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JPH047087A - Treatment of waste water containing sulfur compound - Google Patents

Treatment of waste water containing sulfur compound

Info

Publication number
JPH047087A
JPH047087A JP10865090A JP10865090A JPH047087A JP H047087 A JPH047087 A JP H047087A JP 10865090 A JP10865090 A JP 10865090A JP 10865090 A JP10865090 A JP 10865090A JP H047087 A JPH047087 A JP H047087A
Authority
JP
Japan
Prior art keywords
waste water
ion
wastewater
carrier
ions
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
Application number
JP10865090A
Other languages
Japanese (ja)
Other versions
JP2592538B2 (en
Inventor
Toru Ishii
徹 石井
Yoshinari Yamaguchi
山口 義成
Kiichiro Mitsui
三井 紀一郎
Kunio Sano
邦夫 佐野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nippon Shokubai Co Ltd
Original Assignee
Nippon Shokubai Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nippon Shokubai Co Ltd filed Critical Nippon Shokubai Co Ltd
Priority to JP2108650A priority Critical patent/JP2592538B2/en
Publication of JPH047087A publication Critical patent/JPH047087A/en
Application granted granted Critical
Publication of JP2592538B2 publication Critical patent/JP2592538B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Catalysts (AREA)

Abstract

PURPOSE:To efficiently treat waste water over a long period of time by adding a metal ion such as an Na (I) ion to waste water and subsequently subjecting said waste water to wet oxidizing treatment at temp. of below 370 deg.C under pressure holding the waste water to a liquid phase under the supply of gas containing oxygen using a wet oxidizing reactor packed with a solid catalyst. CONSTITUTION:In treating waste water containing a sulfur compound, a metal ion such as an Na (I) ion and/or a K(I) ion is preliminarily added to said waste water and, subsequently, the waste water is subjected to wet oxidizing treatment at temp. of below 370 deg.C under the supply oxygen-containing gas under pressure holding waste water to a liquid phase using a wet oxidizing reactor packed with a solid catalyst. The affinity of a sulfate ion with a carrier is suppressed and the adhesion of the sulfate ion to the carrier is prohibited and the sulfate ion bonded to the carrier can be also removed. Therefore, waste water containing a sulfur compound can be stably treated over a long period of time.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、イオウ化合物を含む廃水を固体触媒の存在下
に湿式酸化して浄化処理する方法に関する。詳しくはイ
オウ化合物を含む廃水を固体触媒の存在下において湿式
酸化処理する際に触媒が、イオウの触媒毒の作用を受は
難くいようにすることにより長期間安定した廃水処理を
可能とする処理法に関する。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a method for purifying wastewater containing sulfur compounds by wet oxidation in the presence of a solid catalyst. In detail, when wastewater containing sulfur compounds is subjected to wet oxidation treatment in the presence of a solid catalyst, the catalyst is not susceptible to the effects of sulfur catalyst poison, thereby enabling stable wastewater treatment over a long period of time. Regarding the law.

(従来の技術) 廃水の処理方法には、活性汚泥法と呼ばれる生物化学的
方法とチンマーマン法と呼ばれる湿式酸化法が知られて
いる。
(Prior Art) Known wastewater treatment methods include a biochemical method called an activated sludge method and a wet oxidation method called a Zimmerman method.

湿式酸化法には、反応速度を速めるため各種酸化触媒を
使用する方法が提案されている。
In wet oxidation methods, methods using various oxidation catalysts have been proposed in order to speed up the reaction rate.

また、イオウ化合物を含む廃水を酸化触媒の存在下に湿
式酸化処理する場合、イオウが触媒表面に吸着され活性
点を被覆するために経時的に処理効率が低下し、最終的
には触媒が失活してしまうというイオウの触媒毒の問題
がある。
Furthermore, when wastewater containing sulfur compounds is subjected to wet oxidation treatment in the presence of an oxidation catalyst, sulfur is adsorbed onto the catalyst surface and covers the active sites, resulting in a decrease in treatment efficiency over time, and eventually the catalyst is lost. There is a problem with sulfur being a catalytic poison.

(発明が解決しようとする課題) 従って、本発明の目的はイオウ化合物を含む廃水を固体
触媒を充填した湿式酸化反応器を用いて効率よく長期に
わたって処理する方法を提供することにある。
(Problems to be Solved by the Invention) Therefore, an object of the present invention is to provide a method for efficiently treating wastewater containing sulfur compounds over a long period of time using a wet oxidation reactor filled with a solid catalyst.

(課題を解決するための手段) 本発明者らは、上記に述べた問題点を解決すべく鋭意研
究を重ねた結果、イオウ化合物を含む廃水を酸化触媒の
存在下に湿式酸化処理する際に予め廃水にNa(1)イ
オン及び/又はK (I)イオンの金属イオンを添加す
ることで以下に述べるような優れた効果が得られること
を見い出したのである。
(Means for Solving the Problems) As a result of extensive research to solve the above-mentioned problems, the present inventors have found that when wet oxidation treatment of wastewater containing sulfur compounds is carried out in the presence of an oxidation catalyst. It has been found that by adding metal ions such as Na(1) ions and/or K(I) ions to wastewater in advance, excellent effects as described below can be obtained.

すなわち、本発明は、イオウ化合物を含む廃水を処理す
るに際し、予めイオウ化合物を含む廃水にNa(1)イ
オン及び/又はK (I)イオンの金属イオンを添加し
、次いで固体触媒を充填した湿式酸化反応器を用いて3
70 ’C未満の温度、かつ該廃水が液相を保持する圧
力下で酸素を含有するガスの供給下に湿式酸化処理する
ことを特徴とする廃水の処理法である。
That is, in the present invention, when treating wastewater containing sulfur compounds, metal ions such as Na(1) ions and/or K(I) ions are added to the wastewater containing sulfur compounds in advance, and then a wet method is used which is filled with a solid catalyst. 3 using an oxidation reactor
A method for treating wastewater characterized by wet oxidation treatment under the supply of oxygen-containing gas at a temperature below 70'C and a pressure such that the wastewater maintains a liquid phase.

さらに詳しくは、上記の金属イオンを添加することで硫
酸イオンは、これらの物質と、例えば次式に示すような
反応が起こる。
More specifically, by adding the above-mentioned metal ions, the sulfate ions react with these substances, for example, as shown in the following formula.

2Na” + 304”−+ Na、5O42K”  
+  So、2− → K2SO3一方、硫酸イオンが
触媒表面に吸着されて活性低下を起こすのは、イオウ成
分が5o42−、 H5O。
2Na" + 304"-+ Na, 5O42K"
+ So, 2- → K2SO3 On the other hand, sulfuric acid ions are adsorbed on the catalyst surface and cause a decrease in activity when the sulfur component is 5o42-, H5O.

等のように硫酸等のイオン状態で存在している場合に生
じる現象である。前者の反応、すなわち該金属イオンと
硫酸イオンの親和力は、後者の付着反応、すなわち担体
と硫酸イオンの親和力より強いため、前者の反応を生し
させることにより、担体に硫酸イオンを付着することを
抑制し、さらにその親和力により担体に付着した硫酸イ
オンを担体から除去しうる効果もある。したがって、触
媒上への吸着は起こることなく通過する。更に汚泥等の
固形物を含む廃水を処理する場合においても固形物中に
含まれるイオウ化合物は、温式酸化条件下で可溶化反応
を起こし硫酸イオンを生成するもののNa(I)イオン
及び/又はK (1)イオン等を廃水中に存在せしめる
と該イオンの効果により触媒上ヘイオウの吸着を抑制す
る。
This phenomenon occurs when it exists in an ionic state such as sulfuric acid. The former reaction, that is, the affinity between the metal ion and the sulfate ion, is stronger than the latter adhesion reaction, that is, the affinity between the carrier and the sulfate ion. Therefore, by allowing the former reaction to occur, it is possible to prevent the attachment of sulfate ions to the carrier. It also has the effect of suppressing and further removing sulfate ions attached to the carrier due to its affinity. Therefore, adsorption onto the catalyst does not occur and passes through. Furthermore, when treating wastewater containing solids such as sludge, the sulfur compounds contained in the solids undergo a solubilization reaction under warm oxidation conditions to produce sulfate ions, but Na(I) ions and/or When K (1) ions are present in wastewater, the effect of the ions suppresses the adsorption of helium on the catalyst.

したがって、上記で述べた金属イオンを予め廃水に添加
することにより、長期間にわたり安定した触媒活性を維
持することができるのである。
Therefore, by adding the above-mentioned metal ions to wastewater in advance, stable catalytic activity can be maintained over a long period of time.

又、本発明において予め廃水に添加する金属イオンは廃
水を昇温する前に添加することが好ましい 添加するNa(1)イオンおよび/またはK (I)イ
オンとしては、水酸化ナトリウム、硝酸ナトリウム、亜
硝酸ナトリウム、炭酸ナトリウム、炭酸水素ナトリウム
、水酸化カリウム、硝酸カリウム、亜硝酸カリウム、炭
酸カリウム、炭酸水素カリウム等の水溶性の塩のいずれ
を用いてもよいが、好ましくは、水酸化ナトリウム、水
酸化カリウムを用いることができる。
Further, in the present invention, the metal ions to be added to the wastewater in advance are preferably added before heating the wastewater. Examples of the Na(1) ions and/or K(I) ions to be added include sodium hydroxide, sodium nitrate, Any water-soluble salt such as sodium nitrite, sodium carbonate, sodium hydrogen carbonate, potassium hydroxide, potassium nitrate, potassium nitrite, potassium carbonate, potassium hydrogen carbonate, etc. may be used, but preferably sodium hydroxide, sodium hydroxide Potassium can be used.

また、廃水中に添加するNa(I)イオン及び/又はK
 (1)イオンの金属イオンの注入率は、廃水中のイオ
ウ濃度(固形分中の濃度も含む)に対して当量比で1以
上、好ましくは1.1〜5に設定するとよい。
In addition, Na(I) ions and/or K added to wastewater
(1) The injection rate of metal ions is preferably set to an equivalent ratio of 1 or more, preferably 1.1 to 5, relative to the sulfur concentration in wastewater (including the concentration in solid content).

本発明に係る触媒としては、一般に廃水処理に用いられ
るチタニア、シリカ、ジルコニア、アルミナ、活性炭、
ケイソウ土等の担体を用いることが出来る。特にチタニ
アはイオウと結合しやすく、イオウ被毒の影響を受けや
すいので、本発明に係る方法はチタニアを含有する担体
には特に有効なものとなる。またチタニア、チタニア−
シリカの担体は耐熱性を有しているので本方法を用いる
のには好ましい。
Catalysts according to the present invention include titania, silica, zirconia, alumina, activated carbon, which are generally used for wastewater treatment,
A carrier such as diatomaceous earth can be used. In particular, since titania easily binds to sulfur and is susceptible to sulfur poisoning, the method of the present invention is particularly effective for carriers containing titania. Also titania, titania
Silica supports are preferred for use in this method due to their heat resistance.

詳しく述べると、チタニア、ナタニアーシリ力、チタニ
ア−ジルコニア等の担体に、マンガン、鉄、コバルト、
ニッケル、タングステン、銅、セリウム、i艮、金、白
金、パラジウム、ロジウム、ルテニウムおよびイリジウ
ム等触媒活性成分元素の金属またはその水に不溶性また
は難溶性の化合物、例えば、酸化物、塩化物、硫化物を
担持したものが用いられる。
To be more specific, manganese, iron, cobalt,
Catalyst-active component metals such as nickel, tungsten, copper, cerium, metal, gold, platinum, palladium, rhodium, ruthenium, and iridium, or their water-insoluble or sparingly soluble compounds, such as oxides, chlorides, and sulfides. is used.

触媒組成としては、担体75〜99.95重量%、好ま
しくは85〜99.9重量%であり、前記触媒活性成分
元素の金属またはその化合Th0.05〜25重量%、
好ましくは0.1〜15重量%の範囲である。好ましく
は、触媒活性成分元素のうち、マンガン、鉄、コバルト
、ニッケル、タングステン、銅、セリウムおよび銀につ
いては、化合物として0〜15重量%であり、白金、パ
ラジウム、ロジウム、ルテニウム、およびイリジウムの
使用量は金属として0〜5重量%(ただし、両者の合計
量は0.1〜15重量%である)。さらに、好ましくは
チタニア−ジルコニア担体に上記白金族金属が担持され
てなる触媒である。特に、この触媒においてチタニア2
0〜90モル%およびジルコニア10〜80モル%から
なる二元系複合酸化物あるいは混合物を用いた場合には
活性および耐熱水性・耐酸性・耐久性に優れている。
The catalyst composition is 75 to 99.95% by weight of the carrier, preferably 85 to 99.9% by weight, 0.05 to 25% by weight of the metal or compound thereof as the catalyst active component element,
Preferably it is in the range of 0.1 to 15% by weight. Preferably, among the catalyst active component elements, manganese, iron, cobalt, nickel, tungsten, copper, cerium, and silver are used in an amount of 0 to 15% by weight as a compound, and platinum, palladium, rhodium, ruthenium, and iridium are used in an amount of 0 to 15% by weight. The amount is 0 to 5% by weight as metal (however, the total amount of both is 0.1 to 15% by weight). Furthermore, a catalyst in which the above-mentioned platinum group metal is supported on a titania-zirconia carrier is preferable. In particular, in this catalyst titania 2
When a binary composite oxide or a mixture consisting of 0 to 90 mol% and 10 to 80 mol% of zirconia is used, it has excellent activity, hot water resistance, acid resistance, and durability.

また、触媒担体の形状としては、ペレ・ント状、球状、
ハニカム状、リング状等いずれも用いることができるが
、余剰汚泥のような懸濁物を含む廃水を扱う場合には、
固形物、沈殿等により触媒層での閉塞が起こる可能性が
あるため、ハニカム状が特に好ましい。
In addition, the shape of the catalyst carrier is pellet-like, spherical,
Both honeycomb and ring shapes can be used, but when dealing with wastewater containing suspended matter such as excess sludge,
A honeycomb shape is particularly preferred since the catalyst layer may be clogged due to solid matter, precipitation, etc.

本発明に係る湿式酸化反応器としては、通常使用されて
いる単管円筒式反応器、処理される廃水によっては、多
管式反応器等が用いられる。
As the wet oxidation reactor according to the present invention, a commonly used single-tube cylindrical reactor, a multi-tube reactor, etc. are used depending on the wastewater to be treated.

また、廃水の液相状態を保持させるために、反応温度は
370°C未満の温度、かつ該温度の際に液相状態を保
持する圧力以上に設定することによりなされる。
Further, in order to maintain the liquid phase state of the wastewater, the reaction temperature is set to a temperature lower than 370° C. and a pressure higher than that which maintains the liquid phase state at this temperature.

反応に際しては、酸素含有ガスが用いられるが、装置の
コンパクト化等の特殊な場合を除き、価格の安価な空気
が好ましいものである。
In the reaction, an oxygen-containing gas is used, but air is preferable since it is inexpensive, except in special cases such as when making the apparatus more compact.

次に実施例を挙げて本発明をさらに詳細に説明する。Next, the present invention will be explained in more detail with reference to Examples.

なお本発明は、本発明の趣旨に反しない限り、これら実
施例のみに限定されるものではない。
Note that the present invention is not limited to these Examples unless it goes against the spirit of the present invention.

実施例I 第1図は本発明によるリン化合物を含む廃水の処理を行
なうための装置の概略図である。用いられる反応器1の
内径は50rrIfrIかつ管長は10mで管内には、
平均粒径51Ilffl、長さ6mmのペレット触媒(
Pt0.5 wt%をチタニア−ジルコニア担体に担持
したもの)を触媒層長8mになるように充填した。
Example I FIG. 1 is a schematic diagram of an apparatus for treating wastewater containing phosphorus compounds according to the present invention. The reactor 1 used has an inner diameter of 50rrIfrI and a tube length of 10m, and inside the tube are:
Pellet catalyst with an average particle size of 51Ilffl and a length of 6mm (
A titania-zirconia carrier containing 0.5 wt% of Pt supported on the catalyst layer was packed to a catalyst layer length of 8 m.

イオウ化合物(硫酸換算H2SO4500ppm)を含
むC0D(Cr) 40 g / j2の濃度の流れる
廃水ライン10に水酸化ナトリウム溶液をポンプ4によ
り添加した。
A sodium hydroxide solution was added by pump 4 to a flowing wastewater line 10 with a concentration of 40 g/j2 of C0D(Cr) containing sulfur compounds (500 ppm H2SO4 equivalent to sulfuric acid).

一方、空気をコンプレッサー9で昇圧後、廃水供給ポン
プ3から供給される廃水と混合し、熱交換器2で予熱後
、反応器1に供給した。
On the other hand, air was pressurized by a compressor 9, mixed with waste water supplied from a waste water supply pump 3, and after being preheated by a heat exchanger 2, was supplied to the reactor 1.

反応器1で処理された廃水はライン12より排出され、
熱交換器7で冷却されたのち、気液分離器5へ供給され
、ここで無害なガスと水とに分離した。この気液分離器
5においては、液面コントローラーLCにより液面を検
出して液面制御弁6を作動させて一定の液面を保持する
とともに、圧力コントローラーPCにより圧力を検出し
て圧力制御弁7を作動させて一定の圧力を保持するよう
に操作されている。
The wastewater treated in reactor 1 is discharged from line 12,
After being cooled in the heat exchanger 7, it was supplied to the gas-liquid separator 5, where it was separated into harmless gas and water. In this gas-liquid separator 5, a liquid level controller LC detects the liquid level and operates a liquid level control valve 6 to maintain a constant liquid level, and a pressure controller PC detects pressure and operates a pressure control valve 6. 7 to maintain a constant pressure.

このとき反応器1内における処理条件は、反応温度25
0°Cかつ反応圧カフ5kg/aflGであり、廃水供
給量30j!/fir、予め廃水に添加する水酸化ナト
リウム溶液6,100 ppm供給量3f/Hr、空気
量4,800 Nl/Hrであった。そしてこの条件下
でのCOO反応率は99%であり、2.000)1rの
連続運転においてもCOD反応率の低下は認められなか
った。
At this time, the processing conditions in the reactor 1 are as follows: reaction temperature 25
0°C, reaction pressure cuff 5kg/aflG, and wastewater supply amount 30j! /fir, a sodium hydroxide solution added in advance to the wastewater at a supply rate of 6,100 ppm, 3f/Hr, and an air flow rate of 4,800 Nl/Hr. The COO reaction rate under these conditions was 99%, and no decrease in the COD reaction rate was observed even during continuous operation at 2,000)1r.

比較例1 イオウ化合物(硫酸換算H2SO4500ppm)を含
むに00(C:r)  40 g / I!の濃度の廃
水に予め金属イオンを添加することな〈実施例1で用い
た同−装置を用いて、同一処理条件下で連続運転を実施
した。
Comparative Example 1 Contains sulfur compound (H2SO4500ppm in terms of sulfuric acid) 00 (C:r) 40 g/I! Continuous operation was carried out under the same treatment conditions using the same apparatus used in Example 1, without adding metal ions in advance to wastewater having a concentration of .

COD反応率の経時変化を表1で示す。Table 1 shows the change in COD reaction rate over time.

表   1 実施例2 実施例1に準してイオウ化合物(硫酸換算H2SO。Table 1 Example 2 A sulfur compound (H2SO in terms of sulfuric acid) was prepared according to Example 1.

500ppm)を含むC0D(Cr) 40 g / 
IV、の濃度の流れる廃水ライン10に水酸化カリウム
溶液をポンプ4により添加した。
40 g/C0D (Cr) containing 500 ppm)
Potassium hydroxide solution was added by pump 4 to the flowing waste water line 10 at a concentration of IV.

水酸化カリウム溶液の濃度は3.600ppm、供給量
31/Hrである以外は同一処理条件下で連続運転を実
施した。
Continuous operation was carried out under the same treatment conditions except that the concentration of the potassium hydroxide solution was 3.600 ppm and the feed rate was 31/Hr.

この条件下でのCOD反応率は99%であり、2、00
0Hrの連続運転においてもCOD反応率の低下は認め
られなかった。
The COD reaction rate under this condition was 99%, and 2,000
No decrease in COD reaction rate was observed even during continuous operation for 0 hours.

(発明の効果) このように、本発明によれば、イオウ化合物を含む廃水
に予め金属イオンを添加することで硫酸イオンと担体と
の親和性を抑制し、硫酸イオンが担体に付着することを
阻げ、なおかつ担体に付着した硫酸イオンを除去するこ
ともできる。
(Effects of the Invention) As described above, according to the present invention, by adding metal ions in advance to wastewater containing sulfur compounds, the affinity between sulfate ions and the carrier is suppressed, and the attachment of sulfate ions to the carrier is prevented. In addition, it is also possible to remove sulfate ions attached to the carrier.

したがって、イオウ化合物を含む廃水に対して長期間に
わたり安定した廃水処理を実現できる。
Therefore, stable wastewater treatment for a long period of time can be realized for wastewater containing sulfur compounds.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は、本発明の一実施態様を示すフローシートであ
る。 1・・・単管円筒式反応器 2・・・熱交換器 3・・・廃水供給ポンプ 4・・・水酸化ナトリウム溶液供給ポンプ5・・・気液
分離器 6・・・液面制御弁 7・・・圧力 〃 8・・・空気供給ライン 9・・・コンプレッサー 10・・・廃水供給ライン 11・・・水酸化ナトリウム溶液供給ライン12・・・
処理液ライン
FIG. 1 is a flow sheet showing one embodiment of the present invention. 1... Single tube cylindrical reactor 2... Heat exchanger 3... Waste water supply pump 4... Sodium hydroxide solution supply pump 5... Gas-liquid separator 6... Liquid level control valve 7...Pressure 8...Air supply line 9...Compressor 10...Wastewater supply line 11...Sodium hydroxide solution supply line 12...
Processing liquid line

Claims (2)

【特許請求の範囲】[Claims] (1)イオウ化合物を含む廃水を処理するに際し、予め
イオウ化合物を含む廃水にNa( I )イオン及び/又
はK( I )イオンの金属イオンを添加し、次いで固体
触媒を充填した湿式酸化反応器を用いて370℃未満の
温度、かつ該廃水が液相を保持する圧力下で酸素を含有
するガスの供給下に湿式酸化処理することを特徴とする
廃水の処理法。
(1) When treating wastewater containing sulfur compounds, metal ions such as Na(I) ions and/or K(I) ions are added to the wastewater containing sulfur compounds in advance, and then a wet oxidation reactor is filled with a solid catalyst. A method for treating wastewater, characterized in that wet oxidation treatment is carried out at a temperature of less than 370° C. and under a pressure such that the wastewater maintains a liquid phase while supplying an oxygen-containing gas.
(2)固体触媒が、チタニアを含有する酸化物を担体成
分とする触媒である請求項(1)記載の廃水の処理法。
(2) The method for treating wastewater according to claim (1), wherein the solid catalyst is a catalyst whose carrier component is an oxide containing titania.
JP2108650A 1990-04-26 1990-04-26 Treatment of wastewater containing sulfur compounds Expired - Fee Related JP2592538B2 (en)

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Application Number Priority Date Filing Date Title
JP2108650A JP2592538B2 (en) 1990-04-26 1990-04-26 Treatment of wastewater containing sulfur compounds

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JPH047087A true JPH047087A (en) 1992-01-10
JP2592538B2 JP2592538B2 (en) 1997-03-19

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Country Link
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Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5864188A (en) * 1981-10-15 1983-04-16 Osaka Gas Co Ltd Purification of waste water

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5864188A (en) * 1981-10-15 1983-04-16 Osaka Gas Co Ltd Purification of waste water

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