flat non-woven fabric 21 composed of 7 cerium oxide-based composite oxide fibers can be obtained by the following production method. (Smelting and Visiting Wire Method) The water-oxygen-cut composite oxide fiber can be obtained by the following steps 1 to 4, and f ', P will have a main chain represented by the following 1: 11 200936510 Polycarbosilane having a skeleton and a number average molecular weight of 200 to 10000, a modified polycarbosilane modified with an organometallic compound, or a mixture of a denatured polycarbane and an organometallic compound, is subjected to 'melt spinning After the insolubilization treatment, it is fired in the air or in oxygen, whereby the cerium oxide-based composite oxide fiber can be produced.

RR

I —(Si-CH2^- R ❹ (其中,式中之R表示氫原子、低級烷基或苯基。) 第1步驟係製造作為用以製造二氧化矽基複合氧化物 纖維之起始原料使用且數量平均分子量為1〇〇〇〜5〇〇〇〇之變 性聚碳梦垸之步驟。變性聚碳矽烷之基本製造方法,與日 本專利特開昭56-741 26號公報極為類似,但需密切注意並 控制其中所記載之官能基之鍵結狀態。於以下概略說明。 起始原料之變性聚碳矽烷主要係由具有上述化i所表 ❹ 不之主鏈骨架且數量平均分子量為2〇〇〜1〇〇〇〇之聚碳矽 烧、與以通式M(0R,)n4 MR,’m(M為金屬元素,111與11為 大於1之整數)為基本構造之有機金屬化合物所衍生而來 者。 製造具有傾斜構造之二氧化矽基複合氧化物纖維時, 必須選擇僅該有機金屬4匕合物t一部分與聚碳妙垸形成鍵 結之緩慢的反應條件。因此,必須以28(rc以下(較佳為25〇 12 200936510 °c以下)之溫度’於惰性氣體中反應。於此反應條件下,有 機金屬化合物即使與聚碳矽烷反應,仍係以1官能性聚合 物鍵結(亦即鍵結為懸掛(pendant)狀),而不會引起大幅的分 子量增大。一部分鍵結有該有機金屬化合物之變性聚碳妙 烧於提昇聚碳石夕燒與有機金屬化合物之相溶性方面係扮演 重要的角色。 當鍵結2官能基以上之多個官能基時,可確認聚碳碎 烷之交聯構造之形成以及同時之分子量的顯著增大。於該 ® 情形時’於反應中會產生急遽的發熱與熔融黏度的上升。 另一方面’當於僅反應1官能基之下未反應之有機金屬化 合物殘存時,相反地可觀察到熔融黏度降低。 製造具有傾斜構造之二氧化矽基複合氧化物纖維時, 較佳係選擇蓄意使未反應之有機金屬化合物殘存之條件。 主要係使用未與上述變性聚碳梦烧反應之狀態的有機金屬 化合物或2〜3聚物程度之有機金屬化合物共存者作為起始 ◎ 原料,但即使僅變性聚碳矽烷,當含有極低分子量之變性 聚破石夕烧成分時’亦可同樣地作為起始原料使用。 於第2步驟中係將第丨步驟所得之變性聚碳矽烷、或 變性聚碳矽烷與低分子量之有機金屬化合物之混合物(以 下,亦稱為前驅物)加以熔融以製造紡絲原液,視情況將其 過濾以除去微凝膠、雜質等於紡絲時有害之物質,將其以 一般所使用之合成纖維紡絲用裝置進行紡絲。紡絲時之紡 絲原液之溫度係視原料之變性聚碳矽烷之軟化溫度而異, 但較佳為50〜200。(:之溫度範圍。於上述紡絲裝置,亦可視 13 200936510 需要於喷嘴下部言史置加渴加熱 喷嘴之喷出量與設置於紡絲、3。又,纖維徑可藉由改變 速度來調整。 下°卩之尚速捲繞裂置之捲繞 第2步驟除上述熔融紡 變性聚碳矽烷、或變性聚' _ ,係將第1步驟所得之 合物之混合物溶解於例如苯、二低77子量之有機金屬化 變性聚碳彳烧與低分子量 I —甲苯或其他可溶融 ...._ ^ 有機金屬化合物的溶劑來制拌 〇 .'慮乂除去微凝膠、雜質等於钫轉 時有害之物質,料紡_ %專於紡綠 原液以~般所使用之合 絲用裝置以乾式紡絲法進行 、、' 要之纖維。 、、4,控制捲繞速度而可得所 於該等紡絲步驟中,愛i吐 蒸要時可於紡絲裝置安裝紡轉 筒,將該筒内之環境氣氛作Λ l、+. 衣妨絲 衣見軋汛作成上述溶劑中之至少丨種 體之混合環境氣氛,或作成办翕 、 , 作成二氣、惰性氣體、熱空氣、熱 惰性氣體、蒸氣、氨氣、烴氣體 也札篮有機矽化合物氣體之環 境氣氛,藉此可控制紡絲筒中之纖維的固化。I - (Si-CH2^- R ❹ (wherein R represents a hydrogen atom, a lower alkyl group or a phenyl group.) The first step is the production of a raw material for producing a cerium oxide-based composite oxide fiber. A step of using a denatured polycarbamide having a number average molecular weight of 1 〇〇〇 to 5 Å. The basic method for producing a modified polycarbohydrane is very similar to that of Japanese Patent Laid-Open Publication No. SHO 56-741-26, but It is necessary to pay close attention to and control the bonding state of the functional groups described therein, which will be briefly described below. The denatured polycarbosilane of the starting material is mainly composed of the main chain skeleton having the above-mentioned formula i and having a number average molecular weight of 2 Polycarbonate of 〇〇~1〇〇〇〇, and organometallic compound with basic structure M (0R,) n4 MR, 'm (M is a metal element, 111 and 11 are integers greater than 1) In the case of producing a ceria-based composite oxide fiber having a slanted structure, it is necessary to select a reaction condition in which only a part of the organometallic 4 chelate t is bonded to the polycarbene. Therefore, it is necessary. 28 (rc or less (preferably 25〇12 20 The temperature of 0936510 °c or less is reacted in an inert gas. Under the reaction conditions, the organometallic compound is bonded by a monofunctional polymer even if it reacts with polycarbodecane (ie, the bond is a pendant). It does not cause a large increase in molecular weight. A part of the denatured polycarbon which is bonded to the organometallic compound plays an important role in enhancing the compatibility of the polycarbonate with the organometallic compound. When a plurality of functional groups having two or more functional groups are bonded, it is confirmed that the crosslinked structure of the polycarbane is formed and the molecular weight is significantly increased at the same time. In the case of the ®, an imminent heat and melt viscosity are generated in the reaction. On the other hand, when the unreacted organometallic compound remains under the reaction of only the 1-functional group, the decrease in the melt viscosity is observed conversely. When the ceria-based composite oxide fiber having a slanted structure is produced, The best condition is to use an organic metallization in a state in which the unreacted organometallic compound remains. The coexistence of the organometallic compound to the extent of the product or the 2 to 3 polymer is used as the starting material, but even if only the polycarbene is denatured, when it contains a very low molecular weight denatured polysulfide component, it can also be used as a starting point. In the second step, the denatured polycarbane obtained in the second step, or a mixture of the denatured polycarbosilane and the low molecular weight organometallic compound (hereinafter, also referred to as a precursor) is melted to produce a spinning dope. And filtering it to remove microgels, impurities are harmful substances during spinning, and spinning them by a spinning device for spinning fibers generally used. The temperature of the spinning dope at the time of spinning is based on the raw materials. The softening temperature of the denatured polycarbane varies, but is preferably 50 to 200. (: The temperature range. In the above-mentioned spinning device, it is also possible to use 13 200936510 to set the discharge amount of the thirst heating nozzle in the lower part of the nozzle. And set in spinning, 3. Also, the fiber diameter can be adjusted by changing the speed. The second step of the winding of the lower speed winding is carried out. In addition to the above melt-spun denatured polycarbane or the denatured poly', the mixture obtained in the first step is dissolved in, for example, benzene, two low 77. The amount of organometallic denatured polycarbocarbonic calcined with low molecular weight I-toluene or other meltable ...._ ^ solvent of organometallic compound to prepare mash. 'Thickness to remove microgel, impurities equal to twirling Harmful substance, material spinning _ %Specially used for the spinning of the green stock solution, the wire is used in the dry spinning method, and the fiber is required. And 4, controlling the winding speed, in the spinning step, when the steaming is required, the spinning drum can be installed in the spinning device, and the environmental atmosphere in the cylinder is Λ l, +. The silk garment can be seen as a mixed atmosphere of at least the sorghum in the above-mentioned solvent, or as a sputum, as a gas, an inert gas, a hot air, a hot inert gas, a vapor, an ammonia gas, a hydrocarbon gas, and the like. The ambient atmosphere of the organic hydrazine compound gas whereby the curing of the fibers in the spin pack can be controlled.

於第3步驟中,係將第2步驟所得之纺絲纖維,於氧 化環境氣氛中,於張力或無張力之作用下進行預加熱,並 進行上述紡絲纖維之不熔化。該步驟之目的在於使於下一 步驟之燒成時纖維不會熔融、且不與相鄰纖維接著為目的 而進行。處理溫度及處理時間係視組成^,並無特別限 定,但一般係選擇於50〜40(TC之範圍内、數小時〜3〇小時 之處理條件《於氧化環境氣氛中,亦可含有水分、氮氧化 物、臭氧等提高紡絲纖維之氧化力者,亦可主動地改變氧 200936510 分壓。 然而’依原料中所含之低分子量物之比例,紡絲纖維 之軟化溫度亦有低於5(TC的情形,於該情況時,重* ^ 爭先以較 上述處理溫度低之溫度施以促進纖維表面氧化之處理 又’吾人認為於該第2步驟及第3步驟之際,原料中所含 之低分子量物會朝纖維表面進行滲出(Bleed 〇ut),而形成所 要之傾斜組成之底層。In the third step, the spun fiber obtained in the second step is preheated under tension or no tension in an oxidizing atmosphere, and the spun fiber is infusible. The purpose of this step is to prevent the fibers from melting during the next step of firing and not for the purpose of subsequent fibers. The treatment temperature and the treatment time are not particularly limited, but are generally selected from the range of 50 to 40 (the range of TC, several hours to 3 hours), and may contain moisture in an oxidizing atmosphere. Nitrogen oxides, ozone, etc., which increase the oxidizing power of the spun fiber, can also actively change the partial pressure of oxygen 200936510. However, the softening temperature of the spun fiber is also lower than 5 according to the ratio of the low molecular weight contained in the raw material. (In the case of TC, in this case, it is important to apply the treatment for promoting the oxidation of the surface of the fiber at a temperature lower than the above-mentioned treatment temperature.] It is considered that the raw material is included in the second step and the third step. The low molecular weight material will bleed out toward the surface of the fiber to form the underlying layer of the desired tilt.

於第4步驟中,將經第3步驟不熔化處理後之纖維, 於張力或無張力下,以5〇〇〜18〇〇〇c之溫度範圍於氧化環境 氣氛進行燒成,而製得所要之二氧化矽基複合氧化物纖 維,其係由以二氧化矽成分為主體之氧化物相(第丨相)與含In the fourth step, the fiber which has not been melted after the third step is fired in an oxidizing atmosphere at a temperature of 5 〇〇 18 〇〇〇 于 under tension or no tension, and the desired fiber is obtained. The cerium oxide-based composite oxide fiber is composed of an oxide phase (second phase) mainly composed of a cerium oxide component and

Ti之金屬氧化物相(第2相)之複合氧化物相所構成,且構成 第2相之金屬氧化物之Ti存在比例朝表層傾斜地增大。於 該步驟中,不熔化纖維中所含之有機物成分基本上係被氧 化’,但依所選擇之條件,亦有於纖維中殘存碳或碳化物之 匱开/。於如此之狀態時,當不會阻礙所要之功能時可直接 使用’而若會造成阻礙時,可進—步施以氧化處理。此時, :須選擇不會對所要之傾斜組成及結晶構造造成問題之溫 度、處理時間。 :將f 4步驟所得之具光觸媒功能之二氧化矽基複合 作杰纖維作成短纖維後,進行針札(Needle Punch)等,而 作成平板狀不織布21。 (炼融吹襲紡絲㈨卟 又,就其他之製造方 blow)法) 法而言’二氧化矽基複合氧化物 15 200936510 =維所構成之平板狀不織布係使用炫融吹襲纺絲法,將該 月〗驅物熔融’將熔融物由紡絲喷嘴喷出,同時由紡絲喷嘴 周圍噴出加熱氮氣以進行纺絲’以配置於紡絲噴嘴之下部 之接受器捕捉纺絲纖維’藉此形成不織布’接著,將該不 織布不熔化處理後,於氧化環境氣氛中燒成,藉此可製造。 、糸喷嘴之直禮通常係使用瓜左右者。氮氣 速度為30〜30〇m/s左右,速度愈快可得愈細之纖維。 氮氣之加熱溫度只要可得所欲之紡絲纖維即並無特別 限制’但通常係喷出加熱至5〇〇。。左右之氮氣。以往,於一❽ 般=溶融吹襲纺絲法中’喷出氣體係使用空氣但於將上 遂前驅物纺絲時必須使用氣氣。藉由使用氣氣作為噴出氣 體’可更安定地進行紡絲。 _當於配置於紡絲喷嘴下部之接受器捕捉紡絲纖維之 際,較佳係使用可吸入之接受器,而由接受器之下側邊吸 入邊進行紡絲。藉由吸入’纖維可有效地缠繞,而得高強 不織布。吸入速度較佳為2〜l〇m/s左右之範圍。 、將所侍之不織布,藉由進行與上述熔融紡絲同樣的不❹ 溶化處理及燒成,可作成二氧化石夕基複合氧化物纖維之平 板狀不織布21«以上述熔融吹襲紡絲法所製造之二氧化矽 基複合氧化物纖維’若平均纖維徑為卜扣一較佳為Μ "m、更佳為2〜6 /z m),則可作成較熔融紡絲所製造之纖維 更細者。藉此,亦可增大纖維之表面積,而增大觸媒活性。 又,以熔融吹襲紡絲法所製造之平板狀不織布,與熔融紡 絲所製造之將長度40〜50mm左右之短纖維以針扎法作成之 16 200936510 不織布相比,纖維為更長者。其結果,不織布具 伸強度-以上),於加工成過滤器等之際,具 :: 撊加工性。 伯 平板狀不織布之重量或厚度並無特別限定,㈣㈣ 使用重量為50〜500g/m2、厚度較佳為〇 5〜2〇麵者。^ 可視需要藉由積層不織布來調整。當厚度較0.5mm薄時, =媒量過少而無法獲得充分之水的淨化效果。當較20mm ❿推::LI板狀不織布會成為阻抗,壓力損失增大,而難以 仃水處理。平板狀不織布之形狀並無特別限制,可配合 插入平板狀不織布之流動槽的形狀,作成圓形或方形為 了增大平板狀不織布之表面積,亦可作成波浪板狀。 藉由如上述之平板狀不織布21之製造方法,可 :無:維彼此之橋接(Bridging)且於一根一根纖維表面緻: 斤有二氧化鈦等光觸媒成分之構造之光觸媒纖維所構 成之平板^織布21。又,該光觸媒纖維並非以以往之塗 ❿佈方法所侍’故纖維表面之光觸媒成分沒有脫落的問題。 由該纖維所構成之平板狀不織布21為纖維—根一根 '、有疋程度之空隙分散的構造,故處理流體與光觸媒 之接觸面積變将_ &卷 變仔非常大。一般而言,為了充分誘發光觸媒 食匕必須提高光對光觸媒之照射效率和與處理流體之 接觸效率。 接著,使用圖式詳細說明本發明之水淨化裝置之第2 ^。L。圖3係第2實施型態之水淨化裝置之概念截面 2實施型態之水淨化裝置5〇,其之使所欲淨化之水 17 200936510 由左朝右流動、並具備使欲淨化之水循環之循環機構這兩 點係與第1實施型態不同。光觸職2G及紫外線燈3〇係 使用與第1實施型態相同者。 於第2實施型態之水淨化裝置5〇,流動槽52,於上方 具有開口,於下游側(圖3 t右側)之底面,形成有流出口 54。循環機構係形成為長的圓筒狀,其具備:於長邊方向 具有複數個成排形成之流人孔A之流人部56、蓄積流出口 ^所流出之水之循環槽58、連接成可使循環槽μ與流入 4 56之水流動之循環路# 6〇、與設置於循環路徑⑼與流❹ 入。卩56之間且使循環槽58之水通過循環路徑流動至流 入部56之泵p;並且 藉由將流入部56設置於流動槽52之上游側(圖3之左 側)’並將循環槽58設置於流出口 54之下方,可使欲淨化 之水由流動槽52内左側朝右侧流動,並可使流出之水透過 循環槽58、播環路徑6〇及流入部56回到流動槽52。 於第2實施型態之水淨化裝置5〇中,三個光觸媒匣 係並列設置成與流動槽52之流動方向垂直相交。於各光觸〇 媒匣20之間,2根紫外線照射燈3〇係配置成紫外線照射燈 3〇之長邊方向平行於平板狀不織布21之面。於流動槽52 之較最下游側較光觸媒g 2G再更下游側處,配置有2個不 同间度之擋板62,藉此可防止處理水一 口氣朝流出口 54流 入。 於第1實施型態及第2實施型態中,平板狀不織布21 較佳為使用上述者,但只要可使欲淨化之水通過且具光觸 18 200936510 媒功能者即可,可使用周知者,亦可使用二氧化^維或 一氧化鈦-二氧化矽纖維所構成之光觸媒纖維。例如可使用 曰本專利特開平u_347417號公報所記載者。 實施例 以下’說明本發明之水淨化裝置之實施例。 (製造例1) 首先’製造作為實施例所使用之平板狀不織布之二氧 化鈦/二氧化矽纖維。亦即,於5公升之三口燒瓶置入無水 甲苯2.5公升與金屬鈉400g,於氮氣氣流下加熱至甲苯之 沸點,以1小時滴入二甲基二氣矽烷丨公升。滴入結束後, 加熱回流10小時生成沉澱物。將該沉澱過濾,首先以曱醇 洗淨後,以水洗淨,製得白色粉末之聚二甲基矽烷42〇g。 將聚二曱基矽烷250g,裝填至具備水冷回流器之三口燒瓶 中’再於氮氣氣流下以420°C加熱反應30小時製得數量平 均分子量為1200之聚碳矽烷。The composite oxide phase of the metal oxide phase (second phase) of Ti is formed, and the Ti content ratio of the metal oxide constituting the second phase increases obliquely toward the surface layer. In this step, the organic component contained in the infusible fiber is substantially oxidized, but depending on the conditions selected, carbon or carbide remains in the fiber. In such a state, it can be used directly when it does not hinder the desired function, and if it is hindered, it can be further oxidized. At this time, you must select the temperature and processing time that will not cause problems for the desired tilt composition and crystal structure. After the photocatalyst-functional cerium oxide-based composite ytterbium-based fiber obtained as a short fiber is formed into a short fiber, a needle-shaped fabric (Needle Punch) or the like is formed to form a flat-shaped nonwoven fabric 21. (Smelting and blowing, spinning, and squeezing, and other methods, the method of blowing) The cerium oxide-based composite oxide 15 200936510 = the flat-shaped non-woven fabric composed of the ray-forming method Melting the melter's melter's melted from the spinning nozzle while spraying heated nitrogen gas around the spinning nozzle for spinning' to capture the spun fiber at the receptacle disposed below the spinning nozzle This forms a non-woven fabric. Then, the nonwoven fabric is not melted and then fired in an oxidizing atmosphere, whereby it can be produced. The direct gift of the nozzle is usually the use of melons. The nitrogen gas speed is about 30~30〇m/s, and the faster the speed, the finer the fiber. The heating temperature of nitrogen is not particularly limited as long as the desired spun fiber is obtained, but it is usually sprayed and heated to 5 Torr. . Nitrogen around. In the past, in the case of the melt-spray spinning method, the air is used in the gas-jet system, but the gas must be used when spinning the precursor. Spinning can be performed more stably by using gas as the gas to be ejected. _ When the receptacle disposed at the lower portion of the spinning nozzle captures the spun fiber, it is preferred to use a respirable receiver and to perform spinning by sucking the side under the receptacle. By inhaling the 'fibers' can be effectively entangled to obtain a high-strength nonwoven fabric. The suction speed is preferably in the range of about 2 to 1 〇 m/s. By performing the same non-woven treatment and baking as the above-described melt spinning, the non-woven fabric can be used as a flat-shaped nonwoven fabric 21 of the cerium oxide-based composite oxide fiber by the above-described melt-blowing spinning method. The produced cerium oxide-based composite oxide fiber 'when the average fiber diameter is preferably Μ "m, more preferably 2 to 6 /zm), it can be made into a fiber made by melt spinning. Fine. Thereby, the surface area of the fiber can also be increased to increase the catalytic activity. Further, the flat-shaped nonwoven fabric produced by the melt-blowing spinning method is made of a needle-made method of a short fiber having a length of about 40 to 50 mm which is produced by melt spinning, and the fiber is longer than the nonwoven fabric. As a result, the non-woven fabric has a tensile strength of -above), and when processed into a filter or the like, it has a :: 撊 processability. The weight or thickness of the flat non-woven fabric is not particularly limited. (4) (4) The weight is 50 to 500 g/m 2 , and the thickness is preferably 〇 5 to 2 〇. ^ Can be adjusted by layering non-woven as needed. When the thickness is thinner than 0.5 mm, the amount of the medium is too small to obtain a sufficient water purification effect. When it is 20mm ❿::LI plate-like non-woven fabric will become impedance, the pressure loss will increase, and it is difficult to handle the water. The shape of the flat non-woven fabric is not particularly limited, and it may be formed into a circular or square shape in accordance with the shape of a flow groove into which the flat non-woven fabric is inserted, or may be formed into a corrugated plate shape. According to the method for producing the flat-shaped nonwoven fabric 21 as described above, it is possible to: a bridge formed of photocatalyst fibers having a structure of a photocatalyst such as titanium dioxide, which is bridging and brittle with each other on the surface of one fiber; Weaving 21. Further, the photocatalyst fiber does not have the problem that the photocatalyst component of the fiber surface does not fall off by the conventional coating method. The flat non-woven fabric 21 composed of the fibers is a fiber-root one, and has a structure in which the voids are dispersed. Therefore, the contact area between the treatment fluid and the photocatalyst becomes very large. In general, in order to sufficiently induce photocatalyst chyme, it is necessary to increase the efficiency of light irradiation to the photocatalyst and the contact efficiency with the treatment fluid. Next, the second embodiment of the water purification apparatus of the present invention will be described in detail using the drawings. L. Fig. 3 is a conceptual view of a water purification device according to a second embodiment of the present invention. The water purification device 5 of the embodiment is configured to flow the water to be purified 17 200936510 from left to right and to circulate the water to be purified. The two points of the circulation mechanism are different from the first embodiment. The light touch 2G and the ultraviolet light 3 are the same as those in the first embodiment. In the water purifying apparatus 5 of the second embodiment, the flow cell 52 has an opening at the upper side, and an outflow port 54 is formed on the bottom surface of the downstream side (the right side of Fig. 3 t). The circulation mechanism is formed in a long cylindrical shape, and includes a flow person portion 56 having a plurality of flow holes A formed in a row in the longitudinal direction, and a circulation groove 58 for accumulating the water flowing out of the flow outlet The circulation path μ and the circulation path of the water flowing into the 4 56 can be made to flow into the circulation path (9). Between the crucibles 56, the water of the circulation tank 58 is caused to flow to the pump p of the inflow portion 56 through the circulation path; and the inflow portion 56 is disposed on the upstream side of the flow tank 52 (on the left side of FIG. 3) and the circulation groove 58 is provided. Provided below the outflow port 54, the water to be purified flows from the left side to the right side in the flow cell 52, and the outflowing water can be passed back to the flow cell 52 through the circulation groove 58, the sowing ring path 6 and the inflow portion 56. . In the water purification apparatus 5 of the second embodiment, three photocatalysts are arranged in parallel so as to intersect the flow direction of the flow cell 52 perpendicularly. Between each of the photocatalyst media 20, two ultraviolet irradiation lamps 3 are arranged such that the longitudinal direction of the ultraviolet irradiation lamp 3 is parallel to the surface of the flat non-woven fabric 21. On the more downstream side of the flow cell 52, two baffles 62 having different degrees are disposed on the downstream side of the photocatalyst g 2G, thereby preventing the treatment water from flowing into the outflow port 54. In the first embodiment and the second embodiment, the flat non-woven fabric 21 is preferably used as described above. However, as long as the water to be purified can pass through and has the function of light-touching 18 200936510, a well-known person can be used. Photocatalyst fibers composed of oxidized or titanium oxide-cerium oxide fibers may also be used. For example, the one described in Japanese Laid-Open Patent Publication No. H-347417 can be used. EXAMPLES Hereinafter, examples of the water purifying apparatus of the present invention will be described. (Production Example 1) First, a titanium dioxide/cerium oxide fiber which is a flat nonwoven fabric used in the examples was produced. Namely, 2.5 liters of anhydrous toluene and 400 g of metallic sodium were placed in a 5-liter three-necked flask, and heated to a boiling point of toluene under a nitrogen gas stream, and dimethyl dioxane 丨 liter was added dropwise over 1 hour. After the completion of the dropwise addition, the mixture was heated under reflux for 10 hours to form a precipitate. The precipitate was filtered, washed with decyl alcohol, and washed with water to obtain a white powder of polydimethyl decane (42 g). 250 g of polydioxyl decane was charged into a three-necked flask equipped with a water-cooled reflux apparatus, and further heated at 420 ° C for 30 hours under a nitrogen gas stream to obtain a polycarbane having an average molecular weight of 1,200.

於聚碳矽烧16g加入曱苯l〇〇g與四丁氧鈦64g,以ι〇〇 °C預加熱1小時後,緩慢昇溫至15(TC以將曱笨蒸餾除去, 以此狀態直接進行反應5小時,再昇溫至25(TC反應5小 時,合成變性聚碳矽烷。將該變性聚碳矽烷,為了主動使 低分子量之有機金屬化合物共存,係加入5g之四丁氧鈦, 而獲得變性聚碳矽烷與低分子量有機金屬化合物之混合 物。 將該變性聚碳矽烷與低分子量有機金屬化合物之混合 物溶解於甲苯後,裝填至玻璃製之紡絲裝置,將内部充分 19 200936510 以氮取代後,昇溫將甲苯蒸餾除去,再以} 8(rc進行熔融紡 絲。將紡絲纖維於空氣中、階段性地加熱至ΐ5〇Ό使其不熔 化後,於1200°c之空氣中進行燒成1小時,製得二氧化鈦/ 二氧化矽纖維。 (實施例1) 使用製造例1所得之二氧化鈦/二氧化矽纖維,作成圖 2所不之含平板狀不織布之光觸媒匣,設置於圖丨所示之水 淨化裝置。所使用之紫外線燈係三共電氣製G]L16KZF(輸 出.15 W)’外殼構件係使用合成石英。輸出為15W,該紫 外線燈係使用4根。紫外線燈之波長係發射254nnl與丨85nm 兩者。紫外線燈與光觸媒匣之距離定為5〇mm,平板狀不織 布表面之平均紫外線強度為2mW/cm2 ^紫外線強度係使用 TOPCON公司製之UVR-2紫外線照度計測定,由平板狀不 織布表面之中央部起至端部測定9個部位,將其之平均值 視為平均紫外線強度。處理水方面,係將IpA(異丙醇)溶解 於超純水作成l〇ppm之IPA水溶液。該IPA水溶液之 TOC(總有機碳)為6ppm。 將IPA水溶液15L以5L/min之流量使用該水淨化裝置 進行2小時循環處理。測定循環處理後之水的TOC,結果 為0 · 1 ppm以下。調查被處理水之組成’結果未檢出ip A, 僅檢測出些微之IPA之氧化分解物即乙酸及甲酸。由該結 果可知’該水淨化裝置可充分活用紫外線之有機物分解能 力’且可附加光觸媒所致之有機物分解效果。 (比較例1) 200936510 紫外線燈係使用三共電氣製GL16KSH(輸出:15W)、 外殼構件係無臭氧石英之僅發射254nm之光者,除此之外, 製作全部與實施例1相同之淨化裝置。與實施例1同樣地, 將IPA(異丙醇)溶解於超純水,調整為lOppm之IPA水溶 液。該IPA水溶液之TOC(總有機碳)為6ppm。 將IPA水溶液1 5L以5L/min之流量進行2小時循環處 理。測定循環處理後之水的TOC,結果為3.5ppm。調查被 處理水之組成,結果殘存大部分(80%)之IPA,並檢測出些 〇 微之IPA之氧化分解物即乙酸及甲酸。與實施例1之情形 相比,分解效率低之原因可推測為不具1 85nm之光所致之 有機物分解效果。 (比較例2) 除未安裝光觸媒匣之外,製作全部與實施例1相同之 淨化裝置。與實施例1同樣地,將IPA(異丙醇)溶解於超純 水調整為lOppm之IPA水溶液。該IPA水溶液之TOC(總有 機碳)為6ppm。 ® 將IPA水溶液1 5L以5L/min之流量進行2小時循環處 理。測定循環處理後之水的TOC,結果為2.5ppm。調查被 處理水之組成的結果,殘存有機物之總量皆以IPA的形式 殘存,未檢測出IPA之氧化分解物即乙酸及曱酸。與實施 例1之情形相比,分解效率低之原因可推測為不具光觸媒 所具之分解效果。 (比較例3) 使用製造例1所得之二氧化鈦/二氧化矽纖維,製作曰 21 200936510 本專利第3436267之圖: 之圖2所記裁之淨化裝置,冑成形為圓16 g of fluorene xylene and 64 g of titanium tetrabutoxide were added to 16 g of polycarbocarbonate, and preheated at ι ° C for 1 hour, and then slowly heated to 15 (TC to distill off the hydrazine, and directly proceeded in this state. The reaction was carried out for 5 hours, and the temperature was further raised to 25 (TC reaction for 5 hours to synthesize a denatured polycarbane. The denatured polycarbane was used to actively coexist a low molecular weight organometallic compound, and 5 g of tetrabutoxytitanium was added to obtain denaturation. a mixture of a polycarbodecane and a low molecular weight organometallic compound. The mixture of the denatured polycarbosilane and the low molecular weight organometallic compound is dissolved in toluene, and then charged into a spinning device made of glass, and the inside is fully replaced by nitrogen. The temperature was increased, and the toluene was distilled off and then melt-spun at 8 (rc). The spun fiber was heated in the air to a temperature of 5 Torr to be melted, and then fired in air at 1200 ° C. In the hour, the titanium dioxide/cerium dioxide fiber was obtained. (Example 1) Using the titanium dioxide/cerium oxide fiber obtained in Production Example 1, a photocatalyst containing a flat non-woven fabric as shown in Fig. 2 was prepared and placed in the figure. The water purification device shown in the figure. The ultraviolet lamp used is G]L16KZF (output .15 W). The outer casing member is made of synthetic quartz. The output is 15W, and the ultraviolet lamp is used in four. The wavelength of the ultraviolet lamp is emitted. 254nnl and 丨85nm. The distance between the UV lamp and the photocatalyst is 5〇mm, and the average UV intensity of the flat non-woven surface is 2mW/cm2. ^The UV intensity is measured by the UVR-2 ultraviolet illuminometer manufactured by TOPCON. Nine parts were measured from the center of the flat non-woven surface to the end, and the average value was regarded as the average ultraviolet intensity. In terms of treated water, IpA (isopropyl alcohol) was dissolved in ultrapure water to make IPA of 1 〇 ppm. The aqueous solution of the IPA aqueous solution had a TOC (total organic carbon) of 6 ppm. 15 L of the IPA aqueous solution was subjected to a circulation treatment at a flow rate of 5 L/min for 2 hours using the water purification apparatus. The TOC of the water after the circulation treatment was measured, and the result was 0 · 1 Below ppm, the composition of the treated water was investigated. The result was that ip A was not detected, and only the oxidative decomposition products of IPA, namely acetic acid and formic acid, were detected. From this result, it can be seen that the water purification device can be fully lived. The organic matter decomposition ability of ultraviolet light can be added and the organic matter decomposition effect by photocatalyst can be added. (Comparative Example 1) 200936510 Ultraviolet lamp system uses GL16KSH (output: 15W) manufactured by Sankyo Electric Co., Ltd., and the outer casing member is ozone-free quartz which emits only 254 nm light. In the same manner as in Example 1, except that the IPA (isopropyl alcohol) was dissolved in ultrapure water and adjusted to 10 ppm of an IPA aqueous solution, the TOC of the IPA aqueous solution was prepared. The total organic carbon was 6 ppm. 15 L of the IPA aqueous solution was subjected to a circulation treatment at a flow rate of 5 L/min for 2 hours. The TOC of the water after the circulation treatment was measured and found to be 3.5 ppm. The composition of the treated water was investigated, and as a result, most (80%) of the IPA remained, and some oxidized decomposition products of IPA, namely acetic acid and formic acid, were detected. The reason why the decomposition efficiency is low as compared with the case of the first embodiment is presumed to be an organic decomposition effect by light having no light of 185 nm. (Comparative Example 2) A purification apparatus similar to that of Example 1 was produced except that the photocatalyst was not mounted. In the same manner as in Example 1, IPA (isopropyl alcohol) was dissolved in an IPA aqueous solution adjusted to 10 ppm of ultrapure water. The TOC (total organic carbon) of the IPA aqueous solution was 6 ppm. ® 15 L of IPA aqueous solution was circulated at a flow rate of 5 L/min for 2 hours. The TOC of the water after the circulation treatment was measured and found to be 2.5 ppm. As a result of investigating the composition of the treated water, the total amount of residual organic matter remained in the form of IPA, and acetic acid and citric acid which are oxidative decomposition products of IPA were not detected. The reason why the decomposition efficiency is low as compared with the case of the first embodiment is presumed to be that there is no decomposition effect of the photocatalyst. (Comparative Example 3) Using the titanium dioxide/cerium dioxide fiber obtained in Production Example 1, a crucible was produced. 21 200936510 Patent No. 3436267: A purification apparatus as shown in Fig. 2, which is formed into a circle

測定,由E内側面(紫外線燈面)之下部起至上部為止測定9 個部位,將其之平均值視為平均紫外線強度。與實施例丨 ◎ 同樣地,將IPA(異丙醇)溶解於超純水調整為1〇ppm之IpA 水溶液。該IPA水溶液之TOC(總有機碳)為6ppm。 將IPA水溶液15L以5L/min之流量進行2小時循環處. 理。測定循環處理後之水的TOC,結果為2.0ppm。調查被 處理水之組成’結果殘存大部分(85%)之IPA,並檢測出些 微之IPA之氧化分解物即乙酸及甲酸。與實施例丨之情形 相比’分解效率低之原因可推測為雖然於本淨化裝置可充 分獲得光觸媒之分解能力’但由於圓錐台狀之光觸媒匣遮 〇 蔽紫外線,故紫外線所致之有機物分解能力降低。因此, 僅於日本專利第3436267所記載之淨化裝置組裝具有 254nm與185nm兩波長之紫外線燈,無法獲得足夠之淨化 效率。 (比較例4) 除紫外線燈係僅發射254nm之光者以外,製作與比較 例3相同之淨化裝置。與實施例1同樣地,將Ipa(異丙醇) 22 200936510 溶解於超純水調整為1 Oppm之IP A水溶液。該IP A水溶液 之TOC(總有機碳)為6ppm。 將IPA水溶液1 5L以5L/min之流量進行2小時循環處 理。測定循環處理後之水的TOC,結果為2.5ppm。調查被 處理水之組成,結果殘存大部分(85%)之IPA,並檢測出些 微之IP A之氧化分解物即乙酸及曱酸。與比較例3之相比, 分解效率雖些許降低但沒有很大之差別。因此,可知於比 較例3之裝置無法有效利用1 85nm之光。 © (實施例2〜8) 將紫外線燈與光觸媒匣之距離調整為表 1所示之距 離,使不織布表面之平均紫外線強度為0.5〜15mW/cm2,除 此之外,進行與實施例1相同之循環處理及測定。光觸媒 匣表面之平均紫外線強度與循環處理後之TOC之結果係示 於表1。可知隨光觸媒表面之紫外線強度,IPA分解效果有 很大的差異。亦即,當紫外線強度小時,無法充分發揮光 觸媒之分解效果,且若為了提高紫外線強度而使紫外線燈 ® 與光觸媒匣間之距離過小,則由於紫外線受到光觸媒匣所 遮蔽,故紫外線所致之有機物分解能力降低。 表1 平均紫外線強度 紫外線燈與不織布之距離 循環處理後之TOC (mW/cm2) (mm) (PPm) 實施例2 0.5 80 2.2 實施例3 1 70 0.2 實施例4 2 50 <0.1 實施例5 5 40 <0.1 實施例6 8 30 <0.1 23 200936510 實施例7 10 20 0.3 實施例8 15 10 1.2 (實施例9) 使用製造例1所得之二氧化鈦/二氧化矽纖維,作成圖 2所示之含平板狀不織布之光觸媒匣,並設置於圖3所示之 水淨化裝置。所使用之紫外線燈係三共電氣製GL16KZL(輸 出:15 W) ’外殼構件係使用合成石英。輸出為丨5W,該紫 外線燈係使用4根。务外線燈之波長係發射254n'm與1 85nm 兩者。紫外線燈與光觸媒]£之距離.為5 〇 mm,平板狀不織布 表面之平均紫外線強度為2mW/cm2。紫外線強度係使用 ® TOPCON公司製之UVR-2紫外線照度計測定,由平板狀不 織布表面之中央部起至端部測定9個部位,將其之平均值 視為平均紫外線強度。處理水方面,係將ιρA(異丙醇)溶解 於超純水作成l〇ppm之IPA水溶液。該IPA水溶液之 TOC(總有機碳)為6ppm。 將IPA水溶液15L以5L/min之流量使用該水淨化裝置 進行2小時循環處理。測定循環處理後之水的t〇c,結果 為O.lppm以下。調查被處理水之組成,結果未檢出lpA, 〇 僅檢測出些微之IPA之氧化分解物即乙酸及甲酸。由該結 果可知’該水淨化裝置可充分活用紫外線之有機物分解能 力’且可附加光觸媒所致之有機物分解效果。 【圖式簡單說明】 圖1 ’係第1實施型態之水淨化裝置之概念立體圖。 圖2’係光觸媒匣之擴大圖。 圖3 ’係第2實施型態之水淨化裝置之概念截面圖。 24 200936510 【主要元件符號說明】 10、50 水淨化裝置 11、52 流動槽 20 光觸媒匣 21 平板狀不織布 22 網 30 紫外線燈 41 流入口 42、54 流出口 56 流入部 58 循環槽 60 循環路徑 62 檔板 25In the measurement, nine points were measured from the lower portion of the inner side surface (UV surface) to the upper portion, and the average value thereof was regarded as the average ultraviolet light intensity. In the same manner as in Example ◎, IPA (isopropyl alcohol) was dissolved in an IpA aqueous solution adjusted to 1 〇 ppm of ultrapure water. The TOC (total organic carbon) of the IPA aqueous solution was 6 ppm. 15 L of the IPA aqueous solution was circulated at a flow rate of 5 L/min for 2 hours. The TOC of the water after the circulation treatment was measured and found to be 2.0 ppm. The majority of the (85%) IPA remained in the results of the investigation of the composition of the treated water, and some of the oxidative decomposition products of IPA, namely acetic acid and formic acid, were detected. Compared with the case of the embodiment, the reason why the decomposition efficiency is low is presumed to be that the decomposition ability of the photocatalyst can be sufficiently obtained in the purification device, but the organic matter decomposition by the ultraviolet ray is blocked by the truncated cone-shaped photocatalyst. Reduced ability. Therefore, an ultraviolet lamp having two wavelengths of 254 nm and 185 nm is assembled only in the purification apparatus described in Japanese Patent No. 3,436,267, and sufficient purification efficiency cannot be obtained. (Comparative Example 4) A purification apparatus similar to that of Comparative Example 3 was produced except that the ultraviolet light was only emitted at 254 nm. In the same manner as in Example 1, Ipa (isopropyl alcohol) 22 200936510 was dissolved in an IP A aqueous solution adjusted to 10 ppm of ultrapure water. The TOC (total organic carbon) of this IP A aqueous solution was 6 ppm. 15 L of the IPA aqueous solution was subjected to a circulation treatment at a flow rate of 5 L/min for 2 hours. The TOC of the water after the circulation treatment was measured and found to be 2.5 ppm. The composition of the treated water was investigated, and as a result, most (85%) of the IPA remained, and some of the oxidative decomposition products of IP A, namely acetic acid and citric acid, were detected. Compared with Comparative Example 3, the decomposition efficiency was somewhat reduced but not greatly different. Therefore, it can be seen that the device of Comparative Example 3 cannot effectively utilize light of 185 nm. (Examples 2 to 8) The same as in Example 1, except that the distance between the ultraviolet lamp and the photocatalyst was adjusted to the distance shown in Table 1, and the average ultraviolet light intensity of the surface of the nonwoven fabric was 0.5 to 15 mW/cm 2 . Cycling and measurement. The results of the average UV intensity of the photocatalyst surface and the TOC after the cycle treatment are shown in Table 1. It can be seen that with the ultraviolet intensity of the photocatalyst surface, the IPA decomposition effect is greatly different. That is, when the ultraviolet ray intensity is small, the decomposition effect of the photocatalyst cannot be sufficiently exerted, and if the distance between the ultraviolet ray lamp® and the photocatalyst enthalpy is too small in order to increase the ultraviolet ray intensity, since the ultraviolet ray is blocked by the photocatalyst enthalpy, the organic substance due to the ultraviolet ray is The decomposition ability is reduced. Table 1 Average UV Intensity UV Lamp and Non-woven Fabric Distance TOC (mW/cm2) (mm) (PPm) Example 2 0.5 80 2.2 Example 3 1 70 0.2 Example 4 2 50 <0.1 Example 5 5 40 < 0.1 Example 6 8 30 < 0.1 23 200936510 Example 7 10 20 0.3 Example 8 15 10 1.2 (Example 9) The titanium dioxide/cerium oxide fiber obtained in Production Example 1 was used to prepare as shown in Fig. 2 The photocatalyst having a flat non-woven fabric is provided in the water purifying device shown in FIG. The ultraviolet lamp used was a GL16KZL manufactured by Sankyo Electric Co., Ltd. (output: 15 W). The outer casing member was made of synthetic quartz. The output is 丨5W, and the UV lamp system uses 4 pieces. The wavelength of the external line lamp emits both 254n'm and 1 85nm. The distance between the UV lamp and the photocatalyst is £5 mm, and the average UV intensity of the flat non-woven surface is 2 mW/cm2. The ultraviolet ray intensity was measured using a UVR-2 ultraviolet illuminometer manufactured by TOPCON Co., Ltd., and nine points were measured from the center portion to the end portion of the flat nonwoven fabric surface, and the average value thereof was regarded as the average ultraviolet ray intensity. For the treatment of water, ιρA (isopropanol) was dissolved in ultrapure water to make an IPA aqueous solution of 1 〇 ppm. The TOC (total organic carbon) of the IPA aqueous solution was 6 ppm. 15 L of the IPA aqueous solution was subjected to a circulation treatment for 2 hours using the water purification apparatus at a flow rate of 5 L/min. The t〇c of the water after the circulation treatment was measured, and the result was 0.1 ppm or less. The composition of the treated water was investigated, and as a result, lpA was not detected, and only a small amount of IPA oxidative decomposition products, namely acetic acid and formic acid, were detected. From this result, it is known that the water purification device can fully utilize the organic matter decomposition ability of ultraviolet rays and can add an organic substance decomposition effect by a photocatalyst. BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is a conceptual perspective view of a water purification apparatus of a first embodiment. Figure 2' is an enlarged view of the photocatalyst. Fig. 3 is a conceptual cross-sectional view showing a water purification apparatus of a second embodiment. 24 200936510 [Description of main components] 10, 50 Water purification equipment 11, 52 Flow cell 20 Photocatalyst 匣 21 Flat non-woven fabric 22 Net 30 Ultraviolet light 41 Inlet 42, 54 Outlet 56 Inflow 58 Circulation groove 60 Circulation path 62 Board 25

Claims (1)

200936510 十、申請專利範圍: 1 · 一種水淨化裝置,其係具備: 使欲淨化之水朝一方向流動之流動槽、設置於該流動 槽内且可使該欲淨化之水通過之至少一個以上之由具光觸 媒功能之纖維所構成的平板狀不織布、與將紫外線照射於 該平板狀不織布之紫外線照射手段;其特徵在於: 該紫外線照射手段,其構成係具有朝長邊方向延長之 形狀,可照射於l80〜190nm與250〜260nm具有峰值波長 (peakwavelength)之紫外線,且設置成其長邊方向與該平板 狀不織布呈平行。 ❹ 2如申請專利範圍第1項之水淨化裝置,其中,該具 光觸媒功能之纖維係由以二氧化矽成分為主體之氧化物相 (第1相)與含Ti之金屬氧化物相(第2相)之複合氧化物之纖 維所構成之二氧化矽基複合氧化物纖維,而其中構成第2 相之金屬氧化物之Ti的存在比例係朝纖維表層傾斜地增 3.如申請專利範圍第1或2項之水淨化裝置其中, 該平板狀不織布表面之平均紫外線強度為1〜lOmW/cm2。 4_如申請專利範圍第1或2項之水淨化裝置,其中, 該平板狀不織布之面係配置成相對於該流動方向垂直或斜 向相交。 配 5·如申請專利範圍第1或2項之水淨化裝置,其中 該平板狀不織布係配置二個以上,該紫外線照射手段係 置於該平板狀不織布之間。 、 26 200936510 如申π專利範圍第j或2項之水淨化裝置,其中, 該紫外線照射手段係可照射出於⑻咖與Mm具有峰值 波長之紫外線之紫外線燈。 種尺淨化方法,其特徵在⑨ϋ淨化之水於流 通過由具光觸媒功能之纖維所構成的平板狀不織 布而由具有朝長邊方向延長之形狀且設置成該長邊方向 與該平板狀不織布呈平行之紫外線照射手&,對該平板狀 不織布照射於i 8G〜,m與25Q〜26Qnm具有峰值波長之紫 外線。 8.如申請專利範圍第7項之水淨化方法纟中,該具 光觸媒功能之纖維係由以二氧化石夕成分為主體之氧化物相 1相)與含T!之金屬氧化物相(第2相)之複合氧化物之纖 維所構成之二氧化梦基複合氧化物纖維,而其中構成第2 相之金屬氧化物之Ti的存在比例係朝纖維表層傾斜地增 大0 Ο 使中請專利範圍第7或8項之水淨化方法,其係以 織布表面之平均紫外線強度為1〜 的方式照射該紫外線。 1〇·如申請專利範圍第7或8項之水淨化方法,其你 該欲淨化之氽知二 々古具係使 义’朝相對於該平板狀不織布之 之方向流動。 蛋1或斜向 十一、囷式: 如次頁 27200936510 X. Patent application scope: 1 . A water purification device comprising: a flow tank for flowing water to be purified in one direction, at least one of which is disposed in the flow tank and allows the water to be purified to pass through A flat-plate non-woven fabric comprising a photocatalytic fiber and an ultraviolet ray irradiation means for irradiating ultraviolet ray on the flat woven fabric; wherein the ultraviolet ray irradiation means has a shape extending in a longitudinal direction and is illuminable Ultraviolet rays having a peak wavelength of from 180 to 190 nm and from 250 to 260 nm are disposed such that their longitudinal directions are parallel to the flat non-woven fabric. ❹ 2 The water purifying device according to claim 1, wherein the photocatalytic fiber is composed of an oxide phase (first phase) mainly composed of a cerium oxide component and a metal oxide phase containing Ti (first) a cerium oxide-based composite oxide fiber composed of a composite oxide of 2 phases), wherein the ratio of the presence of Ti constituting the metal oxide of the second phase is increased obliquely toward the surface layer of the fiber. Or the water purification device of the two items, wherein the surface of the flat non-woven fabric has an average ultraviolet light intensity of 1 to 10 mW/cm2. The water purification apparatus according to claim 1 or 2, wherein the flat non-woven fabric surface is arranged to intersect perpendicularly or obliquely with respect to the flow direction. 5. The water purifying apparatus according to claim 1 or 2, wherein the flat non-woven fabric is disposed in two or more, and the ultraviolet ray irradiation means is disposed between the flat non-woven fabrics. The water purifying device of the jth or the second aspect of the invention, wherein the ultraviolet ray irradiation means is an ultraviolet lamp which can illuminate ultraviolet rays having a peak wavelength of (8) coffee and Mm. A method for purifying a ruler, characterized in that the water of 9 ϋ purified water flows through a flat non-woven fabric composed of fibers having a photocatalytic function, and has a shape elongated in a longitudinal direction and is disposed such that the longitudinal direction is opposite to the flat non-woven fabric The parallel ultraviolet irradiation hand & irradiated the flat non-woven fabric with ultraviolet rays having a peak wavelength of i 8G 〜m and 25Q 〜26Qnm. 8. In the water purification method according to item 7 of the patent application, the photocatalyst-functional fiber is composed of a phase of an oxide phase mainly composed of a cerium oxide component and a metal oxide phase containing T! a oxidized dream-based composite oxide fiber composed of a composite oxide of 2 phases), wherein the ratio of the presence of Ti constituting the metal oxide of the second phase increases obliquely toward the surface layer of the fiber. The water purification method according to Item 7 or 8, wherein the ultraviolet ray is irradiated so that the average ultraviolet ray intensity of the surface of the woven fabric is 1 〜. 1〇·If you apply for the water purification method in Section 7 or 8 of the patent application, you should use the 氽 二 々 々 々 ’ 流动 流动 流动 流动 朝 朝 朝 朝 朝 朝 朝 朝 朝 朝 朝 。 。 。 。 。 。 。 。 。 。 。 。 。 。 。 Egg 1 or oblique XI, 囷: as the next page 27
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