JPH04141294A - Water and wastewater photochemical treating method - Google Patents
Water and wastewater photochemical treating methodInfo
- Publication number
- JPH04141294A JPH04141294A JP26389990A JP26389990A JPH04141294A JP H04141294 A JPH04141294 A JP H04141294A JP 26389990 A JP26389990 A JP 26389990A JP 26389990 A JP26389990 A JP 26389990A JP H04141294 A JPH04141294 A JP H04141294A
- Authority
- JP
- Japan
- Prior art keywords
- water
- treated
- treatment tank
- ultraviolet
- fine particles
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
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- Physical Water Treatments (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
この発明は、二酸化チタンなどの半導体微粒子を触媒と
した簡便な用廃水の光学的処理法に関するものであり、
例えばトリクロロエチレン、トリクロロエタン、シアン
イオン、重クロム酸イオン、難分解ハロゲン有機化合物
、BOD、TOC等の処理に適する方法に関する。[Detailed Description of the Invention] (Industrial Application Field) This invention relates to a simple optical treatment method for industrial wastewater using semiconductor fine particles such as titanium dioxide as a catalyst.
For example, the present invention relates to a method suitable for treating trichloroethylene, trichloroethane, cyanide ions, dichromate ions, hard-to-decompose halogen organic compounds, BOD, TOC, and the like.
(従来の技術)
用水等の殺菌には従来塩素などの薬品処理が行なわれて
きたが、薬品による殺菌処理は人体への影響から手控え
られる傾向にある。(Prior Art) Conventionally, chemical treatments such as chlorine have been used to sterilize water, but there is a tendency for chemical sterilization treatments to be refrained from due to their effects on the human body.
これに対して、紫外線を利用した被処理水の殺菌は、薬
品殺菌法と異なり、人体への影響が殆どなく効果的に殺
菌処理ができるなどの特性があり、種々の生産分野に応
用され、需要は増大されつつある。On the other hand, unlike chemical sterilization methods, sterilization of water to be treated using ultraviolet rays has the characteristics of being able to sterilize effectively with almost no effect on the human body, and has been applied to various production fields. Demand is increasing.
この紫外線を利用した殺菌法として最も効果が良いとさ
れるのは、外周を保護管で被覆した紫外線ランプを両端
を開放した処理タンク内に挿入するとともに、処理タン
クの両端には被処理水の給木管乃至排水管に接続するよ
うにした紫外線殺菌装置を使用して、被処理水が紫外線
ランプの周囲を通過する間に殺菌を行なう方法があるが
、この紫外線ランプの照射のみによる方法は殺菌分野の
みに有効である。The most effective sterilization method using ultraviolet light is to insert an ultraviolet lamp whose outer periphery is covered with a protective tube into a treatment tank with both ends open. There is a method of sterilizing the water to be treated while it passes around the UV lamp using an ultraviolet sterilizer connected to the feed pipe or drain pipe, but this method using only irradiation with the UV lamp does not sterilize the water. Valid only in the field.
一方、紫外線乃至可視光に照射による用廃水の処理を二
酸化チタン等の半導体微粒子の存在下で行なうと、殺菌
効果の他に、トリクロロエチレン、トリクロロエタン、
シアンイオン、重クロム酸イオン、難分解ハロゲン有機
化合物、BOD、TOC等の分解処理に効果があること
が開示されている(特開平1−94998号)。On the other hand, when wastewater is treated by irradiation with ultraviolet or visible light in the presence of semiconductor fine particles such as titanium dioxide, in addition to the sterilizing effect, trichlorethylene, trichloroethane,
It has been disclosed that it is effective in decomposing cyanide ions, dichromate ions, difficult-to-decompose halogen organic compounds, BOD, TOC, etc. (Japanese Patent Laid-Open No. 1-94998).
(発明が解決しようとする問題点)
この方法は、処理水の中に半導体微粒子を懸濁せしめ、
紫外線乃至可視光を照射することによって、酸化チタン
の価電子帯の電子伝導帯によって強力な酸化力を励起さ
せてトリクロロエチレン等の分解処理を行なうものであ
るが、然し処理水に懸濁した酸化チタン等の半導体微粒
子は処理水と同時に、放流又は使用することができない
ため、反応槽排出後、水と分離して再利用することに大
きなコストを必要とし、またそのまま排出する場合には
二次公害の問題を躍起する。(Problems to be solved by the invention) This method suspends semiconductor fine particles in treated water,
By irradiating it with ultraviolet or visible light, the electron conduction band of the valence band of titanium oxide excites strong oxidizing power to decompose trichlorethylene, etc. However, titanium oxide suspended in treated water Semiconductor fine particles such as these cannot be discharged or used at the same time as the treated water, so it is costly to separate them from the water after they are discharged from the reaction tank and reuse them, and if they are discharged as is, they may cause secondary pollution. to solve the problem.
半導体微粒子と水の分離方法としてはUF高分子膜中に
固定し、逆浸透法で分離する方法が提案されている。As a method for separating semiconductor fine particles from water, a method has been proposed in which they are fixed in a UF polymer membrane and separated by reverse osmosis.
しかしながら2半導体微粒子をOF高分子膜乃至高分子
フィルターで分離する方法では、半導体微粒子と被処理
水である用廃水との平均した接触が十分でなく、したが
って十分な効果を挙げることができない。However, in the method of separating two semiconductor fine particles using an OF polymer membrane or a polymer filter, the average contact between the semiconductor fine particles and the industrial wastewater, which is the water to be treated, is insufficient, and therefore sufficient effects cannot be achieved.
また、半導体微粒子を用廃水中に懸濁させる方法につい
ては、用廃水と半導体微粒子との十分な接触を行なわせ
ることができるが、処理後の水中から半導体微粒子を分
離、回収するのが極めて困難であり、またこれら二酸化
チタン微粒子を完全に分離、回収するには大型の分il
i装置を必要とするなどの難点がある。In addition, the method of suspending semiconductor particles in industrial wastewater allows sufficient contact between the industrial wastewater and the semiconductor particles, but it is extremely difficult to separate and recover the semiconductor particles from the treated water. Moreover, in order to completely separate and recover these titanium dioxide fine particles, a large-scale separation vessel is required.
There are disadvantages such as the need for an i-device.
これに対して、本願発明者は先に限外濾過膜を使用して
二酸化チタン等の微粒子を分離、回収する方法を提案し
た(特願平1−118581号)、シかしこの方法にお
いても装置外に限外濾過膜による分1m装置を設ける必
要かあり、装置が大型化することを避けることができず
、しかも二酸化チタン等の分離、回収など煩雑な作業を
必要とする。In response to this, the inventor of the present application previously proposed a method of separating and recovering fine particles such as titanium dioxide using an ultrafiltration membrane (Japanese Patent Application No. 1-118581). It is necessary to install a 1m minute device using an ultrafiltration membrane outside, which inevitably increases the size of the device, and requires complicated work such as separation and recovery of titanium dioxide and the like.
(問題点を解決するための手段)
この発明は、上記実情に鑑み、その表面に紫外線及び可
視光に応答する半導体微粒子を付着させたファイバーの
束を処理槽内に挿入し、該処理槽内に紫外線乃至太陽光
線をを照射して処理槽内の被処理水を処理することを特
徴とする光化学的用廃水の処理方法を提案するものであ
る。(Means for Solving the Problems) In view of the above-mentioned circumstances, the present invention has been proposed by inserting into a processing tank a bundle of fibers to which fine semiconductor particles that respond to ultraviolet rays and visible light are attached to the surface of the fibers. The present invention proposes a photochemical wastewater treatment method characterized by treating water to be treated in a treatment tank by irradiating it with ultraviolet rays or sunlight.
ここで、ファイバーとしては金属製、プラスチック製、
石英ガラス製、フッ素樹脂製のファイバーを使用するこ
とができ、特に光グラスファイバーの使用が好ましい。Here, the fibers are metal, plastic,
Fibers made of quartz glass or fluororesin can be used, and optical glass fibers are particularly preferred.
ここで、半導体としては、二酸化チタンの他に、三酸化
タングステン、酸化亜鉛等を使用することができ、特に
白金に担持させた二酸化チタンが効果的である。Here, as the semiconductor, in addition to titanium dioxide, tungsten trioxide, zinc oxide, etc. can be used, and titanium dioxide supported on platinum is particularly effective.
これら半導体微粒子をファイバーの表面に付着させる接
着剤としては、例えば紫外線硬化性樹脂を使用すること
ができる。As the adhesive for attaching these semiconductor fine particles to the surface of the fiber, for example, an ultraviolet curing resin can be used.
また、ここで使用する紫外線としては半導体が二酸化チ
タンである場合には、 413nmより短波長の光線、
好ましくは365n++以下の光線を用いる必要があり
、半導体として二酸化タングステンを用いる場合には、
459nmより短波長の光線を用いる必要がある。この
ような光源としては中圧乃至高圧水銀灯、キセノンラン
プ、ハロゲンランプ等を使用することができる。In addition, the ultraviolet rays used here have a wavelength shorter than 413 nm when the semiconductor is titanium dioxide,
Preferably, it is necessary to use a light beam of 365n++ or less, and when using tungsten dioxide as the semiconductor,
It is necessary to use a light beam with a wavelength shorter than 459 nm. As such a light source, a medium pressure to high pressure mercury lamp, a xenon lamp, a halogen lamp, etc. can be used.
紫外線は、処理槽の外部に紫外線ランプを置いて照射し
てもよく、また処理槽内に紫外線ランプを挿入してこれ
より照射せしめてもよい。The ultraviolet rays may be irradiated by placing an ultraviolet lamp outside the processing tank, or by inserting an ultraviolet lamp into the processing tank.
また、太陽光線についても処理槽の外部より照射するよ
うにしてもよい。Furthermore, sunlight may also be irradiated from outside the processing tank.
更に、光グラスファイバーの東の入口から紫外線乃至太
陽光線を処理槽内に照射するようにしてもよく、またこ
れらの方法を組み合わせて紫外線を処理槽内に照射する
ようにしてもよい。Further, ultraviolet rays or sunlight may be irradiated into the processing tank from the east entrance of the optical glass fiber, or ultraviolet rays may be irradiated into the processing tank by combining these methods.
紫外線の照射時間は用廃水中の有害物質濃度、光の強度
等により異なり、有害物質が実質上分解されるまでの時
間であるが、通常5〜20mw/cm2で、lO分〜1
時間である。The irradiation time of ultraviolet rays varies depending on the concentration of harmful substances in wastewater, the intensity of light, etc., and is the time until the harmful substances are substantially decomposed, but it is usually 5 to 20 mw/cm2 and 10 minutes to 1 minute.
It's time.
なお、この場合被処理水である用廃水中に酸化剤を加え
ておくと、より効果的である。この酸化剤としては、過
酸化水素、次亜塩素酸、過ヨウ素酸カリウムなどの無機
過酸化物が好ましく、特に過酸化水素が好ましい。In this case, it is more effective to add an oxidizing agent to the wastewater that is the water to be treated. As the oxidizing agent, inorganic peroxides such as hydrogen peroxide, hypochlorous acid, and potassium periodate are preferred, and hydrogen peroxide is particularly preferred.
この発明で処理できる物質は有機物の分解処理、微生物
の殺菌処理等を行なうことができるが、他の方法では分
解したり、除去できない、例えば有機ハロゲン化合物、
界面活性剤、有機リン化合物、フェノール類、BOD、
TOC1殺菌処理することができる。Substances that can be treated with this invention can be subjected to decomposition treatment of organic matter, sterilization treatment of microorganisms, etc., but substances that cannot be decomposed or removed by other methods, such as organic halogen compounds,
Surfactants, organic phosphorus compounds, phenols, BOD,
TOC1 can be sterilized.
(作用)
即ち、この発明によればその表面に二酸化チタン等の半
導体微粒子を付着させたファイバーの束を処理槽内に挿
入されでいるため、半導体微粒子は処理槽内の被処理水
中に分散され、したがってこのなかに紫外線乃至太陽光
線を照射すると、被処理水中の有機物の分解或は微生物
の殺菌処理等が効果的に行なえる。(Function) That is, according to the present invention, a bundle of fibers having semiconductor fine particles such as titanium dioxide attached to the surface thereof is inserted into the treatment tank, so that the semiconductor fine particles are dispersed in the water to be treated in the treatment tank. Therefore, by irradiating the water with ultraviolet rays or sunlight, it is possible to effectively decompose organic matter or sterilize microorganisms in the water to be treated.
また、この発明によれば処理後、ファイバーの束を被処
理水中から引き上げるだけで、半導体微粒子を被処理水
から分離、回収できるため、往来のように大掛かりな分
離、回収作業を必要としない。Further, according to the present invention, semiconductor fine particles can be separated and recovered from the water to be treated by simply pulling the bundle of fibers out of the water to be treated after treatment, so there is no need for large-scale separation and recovery work as in conventional methods.
更に、表面に半導体微粒子の付着したファイバーを入れ
替えるだけで、半導体微粒子の交換を容易に行なうこと
ができる。Furthermore, the semiconductor particles can be easily replaced by simply replacing the fiber to which the semiconductor particles are attached.
一方、紫外線乃至太陽光線を光グラスファイバーの束の
入口から処理槽内に照射すると、紫外線乃至太陽光線は
半導体微粒子の付着した光グラスファイバーの間から処
理槽内に入射されるので、より効果的な被処理水の光学
的処理を行なうことができる。On the other hand, when ultraviolet rays or sunlight are irradiated into the processing tank from the entrance of a bundle of optical glass fibers, the ultraviolet rays or sunlight enters the processing tank through between the optical glass fibers to which semiconductor fine particles are attached, making it more effective. Optical treatment of water to be treated can be performed.
(実施例)
以下、この発明を図示の実施例に基づいて詳細に説明す
る。(Example) Hereinafter, this invention will be explained in detail based on the illustrated example.
第1図は、この発明の一実施例を示すもので、1は上部
の入口1aより使用済みの風呂水等の被処理水を送入し
、下部の出口1bより処理水を排出する処理槽て、処理
槽lの内部にはその外周に石英ガラス等の保護管2を設
けた高圧水銀灯3を挿入し、更に保護管2の回りにはそ
の表面に二酸化チタン等fr′$導体微粒子4.・・−
を付着させたグラスファイバー58の束5.・・・を配
置する。FIG. 1 shows an embodiment of the present invention, in which 1 is a treatment tank into which water to be treated, such as used bath water, is fed through an upper inlet 1a and treated water is discharged through a lower outlet 1b. A high-pressure mercury lamp 3 having a protection tube 2 made of quartz glass or the like on its outer periphery is inserted into the treatment tank 1, and conductive fine particles 4.of titanium dioxide or the like are coated around the protection tube 2 on its surface.・・−
A bundle of glass fibers 58 to which 5. Place...
グラスファイバー5aの表面に半導体微粒子4゜・・・
を付着させるには、例えばグラスファイバーの表面に紫
外線硬化性樹脂を塗布し、その後半導体微粒子4.・・
・を付着させ、更に紫外線を照射して樹脂を硬化せしめ
る。Semiconductor fine particles 4°... on the surface of the glass fiber 5a.
To attach semiconductor particles, for example, an ultraviolet curable resin is applied to the surface of glass fiber, and then semiconductor fine particles 4.・・・
・Attach and further irradiate with ultraviolet rays to harden the resin.
また、保護管2の回りにグラスファイバー5aの東5.
・・・を配置するには、処理槽1の上端に保護管2の回
りに適宜間隔で保持穴6a、・・・を有する枠体6を設
け、この保持穴6a、・・・にはグラスファイバーの東
5を先端部を揃えて挿入して行なう。Also, around the protection tube 2, attach the glass fiber 5a to the east 5.
. . , a frame body 6 having holding holes 6a, . Insert the fiber east 5 with the tips aligned.
更に、枠体6の上方には集光レンズ7を配置する。Furthermore, a condenser lens 7 is arranged above the frame 6.
以上のような構成において、入口1aより処理槽1内に
送入される被処理水に対しては高圧水銀灯3より紫外線
を照射せしめる。In the above configuration, ultraviolet rays are irradiated from the high-pressure mercury lamp 3 to the water to be treated that is fed into the treatment tank 1 from the inlet 1a.
また、紫外線は処理槽1の外部より照射せしめてもよく
、この場合の紫外線の波長は365nm程度のものを使
用する。Further, the ultraviolet rays may be irradiated from the outside of the processing tank 1, and in this case, the wavelength of the ultraviolet rays used is about 365 nm.
一方、太陽光線は集光レンズ7で集光するとともに、グ
ラスファイバー0束5の先端部よりグラスファイバー5
a内に送入され、グラスファイバー5aの側部乃至先端
部より紫外線を用廃水の処理槽1内に照射せしめる。On the other hand, the sunlight is condensed by the condensing lens 7, and from the tip of the glass fiber bundle 5, the glass fiber 5
The ultraviolet rays are introduced into the wastewater treatment tank 1 from the sides and tips of the glass fibers 5a.
以上のように、処理槽1内に紫外線乃至太陽光線を照射
して、処理槽l内に送入される使用済みの風呂水を二酸
化チタンからなる半導体微粒子4、−・・の存在下に光
学的な処理を行なった。この結果、風呂水は再利用可能
な程度に浄化された。As described above, the treatment tank 1 is irradiated with ultraviolet rays or sunlight, and the used bath water fed into the treatment tank 1 is optically exposed to the semiconductor particles 4 made of titanium dioxide. processing was carried out. As a result, the bath water was purified to the extent that it could be reused.
なお、この実施例では集光レンズ7には太陽光線を照射
するようにしたが、紫外線を照射させるようにしてもよ
い。In this embodiment, the condensing lens 7 is irradiated with sunlight, but it may also be irradiated with ultraviolet rays.
また、処理槽■内に紫外線ランプ3を挿入せずに、外部
より紫外線を照射するようにしても。Alternatively, the ultraviolet rays may be irradiated from the outside without inserting the ultraviolet lamp 3 into the treatment tank.
い。stomach.
(発明の効果)
以上要するに、この発明によればその表面に判導体微粒
子を付着させたファイバーを束ねて被処理水の処理槽内
に挿入し、この処理槽内に紫外影を照射するため、半導
体微粒子は被処理水中に夕敢され、効果的な被処理水の
光学的処理を行なうことができる。(Effects of the Invention) In summary, according to the present invention, fibers having conductor fine particles attached to their surfaces are bundled and inserted into a treatment tank for water to be treated, and ultraviolet light is irradiated into the treatment tank. The semiconductor fine particles are introduced into the water to be treated and can perform effective optical treatment of the water to be treated.
また、処理後はファイバーを引き上げるだ巳ブで、半導
体微粒子を被処理水から分離、回収できるため、従来の
ように処理後、被処理水中に懸渣する半導体微粒子を被
処理水中より分離、回収する作業を必要としない。In addition, after treatment, the semiconductor particles can be separated and recovered from the water to be treated using a lever that pulls up the fibers. No additional work is required.
更に、紫外線をグラスファイバーの束ねた入口より照射
すれば、半導体微粒子の付着するグラスファイバーの間
より被処理水中に入射されるため、より効果的な処理を
行なうことができる。Furthermore, if ultraviolet rays are irradiated from the inlet of a bundle of glass fibers, the water to be treated will be incident from between the glass fibers to which the semiconductor fine particles are attached, so that more effective treatment can be performed.
第1図はこの発明の一実施例を示す縦断側面図、第2図
は同上の]1− H線断面図、第3図は同上のIII
−III線断面図、第4図はグラスファイバーの一部拡
大縦断側面図である。
図中、■は処理槽、3は高圧水銀灯、4は半導体微粒子
、5はグラスファイバー0束、 5aはグラスファイバ
ーFig. 1 is a vertical sectional side view showing one embodiment of the present invention, Fig. 2 is a sectional view taken along line 1-H of the same as above, and Fig. 3 is a sectional view of III of the same as above.
-III line sectional view, and FIG. 4 is a partially enlarged longitudinal sectional side view of the glass fiber. In the figure, ■ is a treatment tank, 3 is a high-pressure mercury lamp, 4 is semiconductor fine particles, 5 is 0 bundles of glass fibers, and 5a is glass fibers.
Claims (4)
粒子を付着させたファイバーの束を処理槽内に挿入し、
該処理槽内に紫外線乃至太陽光線をを照射して処理槽内
の被処理水を処理することを特徴とする光化学的用廃水
の処理方法。(1) A bundle of fibers with semiconductor particles that respond to ultraviolet and visible light attached to their surfaces is inserted into a processing tank,
A photochemical wastewater treatment method, which comprises treating the water in the treatment tank by irradiating the treatment tank with ultraviolet rays or sunlight.
ランプを挿入し、該ランプの周りに上記ファイバーの束
を配置するようにした特許請求の範囲第1項記載の方法
。(2) The method according to claim 1, wherein an ultraviolet lamp or a medium-pressure to high-pressure mercury lamp is inserted into the treatment tank, and the bundle of fibers is arranged around the lamp.
特許請求の範囲第1項又は第2項記載の方法。(3) The method according to claim 1 or 2, wherein an optical glass fiber is used as the fiber.
太陽光線を処理槽内に照射する特許請求の範囲第3項記
載の方法。(4) The method according to claim 3, wherein the treatment tank is irradiated with ultraviolet rays or sunlight from the entrance of the bundle of optical glass fibers.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2263899A JPH06102192B2 (en) | 1990-10-03 | 1990-10-03 | Photochemical wastewater treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2263899A JPH06102192B2 (en) | 1990-10-03 | 1990-10-03 | Photochemical wastewater treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04141294A true JPH04141294A (en) | 1992-05-14 |
| JPH06102192B2 JPH06102192B2 (en) | 1994-12-14 |
Family
ID=17395805
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2263899A Expired - Fee Related JPH06102192B2 (en) | 1990-10-03 | 1990-10-03 | Photochemical wastewater treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH06102192B2 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0839057A (en) * | 1994-08-01 | 1996-02-13 | Naoharu Hinuma | Water purifier |
| JPH11333451A (en) * | 1998-05-28 | 1999-12-07 | Raizaa Kogyo Kk | Method and apparatus for sterilization/purification by ultraviolet light |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6044091A (en) * | 1983-08-22 | 1985-03-08 | Naoharu Hinuma | Aeration and light condensing catalytic water purifying apparatus |
| JPS6161015U (en) * | 1984-09-26 | 1986-04-24 | ||
| JPH0268190A (en) * | 1988-09-01 | 1990-03-07 | Matsushita Electric Ind Co Ltd | Water sterilizing and purifying apparatus |
-
1990
- 1990-10-03 JP JP2263899A patent/JPH06102192B2/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6044091A (en) * | 1983-08-22 | 1985-03-08 | Naoharu Hinuma | Aeration and light condensing catalytic water purifying apparatus |
| JPS6161015U (en) * | 1984-09-26 | 1986-04-24 | ||
| JPH0268190A (en) * | 1988-09-01 | 1990-03-07 | Matsushita Electric Ind Co Ltd | Water sterilizing and purifying apparatus |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0839057A (en) * | 1994-08-01 | 1996-02-13 | Naoharu Hinuma | Water purifier |
| JPH11333451A (en) * | 1998-05-28 | 1999-12-07 | Raizaa Kogyo Kk | Method and apparatus for sterilization/purification by ultraviolet light |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH06102192B2 (en) | 1994-12-14 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
| LAPS | Cancellation because of no payment of annual fees |