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JP3395669B2 - Deodorizing device - Google Patents
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JP3395669B2 - Deodorizing device - Google Patents

Deodorizing device

Info

Publication number
JP3395669B2
JP3395669B2 JP28809198A JP28809198A JP3395669B2 JP 3395669 B2 JP3395669 B2 JP 3395669B2 JP 28809198 A JP28809198 A JP 28809198A JP 28809198 A JP28809198 A JP 28809198A JP 3395669 B2 JP3395669 B2 JP 3395669B2
Authority
JP
Japan
Prior art keywords
ozone
tower
deodorizing
dissolved water
catalyst
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.)
Expired - Fee Related
Application number
JP28809198A
Other languages
Japanese (ja)
Other versions
JP2000117047A (en
Inventor
昭男 大山
克也 丸山
春夫 田極
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries 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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP28809198A priority Critical patent/JP3395669B2/en
Publication of JP2000117047A publication Critical patent/JP2000117047A/en
Application granted granted Critical
Publication of JP3395669B2 publication Critical patent/JP3395669B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Oxygen, Ozone, And Oxides In General (AREA)
  • Treating Waste Gases (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は脱臭装置に係り、特
に、下水処理場で発生する硫黄系の臭気をオゾンの酸化
力により効率的に分解して脱臭する装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a deodorizing device, and more particularly to a device for efficiently decomposing a sulfur-based odor generated in a sewage treatment plant by the oxidizing power of ozone.

【0002】[0002]

【従来の技術】下水処理場の汚水ないし汚泥処理設備で
発生する硫黄系の臭気(臭気成分として、硫化水素(H
2S),メチルメルカプタン(CH3SH),硫化メチル
((CH32S,二硫化メチル((CH322)を含
む。)等の脱臭法として、オゾンの酸化力を利用して臭
気成分を脱臭するオゾン脱臭法が知られている。このオ
ゾン脱臭方法には、臭気ガス中に直接オゾンガスを吹き
込み気−気接触で臭気成分を分解する乾式法(特開昭5
2−135869号公報)と、臭気ガスを上向流通気し
ている充填塔にオゾン溶解水を散水し、気−液接触で臭
気成分を分解する湿式法(特開昭57−167723号
公報)とがある。なお、湿式法で使用される充填塔の充
填材は、単に、気−液接触効率を向上させるためのもの
であり、セラミックス材やプラスチック材よりなる。
2. Description of the Related Art Sulfur-based odor generated in sewage treatment plant sewage or sludge treatment equipment (hydrogen sulfide (H
2 S), methyl mercaptan (CH 3 SH), methyl sulfide (including (CH 3 ) 2 S, methyl disulfide ((CH 3 ) 2 S 2 ), etc.) is used as a deodorizing method by utilizing the oxidizing power of ozone There is known an ozone deodorizing method for deodorizing odorous components. This ozone deodorization method is a dry method in which ozone gas is directly blown into the odor gas to decompose the odor components by air-gas contact (Japanese Patent Laid-Open No. Sho 5).
No. 2-135869) and a wet method in which ozone-dissolved water is sprinkled into a packed tower in which odorous gas is flowing upward, and odorous components are decomposed by gas-liquid contact (JP-A-57-167723). There is. The packing material for the packed tower used in the wet method is merely for improving the gas-liquid contact efficiency, and is made of a ceramic material or a plastic material.

【0003】[0003]

【発明が解決しようとする課題】従来の乾式オゾン酸化
による脱臭法では、気−気接触による分解反応の反応効
率が極めて低く、臭気成分の除去率も高々20%程度で
ある上に、オゾンの使用効率も20%程度と非常に低
い。
In the conventional deodorization method by dry ozone oxidation, the reaction efficiency of the decomposition reaction by gas-gas contact is extremely low, and the removal rate of odorous components is about 20% at the most. The usage efficiency is also very low, about 20%.

【0004】これに対して、湿式オゾン酸化による脱臭
法では、気−液接触による分解反応の反応効率が高く、
このため充填塔へ通気する臭気の通気空塔速度(SV)
が600〜1000hr-1という比較的高い負荷で脱臭
処理することが可能であるが、装置設備の小型化、処理
時間の短縮が常に望まれる状況において、より一層の反
応効率の向上が求められている。
On the other hand, in the deodorization method by wet ozone oxidation, the reaction efficiency of the decomposition reaction by gas-liquid contact is high,
For this reason, the aeration air velocity (SV) of the odor vented to the packed tower
It is possible to perform deodorizing treatment with a relatively high load of 600 to 1000 hr -1 , but in situations where it is always desired to downsize the equipment and shorten the treatment time, further improvement in reaction efficiency is required. There is.

【0005】本発明は上記従来の実情に鑑みてなされた
ものであって、湿式オゾン酸化による脱臭装置であっ
て、脱臭効率が著しく高く、装置設備の小型化、処理効
率の向上が可能な脱臭装置を提供することを目的とす
る。
The present invention has been made in view of the above-mentioned conventional circumstances, and is a deodorizing apparatus by wet ozone oxidation, which has a remarkably high deodorizing efficiency, and is capable of downsizing the equipment and improving the processing efficiency. The purpose is to provide a device.

【0006】[0006]

【課題を解決するための手段】本発明の脱臭装置は、オ
ゾン溶解水製造手段と、触媒が充填された脱臭塔と、該
脱臭塔内に臭気を上向流通気する手段と、該脱臭塔内の
上部からオゾン溶解水を散水する手段と、該脱臭塔から
排出される排ガス中の残留オゾンを分解する手段とを備
えてなることを特徴とする。
The deodorizing apparatus of the present invention comprises means for producing ozone-dissolved water, a deodorizing tower filled with a catalyst, means for upwardly flowing odor into the deodorizing tower, and the deodorizing tower. It is characterized by comprising means for spraying ozone-dissolved water from the upper part of the inside and means for decomposing residual ozone in the exhaust gas discharged from the deodorization tower.

【0007】本発明においては、湿式オゾン酸化による
脱臭に当り、触媒を存在させることにより、下記反応式
に示すように、硫黄系の臭気成分の硫黄(S)に対して
オゾンを等モルで作用させて効率的に分解することが可
能となり、反応効率、オゾンの利用効率を高めることが
できる。
In the present invention, upon deodorization by wet ozone oxidation, the presence of a catalyst causes ozone to act in an equimolar amount with respect to sulfur (S), which is a sulfur-based odor component, as shown in the following reaction formula. By doing so, it becomes possible to decompose efficiently, and the reaction efficiency and ozone utilization efficiency can be improved.

【0008】H2S+O3→H2O+SO2 (CH322+2O3→2CH3O+2SO2 本発明の脱臭装置では、オゾン溶解効率95%以上でオ
ゾン溶解水を製造し、このオゾン溶解水を臭気と触媒の
存在下に向流接触させることで、SV1000〜200
0hr-1の高負荷処理でも、オゾン使用率99%以上、
臭気成分除去率99.9%以上を達成することができ、
脱臭塔の容量を従来の湿式オゾン酸化による脱臭法に比
べて約1/2に小型化した上で効率的な脱臭を行える。
H 2 S + O 3 → H 2 O + SO 2 (CH 3 ) 2 S 2 + 2O 3 → 2CH 3 O + 2SO 2 In the deodorizing apparatus of the present invention, ozone-dissolved water is produced with an ozone-dissolving efficiency of 95% or more. By contacting water countercurrently in the presence of odor and a catalyst, SV1000-200
Even with high load treatment of 0 hr -1 , ozone usage rate is 99% or more,
It is possible to achieve an odor component removal rate of 99.9% or more,
The capacity of the deodorization tower can be reduced to about 1/2 of that of the conventional deodorization method using wet ozone oxidation, and efficient deodorization can be performed.

【0009】[0009]

【発明の実施の形態】以下に図面を参照して本発明の実
施の形態を詳細に説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described in detail below with reference to the drawings.

【0010】図1は本発明の脱臭装置の実施の形態を示
す系統図である。
FIG. 1 is a system diagram showing an embodiment of a deodorizing apparatus of the present invention.

【0011】1は酸素発生機であり、原料空気の酸素濃
度を高め、オゾン発生機2で得られるオゾン化空気の容
量を小さくするために設けられる。この酸素発生機1で
酸素濃度を高めた空気をオゾン発生機2に送給してオゾ
ンを発生させ、オゾン化空気を得る。
An oxygen generator 1 is provided for increasing the oxygen concentration of the raw material air and reducing the capacity of the ozonized air obtained by the ozone generator 2. The air whose oxygen concentration has been increased by the oxygen generator 1 is fed to the ozone generator 2 to generate ozone and obtain ozonized air.

【0012】オゾン化空気は配管11より、オゾン溶解
塔3に送給し、塔底部の散気管3Aから散気して攪拌
し、水中に溶解させる。このオゾン溶解塔3において
は、オゾンの溶解効率を高めるために、オゾンを気泡径
1mm程度の微細気泡として散気することが好ましく、
このような微細気泡の散気が行えるような散気手段を設
けるのが好ましい。また、オゾン溶解効率約95%が達
成させるように、水深及びオゾンの滞留時間を設定する
のが好ましく、水深4.0〜5.0mで滞留時間(HR
T)10〜15分、特に水深5mでHRT15分程度と
するのが好ましい。このオゾン溶解塔3で得られるオゾ
ン溶解水のオゾン濃度は2.0〜5.0mg/L程度が
好適である。
The ozonized air is supplied to the ozone dissolution tower 3 through the pipe 11, diffused and stirred from the diffuser pipe 3A at the bottom of the tower, and dissolved in water. In this ozone dissolution tower 3, it is preferable to diffuse ozone as fine bubbles having a bubble diameter of about 1 mm in order to enhance the dissolution efficiency of ozone.
It is preferable to provide an air diffusing means for diffusing such fine air bubbles. Further, it is preferable to set the water depth and the residence time of ozone so that the ozone dissolution efficiency of about 95% can be achieved, and the residence time (HR
T) 10 to 15 minutes, and particularly preferably 5 minutes at a water depth of about 15 minutes for HRT. The ozone concentration of the ozone-dissolved water obtained in the ozone-dissolving tower 3 is preferably about 2.0 to 5.0 mg / L.

【0013】オゾン溶解塔3のオゾン溶解水は配管12
により脱臭塔4に送給され、塔内上部に設けられた散気
管5より散水される。なお、オゾン溶解塔3の未溶解オ
ゾンは配管13より取り出し、臭気と共に脱臭塔4に送
給して臭気成分の分解に利用する。
The ozone-dissolved water in the ozone-dissolving tower 3 is connected to the pipe 12
Is sent to the deodorizing tower 4 and is sprayed with water from an air diffuser 5 provided in the upper part of the tower. The undissolved ozone in the ozone dissolution tower 3 is taken out from the pipe 13 and sent to the deodorization tower 4 together with the odor to be used for decomposing the odorous components.

【0014】脱臭塔4内には、触媒充填層6が形成され
ており、散水管5から散水されたオゾン溶解水と、塔下
部から配管14より導入される臭気とがこの触媒充填層
6で気−液向流接触する湿式触媒オゾン酸化により、臭
気成分が効率的に分解される。
A catalyst packed layer 6 is formed in the deodorization tower 4, and the ozone dissolved water sprinkled from the sprinkling pipe 5 and the odor introduced from the pipe 14 from the lower part of the tower are the catalyst packed layer 6. Odor components are efficiently decomposed by the wet catalytic ozone oxidation in contact with gas-liquid countercurrent.

【0015】脱臭塔4に充填する触媒としては、鉄,マ
ンガン,コバルト,ニッケル,チタン,銅,銀,白金,
パラジウム等の金属の酸化物を、ゼオライト,アルミ
ナ,活性炭等の担体に5〜10重量%の割合で担持した
ものを用いることができる。触媒の大きさとしては5〜
10mm程度が好適である。触媒の形状には特に制限は
なく、ハニカム状,ペレット状,円柱状,筒状,板状等
各種の形状のものを採用できる。
As catalysts to be filled in the deodorization tower 4, iron, manganese, cobalt, nickel, titanium, copper, silver, platinum,
A metal oxide such as palladium supported on a carrier such as zeolite, alumina or activated carbon at a ratio of 5 to 10% by weight can be used. The size of the catalyst is 5
About 10 mm is suitable. The shape of the catalyst is not particularly limited, and various shapes such as a honeycomb shape, a pellet shape, a column shape, a cylinder shape, and a plate shape can be adopted.

【0016】脱臭塔4への触媒の充填量は、臭気をSV
1000〜2000hr-1で通気した場合において、臭
気成分の分解効率99.9%以上を達成することができ
るような充填量で設定し、臭気成分の濃度に応じて臭気
のSVを1000〜2000hr-1の範囲で調整すれ
ば、常に99.9%以上の分解効率が得られるようにす
るのが好ましい。
The amount of catalyst packed in the deodorization tower 4 is set so that the odor is SV.
When aeration is carried out at 1000 to 2000 hr −1 , the filling amount is set so that the decomposition efficiency of odorous components can reach 99.9% or more, and the SV of odor is 1000 to 2000 hr depending on the concentration of odorous components. If it is adjusted within the range of 1 , it is preferable to always obtain a decomposition efficiency of 99.9% or more.

【0017】脱臭塔4で脱臭処理された排ガスは、ファ
ン7により配管15を経て排出され、オゾン分解塔8で
残留オゾンが分解された後、配管16より大気に放散さ
れる。
The exhaust gas deodorized by the deodorizing tower 4 is discharged by the fan 7 through the pipe 15, the residual ozone is decomposed by the ozone decomposing tower 8, and then released into the atmosphere through the pipe 16.

【0018】このオゾン分解塔8としては、活性炭充填
層や、二酸化マンガン,亜酸化銀等の触媒充填層を形成
したものが好適である。
As the ozone decomposing tower 8, one having an activated carbon packed layer and a catalyst packed layer of manganese dioxide, silver suboxide or the like is preferably used.

【0019】なお、脱臭塔4で散水されたオゾン溶解水
は、塔底部からポンプ9により、配管17を経て抜き出
され、オゾン溶解塔3に返送される。
The ozone-dissolved water sprinkled in the deodorizing tower 4 is withdrawn from the bottom of the tower by the pump 9 through the pipe 17 and returned to the ozone-dissolving tower 3.

【0020】このようにオゾン溶解水を循環使用するこ
とで、水中に溶解した硫黄系臭気成分の分解生成物が増
加してpHが低下してくるため、適宜オゾン溶解水を系
外へ排出すると共に、配管18より水を補給してオゾン
溶解水のpHがほぼ一定になるように制御する。
By circulating and using the ozone-dissolved water in this way, the decomposition products of the sulfur-based odorous components dissolved in the water are increased and the pH is lowered, so that the ozone-dissolved water is appropriately discharged out of the system. At the same time, water is replenished from the pipe 18 to control the pH of the ozone-dissolved water to be substantially constant.

【0021】[0021]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。
EXAMPLES The present invention will be described more specifically with reference to Examples and Comparative Examples below.

【0022】実施例1 臭気成分として、H2S:5ppm,(CH32S:1
ppm,CH3SH:2ppm,(CH322:0.5
ppmを含む臭気0.15m3/minを図1に示す脱
臭装置で脱臭した。
Example 1 As an odor component, H 2 S: 5 ppm, (CH 3 ) 2 S: 1
ppm, CH 3 SH: 2 ppm, (CH 3 ) 2 S 2 : 0.5
An odor of 0.15 m 3 / min containing ppm was deodorized by the deodorizing device shown in FIG.

【0023】各部の仕様及び処理条件等は次の通りであ
る。
The specifications and processing conditions of each part are as follows.

【0024】 [オゾン発生機] オゾン発生量 :0.1kg−O/hr [オゾン溶解塔(散気筒)] 水深 :5m オゾン滞留時間(HRT):15min オゾン溶解水オゾン濃度 :5.0mg/L [脱臭塔] 触媒種 :ゼオライトにC を0.05g−C /g− 担体の割合で担持させたもの(ペレット形状で大きさは約 10mm) 触媒充填量 :4.5L 触媒充填高さ :2m 臭気のSV :2000hr−1 オゾン溶解水の散水量:150L/hr [オゾン分解・(触媒)塔] 触媒種 :マンガン触媒 得られた処理ガスの臭気成分濃度を調べたところ、いず
れも99.9%の高い除去率で除去されていることが確
認された。なお、オゾン溶解塔でのオゾン溶解効率は9
5%と非常に高く、また、オゾン使用率は99%以上で
あり、発生オゾンのほぼ全量が脱臭反応に有効利用され
たことが確認された。
[0024] [Ozone generator]         Ozone generation rate: 0.1kg-OThree/ Hr [Ozone dissolution tower (scattering cylinder)]         Water depth: 5m         Ozone retention time (HRT): 15 min         Ozone-dissolved water Ozone concentration: 5.0 mg / L [Deodorization tower]         Catalyst type: Zeolite Co ThreeOFour0.05 g-Co ThreeOFour/ G-                     Carried in the proportion of carrier (in pellet form, size is approx.                     10 mm)         Catalyst filling amount: 4.5L         Catalyst filling height: 2m         Odor SV: 2000hr-1         Sprinkling amount of ozone-dissolved water: 150 L / hr [Ozone decomposition / (catalyst) tower]             Catalyst type: Manganese catalyst When the odorous component concentration of the obtained treated gas was examined, it was found that
It is sure that these are also removed with a high removal rate of 99.9%.
It has been certified. The ozone dissolution efficiency in the ozone dissolution tower is 9
It is very high at 5%, and the ozone usage rate is 99% or more.
Yes, almost all of the generated ozone is effectively used for the deodorization reaction.
It was confirmed that

【0025】比較例1 実施例1において脱臭塔に触媒を充填する代りに、市販
のプラスチック充填材(形状及び大きさは実施例1で用
いた触媒とほぼ同等)を充填したこと以外は実施例1と
同様にして脱臭処理を行ったところ、各臭気成分の除去
率は95〜99%程度と低く、また、オゾンの使用率も
90%であった。
Comparative Example 1 An example except that the deodorization tower in Example 1 was filled with a commercially available plastic filler (shape and size are almost the same as those of the catalyst used in Example 1) instead of being filled with the catalyst. When the deodorizing process was performed in the same manner as in No. 1, the removal rate of each odorous component was as low as about 95 to 99%, and the usage rate of ozone was 90%.

【0026】この比較例において、臭気成分の除去率を
実施例1と同等にするためには、臭気のSVを1000
hr-1にまで低くする必要があった。この場合において
もオゾンの使用率の向上は認められなかった。
In this comparative example, in order to make the odorous component removal rate equal to that in Example 1, the odor SV is 1000.
It had to be lowered to hr -1 . Even in this case, no improvement in the usage rate of ozone was observed.

【0027】[0027]

【発明の効果】以上詳述した通り、本発明の脱臭装置に
よれば、オゾン利用効率及びオゾンによる臭気成分の酸
化分解効率を高め、極めて効率的な脱臭を行える。
As described above in detail, according to the deodorizing apparatus of the present invention, the efficiency of ozone utilization and the efficiency of oxidative decomposition of odorous components by ozone can be enhanced, and extremely efficient deodorization can be performed.

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

【図1】本発明の脱臭装置の実施の形態を示す系統図で
ある。
FIG. 1 is a system diagram showing an embodiment of a deodorizing device of the present invention.

【符号の説明】[Explanation of symbols]

1 酸素発生機 2 オゾン発生機 3 オゾン溶解塔 4 脱臭塔 6 触媒充填層 8 オゾン分解塔 1 oxygen generator 2 Ozone generator 3 ozone dissolution tower 4 deodorization tower 6 catalyst packed bed 8 ozone decomposition tower

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭51−17174(JP,A) 特開 昭58−89931(JP,A) 特開 昭54−119371(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 53/34 ─────────────────────────────────────────────────── ─── Continuation of front page (56) References JP-A-51-17174 (JP, A) JP-A-58-89931 (JP, A) JP-A-54-119371 (JP, A) (58) Field (Int.Cl. 7 , DB name) B01D 53/34

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 オゾン溶解水製造手段と、 触媒が充填された脱臭塔と、 該脱臭塔内に臭気を上向流通気する手段と、 該脱臭塔内の上部からオゾン溶解水を散水する手段と、 該脱臭塔から排出される排ガス中の残留オゾンを分解す
る手段とを備えてなることを特徴とする脱臭装置。
1. A means for producing ozone-dissolved water, a deodorizing tower filled with a catalyst, means for upwardly flowing odor into the deodorizing tower, and means for sprinkling ozone-dissolved water from the upper part of the deodorizing tower. And a means for decomposing residual ozone in the exhaust gas discharged from the deodorization tower.
【請求項2】 請求項1において、前記オゾン溶解水製
造手段がオゾン濃度2.0〜5.0mg/Lのオゾン溶
解水を得るためのものであることを特徴とする脱臭装
置。
2. The ozone-dissolved water product according to claim 1,
Manufacturing means is ozone dissolution with ozone concentration of 2.0-5.0 mg / L
Deodorizing device characterized by being for obtaining water dissolution
Place
【請求項3】 請求項1又は2において、該脱臭塔で散
水されたオゾン溶解水を循環使用するための循環手段
と、該オゾン溶解水のpHがほぼ一定になるように制御
するための制御手段とを備えたことを特徴とする脱臭装
置。
3. The deodorizing tower according to claim 1 or 2,
Circulating means for recycling hydrated ozone-dissolved water
And control so that the pH of the ozone-dissolved water becomes almost constant
Deodorizing device, characterized by comprising:
Place
【請求項4】 請求項1ないし3のいずれか1項におい
て、前記触媒が金属の酸化物を担体に5〜10重量%の
割合で担持した触媒であることを特徴とする脱臭装置。
4. The odor according to any one of claims 1 to 3.
The catalyst contains 5 to 10% by weight of metal oxide as a carrier.
A deodorizing device, characterized in that it is a catalyst supported in proportion.
JP28809198A 1998-10-09 1998-10-09 Deodorizing device Expired - Fee Related JP3395669B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP28809198A JP3395669B2 (en) 1998-10-09 1998-10-09 Deodorizing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP28809198A JP3395669B2 (en) 1998-10-09 1998-10-09 Deodorizing device

Publications (2)

Publication Number Publication Date
JP2000117047A JP2000117047A (en) 2000-04-25
JP3395669B2 true JP3395669B2 (en) 2003-04-14

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Application Number Title Priority Date Filing Date
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Country Link
JP (1) JP3395669B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101116189B1 (en) * 2011-10-31 2012-03-06 진우통상(주) Ductless dust collector using ozon water
JP5808663B2 (en) * 2011-12-16 2015-11-10 株式会社日立製作所 Method and apparatus for treating 1,4-dioxane in wastewater

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