JP2003093866A - Method and apparatus for treating dye waste liquid - Google Patents

Method and apparatus for treating dye waste liquid

Info

Publication number
JP2003093866A
JP2003093866A JP2001289820A JP2001289820A JP2003093866A JP 2003093866 A JP2003093866 A JP 2003093866A JP 2001289820 A JP2001289820 A JP 2001289820A JP 2001289820 A JP2001289820 A JP 2001289820A JP 2003093866 A JP2003093866 A JP 2003093866A
Authority
JP
Japan
Prior art keywords
dye
waste liquid
treatment
hydrothermal reaction
based waste
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
JP2001289820A
Other languages
Japanese (ja)
Inventor
Masatada Yamashita
正忠 山下
Ryuzo Hiraoka
龍三 平岡
Keiichi Miwa
敬一 三輪
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.)
IHI Corp
Original Assignee
IHI 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 IHI Corp filed Critical IHI Corp
Priority to JP2001289820A priority Critical patent/JP2003093866A/en
Publication of JP2003093866A publication Critical patent/JP2003093866A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/54Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids

Abstract

PROBLEM TO BE SOLVED: To provide a treatment method capable of satisfactorily treating dye waste liquid containing dyes and a treatment apparatus suitable for executing the treatment method. SOLUTION: The dye waste liquid containing the dyes is decomposed by a hydrothermal reaction under a subcritical water condition or a supercritical water condition.

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、毛染め液や衣類用
の染料などの染料を含む染料系廃液を処理する方法と、
この処理方法の実施に好適な処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating a dye-based waste liquid containing a dye such as a hair dye or a dye for clothes, and
The present invention relates to a processing apparatus suitable for carrying out this processing method.

【0002】[0002]

【従来の技術】一般に、染料を含む廃液の処理方法とし
ては、焼却処理や化学的酸化分解処理が知られている。
2. Description of the Related Art Generally, incineration treatment and chemical oxidative decomposition treatment are known as treatment methods for waste liquid containing a dye.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、焼却処
理では、排ガスとしてダイオキシンなどの有害物が発生
してしまうおそれがある。また、化学的酸化分解処理で
は、処理スペースが大規模となったり、処理時間が長く
なりやすい。
However, in the incineration process, harmful substances such as dioxins may be generated as exhaust gas. Further, in the chemical oxidative decomposition treatment, the treatment space tends to be large and the treatment time tends to be long.

【0004】本発明は、上述する事情に鑑みてなされた
ものであり、その目的は、染料を含む染料系廃液を良好
に処理することができる処理方法と、この処理方法の実
施に好適な処理装置を提供することにある。
The present invention has been made in view of the above circumstances, and an object thereof is a treatment method capable of favorably treating a dye waste liquid containing a dye, and a treatment suitable for carrying out this treatment method. To provide a device.

【0005】[0005]

【課題を解決するための手段】本発明の染料系廃液の処
理方法では、染料を含む染料系廃液を、亜臨界水条件あ
るいは超臨界水条件下の水熱反応により分解処理する水
熱反応処理工程を備えることを前記課題の解決手段とし
た。
In the method for treating a dye-based waste liquid according to the present invention, a hydrothermal reaction treatment for decomposing a dye-based waste liquid containing a dye by hydrothermal reaction under subcritical water conditions or supercritical water conditions. The provision of the steps was taken as a means for solving the above problems.

【0006】この処理方法によれば、染料系廃液を、亜
臨界水あるいは超臨界水下の水熱反応により分解処理す
ることにより、染料に含まれる有機分を良好に分解する
ことができる。
According to this treatment method, the organic waste contained in the dye can be satisfactorily decomposed by decomposing the dye-based waste liquid by hydrothermal reaction under subcritical water or supercritical water.

【0007】この場合において、分解処理された水熱反
応処理物を、湿式酸化処理する湿式酸化処理工程を備え
てもよい。
In this case, a wet oxidation treatment step of subjecting the decomposed hydrothermal reaction treated product to a wet oxidation treatment may be provided.

【0008】この場合、湿式酸化によって染料に含まれ
る有機分がさらに良好に分解される。
In this case, the organic matter contained in the dye is decomposed more favorably by the wet oxidation.

【0009】本発明の染料系廃液の処理装置では、染料
を含む染料系廃液を、亜臨界水条件あるいは超臨界水条
件下の水熱反応により分解処理する水熱反応処理装置を
備えることを前記課題の解決手段とした。
The dye waste liquid treatment apparatus of the present invention comprises a hydrothermal reaction treatment device for decomposing a dye waste liquid containing a dye by hydrothermal reaction under subcritical water conditions or supercritical water conditions. It was used as a solution to the problem.

【0010】この処理装置によれば、上記の処理方法を
実施できることから、染料に含まれる有機分を良好に分
解することができる。
According to this processing apparatus, since the above processing method can be carried out, the organic components contained in the dye can be decomposed satisfactorily.

【0011】この場合において、分解処理された水熱反
応処理物を、湿式酸化処理する湿式酸化処理装置を備え
てもよい。
In this case, a wet oxidation treatment device for performing wet oxidation treatment on the decomposed hydrothermal reaction treatment product may be provided.

【0012】この場合、湿式酸化によって染料に含まれ
る有機分がさらに良好に分解される。
In this case, the organic component contained in the dye is decomposed more favorably by the wet oxidation.

【0013】[0013]

【発明の実施の形態】以下、本発明を詳しく説明する。
図1は、本発明の染料系廃液の処理装置の一実施形態例
を説明するための概略構成図であり、図1中符号1は染
料系廃液の処理装置である。この処理装置1は、特に、
毛染め液や衣類用の染料などの染料を含む染料系廃液の
処理に好適なもので、染料系廃液を分解処理する水熱反
応処理装置2を備えて構成されている。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention is described in detail below.
FIG. 1 is a schematic configuration diagram for explaining an embodiment of an apparatus for treating a dye-based waste liquid according to the present invention. Reference numeral 1 in FIG. 1 is a treatment apparatus for a dye-based waste liquid. This processing device 1
It is suitable for treating a dye-based waste liquid containing a dye such as a hair dyeing liquid or a dye for clothes, and is provided with a hydrothermal reaction treatment device 2 for decomposing the dye-based waste liquid.

【0014】水熱反応処理装置2は、ポンプ等によって
反応室内に送られてきた廃液を、亜臨界水条件あるいは
超臨界水条件下、具体的には例えば150〜374℃、
0.48〜22MPaの亜臨界水条件もしくは22MP
a以上の超臨界水条件下、より好ましくは200〜28
0℃、1.55〜6.42MPaでの水熱反応によって
組成分解するものである。水熱反応処理装置2は、染料
系廃液を昇圧して反応室に送る昇圧手段としての昇圧ポ
ンプ、昇圧された染料系廃液の流量を制御するための流
量制御装置、水熱反応を促進させるために反応室内の染
料系廃液を攪拌するための攪拌装置、誘導過熱方式など
により反応室内を加熱する加熱装置、分解処理した水熱
反応処理物を下流側に排出可能な温度にまで冷却する熱
交換器などの冷却装置(いずれも図示せず)等を含んで
構成されている。
The hydrothermal reaction treatment device 2 treats the waste liquid sent into the reaction chamber by a pump or the like under subcritical water conditions or supercritical water conditions, specifically, 150 to 374 ° C., for example.
0.48-22MPa subcritical water condition or 22MP
a or more supercritical water conditions, more preferably 200 to 28
The composition is decomposed by a hydrothermal reaction at 0 ° C. and 1.55 to 6.42 MPa. The hydrothermal reaction treatment device 2 is a step-up pump as a pressurizing means for pressurizing the dye-based waste liquid and sending it to the reaction chamber, a flow rate control device for controlling the flow rate of the dye-based waste liquid that has been boosted, and for promoting the hydrothermal reaction. In addition, a stirring device for stirring the waste dye solution in the reaction chamber, a heating device that heats the reaction chamber by induction heating, etc., a heat exchange that cools the hydrothermal reaction product after decomposition to a temperature at which it can be discharged downstream. It is configured to include a cooling device (not shown) such as a container.

【0015】また、本例では、処理装置1は、上記水熱
反応処理装置2で分解処理された水熱反応処理物を、水
熱湿式酸化処理する水熱湿式酸化処理装置3を備えてい
る。なお、上記水熱反応処理装置2だけで染料系廃液が
十分に分解処理される場合には、水熱湿式酸化処理装置
3を備えなくてもよい。水熱湿式酸化処理装置3が必要
か否かは処理対象の染料系廃液に応じて適宜定められ
る。
Further, in this example, the processing apparatus 1 is provided with a hydrothermal wet oxidation processing apparatus 3 for performing hydrothermal wet oxidation processing on the hydrothermal reaction processed product decomposed by the hydrothermal reaction processing apparatus 2. . When the dye-based waste liquid is sufficiently decomposed only by the hydrothermal reaction treatment device 2, the hydrothermal wet oxidation treatment device 3 may not be provided. Whether or not the hydrothermal wet oxidation treatment apparatus 3 is necessary is appropriately determined according to the dye waste liquid to be treated.

【0016】水熱湿式酸化処理装置3は、水熱反応処理
後の処理物を、加熱・加圧して亜臨界水条件あるいは超
臨界水条件とし、このような反応条件に基づいて水熱反
応させるもので、反応性を高めるために反応室にラシヒ
リングやベルルサドルなどの充填物を充填したものであ
る。また、反応室には、CODを低減するのに有効な触
媒、すなわち処理対象によって適宜に選択される触媒
(例えば白金族元素)が、前記充填物間に、あるいは充
填物そのものとして充填されている。なお、水熱反応処
理後の処理物が十分に高い温度及び圧力を有している場
合にはそのエネルギーをそのまま利用し、加熱・加圧手
段を省略したり簡略化してもよい。
The hydrothermal wet oxidation treatment apparatus 3 heats and pressurizes the treated material after the hydrothermal reaction treatment to make it a subcritical water condition or a supercritical water condition, and causes a hydrothermal reaction based on such a reaction condition. The reaction chamber is filled with a material such as Raschig ring or berl saddle in order to enhance the reactivity. Further, the reaction chamber is filled with a catalyst effective for reducing COD, that is, a catalyst (for example, a platinum group element) appropriately selected depending on the object to be treated, between the packings or as the packing itself. . When the processed product after the hydrothermal reaction process has a sufficiently high temperature and pressure, the energy may be used as it is, and the heating / pressurizing means may be omitted or simplified.

【0017】次に、このような構成の染料系廃液の処理
装置1による処理方法に基づき、本発明の染料系廃液の
処理方法を説明する。まず、処理対象である染料系廃液
を、水熱反応処理装置2に導入する。そして、この水熱
反応処理装置2において、亜臨界水条件あるいは超臨界
水条件下、例えば150〜400℃、4.9〜220気
圧の亜臨界圧条件もしくは220気圧以上の超臨界圧条
件下、より好ましくは200〜280℃、1.55〜
6.42MPaで水熱反応を行い、染料系廃液を組成分
解する。この水熱反応により、染料に含まれる有機化合
物の高分子の結合が切断されて低分子化される。
Next, the method for treating the dye-based waste liquid of the present invention will be described based on the method for treating the dye-based waste liquid by the treating apparatus 1 having the above-mentioned structure. First, the dye waste liquid to be treated is introduced into the hydrothermal reaction treatment device 2. In the hydrothermal reaction treatment device 2, subcritical water conditions or supercritical water conditions, for example, 150 to 400 ° C., 4.9 to 220 atm subcritical pressure conditions or 220 atm supercritical pressure conditions, More preferably 200 to 280 ° C., 1.55
Hydrothermal reaction is performed at 6.42 MPa to decompose the composition of the dye-based waste liquid. By this hydrothermal reaction, the bond of the polymer of the organic compound contained in the dye is cut and the molecular weight is lowered.

【0018】次に、水熱反応処理装置2からの処理物を
水熱湿式酸化処理装置3に導入する。そして、ここで導
入した処理物を水熱湿式酸化処理することにより、染料
に含まれる有機分をさらに分解し、そのCOD(化学的
酸素要求量)を、放流基準の濃度以下に低減する。その
後、必要に応じて放流基準を満たすための処理を行った
後、この処理物を一般の下水、あるいは河川等に放流す
る。
Next, the treated product from the hydrothermal reaction treatment device 2 is introduced into the hydrothermal wet oxidation treatment device 3. Then, the treated matter introduced here is subjected to a hydrothermal wet oxidation treatment to further decompose the organic components contained in the dye, and reduce the COD (chemical oxygen demand amount) thereof to a concentration equal to or lower than the discharge standard concentration. After that, if necessary, the treated product is discharged to meet the discharge standard, and then the treated product is discharged into general sewage or a river.

【0019】このような染料系廃液の処理装置1とこれ
を用いてなる処理方法にあっては、亜臨界水条件あるい
は超臨界水条件下の水熱反応によって、染料系廃液を分
解処理するので、染料に含まれる有機分を良好に分解す
ることができる。また、水熱反応処理した処理物を水熱
湿式酸化処理することにより、染料に含まれる有機分を
完全に分解し、排水として放流処理することが可能とな
る。
In such a treatment apparatus 1 for a dye-based waste liquid and a treatment method using the same, the dye-based waste liquid is decomposed by hydrothermal reaction under subcritical water conditions or supercritical water conditions. The organic components contained in the dye can be decomposed well. Further, by subjecting the treated product subjected to the hydrothermal reaction treatment to the hydrothermal wet oxidation treatment, the organic components contained in the dye can be completely decomposed and discharged as waste water.

【0020】すなわち、本例では、水熱反応処理を行う
ことにより、水熱湿式酸化処理で分解されやすい状態に
染料系廃液を変化させ、これを水熱湿式酸化処理するこ
とにより、染料に含まれる有機分を確実に分解処理する
ことができる。また、染料に含まれる有機分の分解に伴
い、染料系廃液を脱色することができる。
That is, in this example, the dye-based waste liquid is changed to a state in which it is easily decomposed by the hydrothermal wet oxidation treatment by performing the hydrothermal reaction treatment, and the dye-based waste liquid is subjected to the hydrothermal wet oxidation treatment so as to be contained in the dye. It is possible to surely decompose the organic components to be decomposed. Further, the dye-based waste liquid can be decolorized by the decomposition of the organic components contained in the dye.

【0021】(実験例)次に、染料系廃液として、
(1)染料を多く含む廃液(M1)と、(2)定着液を
多く含む廃液(M2)とに対し、水熱反応処理を行い、
処理後の有機分の濃度を調べた。得られた結果を表1及
び図2〜図5に示す。なお、水熱反応処理については、
試験装置として、バッチ式超臨界水・水熱反応試験装置
(オートクレーブ)を用いて行った。この水熱反応試験
装置の仕様は以下の通りである。 「仕様」 ・最高使用温度;500℃ ・最高使用圧力;50MPa ・反応容器 ;材質:炭素鋼にハステロイ内張り(容
量:45ml) ・加熱方式 ;誘導加熱方式(昇温速度50℃/mi
n) ・攪拌方式 ;加熱炉ロッキングによる攪拌(攪拌ボ
ール) 「試験条件」 ・処理温度 ;180、200、230、250、2
80、300、350℃ ・固液比 ;原料のまま ・処理時間 ;30分、10分(処理温度280℃の
み) ・気相部 ;アルゴン
(Experimental example) Next, as a dye-based waste liquid,
(1) The waste liquid containing a large amount of dye (M1) and (2) the waste liquid containing a large amount of fixing liquid (M2) are subjected to hydrothermal reaction treatment,
The concentration of organic components after the treatment was examined. The obtained results are shown in Table 1 and FIGS. Regarding the hydrothermal reaction treatment,
A batch type supercritical water / hydrothermal reaction test device (autoclave) was used as a test device. The specifications of this hydrothermal reaction test device are as follows. "Specifications" -Maximum operating temperature: 500 ° C-Maximum operating pressure: 50 MPa-Reaction vessel; Material: Carbon steel with Hastelloy lining (capacity: 45 ml) -Heating method: Induction heating method (heating rate 50 ° C / mi)
n) -Stirring method; Stirring by heating furnace rocking (stirring ball) "Test conditions" -Processing temperature; 180, 200, 230, 250, 2
80, 300, 350 ℃ ・ Solid-liquid ratio ; as raw materials ・ Processing time ; 30 minutes, 10 minutes (processing temperature 280 ℃ only) ・ Gas phase part ; Argon

【0022】[0022]

【表1】 [Table 1]

【0023】染料系廃液(M1)について、表1、図2
及び図3に示した結果より、水熱反応処理後のCODm
n及びCODcrは、処理温度が180℃及び200℃
において処理前に比べて上昇傾向を示した。これは難分
解性の有機質分が水熱反応により分解し、分解されやす
い形に変化したものと考えられる。また、CODmn及
びCODcrは、その後、処理温度が高くなるにつれて
低下する傾向にあった。ただし、処理温度が300℃を
超えると、CODmn及びCODcrともに上昇する傾
向にあった。また、SS(懸濁物)分は、処理温度が高
くなるにつれてわずかずつ上昇する傾向にあった。特
に、230℃の処理温度を境に、それ以上の処理温度に
なるとSS分は上昇する傾向にあった。
Regarding the dye-based waste liquid (M1), Table 1 and FIG.
And from the results shown in FIG. 3, CODm after hydrothermal reaction treatment
n and CODcr have processing temperatures of 180 ° C and 200 ° C
Showed a tendency to increase compared to before treatment. It is considered that this is because the hardly decomposable organic matter was decomposed by the hydrothermal reaction and changed into a form that was easily decomposed. Further, CODmn and CODcr tended to decrease thereafter as the treatment temperature increased. However, when the treatment temperature exceeded 300 ° C., both CODmn and CODcr tended to increase. Further, the SS (suspension) content tended to increase little by little as the treatment temperature increased. In particular, when the processing temperature of 230 ° C. was used as a boundary and the processing temperature was higher than that, the SS content tended to increase.

【0024】この結果より、染料系廃液(M1)につい
て、CODmn及びCODcrを低下させるには、処理
温度を250〜280℃、処理時間を30分とするのが
望ましいことが分かった。また、SS分を1000mg
/l以下に抑えるには、処理温度を250℃程度以下に
するのが望ましいことが分かった。
From these results, it was found that the treatment temperature is preferably 250 to 280 ° C. and the treatment time is 30 minutes in order to reduce CODmn and CODcr of the dye waste liquid (M1). Also, SS content is 1000 mg
It has been found that it is desirable to set the treatment temperature to about 250 ° C. or less in order to suppress the temperature to 1 / l or less.

【0025】次に、染料系廃液(M2)について、表
1、図4及び図5に示した結果より、水熱反応処理後の
CODmn及びCODcrは、180〜280℃におい
て、処理前に比べて大幅に低下する傾向にあった。ただ
し、処理温度が300℃以上になると、CODmn及び
CODcrともに上昇する傾向にあった。また、SS分
は、処理温度が高くなるにつれてわずかずつ上昇する傾
向にあった。
Next, regarding the dye-based waste liquid (M2), from the results shown in Table 1, FIG. 4 and FIG. 5, CODmn and CODcr after hydrothermal reaction treatment were 180 to 280 ° C. as compared with those before treatment. It tended to drop significantly. However, when the treatment temperature was 300 ° C. or higher, both CODmn and CODcr tended to increase. Further, the SS content tended to increase little by little as the treatment temperature increased.

【0026】この結果より、染料系廃液(M2)につい
て、CODmn及びCODcrを低下させるには、処理
温度を250〜280℃、処理時間を30分とするのが
望ましいことが分かった。
From these results, it was found that it is desirable that the treatment temperature is 250 to 280 ° C. and the treatment time is 30 minutes in order to reduce CODmn and CODcr of the dye waste liquid (M2).

【0027】次に、CODmn及びCODcrの値が比
較的大きい水熱反応処理後の染料系廃液(M1)の処理
物に対し、水熱湿式酸化処理を行い、処理後の有機分の
濃度を調べた。なお、この水熱湿式酸化処理の試験条件
は以下の通りである。 「試験条件」 ・処理温度 ;220℃ ・空気流量 ;1.8l/min ・処理時間 ;60分 ・触媒 ;金属(Pt)系
Next, the treated product of the dye-based waste liquid (M1) after the hydrothermal reaction treatment, in which the values of CODmn and CODcr are relatively large, is subjected to hydrothermal wet oxidation treatment, and the concentration of organic components after the treatment is investigated. It was The test conditions for this hydrothermal wet oxidation treatment are as follows. "Test conditions" -Treatment temperature; 220 ° C-Air flow rate; 1.8 l / min-Treatment time; 60 minutes-Catalyst; Metal (Pt) system

【0028】上記水熱湿式酸化処理を行った結果、染料
系廃液(M1)について、水熱反応処理後の有機分はほ
ぼ100%分解したことが確認された。例えば、COD
crは、処理前の値が30250mg/lであったのに
対し、処理後の値が357mg/lであった。
As a result of carrying out the hydrothermal wet oxidation treatment, it was confirmed that the dye-based waste liquid (M1) was decomposed to an organic content of almost 100% after the hydrothermal reaction treatment. For example, COD
The cr value was 30250 mg / l before the treatment, whereas the value after the treatment was 357 mg / l.

【0029】この結果から、水熱反応処理した処理物を
水熱湿式酸化処理することにより、染料に含まれる有機
分をほぼ完全に分解することが可能となることが分かっ
た。特に、水熱反応処理を行うことにより、水熱湿式酸
化処理で分解されやすい状態に染料系廃液が変化してお
り、染料に含まれる有機分を確実に分解処理することが
できることが分かった。
From these results, it was found that it is possible to almost completely decompose the organic components contained in the dye by subjecting the treated product subjected to the hydrothermal reaction treatment to the hydrothermal wet oxidation treatment. In particular, it has been found that by performing the hydrothermal reaction treatment, the dye-based waste liquid is changed to a state in which it is easily decomposed by the hydrothermal wet oxidation treatment, and the organic component contained in the dye can be reliably decomposed.

【0030】以上、添付図面を参照しながら本発明に係
る好適な実施形態について説明したが、本発明は係る例
に限定されないことは言うまでもない。上述した例にお
いて示した各構成部材の諸形状や組み合わせ等は一例で
あって、本発明の主旨から逸脱しない範囲において設計
要求等に基づき種々変更可能である。
The preferred embodiments of the present invention have been described above with reference to the accompanying drawings, but it goes without saying that the present invention is not limited to such examples. The shapes, combinations, and the like of the respective constituent members shown in the above-described examples are merely examples, and various changes can be made based on design requirements and the like without departing from the spirit of the present invention.

【0031】[0031]

【発明の効果】以上説明したように、本発明の染料系廃
液の処理方法は、染料系廃液を、亜臨界水あるいは超臨
界水下の水熱反応により分解処理することにより、染料
に含まれる有機分を良好に分解することができる。ま
た、本発明の染料系廃液の処理装置は、上記の処理方法
を実施できるものであるから、染料に含まれる有機分を
良好に分解することができる。
As described above, the method for treating a dye-based waste liquid according to the present invention includes a dye-based waste liquid in a dye by decomposing the dye-based waste liquid by hydrothermal reaction under subcritical water or supercritical water. Organic matter can be decomposed well. Further, since the treatment apparatus for a dye-based waste liquid of the present invention can carry out the above-mentioned treatment method, it can satisfactorily decompose the organic components contained in the dye.

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

【図1】 本発明の染料系廃液の処理装置の一実施形態
例の、概略構成を説明するための図である。
FIG. 1 is a diagram for explaining a schematic configuration of an embodiment of an apparatus for treating a dye-based waste liquid according to the present invention.

【図2】 染料系廃液M1について、水熱反応処理後の
CODmnの値を示すグラフ図である。
FIG. 2 is a graph showing the CODmn value of the dye-based waste liquid M1 after hydrothermal reaction treatment.

【図3】 染料系廃液M1について、水熱反応処理後の
CODcrの値を示すグラフ図である。
FIG. 3 is a graph showing the CODcr value after the hydrothermal reaction treatment for the dye-based waste liquid M1.

【図4】 染料系廃液M2について、水熱反応処理後の
CODmnの値を示すグラフ図である。
FIG. 4 is a graph showing the CODmn value after the hydrothermal reaction treatment for the dye-based waste liquid M2.

【図5】 染料系廃液M2について、水熱反応処理後の
CODcrの値を示すグラフ図である。
FIG. 5 is a graph showing the CODcr value after the hydrothermal reaction treatment for the dye-based waste liquid M2.

【符号の説明】[Explanation of symbols]

1 染料系廃液の処理装置、 2 水熱反応処理装置、 3 水熱湿式酸化処理装置。 1 Dye-based waste liquid treatment equipment, 2 Hydrothermal reaction treatment equipment, 3 Hydrothermal wet oxidation treatment equipment.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 平岡 龍三 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社機械・プラント開 発センター内 (72)発明者 三輪 敬一 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社機械・プラント開 発センター内 Fターム(参考) 4D050 AA13 AB03 BB01 BC01 BC02 BC06 BD02 CA20    ─────────────────────────────────────────────────── ─── Continued front page    (72) Inventor Ryuzo Hiraoka             Stone, Shin-Nakahara-cho, Isogo-ku, Yokohama-shi, Kanagawa             Kawashima Harima Heavy Industries Co., Ltd. Machinery and plant opening             In the departure center (72) Inventor Keiichi Miwa             Stone, Shin-Nakahara-cho, Isogo-ku, Yokohama-shi, Kanagawa             Kawashima Harima Heavy Industries Co., Ltd. Machinery and plant opening             In the departure center F term (reference) 4D050 AA13 AB03 BB01 BC01 BC02                       BC06 BD02 CA20

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 染料を含む染料系廃液を、亜臨界水条件
あるいは超臨界水条件下の水熱反応により分解処理する
水熱反応処理工程を備えることを特徴とする染料系廃液
の処理方法。
1. A method for treating a dye-based waste liquid, comprising a hydrothermal reaction treatment step of decomposing a dye-based waste liquid containing a dye by a hydrothermal reaction under subcritical water conditions or supercritical water conditions.
【請求項2】 分解処理された水熱反応処理物を、湿式
酸化処理する湿式酸化処理工程を備えることを特徴とす
る請求項1に記載の染料系廃液の処理方法。
2. The method for treating a dye-based waste liquid according to claim 1, further comprising a wet oxidation treatment step of performing a wet oxidation treatment on the decomposed hydrothermal reaction-treated product.
【請求項3】 染料を含む染料系廃液を、亜臨界水条件
あるいは超臨界水条件下の水熱反応により分解処理する
水熱反応処理装置を備えることを特徴とする染料系廃液
の処理装置。
3. A treatment apparatus for a dye-based waste liquid, comprising a hydrothermal reaction treatment device for decomposing a dye-based waste liquid containing a dye by hydrothermal reaction under subcritical water conditions or supercritical water conditions.
【請求項4】 分解処理された水熱反応処理物を、湿式
酸化処理する湿式酸化処理装置を備えることを特徴とす
る請求項3に記載の染料系廃液の処理装置。
4. The treatment apparatus for a dye-based waste liquid according to claim 3, further comprising a wet oxidation treatment apparatus for performing a wet oxidation treatment on the hydrothermal reaction-treated product decomposed.
JP2001289820A 2001-09-21 2001-09-21 Method and apparatus for treating dye waste liquid Pending JP2003093866A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001289820A JP2003093866A (en) 2001-09-21 2001-09-21 Method and apparatus for treating dye waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001289820A JP2003093866A (en) 2001-09-21 2001-09-21 Method and apparatus for treating dye waste liquid

Publications (1)

Publication Number Publication Date
JP2003093866A true JP2003093866A (en) 2003-04-02

Family

ID=19112260

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001289820A Pending JP2003093866A (en) 2001-09-21 2001-09-21 Method and apparatus for treating dye waste liquid

Country Status (1)

Country Link
JP (1) JP2003093866A (en)

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