JPS61141995A - Treatment of waste water containing water-soluble dye - Google Patents

Treatment of waste water containing water-soluble dye

Info

Publication number
JPS61141995A
JPS61141995A JP26305484A JP26305484A JPS61141995A JP S61141995 A JPS61141995 A JP S61141995A JP 26305484 A JP26305484 A JP 26305484A JP 26305484 A JP26305484 A JP 26305484A JP S61141995 A JPS61141995 A JP S61141995A
Authority
JP
Japan
Prior art keywords
water
treatment
wastewater
dye
soluble dye
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
JP26305484A
Other languages
Japanese (ja)
Inventor
Akihiro Kadoi
門井 明博
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.)
SHINYUU KASEI KK
Mitsubishi Kasei Corp
Original Assignee
SHINYUU KASEI KK
Mitsubishi Kasei Corp
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 SHINYUU KASEI KK, Mitsubishi Kasei Corp filed Critical SHINYUU KASEI KK
Priority to JP26305484A priority Critical patent/JPS61141995A/en
Publication of JPS61141995A publication Critical patent/JPS61141995A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PURPOSE:To sufficiently perform the removal of a water-soluble dye, by adding a magnesium compound to waste water containing the water-soluble dye and subsequently making said waste water alkaline. CONSTITUTION:300-3000 ppm of a magnesium compound is added to waste water containing a water-soluble dye. subsequently, an alkali compound such as caustic soda, caustic potash or soda ash is added to waste water to adjust the pH thereof to 10-14 to sediment and separate the dye which is, in turn, separated and removed by filtering or centrifual separation.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は水溶性染料含有廃水の処理方法に関するもので
ある。
DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a method for treating wastewater containing water-soluble dyes.

(従来の技術) 従来、水溶性染料含有廃水の脱色方法としては、活性炭
吸着処理方法やオゾン酸化処理方法が知られている。
(Prior Art) Conventionally, activated carbon adsorption treatment methods and ozone oxidation treatment methods are known as methods for decolorizing wastewater containing water-soluble dyes.

(発明が解決しようとする問題点) しかし、これらの従来法は、設備が複雑であり、また操
作が繁雑であシ、しかも染料着色の除去を充分に行なう
ことが困難である。
(Problems to be Solved by the Invention) However, these conventional methods require complicated equipment and complicated operations, and furthermore, it is difficult to remove dye coloration sufficiently.

(発明の目的) 本発明は、水溶性染料を含有する廃水を簡単な操作によ
シ染料の着色を除去する処理方法を提供することを目的
とする。
(Objective of the Invention) An object of the present invention is to provide a method for treating wastewater containing a water-soluble dye to remove the coloring of the dye by a simple operation.

(問題点を解決するための手段) 本発明は、水溶性染料を含有する廃水にマグネシウム化
合物を添加し、次いで該廃水をアルカリ性にすることに
より脱色することを特徴とする水溶性染料含有廃水の処
理方法を要旨とする。
(Means for Solving the Problems) The present invention is a method of decolorizing wastewater containing water-soluble dyes by adding a magnesium compound to the wastewater containing water-soluble dyes and then making the wastewater alkaline. The gist is the processing method.

本発明の対象とする水溶性染料としては、反応染料、直
接染料、酸性染料などをあげることができる。これらは
一般に使用されているものでよく、たとえば反応染料と
しては、C,L Reactive Yellow(リ
アクティブ イエロー)57、C,I@ Reacti
veBlue (リアクティブ ブルー 15 、 C
s1. ReactiveBlue (リアクティブ 
ブルー)112)C,1,ReactiveBlack
 (リアクティブブラック)5等が、直接染料としては
C,1,Direct Red (ダイレクト v、t
ド)23、C,L Direct Brown (ダイ
レクト ブラウン)210等が、また酸性染料としては
C,I。Ac1d Red(アシド レッド)158、
C,1,Ac1d Brown (アシド ブラウン)
333等があげられ、さらに詳しくは新版染料便覧〔有
機合成化学協会編、丸善株式%式%5 〜390頁(直接染料)及び第391〜526頁(酸性
染料)に記載された染料等があげられる。
Water-soluble dyes that are the object of the present invention include reactive dyes, direct dyes, acid dyes, and the like. These may be those commonly used. For example, as reactive dyes, C,L Reactive Yellow 57, C,I@Reacti
veBlue (Reactive Blue 15, C
s1. ReactiveBlue
Blue) 112) C, 1, Reactive Black
(Reactive Black) 5 etc., direct dyes are C, 1, Direct Red (Direct v, t
C) 23, C, L Direct Brown 210, etc., and acid dyes such as C, I. Ac1d Red 158,
C,1,Ac1d Brown
333, etc., and for more details, the dyes etc. listed in the new edition dye handbook [edited by the Organic Synthetic Chemistry Association, Maruzen Stock % Formula %, pages 5 to 390 (direct dyes) and pages 391 to 526 (acid dyes). It will be done.

本発明のマグネシウム化合物としては、一般式g−X 〔式中、XはC42)SO4、(OH)2)PO4、H
PO4H2PO4、HCO3、No5、(CH2COO
)2.0204等を示す。〕で表わされる化合物があげ
られる。
The magnesium compound of the present invention has the general formula g-X [wherein, X is C42]SO4, (OH)2)PO4, H
PO4H2PO4, HCO3, No5, (CH2COO
)2.0204 etc. ] Examples include compounds represented by:

マグネシウム化合物を添加した廃水をアルカリ性にする
アルカリ剤としては、苛性ソーダ、苛性カリ、ソーダ灰
、消石灰などがあげられる。
Examples of alkaline agents that make wastewater containing magnesium compounds alkaline include caustic soda, caustic potash, soda ash, and slaked lime.

マグネシウム化合物の添加量としては、一般的に300
〜3000 ppmの範囲であり、アルカリの程度とし
ては、pH10〜14の範囲であるが、通常はpH10
,5〜12.0の範囲が適当である。
The amount of magnesium compound added is generally 300
~3000 ppm, and the degree of alkalinity is in the range of pH 10 to 14, but usually pH 10
, 5 to 12.0 is appropriate.

マグネシウム化合物は水溶液として添加するのが好まし
いが、完全に溶解した状態でなくても、たとえば多少の
不溶解物が存在していても差支えがない。
Although it is preferable to add the magnesium compound as an aqueous solution, there is no problem even if the magnesium compound is not completely dissolved, for example, some undissolved matter may be present.

本発明のマグネシウム化合物処理後に、或いは該マグネ
シウム化合物処理と同時に、従来一般に廃水処理に使用
されている無機或いは有機高分子凝集剤で処理を行なっ
てもよい。
After the treatment with the magnesium compound of the present invention, or simultaneously with the treatment with the magnesium compound, treatment may be performed with an inorganic or organic polymer flocculant conventionally generally used in wastewater treatment.

無機凝集剤としては、硫酸バンド、ポリ塩化アルミニウ
ム、硫酸第一鉄等があげられる。
Examples of inorganic flocculants include aluminum sulfate, polyaluminum chloride, ferrous sulfate, and the like.

有機高分子凝集剤としては、ポリアクリルアマイド(ノ
ニオン)〔−CH2・CH−CONH2〕。、ポリアク
リルアマイド(アニオン)C−CH2・CH−Co・N
H2−)。・〔−CH2・CH−CO・0Na−〕□、
ポリアクリル酸ソーダ(アニオン) [−CH2・CM
−Co−ONa−) n等があげられる。
As the organic polymer flocculant, polyacrylamide (nonionic) [-CH2.CH-CONH2] is used. , polyacrylamide (anion) C-CH2・CH-Co・N
H2-).・[-CH2・CH-CO・0Na-]□,
Sodium polyacrylate (anion) [-CH2・CM
-Co-ONa-) n, etc.

本発明の水溶性染料を含有する廃水の処理方法を適用す
ることによシ、該水溶性染料はフロックとなって廃水よ
シ沈降分離されることになる。
By applying the method for treating wastewater containing water-soluble dyes of the present invention, the water-soluble dyes become flocs and are separated by sedimentation from the wastewater.

次いて、適当な分離操作、たとえば濾過、遠心沈降分離
等によ)該フロックを廃水よシ分離除去すればよい。
The flocs may then be separated and removed from the wastewater by an appropriate separation operation, such as filtration, centrifugal sedimentation, etc.

このように処理され、そして脱色された廃水は、そのま
ま、或いはさらに声調整、微生物処理等の処理を行なう
ことによシ、再利用、或いは放流等を行なうことができ
る。
The wastewater treated and decolorized in this manner can be reused or discharged as is, or after further treatment such as voice control or microbial treatment.

(作用効果) 本発明の水溶性染料を含有する廃水にマグネシウム化合
物を添加してアルカリ性にすることにより該染料が凝集
除法できる機構については、今のところ不明であるが、
マグネシウム化合物がアルカリ剤と反応して不溶化する
際に生ずる不溶性塩が該染料を抱合除去する性質がある
ものと考えられる。
(Operation and Effect) The mechanism by which the dye can be removed from coagulation by adding a magnesium compound to the wastewater containing the water-soluble dye of the present invention to make it alkaline is currently unknown.
It is thought that the insoluble salt produced when the magnesium compound reacts with an alkaline agent and becomes insolubilized has the property of conjugating and removing the dye.

本発明のマグネシウム化合物を水溶性染料含有廃水に添
加し、アルカリ性にする凝集処理法によシ、該水溶性染
料のほとんどを沈降除去することができるが、その際に
さらに副次的に該廃水のCODをも減少させることがで
きる。
By adding the magnesium compound of the present invention to wastewater containing a water-soluble dye and making it alkaline, most of the water-soluble dye can be sedimented and removed. COD can also be reduced.

(実施例等) 次に、実施例等をあげて本発明を説明するが、本発明は
実施例に限定されるものではない。
(Examples, etc.) Next, the present invention will be described with reference to Examples, but the present invention is not limited to the Examples.

なお、これらの例に記載の処理後の上澄液の着色の評価
は下記の基準にしたがって判定した。
The coloring of the supernatant liquid after the treatments described in these examples was evaluated according to the following criteria.

5級  全く着色なし 4級  わずかに着色している 3級  やや着色している 2級  やや着色が除かれている 1級  廃水原液と同じ着色である 実施例1 この例は反応染料含有廃水の処理例である。Grade 5: No coloring at all Grade 4: Slightly colored Grade 3: Slightly colored 2nd grade, some coloring has been removed Class 1: The same color as the wastewater undiluted solution Example 1 This example is an example of the treatment of wastewater containing reactive dyes.

C,1,Roactiva Yellow (リアクテ
ィブ イエロ)23を0.71/l 、C,1,−Re
active Red (リアクティブレッド)21を
0.71/l 、 C,1,Reactive Blu
e(リアクティブ ブルー)77を0.711/l 、
ソーダ灰2011/13 、及び芒硝5011/lを混
合溶解した染料溶液を60℃で60分間加熱し、これを
更に水で20倍に稀釈し、硫酸でPH9に調整したもの
を廃水原液とした。
C,1,Roactiva Yellow 23 at 0.71/l, C,1,-Re
active Red (reactive red) 21 at 0.71/l, C, 1, Reactive Blue
e (reactive blue) 77 at 0.711/l,
A dye solution in which soda ash 2011/13 and Glauber's salt 5011/l were mixed and dissolved was heated at 60° C. for 60 minutes, further diluted 20 times with water, and adjusted to pH 9 with sulfuric acid, which was used as a wastewater stock solution.

この廃水原液に塩化マグネシウム六水和物を塩化マグネ
シウムとして2000 ppmとなるように添加し、次
いで10%苛性ソーダ水溶液を加えて戸11.0に調整
したところ、約20分後にわずかに着色した上澄液(4
級)と沈でん(フロック)とに分離した。
Magnesium chloride hexahydrate was added to this wastewater stock solution to give a concentration of 2000 ppm as magnesium chloride, and then a 10% aqueous solution of caustic soda was added to adjust the temperature to 11.0. After about 20 minutes, a slightly colored supernatant was found. liquid (4
It was separated into floc) and floc.

参考例1 実施例1で得られた上澄液と沈でんとを充分に攪拌した
のち、アニオン系高分子凝集剤の辿りアクリルアミド(
三共化成株式会社商品名 サン7J?リ−305)を3
 ppmになるように添加して凝集処理を行なったとこ
ろ、その上澄液の着色度は実施例1の上澄液と変らなか
ったが、凝集速度が約1分と速くなシ、沈でんの沖過分
離が良好であった。
Reference Example 1 After thoroughly stirring the supernatant liquid and precipitate obtained in Example 1, the anionic polymer flocculant trace acrylamide (
Sankyo Kasei Co., Ltd. Product name Sun 7J? Lee-305) 3
ppm and flocculation treatment, the degree of coloration of the supernatant liquid was the same as that of the supernatant liquid of Example 1, but the flocculation speed was as fast as about 1 minute. Good over-separation was achieved.

比較例1 実施例1の廃水原液に硫酸バンド水溶液を硫酸アルミニ
ウムとして5000 plumになるように添加し、次
いで10%苛性ソーダ水溶液を加えてpH6,Bとし、
この液に参考例1に記載のアニオン系高分子凝集剤を3
 ppmになるように添加して凝集処理を行なったとこ
ろ、上澄液の着色は廃水原液と同じ(1級)であった。
Comparative Example 1 A sulfuric acid band aqueous solution was added as aluminum sulfate to the wastewater stock solution of Example 1 to a total amount of 5000 plum, and then a 10% caustic soda aqueous solution was added to adjust the pH to 6.B.
To this liquid, add 3 ml of the anionic polymer flocculant described in Reference Example 1.
When a flocculation treatment was carried out by adding ppm, the coloring of the supernatant liquid was the same as that of the waste water stock solution (first grade).

実施例2 この例も反応染料含有廃水の処理例である。Example 2 This example is also an example of treatment of wastewater containing reactive dye.

CAL Reactive Yallow (リアクテ
ィブ イエo−)’84を0.71/l 、 C,1,
Reac目veB1ue(リアクティブ ゾル−)5を
0.7 El/IJ 、 C,1,Reae目veRe
d (リアクティブ レッド)120を0.71/13
 。
CAL Reactive Yellow '84 0.71/l, C,1,
Reac's veB1ue (reactive sol-) 5 to 0.7 El/IJ, C,1, Reac's veRe
d (reactive red) 120 0.71/13
.

ソーダ灰2011/13 、及び芒硝50g/lを混合
溶解した染料溶液を80℃で60分間加熱し、これを更
に水で20倍に稀釈し、硫酸でpH9に調整したものを
廃水原液とした。
A dye solution in which soda ash 2011/13 and 50 g/l of Glauber's salt were mixed and dissolved was heated at 80° C. for 60 minutes, further diluted 20 times with water, and adjusted to pH 9 with sulfuric acid to obtain a wastewater stock solution.

以下、実施例1と同様の処理を行なったところ、上澄液
の着色は4級であった。
Thereafter, the same treatment as in Example 1 was carried out, and the coloring of the supernatant liquid was grade 4.

比較例2 実施例2において使用した廃水原液に比較例1と同様に
獣酸バンドで処理した。その上澄液の着色は1級であっ
た。
Comparative Example 2 The wastewater stock solution used in Example 2 was treated with animal acid band in the same manner as in Comparative Example 1. The coloring of the supernatant liquid was first grade.

実施例3 この例は直接染料含有廃水の処理例である。Example 3 This example is of the treatment of wastewater containing direct dyes.

C,1,Direct Yellow (ダイレクト 
イエ0−)86を0.71/13 、 C,I。Dir
ect Red (ダイレクト レッド)243を0.
71/lSC,I* Direct Blue (ダイ
レクト ブルー)192を0.7 g/l、及び芒硝2
0V4を混合溶解した染料溶液を95℃で60分間加熱
し、これを更に水で20倍に稀釈したものを廃水原液と
した。
C, 1, Direct Yellow
Ye0-)86 0.71/13, C,I. Dir
ect Red (Direct Red) 243 to 0.
71/lSC, I* Direct Blue 192 at 0.7 g/l, and Glauber's Salt 2
A dye solution in which 0V4 was mixed and dissolved was heated at 95° C. for 60 minutes, and this was further diluted 20 times with water to obtain a wastewater stock solution.

以下、実施例1と同様の処理を行なったところ、その上
澄液の着色は4級であった。
Thereafter, the same treatment as in Example 1 was carried out, and the coloring of the supernatant liquid was grade 4.

比較例3 実施例3において使用した廃水原液に比較例1と同様に
硫酸バンドで処理したところ、その上澄液の着色は2級
であった。
Comparative Example 3 When the waste water stock solution used in Example 3 was treated with sulfate band in the same manner as in Comparative Example 1, the coloring of the supernatant liquid was second grade.

実施例4 この例は酸性染料含有廃水の処理例である。Example 4 This example is an example of treatment of acid dye-containing wastewater.

C,1,Ac1d Red (アシド レッド)145
を0.51/11 、 C,1,Ac1d Black
 (アシド ブラック)107を1.5Vノ混合溶解し
た染料溶液を95℃で60分間加熱し、これを更に水で
20倍に稀釈したものを廃水原液とした。
C, 1, Ac1d Red (Acid Red) 145
0.51/11, C, 1, Ac1d Black
A dye solution in which Acid Black 107 was mixed and dissolved at 1.5 V was heated at 95° C. for 60 minutes, and this was further diluted 20 times with water to obtain a wastewater stock solution.

以下、実施例1と同様の処理をしたところ、上澄液の着
色は4級であった。
Thereafter, the same treatment as in Example 1 was carried out, and the coloring of the supernatant liquid was grade 4.

比較例4 実施例4の廃水原液を使用し、比較例1と同様に硫酸バ
ンドで処理をしたところ、その上澄液の着色は1級であ
った。
Comparative Example 4 When the waste water stock solution of Example 4 was treated with sulfuric acid band in the same manner as in Comparative Example 1, the coloring of the supernatant liquid was first grade.

実施例5 ダイアミラー エロー 5−RNを2 g/l 1 ソ
ーダ灰を2011/13、及び芒硝501//11を混
合溶解した染料溶液を60℃で60分間加熱し、これを
更に水で20倍に稀釈し、硫酸でpHgに調整したもの
を廃水原液とした。
Example 5 Diamirror Yellow 5-RN at 2 g/l 1 A dye solution in which soda ash 2011/13 and Glauber's Salt 501//11 were mixed and dissolved was heated at 60°C for 60 minutes, and then diluted 20 times with water. The wastewater stock solution was prepared by diluting the solution and adjusting the pH with sulfuric acid.

この廃水原液に塩化マグネシウム、硫酸マグネシウム、
硝酸マグネシウム、酢酸マグネシウム、リン酸ブグネシ
ウム、炭酸マグネシウム、水酸化マグネシウム、又はシ
ュウ酸マグネシウムが各々2000 ppmになるよう
にそれぞれの化合物を添加し、そのほかは実施例1と同
様に処理を行ったところ、それぞれの上澄液の着色は下
記のとおりであった。
Magnesium chloride, magnesium sulfate,
Magnesium nitrate, magnesium acetate, bugnesium phosphate, magnesium carbonate, magnesium hydroxide, or magnesium oxalate were added to each compound so that the amount was 2000 ppm, and the process was otherwise carried out in the same manner as in Example 1. The coloring of each supernatant was as follows.

Claims (3)

【特許請求の範囲】[Claims] (1)水溶性染料を含有する廃水にマグネシウム化合物
を添加し、次いで該廃水をアルカリ性にすることにより
脱色することを特徴とする水溶性染料含有廃水の処理方
法。
(1) A method for treating wastewater containing water-soluble dyes, which comprises adding a magnesium compound to wastewater containing water-soluble dyes, and then decolorizing the wastewater by making it alkaline.
(2)特許請求の範囲第1項の水溶性染料含有廃水の処
理方法において、アルカリ性がpH10以上である方法
(2) A method for treating water-soluble dye-containing wastewater according to claim 1, wherein the alkalinity is pH 10 or higher.
(3)特許請求の範囲第1項の水溶性染料含有廃水の処
理方法において、アルカリ性がpH10.5〜12.0
の範囲である方法。
(3) In the method for treating water-soluble dye-containing wastewater according to claim 1, the alkaline pH is 10.5 to 12.0.
A method that is within the range of.
JP26305484A 1984-12-14 1984-12-14 Treatment of waste water containing water-soluble dye Pending JPS61141995A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26305484A JPS61141995A (en) 1984-12-14 1984-12-14 Treatment of waste water containing water-soluble dye

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26305484A JPS61141995A (en) 1984-12-14 1984-12-14 Treatment of waste water containing water-soluble dye

Publications (1)

Publication Number Publication Date
JPS61141995A true JPS61141995A (en) 1986-06-28

Family

ID=17384212

Family Applications (1)

Application Number Title Priority Date Filing Date
JP26305484A Pending JPS61141995A (en) 1984-12-14 1984-12-14 Treatment of waste water containing water-soluble dye

Country Status (1)

Country Link
JP (1) JPS61141995A (en)

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JP2012035183A (en) * 2010-08-05 2012-02-23 Ishii Shoji Kk Method for decoloring and purifying water
CN104193045A (en) * 2014-07-11 2014-12-10 奈曼明州化工科技有限公司 Active turquoise blue dye production wastewater reclamation process
CN108101179A (en) * 2017-12-28 2018-06-01 新疆水处理工程技术研究中心有限公司 A kind of composite decoloration flocculant and preparation method thereof

Citations (2)

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