CN106698597A - Method of fast advanced treatment of dye wastewater - Google Patents

Method of fast advanced treatment of dye wastewater Download PDF

Info

Publication number
CN106698597A
CN106698597A CN201611199409.6A CN201611199409A CN106698597A CN 106698597 A CN106698597 A CN 106698597A CN 201611199409 A CN201611199409 A CN 201611199409A CN 106698597 A CN106698597 A CN 106698597A
Authority
CN
China
Prior art keywords
dyestuff
waste water
intermediate pool
electro
dye wastewater
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
CN201611199409.6A
Other languages
Chinese (zh)
Inventor
魏永
石舟翔
江晓栋
姚维昊
赵威
徐斓
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.)
Changzhou University
Original Assignee
Changzhou University
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 Changzhou University filed Critical Changzhou University
Priority to CN201611199409.6A priority Critical patent/CN106698597A/en
Publication of CN106698597A publication Critical patent/CN106698597A/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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (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)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention relates to a method of fast advanced treatment of dye wastewater. Organic matters are degraded in an electrocatalytic oxidation technology mainly through direct oxidation and indirect oxidation, the removing speed is fast and the efficiency is high, and the technology has a good removing effect to the dye wastewater. According to the technical scheme, the method specifically comprises the steps that 1, the dye wastewater enters an intermediate water pool after being treated by a secondary sewage plant, and the intermediate water pool plays a role in water volume buffering adjustment and intermediate storage; 2, the intermediate water pool sewage enters an electro-catalysis oxidative system after being lifted by a lift pump, an electro-catalysis oxidative reaction groove body is divided into multiple reaction grooves, the reaction grooves are communicated and connected in series, positive and negative electrodes are arranged in each reaction groove, wherein the positive electrode adopts a PbO2 polar plate, the negative electrode adopts a stainless steel polar plate, and the interval between the polar plates is 5-15 cm, the bottom of a reactor is provided with an aeration perforated tube, which controls aeration intensity through compressing air volume, a direct current stabilized power supply is adopted on a power supply, the voltage output range is 0-36 V, and the current output range is 0-30 A; 3, the chosen process operating parameters are that the PH value is 4.0-7.5, the current density is 5-15 mA/cm<2>, and the hydraulic retention time is 1-5 h. The electro-catalysis yielding water satisfies the first standard of emissions standards for major pollutants in the chemical industry, and satisfies standardized discharge.

Description

A kind of method that fast deep processes waste water from dyestuff
Technical field
The present invention relates to a kind of method of water-treatment technology field, specifically a kind of electrocatalytic oxidation PROCESS FOR TREATMENT dyestuff Method, electrocatalytic oxidation technique is mainly by direct oxidation and indirect oxidation degradation of organic substances, and removal rate is fast and efficiency high, right There is preferable removal effect in waste water from dyestuff.
Background technology
Dye industry as China traditional industries, the waste water that it is produced is with organic concentration is high, complicated component, color The features such as degree is high, hard-degraded substance is more, becomes a great problem of water treatment field.With industrial wastewater discharge standard increasingly Improve, enterprise needs to improve original handling process or carry out bio-chemical effluent advanced treating to propose mark transformation.
The further treatment technique of application waste water from dyestuff mainly has physical-chemical process, oxidizing process, electrochemical process etc. at present.Wherein Electrocatalytic Oxidation in electrochemical process with its equipment it is simple, reaction speed is fast, non-secondary pollution, can make recalcitrant substance Be converted into bio-degradable material or by organic matter deep oxidation be CO2And H2O.Electrocatalytic oxidation technique is mainly by direct Oxidation and indirect oxidation degradation of organic substances, wherein indirect oxidation refer to by producing the intermediate product with strong oxidizing property (such as OH, HClO or O3Deng) cause organic matter degradation.
The content of the invention
It is an object of the invention to a kind of method of electrocatalytic oxidation PROCESS FOR TREATMENT waste water from dyestuff, while removing COD and taking off Color, can be used for the pretreatment of waste water from dyestuff and advanced treating, be obtained in that qualified effluent quality.The present invention is by following skill What art scheme was realized, specifically include following steps:
(1) intermediate pool is entered after waste water from dyestuff is managed through B-grade sewage factory and office, intermediate pool plays water buffering regulation with Between store effect.
(2) the boosted pump of intermediate pool sewage is lifted into electrocatalytic oxidation system, and electrocatalysis oxidation reaction cell body is divided It is several reactive tanks, series connection is communicated, there is each 1 of positive and negative electrode in each reactive tank, wherein positive pole uses PbO2Pole plate, negative pole Using stainless steel polar plate, pole plate spacing is 5~15cm.Reactor bottom sets aeration perforated pipe, by air supply control Aeration intensity, power supply uses D.C. regulated power supply, and voltage output range is 0~36V, and range of current output is 0~30A.
(3) selection Process operating parameters are:PH value 4.0~7.5,5~15mA/cm of current density2, hydraulic detention time 1 ~5h.Electro-catalysis water outlet meets《Chemical industry discharge of major pollutant standard》Primary standard, meets qualified discharge.
Specific embodiment
Embodiments of the invention are elaborated below:The present embodiment is carried out under premised on technical solution of the present invention Implement, give detailed implementation method, but protection scope of the present invention is not limited to following embodiments.
Embodiment 1
(1) waste water from dyestuff after being managed through dye wastewater factory and office in second pond to middle hopper (30L) is chosen.Water quality is specific Parameter COD:189mg/L;BOD5:25mg/L;pH7.2;NH3-N:5.6;Colourity 136.
(2) middle tank sewage is lifted into electrocatalysis oxidation reaction groove through peristaltic pump, size be 40cm × 40cm × 40cm, dischargeable capacity is 36L.Cell body is divided into 3 reactive tanks, and series connection is communicated, and has each 1 of positive and negative electrode in each reactive tank, Wherein positive pole uses PbO2Pole plate, negative pole uses stainless steel polar plate, and pole plate is between 20cm × 30cm, pole plate just to effective area Away from being 8cm.Reactor bottom sets aeration perforated pipe, controls aeration intensity, power supply to use DC voltage-stabilizing by air supply Power supply, voltage output range is 0~36V, and range of current output is 0~30A.
(3) Process operating parameters:PH value 5.6, current density 8.2mA/cm2, hydraulic detention time 2.5h, electro-catalysis water outlet Water-quality COD:72mg/L;BOD5:10mg/L;NH3-N:3;Colourity 30.Meet《Chemical industry discharge of major pollutant standard》One-level Standard, can be with qualified discharge.

Claims (3)

1. a kind of method that fast deep processes waste water from dyestuff, it is characterised in that specifically include following steps:
(1) intermediate pool is entered after waste water from dyestuff is managed through B-grade sewage factory and office, intermediate pool plays the regulation of water buffering and store with middle The effect deposited.
(2) the boosted pump of intermediate pool sewage is lifted into electrocatalytic oxidation system, if electrocatalysis oxidation reaction cell body is divided into Dry reactive tank, series connection is communicated, and has each 1 of positive and negative electrode in each reactive tank, and wherein positive pole uses PbO2Pole plate, negative pole is used Stainless steel polar plate, pole plate spacing is 5~15cm.Reactor bottom sets aeration perforated pipe, controls to be aerated by air supply Intensity, power supply uses D.C. regulated power supply, and voltage output range is 0~36V, and range of current output is 0~30A.
(3) selection Process operating parameters are:PH value 4.0~7.5,5~15mA/cm of current density2, 1~5h of hydraulic detention time. Electro-catalysis water outlet meets《Chemical industry discharge of major pollutant standard》Primary standard, meets qualified discharge.Such as claim 1 step The method that a kind of rapid described fast deep processes waste water from dyestuff, it is characterised in that waste water from dyestuff is through two grades described in step (1) Enter intermediate pool after Sewage Plant treatment, subsequently into advanced treatment unit system.
2. the method that a kind of fast deep as claimed in claim 1 processes waste water from dyestuff, it is characterised in that institute in step (2) State the boosted pump of intermediate pool sewage and be lifted into electrocatalytic oxidation system, design of major parts and the voltage electricity of electrolysis reactor Flow control tool there are certain requirements.
3. the method that a kind of fast deep as claimed in claim 1 processes waste water from dyestuff, it is characterised in that institute in step (3) The selection Process operating parameters stated will control within the specific limits, to be otherwise extremely difficult to good treatment effect.
CN201611199409.6A 2016-12-22 2016-12-22 Method of fast advanced treatment of dye wastewater Pending CN106698597A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611199409.6A CN106698597A (en) 2016-12-22 2016-12-22 Method of fast advanced treatment of dye wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611199409.6A CN106698597A (en) 2016-12-22 2016-12-22 Method of fast advanced treatment of dye wastewater

Publications (1)

Publication Number Publication Date
CN106698597A true CN106698597A (en) 2017-05-24

Family

ID=58901998

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611199409.6A Pending CN106698597A (en) 2016-12-22 2016-12-22 Method of fast advanced treatment of dye wastewater

Country Status (1)

Country Link
CN (1) CN106698597A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101704600A (en) * 2009-11-19 2010-05-12 同济大学 Segmented treatment method of high-concentration high-chromaticity dye wastewater
CN205328814U (en) * 2016-01-13 2016-06-22 江苏瑞达环保科技有限公司 Handle alkaline dye wastewater's device

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101704600A (en) * 2009-11-19 2010-05-12 同济大学 Segmented treatment method of high-concentration high-chromaticity dye wastewater
CN205328814U (en) * 2016-01-13 2016-06-22 江苏瑞达环保科技有限公司 Handle alkaline dye wastewater's device

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
李永峰 等主编: "《现代环境工程材料》", 31 January 2012 *

Similar Documents

Publication Publication Date Title
CN102786183B (en) Method for processing garbage leachate
CN102603119B (en) Garbage leachate treatment device and treatment method thereof
CN102786182B (en) Device for processing landfill leachate
US20130264197A1 (en) Nanocatalytic electrolysis and flocculation apparatus
CN204727706U (en) A kind of film electrical coupling system of Sewage advanced treatment
CN102718349B (en) Device and method for electrolytic treatment of acid organic wastewater with high salinity
CN107032537A (en) A kind of processing method of refuse leachate nanofiltration concentrated water
CN110240367B (en) Sewage treatment system and method for synchronous and efficient removal of carbon, nitrogen and phosphorus
CN101723490A (en) Pulse electro-flocculation treatment process and device of berberine waste water
CN101428946A (en) Integrated treatment process and equipment for domestic wastewater
CN107098441A (en) The method that electrochemistry removes Determination of Total Nitrogen in Waste Water
CN109179934A (en) A kind of method of electrochemical advanced oxidation reaction treatment excess sludge
CN101269898B (en) Advanced treatment apparatus for printing and dyeing wastewater
KR101306509B1 (en) Energy self-sufficient advanced wastewater treatment system by combination of microbial fuel cells and microbial electrolysis cells
CN112174434B (en) Reactor and method for treating landfill leachate by combining electric Fenton with denitrification biofilter
CN103613168B (en) Method and system for recycling waste water by combining spark generation plasma with multistage membrane technology
CN111170567B (en) Integrated electrochemical coupling membrane aeration biomembrane reactor and application thereof
CN203461851U (en) Electrolytic oxidation device for garbage percolate
CN202610073U (en) Processing apparatus of garbage percolating liquid
CN203781882U (en) Oxidation-flocculation complex bed device for landfill leachate
CN107986519A (en) A kind of electro-catalysis and photocatalysis sewage processing method
CN203625089U (en) Wastewater recycling system of spark discharge plasma synergistic multi-level membrane technology
CN207210198U (en) Multidimensional is electrolysed MBR sewage disposal devices
CN106698597A (en) Method of fast advanced treatment of dye wastewater
CN203960004U (en) A kind of printing ink wastewater iron carbon treatment facility

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170524