JPH078989A - Method and apparatus for decolorizing of colored waste water - Google Patents

Method and apparatus for decolorizing of colored waste water

Info

Publication number
JPH078989A
JPH078989A JP18076993A JP18076993A JPH078989A JP H078989 A JPH078989 A JP H078989A JP 18076993 A JP18076993 A JP 18076993A JP 18076993 A JP18076993 A JP 18076993A JP H078989 A JPH078989 A JP H078989A
Authority
JP
Japan
Prior art keywords
tank
water
decolorizing
distribution
filling
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.)
Pending
Application number
JP18076993A
Other languages
Japanese (ja)
Inventor
Kozo Konishi
功三 小西
Keiji Taniguchi
敬次 谷口
Shoichi Chisaki
正一 地崎
Emio Shinpo
延峰雄 新保
Shuzo Fujii
修三 藤井
Yasuhiko Miyoshi
康彦 三好
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.)
Denka Consultant and Engineering Co Ltd
Original Assignee
Denka Consultant and Engineering 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 Denka Consultant and Engineering Co Ltd filed Critical Denka Consultant and Engineering Co Ltd
Priority to JP18076993A priority Critical patent/JPH078989A/en
Publication of JPH078989A publication Critical patent/JPH078989A/en
Pending legal-status Critical Current

Links

Classifications

    • Y02W10/12

Landscapes

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE:To provide a method and an apparatus wherein a mixed colored waste water derived from various dyes is decolorized economically without depending on a large-scale installation. CONSTITUTION:A colored waste water and a part of a treated water passed through a tank 2 packed with an anaerobic microorganism-immobilized carrier are circulated into the packed tank 2 through a distribution tank 3 and by introducing into an adjusting tank 1 and a decolorized treated water is obtd. from the distribution tank 3 and if necessary, this treated water can be completely decolorized by introducing additionally it into an aerobic microorganism treating apparatus.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、染料製造工場或いは
染色工場等から排出される着色廃水を脱色する方法及び
その装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for decolorizing colored wastewater discharged from a dye manufacturing factory or a dyeing factory.

【0002】[0002]

【従来の技術】染料、染色工場からの排出水は、種類の
異なる染料の混合液であるばかりでなく、色度が100
〜20,000程度とばらつきがあるため、従来の着色
廃水の脱色方法である活性炭吸着法、電気分解法、微生
物法等をそのまま適用することができない。一方、着色
廃水の規制は年々厳しくなり、最近では色度80以下
(排出水を80倍まで希釈したときの蒸留水と同等の透
明度)にすることが要求されるに至った。このため、工
場側では処理施設に莫大な投資が必要とされている。
2. Description of the Related Art The water discharged from dyestuffs and dyeing factories is not only a mixed solution of different types of dyestuffs, but also has a chromaticity of 100.
Since there is a variation of about 20,000, the conventional decolorization method of colored wastewater, such as the activated carbon adsorption method, the electrolysis method, the microorganism method, etc., cannot be applied as it is. On the other hand, regulations on colored wastewater have become stricter year by year, and recently, it has been required to set the chromaticity to 80 or less (transparency equivalent to distilled water when the discharged water is diluted up to 80 times). For this reason, a huge investment is required in the treatment facility on the factory side.

【0003】[0003]

【発明が解決しようとする課題】本発明者等は大型の設
備を必要とせず、且つ、運転コストの安い脱色装置と方
法について種々検討し研究した結果、実用されている殆
どの染料成分が嫌気性微生物によって分解され易いこ
と、着色排水中に比較的大量に存在する可溶性有機着色
成分と嫌気性微生物によって分解されない染料成分とが
混合されていても嫌気性微生物処理水が更に好気性微生
物処理によってほぼ完全に脱色される事実を確認すると
共にこれを工業的に実施することを可能にする手段とし
て微生物を固定化した担体の利用が有効であることを確
認して本発明に至ったものである。
DISCLOSURE OF INVENTION Problems to be Solved by the Invention As a result of various studies and researches on a decolorizing apparatus and method which do not require large-scale equipment and have low operating costs, the present inventors have found that most of the dye components in practical use are anaerobic. The anaerobic microbial treated water is further decomposed by the aerobic microbial treatment even if the soluble organic coloring component present in a relatively large amount in the colored waste water and the dye component not decomposed by the anaerobic microbial are mixed. The present invention was achieved by confirming the fact that almost complete decolorization and confirming that the use of a carrier on which microorganisms are immobilized is effective as means for enabling this to be carried out industrially. .

【0004】[0004]

【課題を解決するための手段】本発明方法は、廃水中の
着色成分の主成分が可溶性有機染料の場合においては、
粉状無機物質によって被覆されたポリマ粒子表面に嫌気
性菌を固定化した顆粒状担体の充填層に上記着色廃水を
上向流で通水する方法である。この場合において導入す
る廃水に充填層を通過した処理水の一部を環流して供給
することが有効である。長期間充填層への廃水の導入に
より、該担体表面に嫌気性菌膜が肥大して吸着し、廃水
の導入時の圧力損失が大きくなった場合は、工業用水を
通水し逆洗する。また、着色廃水が嫌気性菌で分解され
ない可溶性有機染料及び他の成分を含む場合は、その後
に好気性菌を固定化した顆粒状担体の充填流動層に通水
して処理する方法である。本発明において顆粒状担体を
構成するポリマー粒子は例えば完全鹸化PVAを撹拌下
で水を結合剤として造粒し、表面を微粉末活性炭でコー
ティングした顆粒状物質である(特公平1−6031
8)。微生物固定化担体は、上記ポリマー粒子の吸水に
伴う膨潤作用を利用して嫌気性微生物又は好気性微生物
を培養した液中に約1昼夜浸漬することによって前記無
機物質被覆層に吸着固定化したものである。
According to the method of the present invention, when the main component of the coloring component in the wastewater is a soluble organic dye,
This is a method in which the colored wastewater is passed in an upward flow through a packed bed of a granular carrier having anaerobic bacteria immobilized on the surface of polymer particles coated with a powdery inorganic substance. In this case, it is effective to recirculate and supply a part of the treated water that has passed through the packed bed to the waste water to be introduced. When the waste water is introduced into the packed bed for a long period of time and the anaerobic pellicle is enlarged and adsorbed on the surface of the carrier, and the pressure loss at the time of introduction of the waste water becomes large, industrial water is passed through and backwashed. When the colored wastewater contains a soluble organic dye and other components which are not decomposed by anaerobic bacteria, it is a method in which water is then passed through a packed fluidized bed of a granular carrier on which aerobic bacteria are immobilized for treatment. In the present invention, the polymer particles constituting the granular carrier are, for example, a granular substance obtained by granulating fully saponified PVA with stirring using water as a binder and coating the surface with fine powder activated carbon (Japanese Patent Publication No. 1-6031).
8). The microorganism-immobilized carrier is one that is adsorbed and immobilized on the inorganic substance coating layer by immersing it in a liquid in which an anaerobic microorganism or an aerobic microorganism is cultured for about one day and night by utilizing the swelling action of the above-mentioned polymer particles due to water absorption. Is.

【0005】[0005]

【実施例】本発明の嫌気性微生物を固定化した担体を利
用した生物脱色装置は図1の如く調整槽1、嫌気性微生
物固定化担体充填槽2、分配槽3及び処理水槽4の槽類
を接続して構成され、調整槽1には廃水導入管11から
着色廃水と、充填槽2で脱色処理された処理水が分配槽
3から環流管12を通して導入される。上記混合水はフ
ィードポンプ10によって充填槽2の下部導入口22に
送給される。充填槽2には嫌気性微生物を固定化した顆
粒状担体を充填した充填槽21が設けられ、槽の上面に
は排気弁23が設けられている。13は逆洗時の排水管
である。24は排出管であって、充填槽の上部に連結さ
れ、分配槽3への供給管となる。31は処理水導管、5
0は逆洗用の工業用水導入管であって逆洗時にポンプ5
1によって逆洗水を充填槽2の導入口22に導入する。
図2は、図1に示した嫌気性生物処理装置の後段に接続
する好気性生物処理装置であって、6は三相流動槽であ
って上部から分配槽3からの一次脱色処理水を導入し、
好気性微生物固定化担体61が充填され、底部に曝気手
段62を備えている。63はブロワー、64は傾斜壁、
65はドラフト板、66は整流板、67は担体沈降部、
68は汚泥沈降槽7への導水管である。沈降槽は、嫌気
性微生物と好気性微生物の生物凝集によって生成した汚
泥を沈降分離する役目をする。71は溢流管、72は汚
泥取出管である。8は処理水槽であって、処理水は完全
脱色されている。上記装置において、嫌気性担体充填層
への通水速度は、含有される染料の生物分解速度に対応
させて決められるが、反応性酸性染料の場合、該担体充
填層に対する滞留時間の実験値は1〜2Hrである。ま
た、好気性流動層の通水速度は、分散染料の場合、該担
体の充填率約20%の循環流動層に対する滞留時間の実
験値は0.5〜1Hrである。
EXAMPLE A biological decolorizing apparatus using a carrier on which anaerobic microorganisms are immobilized according to the present invention is a tank including an adjusting tank 1, an anaerobic microorganisms-immobilized carrier filling tank 2, a distribution tank 3 and a treated water tank 4 as shown in FIG. The colored wastewater and the treated water decolorized in the filling tank 2 are introduced into the adjusting tank 1 from the distribution tank 3 through the reflux pipe 12 into the adjusting tank 1. The mixed water is fed to the lower introduction port 22 of the filling tank 2 by the feed pump 10. The filling tank 2 is provided with a filling tank 21 filled with a granular carrier in which anaerobic microorganisms are immobilized, and an exhaust valve 23 is provided on the upper surface of the tank. Reference numeral 13 is a drain pipe at the time of backwashing. A discharge pipe 24 is connected to the upper portion of the filling tank and serves as a supply pipe to the distribution tank 3. 31 is a treated water conduit, 5
Reference numeral 0 is an industrial water introduction pipe for backwashing, and a pump 5 is used for backwashing.
1, the backwash water is introduced into the inlet 22 of the filling tank 2.
2 is an aerobic biological treatment apparatus connected to the latter stage of the anaerobic biological treatment apparatus shown in FIG. 1, 6 is a three-phase flow tank, and the primary decolorized treated water from the distribution tank 3 is introduced from the upper part. Then
An aerobic microorganisms-immobilized carrier 61 is filled and an aeration means 62 is provided at the bottom. 63 is a blower, 64 is an inclined wall,
65 is a draft plate, 66 is a straightening plate, 67 is a carrier settling section,
68 is a water conduit to the sludge settling tank 7. The settling tank serves to settle and separate sludge generated by bioaggregation of anaerobic microorganisms and aerobic microorganisms. Reference numeral 71 is an overflow pipe, and 72 is a sludge extraction pipe. Reference numeral 8 is a treated water tank, in which the treated water is completely decolorized. In the above apparatus, the water flow rate to the anaerobic carrier packed bed is determined in accordance with the biodegradation rate of the dye contained therein. It is 1-2 Hr. Regarding the water flow rate in the aerobic fluidized bed, in the case of the disperse dye, the experimental value of the residence time in the circulating fluidized bed with the carrier filling rate of about 20% is 0.5 to 1 hr.

【0006】[0006]

【試験例1】図1の装置に、C.I.Reactive
Red 120反応性酸性染料廃水を通水した。充填
槽2の容量を100L(直径35cm,高さ120c
m)として嫌気性微生物固定化担体50Lを充填し、上
記染料廃水と循環処理水の合計水量を100L/Hrに
して供給した。脱色処理した結果は次表の如くであっ
た。
[Test Example 1] The apparatus of FIG. I. Reactive
Red 120 reactive acid dye wastewater was passed through. The capacity of the filling tank 2 is 100 L (diameter 35 cm, height 120 c
As m), 50 L of the anaerobic microorganisms-immobilized carrier was filled, and the total amount of the dye wastewater and the circulating treated water was supplied at 100 L / Hr. The results of the decolorization treatment are shown in the following table.

【0007】[0007]

【表1】 希釈度:蒸留水を対照液にして、着色廃水又は脱色処理
水を蒸留水で希釈して対照液と同等の透明度にする希釈
倍数 吸光度(1):波長560Nmにおける吸光度
[Table 1] Dilution degree: Dilution water is used as a control solution, and coloring waste water or decolorized water is diluted with distilled water to obtain transparency equivalent to that of the control solution. Absorbance (1): Absorbance at wavelength of 560 Nm

【0008】[0008]

【試験例2】図1の装置にC.I.Reactive
Red 120及びC.I.Disperse Yel
low分散染料の混合廃水を試験例1と同条件で処理し
た後、図2の三相流動槽6の容量を12.5Lとして好
気性微生物固定化担体5Lを充填し、前記染料廃水に相
当する水量の嫌気性処理水を供給した。脱色処理した結
果は次表の如くであった。
[Test Example 2] The apparatus of FIG. I. Reactive
Red 120 and C.I. I. Disperse Yel
After treating the mixed wastewater of low disperse dye under the same conditions as in Test Example 1, the volume of the three-phase flow tank 6 in FIG. 2 was set to 12.5 L, and 5 L of aerobic microorganism-immobilized carrier was filled to correspond to the dye wastewater. A quantity of anaerobic treated water was supplied. The results of the decolorization treatment are shown in the following table.

【0009】[0009]

【表2】 吸光度(2):波長403Nmにおける吸光度[Table 2] Absorbance (2): Absorbance at a wavelength of 403 Nm

【0010】[0010]

【効果】本発明によれば可溶性染料による着色廃水は図
1の装置及び方法によって効率良く脱色することが可能
であり、更に各種の染料等による混合着色廃水も図2の
装置及び方法を付加することによって従来法によっては
期待できない顕著な脱色能力を発揮させることができ
る。本発明において顆粒担体に微生物膜が付着して肥厚
したり、他の夾雑物が付着した場合は逆洗によって容易
に再生できるからランニングコストを低廉化でき、従来
設備と比較して極めて経済的な脱色装置を提供できる。
[Effects] According to the present invention, the coloring wastewater with the soluble dye can be efficiently decolorized by the apparatus and method of FIG. 1, and the mixed coloring wastewater with various dyes and the like also has the apparatus and method of FIG. As a result, a remarkable decolorizing ability that cannot be expected by the conventional method can be exhibited. In the present invention, the microbial membrane adheres to the granule carrier to thicken it, or when other contaminants adhere to it, it can be easily regenerated by backwashing so that the running cost can be reduced and it is extremely economical compared to conventional equipment. A decolorizing device can be provided.

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

【図1】嫌気性微生物脱色処理装置の概要図。FIG. 1 is a schematic diagram of an anaerobic microbial decolorization treatment apparatus.

【図2】図1の装置の後段に設置する好気性微生物脱色
装置の概要図。
FIG. 2 is a schematic diagram of an aerobic microbial decolorizing device installed in the latter stage of the device of FIG.

【符号の説明】[Explanation of symbols]

1 廃水及び処理水一部環流水混合貯水槽 2 嫌気性微生物固定化担体充填槽 3 分配槽 6 好気性担体充填三相流動槽 7 沈降槽 1 Waste water and treated water Partly circulating water mixed water storage tank 2 Anaerobic microbial immobilization carrier filling tank 3 Distribution tank 6 Aerobic carrier filling three-phase flow tank 7 Sedimentation tank

フロントページの続き (72)発明者 新保 延峰雄 東京都中央区八丁堀2−16−3 デンカエ ンジニアリング株式会社内 (72)発明者 藤井 修三 東京都中央区八丁堀2−16−3 デンカエ ンジニアリング株式会社内 (72)発明者 三好 康彦 東京都調布市深大寺北町2−9−10 ハウ ス中山101Front page continuation (72) Inventor Nobumine Shinbo 2-16-3 Hatchobori, Chuo-ku, Tokyo Denka Engineering Co., Ltd. (72) Inventor Shuzo Fujii 2-16-3 Hatchobori, Chuo-ku, Tokyo Denka Engineering Co., Ltd. (72) Inventor Yasuhiko Miyoshi 2-9-10 Kita-cho, Jindaiji, Chofu-shi, Tokyo House 101, Nakayama

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 調整槽と嫌気性微生物固定化担体が充填
された充填槽と分配槽が接続された装置において、前記
調整槽において着色廃水と前記分配槽からの処理水の一
部が環流水として混合され、該混合液を前記充填槽の下
部導入口に上向流として通水することを特徴とする着色
廃水の脱色方法。
1. An apparatus in which an adjusting tank, a filling tank filled with an anaerobic microorganisms-immobilized carrier and a distribution tank are connected to each other, the colored waste water in the adjusting tank and a part of the treated water from the distribution tank are reflux water. A method for decolorizing colored wastewater, characterized in that the mixed liquid is passed as an upward flow to the lower inlet of the filling tank.
【請求項2】 調整槽と嫌気性微生物固定化担体が充填
された充填槽と分配槽及び好気性微生物固定化担体が充
填された三相流動槽が直列に接続されて構成された装置
において、前記調整槽において着色廃水と前記分配槽か
らの処理水の一部が環流水として混合され、該混合液を
前記充填槽の下部導入口に上向流として通水すると共に
前記分配槽の処理水を前記三相流動槽に通水して脱色処
理することを特徴とする着色廃水の脱色方法。
2. An apparatus comprising a regulating tank, a filling tank filled with an anaerobic microorganisms-immobilized carrier, a distribution tank, and a three-phase flow tank filled with an aerobic microorganisms-immobilized carrier, which are connected in series. Colored wastewater and a part of the treated water from the distribution tank are mixed as reflux water in the adjustment tank, and the mixed liquid is passed as an upward flow to the lower inlet of the filling tank, and the treated water of the distribution tank is also supplied. A method for decolorizing colored wastewater, characterized in that the decolorizing treatment is carried out by passing water through the three-phase flow tank.
【請求項3】 調整槽と嫌気性微生物固定化担体が充填
された充填槽と分配槽が直列に接続されると共に前記分
配槽から前記調整槽に環流管が配設されて構成されてな
る着色廃水の脱色装置。
3. A coloring formed by connecting a regulating tank, a filling tank filled with an anaerobic microorganisms-immobilized carrier and a distributing tank in series, and arranging a reflux pipe from the distributing tank to the adjusting tank. Waste water decolorizing device.
【請求項4】 調整槽と嫌気性微生物固定化担体が充填
された充填槽と分配槽及び好気性微生物固定化担体が充
填された三相流動槽が直列に接続されると共に前記分配
槽から前記調整槽に環流管が配設されて構成されてなる
着色廃水の脱色装置。
4. An adjusting tank, a filling tank filled with an anaerobic microorganisms-immobilized carrier, a distribution tank, and a three-phase flow tank filled with an aerobic microorganisms-immobilized carrier are connected in series, and the distribution tank is used to A decolorizing device for colored wastewater, which comprises a circulation tank arranged in an adjusting tank.
JP18076993A 1993-06-25 1993-06-25 Method and apparatus for decolorizing of colored waste water Pending JPH078989A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP18076993A JPH078989A (en) 1993-06-25 1993-06-25 Method and apparatus for decolorizing of colored waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP18076993A JPH078989A (en) 1993-06-25 1993-06-25 Method and apparatus for decolorizing of colored waste water

Publications (1)

Publication Number Publication Date
JPH078989A true JPH078989A (en) 1995-01-13

Family

ID=16089008

Family Applications (1)

Application Number Title Priority Date Filing Date
JP18076993A Pending JPH078989A (en) 1993-06-25 1993-06-25 Method and apparatus for decolorizing of colored waste water

Country Status (1)

Country Link
JP (1) JPH078989A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100325024B1 (en) * 1999-12-17 2002-02-25 김동우 Method of treating dye containing waste water
JP2004082107A (en) * 2002-06-24 2004-03-18 Kuraray Co Ltd Equipment and method for treating waste water containing nitrogen-containing dyestuff
JP2012076001A (en) * 2010-09-30 2012-04-19 Kuraray Co Ltd Anaerobic wastewater treatment apparatus
KR101418650B1 (en) * 2012-10-23 2014-07-10 강민구 Anaerobe digestor and operating method for anaerobe digest
CN104129848A (en) * 2014-07-02 2014-11-05 山东太平洋环保有限公司 Cassava alcohol waste water mash anaerobic high-temperature fermentation cylinder water distributing system
CN104591484A (en) * 2014-12-30 2015-05-06 东莞市蓝天碧水环境科技工程有限公司 Enzyme catalyzed oxidation process for printing and dyeing wastewater

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Publication number Priority date Publication date Assignee Title
JPS6125697A (en) * 1984-07-13 1986-02-04 Hitachi Plant Eng & Constr Co Ltd Denitrification apparatus for waste water
JPS62102897A (en) * 1985-10-28 1987-05-13 Hitachi Zosen Corp Treatment of organic waste water containing colored material
JPH04341397A (en) * 1991-05-20 1992-11-27 Shimizu Corp Methane fermentation treatment apparatus and methane fermentation method

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6125697A (en) * 1984-07-13 1986-02-04 Hitachi Plant Eng & Constr Co Ltd Denitrification apparatus for waste water
JPS62102897A (en) * 1985-10-28 1987-05-13 Hitachi Zosen Corp Treatment of organic waste water containing colored material
JPH04341397A (en) * 1991-05-20 1992-11-27 Shimizu Corp Methane fermentation treatment apparatus and methane fermentation method

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100325024B1 (en) * 1999-12-17 2002-02-25 김동우 Method of treating dye containing waste water
JP2004082107A (en) * 2002-06-24 2004-03-18 Kuraray Co Ltd Equipment and method for treating waste water containing nitrogen-containing dyestuff
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