CN108423903A - Dyeing waste water zero-discharge treatment system - Google Patents

Dyeing waste water zero-discharge treatment system Download PDF

Info

Publication number
CN108423903A
CN108423903A CN201810163482.0A CN201810163482A CN108423903A CN 108423903 A CN108423903 A CN 108423903A CN 201810163482 A CN201810163482 A CN 201810163482A CN 108423903 A CN108423903 A CN 108423903A
Authority
CN
China
Prior art keywords
water
production
counter
level
zero
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
CN201810163482.0A
Other languages
Chinese (zh)
Inventor
宋岱峰
许锦鹏
李利松
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.)
Sichuan Fute Water Co Ltd
Original Assignee
Sichuan Fute Water 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 Sichuan Fute Water Co Ltd filed Critical Sichuan Fute Water Co Ltd
Priority to CN201810163482.0A priority Critical patent/CN108423903A/en
Publication of CN108423903A publication Critical patent/CN108423903A/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
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/04Chlorides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D5/00Sulfates or sulfites of sodium, potassium or alkali metals in general
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

The invention belongs to water treatment fields, are related to treatment of dyeing wastewater field, and in particular to a kind of dyeing waste water zero-discharge treatment system, the zero-discharge treatment system include pretreatment system, film concentration systems, crystal system, reclaiming system;Pretreatment system includes ozone water outlet and melded system;Film concentration systems include counter-infiltration system, nanofiltration system, seawater reverse osmosis permeable system, super counter-infiltration system, super nanofiltration system and production pond;Crystal system uses freezing and crystallizing and/or evaporative crystallization;Water inlet obtains solidfied material by the pretreatment system, the film concentration systems and the crystal system successively, and the film concentration systems are connected with the reclaiming system;The solidfied material is sodium chloride or sodium sulphate.The present invention have system operatio it is simple, technique is flexible, stable, and effluent quality is good, be convenient for automatic management the characteristics of.

Description

Dyeing waste water zero-discharge treatment system
Technical field
The invention belongs to water treatment fields, are related to treatment of dyeing wastewater field, and in particular to a kind of dyeing waste water zero-emission Processing system.
Background technology
Dyeing waste water contains a large amount of dyestuffs, auxiliary agent, slurry, soda acid and inorganic salts etc., its main feature is that composition is complicated, salt content The features such as height, high organic content, basicity are high, coloration is deep, biodegradability is poor.If do not handled before discharge it, The soluble inorganic salt of Coal Gas Washing Cycling Water and toxic organic compound difficult to degrade can cause serious environmental pollution, to soil and ground Table water, underground water damage.Since printing and dyeing enterprise produces the diversity of kind, the complexity of waste water composition is determined, therefore, Single treatment technology and technique are extremely difficult to require.Although the techniques of Dyeing Wastewater Treatment and technique of domestic and international practical application compared with It is more, but be still the combination of biological treatment and materialization treatment process or its technology mostly.And the zero-emission relatively difficult to achieve of these technologies, and And it is faced with the secondary pollutions problems such as processing biochemical sludge, crystallization mixed salt;Energy consumption is big;Huge structure;Dwell time of sewage length, Sewage degree of transitivity is more;The degree of automation is poor;Take up a large area, the time limit of constructing it is longer;Construction by geographical environment, geology and geomorphology, The restriction of seasonal factor;Operational administrative cumbersome the shortcomings of being not easy to realize.
Wastewater zero discharge refers to that industrial wastewater is reached all (99% or more) recyclings, the salt in water by handling Class and pollutant are discharged using solid forms by condensing crystallizing or as industrial chemicals.By realizing the zero-emission of dyeing waste water, It can realize emission reduction targets, waste water reclaiming, non-wastewater discharge, while reduce water consumption, reduce operating cost, can be used for The Nacl of industrial use, solves the problems, such as wastewater treatment.Final means of the evaporation technique as realization technique of zero discharge, by It is very big in the required energy of its phase transition process, become the key for restricting zero-emission cost.Most current technique is directly to place Reason waste water is evaporated, and the operating cost of zero-emission has been significantly greatly increased.Therefore, by technological design, its final evaporation is reduced Treating capacity is the core for reducing zero discharge waste-water processing cost.
Invention content
It is an object of the present invention to for the problem present on, a kind of dyeing waste water zero-discharge treatment system is provided.
For this purpose, the above-mentioned purpose of the present invention is achieved through the following technical solutions:
Dyeing waste water zero-discharge treatment system, including pretreatment system, film concentration systems, crystal system, reclaiming system;
The pretreatment system includes ozone water outlet and melded system;
The film concentration systems include counter-infiltration system, nanofiltration system, seawater reverse osmosis permeable system, super counter-infiltration system, surpass Grade nanofiltration system and production pond;
The crystal system uses freezing and crystallizing and/or evaporative crystallization;
Water inlet obtains solidfied material, the film by the pretreatment system, the film concentration systems and the crystal system successively Concentration systems are connected with the reclaiming system;
The solidfied material is sodium chloride or sodium sulphate.
Further, the sludge that the melded system generates enters filter press filter-press dehydration after being pumped into sludge concentration tank decrement Filter cake and concentrated water are generated, the concentrated water that the filter press filter-press dehydration generates is squeezed into the ozone water outlet, the sludge concentration tank The concentrated water generated during decrement treatment is squeezed into the ozone water outlet.
Further, the melded system water outlet enters the film concentration systems, and the film concentration systems include anti- Osmosis system, nanofiltration system, seawater reverse osmosis permeable system, super counter-infiltration system, super nanofiltration system and production pond;
The first order production water and first order concentrated water that melded system water outlet is handled by the counter-infiltration system, described the Level-one produces water and enters the production pond, and the first order concentrated water is handled into the nanofiltration system;
It handles to obtain second level production water and second level concentrated water through the nanofiltration system, water is produced through the seawater reverse osmosis in the second level Permeable system handle the third level production water and third level concentrated water, the second level concentrated water handle to obtain into the super nanofiltration system Level V concentrated water and level V produce water;
The third level concentrated water handles to obtain fourth stage production water and fourth stage concentrated water, the third through the super counter-infiltration system Grade production water and fourth stage production water are directly entered the production pond, and the fourth stage concentrated water is directly entered crystal system;
The level V concentrated water is directly entered crystal system, and the level V production water handles to obtain the 6th through the counter-infiltration system Grade production water and the 6th grade of concentrated water, the 6th grade of production water are directly entered the production pond, and the 6th grade of concentrated water is recycled into institute State in nanofiltration system with the first concentrated water mixed processing.
Further, super counter-infiltration system water outlet enters the crystal system, and the crystal system is chlorine Change sodium solution evaporator, the super counter-infiltration system water outlet evaporates to obtain purity >=98% by sodium chloride solution evaporator The sodium chloride that sodium chloride and purity are 50~65%.
The super nanofiltration system water outlet enters the crystal system, and the crystal system includes freezing and crystallizing, sodium sulphate Evaporator and the evaporation of metabisulfite solution evaporator, freezing and crystallizing is passed through in the super nanofiltration system water outlet successively, sodium sulphate evaporates Device evaporates and metabisulfite solution evaporator evaporates to obtain the sodium sulphate of purity >=98.5% and purity for 60~70% sodium sulphate.
The sal glauberi that purity >=98% is obtained in the refrigeration crystallization process, controlled at -5~-10 DEG C.
The evaporator that the evaporation and crystal process uses is MVR evaporators.
Water produces water into the reclaiming system, the production pond Zhong Shui after counter-infiltration system is handled in the production pond The concentrated water obtained after counter-infiltration system is handled enters the crystal system.
The crystal system is metabisulfite solution evaporator, and the metabisulfite solution evaporator is MVR evaporators.
The counter-infiltration system is reverse osmosis using one or more levels.
Hereinafter, being described in detail with regard to dyeing waste water zero-discharge treatment system.
Melded system main function is the suspended matter and partial organic substances reduced in ozone water outlet in pretreatment, in combination with Liquid caustic soda, sodium carbonate dosing, effectively reduce hardness.Concrete operations principle is as follows:Liquid caustic soda, carbonic acid are sequentially added in melded system Sodium removes the total hardness in waste water, it is dense after flocculation reaction then to add aluminium polychloride, anion-polyacrylamide Water detaches, and most of total hardness, suspended matter and the colloid in ozone water outlet are removed, and stablizes fortune for subsequent film concentration systems Row creates favorable conditions.
Film concentration systems include counter-infiltration system, nanofiltration system, seawater reverse osmosis permeable system, super counter-infiltration system, super Nanofiltration system and production pond.The melded system water outlet obtained after pretreatment enters film concentration systems to TDS, chlorion, sulphur Acid group and COD etc. carry out interception filtering, and achieve the purpose that decrement concentration, and production water enters the processing that production pond waits for next step. Counter-infiltration system be it is a kind of using pressure difference as motive force solution in sub-argument go out solvent UF membrane operation, with naturally osmotic Effect is on the contrary, achieve the purpose that separation, extraction, purifying and concentration.Nanofiltration system carries out cross-flow filtration to first order concentrated water, right Sulfate intercepts, and is not intercepted to sodium chloride, therefore a large amount of sodium chloride enters in second level production water, and a large amount of sodium sulphate enter second In grade concentrated water.Super nanofiltration system carries out cross-flow filtration to second level concentrated water, and rejection is higher than nanofiltration system, makes sodium chloride It is produced in water into level V, sodium sulphate enters in level V concentrated water, and level V concentrated water is directly entered crystal system.Sea-water reverse osmose System carries out interception filtering using to COD, TDS, chlorion and sulfate radical etc., and third level production water is directly entered under the waiting of production pond The processing of one step, to achieve the purpose that decrement concentration;Seawater reverse osmosis permeable system can bear the pressure of bigger, relative to other films For system, the salinity in concentrated water can do more.Super counter-infiltration system still be using to COD, TDS, chlorion and Sulfate radical etc. carries out interception filtering, and fourth stage production water is directly entered production pond, and fourth stage concentrated water is directly entered crystal system, to reach To the purpose of decrement concentration.
4th concentrated water and the 5th concentrated water respectively enter crystal system, and the 4th concentrated water is directly entered sodium chloride solution evaporation Device is evaporated crystallization, finally obtains sodium chloride and the purity of purity >=98% as 50~65% sodium chloride.5th concentrated water First freezing and crystallizing obtains the sal glauberi of purity >=98% at a temperature of -5~-10 DEG C, then by ten water of freezing and crystallizing Sodium sulphate takes out from the 5th concentrated water, obtains the sodium sulphate of purity >=98.5% into sodium sulphate evaporator, will take out freezing and crystallizing Process recycled before the 5th concentrated water afterwards returns.It is molten that the water produced in pond is introduced into sodium sulphate after counter-infiltration system is handled It is evaporated crystallization in liquid evaporator and obtains the sodium sulphate that purity is 60~70%.
The indirect steam generated in evaporative crystallization uses cooling water condensation at condensed water again, and the thermal energy in indirect steam is transmitted to It is diffused into again in air in cooling water and causes thermal energy waste and cooling-water consumption.What evaporator was generated evaporator using compressor Indirect steam, which carries out compression, makes its pressure and temperature increase, and then substitutes steam as the heat source of evaporator, realizes indirect steam The recycling of middle thermal energy so that the heat energy recycling of evaporator.
Dyeing waste water zero-discharge treatment system provided by the invention, has the advantages that:
(1)The present invention uses materializing strategy, film concentration to crystallize, and reuse treatment process realizes the whole zero-emission of dyeing waste water Target, waste water fully recovering, generated sludge, solidfied material can be used as fuel combustion or Nacl reuse after dehydration completely, It preserves the ecological environment;
(2)The system of the present invention carries out decrement concentration reuse to dyeing waste water, reduces the external water consumption in dyeing and printing process, drops Low overall operation cost;
(3)Zero discharging system mesophytization treatment process combination of the present invention, improves the treatment effeciency to pollutant, ensure that follow-up The normal operation of system;
(4)Present system pretreatment stage is discharged using ozone and melded system, the total hardness of waste water is reduced, after alleviating The load of continuous film concentration systems, extends membranous system service life;
(5)Inventive film enriching stage is combined using reverse osmosis, nanofiltration, sea water desalination etc., and containing for follow-up concentrated water is greatly improved Salt amount reduces the processing energy consumption of evaporation technology, reduces operating cost;
(6)The system operatio of the present invention is simple, and technique is flexible, stable, and effluent quality is good, is convenient for automatic management.
Description of the drawings
In order to illustrate more clearly of technical solution of the present invention, the required attached drawing of the present invention will be made simply below It introduces, it should be apparent that, drawings discussed below is only the related legend of the present invention, and those of ordinary skill in the art are come It says, without creative efforts, other attached drawings still can be obtained according to the attached body of offer.
Fig. 1 is the flow diagram of dyeing waste water zero-discharge treatment system provided by the invention;
Fig. 2 is the flow chart of pretreatment system in Fig. 1;
Fig. 3 is the flow chart of film concentration systems in Fig. 1;
Fig. 4 is the flow chart one of crystal system in Fig. 1;
Fig. 5 is the flowchart 2 of crystal system in Fig. 1.
Specific implementation mode
Clear, complete description is carried out to technical scheme of the present invention with reference to the accompanying drawings and examples, it is clear that described Embodiment be only a part of the embodiment of the present invention, instead of all the embodiments.Based on embodiment in the present invention, this field The every other embodiment that those of ordinary skill is obtained without making creative work, belongs to protection of the present invention Range.
As shown in Figure 1, dyeing waste water zero-discharge treatment system include pretreatment system, film concentration systems, crystal system and Reclaiming system.Water inlet passes through pretreatment system, film concentration systems and crystal system and obtains solidfied material successively, film concentration systems with time It is connected with system;Solidfied material is sodium chloride or sodium sulphate.
As shown in Fig. 2, pretreatment system includes ozone water outlet, melded system and sludge condensation, water inlet by ozone water outlet, Melded system processing degrades the total hardness of water inlet to obtain melded system water outlet, and the sludge generated in melded system is taken out Enter filter press filter-press dehydration generation filter cake and concentrated water after entering sludge concentration tank decrement, the concentrated water that filter press filter-press dehydration generates is beaten Enter in ozone water outlet, the concentrated water generated during sludge concentration tank decrement treatment is squeezed into ozone water outlet.Softening system in pretreatment System main function is that the suspended matter and partial organic substances reduced in ozone water outlet is effectively dropped in combination with liquid caustic soda, sodium carbonate dosing Soft.Concrete operations principle is as follows:Liquid caustic soda, sodium carbonate are sequentially added in melded system, remove the total hardness in waste water, so After add aluminium polychloride, anion-polyacrylamide after flocculation reaction concentrated water detach, ozone water outlet in big portion Point total hardness, suspended matter and colloid are removed, and are created favorable conditions for subsequent film concentration systems stable operation.
As shown in figure 3, melded system water outlet enters film concentration systems, film concentration systems include counter-infiltration system, nanofiltration system System, seawater reverse osmosis permeable system, super counter-infiltration system, super nanofiltration system and production pond.The softening obtained after pretreatment System water outlet carries out interception filtering into film concentration systems to TDS, chlorion, sulfate radical and COD etc., and reaches decrement concentration Purpose, production water enter the processing that production pond waits for next step.Melded system water outlet passes through counter-infiltration system is handled first Grade production water and first order concentrated water, first order production water enter production pond, and first order concentrated water enters nanofiltration system processing, nanofiltration system pair First order concentrated water carries out cross-flow filtration, intercepts to sulfate, is not intercepted to sodium chloride, therefore a large amount of sodium chloride enters second In grade production water, a large amount of sodium sulphate enter in the concentrated water of the second level.Counter-infiltration system is one kind using pressure difference as in motive force solution Sub-argument goes out the UF membrane operation of solvent, with the effect of naturally osmotic on the contrary, achieving the purpose that detach, extract, purify and concentrate. It handles to obtain second level production water and second level concentrated water through nanofiltration system, second level production water handles to obtain third through seawater reverse osmosis permeable system Grade production water and third level concentrated water.Seawater reverse osmosis permeable system carries out interception filtering using to COD, TDS, chlorion and sulfate radical etc., Third level production water is directly entered the processing that production pond waits for next step, to achieve the purpose that decrement concentration;Seawater reverse osmosis permeable system The pressure that can bear bigger, for other membranous systems, the salinity in concentrated water can do more.Second level concentrated water enters Super nanofiltration system processing, super nanofiltration system carry out cross-flow filtration to second level concentrated water, and rejection is higher than nanofiltration system, Sodium chloride is set to enter in level V production water, sodium sulphate enters in level V concentrated water, and level V concentrated water is directly entered crystal system.The Three-level concentrated water handles to obtain fourth stage production water and fourth stage concentrated water through super counter-infiltration system, and the third level produces water and the fourth stage produces water It is directly entered production pond, fourth stage concentrated water is directly entered crystal system.Super counter-infiltration system still be using to COD, TDS, chlorion and sulfate radical etc. carry out interception filtering, to achieve the purpose that decrement concentration.Level V concentrated water is directly entered crystallization System, level V produce water and handle to obtain the 6th grade of production water and the 6th grade of concentrated water through counter-infiltration system, and the 6th grade of production water is directly entered Is produced from pond, the 6th grade of concentrated water is recycled into nanofiltration system and the first concentrated water mixed processing.
As shown in figure 4, it is that fourth stage concentrated water enters that crystal system, which uses evaporation and crystallization system, super counter-infiltration system water outlet, Evaporation and crystallization system, the evaporation and crystallization system are sodium chloride solution evaporator, which is MVR evaporators, super reverse osmosis System water outlet is that fourth stage concentrated water evaporates to obtain purity to be 98.5% sodium chloride and 60% chlorine by sodium chloride solution evaporator Change sodium.
As shown in figure 5, crystal system uses freezing and crystallizing and evaporation and crystallization system, super nanofiltration system water outlet the i.e. the 5th dense Water freezing and crystallizing at a temperature of -5~-10 DEG C obtains the sal glauberi that purity is 99%, then by ten water of freezing and crystallizing Sodium sulphate takes out from the 5th concentrated water, and into evaporation and crystallization system, which is sodium sulphate evaporator, the evaporator For MVR evaporators, the sal glauberi that purity is 99% obtains the sodium sulphate of purity 99% through sodium peroxydisulfate evaporator evaporative crystallization, Process recycled before the 5th concentrated water after taking-up freezing and crystallizing is returned.The water in pond will be produced to handle by counter-infiltration system After introduce evaporation and crystallization system, which is metabisulfite solution evaporator and the evaporator is in MVR evaporators, is steamed Hair crystallization obtains the sodium sulphate that purity is 64%.
The indirect steam generated in evaporative crystallization uses cooling water condensation at condensed water again, and the thermal energy in indirect steam is transmitted to It is diffused into again in air in cooling water and causes thermal energy waste and cooling-water consumption.What evaporator was generated evaporator using compressor Indirect steam, which carries out compression, makes its pressure and temperature increase, and then substitutes steam as the heat source of evaporator, realizes indirect steam The recycling of middle thermal energy so that the heat energy recycling of evaporator.

Claims (10)

1. dyeing waste water zero-discharge treatment system, which is characterized in that the zero-discharge treatment system includes pretreatment system, film concentration System, crystal system, reclaiming system;
The pretreatment system includes ozone water outlet and melded system;
The film concentration systems include counter-infiltration system, nanofiltration system, seawater reverse osmosis permeable system, super counter-infiltration system, surpass Grade nanofiltration system and production pond;
The crystal system uses freezing and crystallizing and/or evaporative crystallization;
Water inlet obtains solidfied material, the film by the pretreatment system, the film concentration systems and the crystal system successively Concentration systems are connected with the reclaiming system;
The solidfied material is sodium chloride or sodium sulphate.
2. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that the melded system generated Sludge enters filter press filter-press dehydration generation filter cake and concentrated water, the filter press filter-press dehydration production after being pumped into sludge concentration tank decrement Raw concentrated water is squeezed into the ozone water outlet, and the concentrated water generated during the sludge concentration tank decrement treatment squeezes into the ozone In water outlet.
3. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that the melded system be discharged into Enter the film concentration systems, the film concentration systems include counter-infiltration system, nanofiltration system, seawater reverse osmosis permeable system, super Counter-infiltration system, super nanofiltration system and production pond;
The first order production water and first order concentrated water that melded system water outlet is handled by the counter-infiltration system, described the Level-one produces water and enters the production pond, and the first order concentrated water is handled into the nanofiltration system;
It handles to obtain second level production water and second level concentrated water through the nanofiltration system, water is produced through the seawater reverse osmosis in the second level Permeable system handle the third level production water and third level concentrated water, the second level concentrated water handle to obtain into the super nanofiltration system Level V concentrated water and level V produce water;
The third level concentrated water handles to obtain fourth stage production water and fourth stage concentrated water, the third through the super counter-infiltration system Grade production water and fourth stage production water are directly entered the production pond, and the fourth stage concentrated water is directly entered crystal system;
The level V concentrated water is directly entered crystal system, and the level V production water handles to obtain the 6th through the counter-infiltration system Grade production water and the 6th grade of concentrated water, the 6th grade of production water are directly entered the production pond, and the 6th grade of concentrated water is recycled into institute State in nanofiltration system with the first concentrated water mixed processing.
4. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that the super reverse osmosis system System water outlet enters the crystal system, and the crystal system is sodium chloride solution evaporator, the super counter-infiltration system water outlet Evaporate to obtain sodium chloride and the purity of purity >=98% by sodium chloride solution evaporator for 50~65% sodium chloride.
5. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that the super nanofiltration system goes out Water enters the crystal system, and the crystal system includes that freezing and crystallizing, sodium sulphate evaporator and metabisulfite solution evaporator steam Hair, the super nanofiltration system water outlet are passed through freezing and crystallizing, the evaporation of sodium sulphate evaporator and metabisulfite solution evaporator and are steamed successively The sodium sulphate that hair obtains the sodium sulphate of purity >=98.5% and purity is 60~70%.
6. dyeing waste water zero-discharge treatment system according to claim 5, which is characterized in that in the refrigeration crystallization process The sal glauberi of purity >=98% is obtained, controlled at -5~-10 DEG C.
7. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that the evaporation and crystal process The evaporator used is MVR evaporators.
8. dyeing waste water zero-discharge treatment system according to claim 1, which is characterized in that water passes through in the production pond Production water enters the reclaiming system after counter-infiltration system processing, and water obtains dense after counter-infiltration system is handled in the production pond Water enters the crystal system.
9. dyeing waste water zero-discharge treatment system according to claim 8, which is characterized in that the crystal system is sulfuric acid Sodium solution evaporator, and the metabisulfite solution evaporator is MVR evaporators.
10. dyeing waste water zero-discharge treatment system according to claim 8, which is characterized in that the counter-infiltration system is adopted It is reverse osmosis with one or more levels.
CN201810163482.0A 2018-02-27 2018-02-27 Dyeing waste water zero-discharge treatment system Pending CN108423903A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810163482.0A CN108423903A (en) 2018-02-27 2018-02-27 Dyeing waste water zero-discharge treatment system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810163482.0A CN108423903A (en) 2018-02-27 2018-02-27 Dyeing waste water zero-discharge treatment system

Publications (1)

Publication Number Publication Date
CN108423903A true CN108423903A (en) 2018-08-21

Family

ID=63157286

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810163482.0A Pending CN108423903A (en) 2018-02-27 2018-02-27 Dyeing waste water zero-discharge treatment system

Country Status (1)

Country Link
CN (1) CN108423903A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109717339A (en) * 2019-01-17 2019-05-07 天津中民普健海水淡化科技发展有限公司 A kind of preparation method of the specific use beverage from seawater and obtained specific use beverage

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8877690B2 (en) * 2011-08-31 2014-11-04 Prochemtech International, Inc. Treatment of gas well production wastewaters
CN105417820A (en) * 2015-12-01 2016-03-23 杭州(火炬)西斗门膜工业有限公司 Separation recycling system of chloride radicals and sulfate radicals in high-salinity wastewater
CN205653287U (en) * 2016-02-05 2016-10-19 大唐环境产业集团股份有限公司 Device that zero release of desulfurization waste water was handled
CN106396228A (en) * 2016-09-18 2017-02-15 内蒙古久科康瑞环保科技有限公司 Device and method for treating industrial wastewater with high salt content
CN106396232A (en) * 2016-11-17 2017-02-15 杭州水处理技术研究开发中心有限公司 Zero emission system and method for high-salinity printing and dyeing waste water
CN106966535A (en) * 2016-01-14 2017-07-21 麦王环境技术股份有限公司 Strong brine zero-emission film is concentrated and sub-prime crystallization processes and equipment
CN106966536A (en) * 2016-01-14 2017-07-21 麦王环境技术股份有限公司 Strong brine zero-emission film concentration technology and equipment
CN206799345U (en) * 2017-03-30 2017-12-26 杭州水处理技术研究开发中心有限公司 A kind of system of high-salt wastewater purified salt

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8877690B2 (en) * 2011-08-31 2014-11-04 Prochemtech International, Inc. Treatment of gas well production wastewaters
CN105417820A (en) * 2015-12-01 2016-03-23 杭州(火炬)西斗门膜工业有限公司 Separation recycling system of chloride radicals and sulfate radicals in high-salinity wastewater
CN106966535A (en) * 2016-01-14 2017-07-21 麦王环境技术股份有限公司 Strong brine zero-emission film is concentrated and sub-prime crystallization processes and equipment
CN106966536A (en) * 2016-01-14 2017-07-21 麦王环境技术股份有限公司 Strong brine zero-emission film concentration technology and equipment
CN205653287U (en) * 2016-02-05 2016-10-19 大唐环境产业集团股份有限公司 Device that zero release of desulfurization waste water was handled
CN106396228A (en) * 2016-09-18 2017-02-15 内蒙古久科康瑞环保科技有限公司 Device and method for treating industrial wastewater with high salt content
CN106396232A (en) * 2016-11-17 2017-02-15 杭州水处理技术研究开发中心有限公司 Zero emission system and method for high-salinity printing and dyeing waste water
CN206799345U (en) * 2017-03-30 2017-12-26 杭州水处理技术研究开发中心有限公司 A kind of system of high-salt wastewater purified salt

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109717339A (en) * 2019-01-17 2019-05-07 天津中民普健海水淡化科技发展有限公司 A kind of preparation method of the specific use beverage from seawater and obtained specific use beverage

Similar Documents

Publication Publication Date Title
Mavukkandy et al. Brine management in desalination industry: From waste to resources generation
CN106830465B (en) Salt separation and purification recovery method of salt-containing wastewater
CN109292797A (en) A kind of brine waste sub-prime recovery method
CN102583862B (en) Method and system for treating saline wastewater to zero discharge and recycling
CN101481190B (en) Process for treating saponification wastewater by chlorohydrination
CN108083552A (en) A kind of processing method of textile waste
CN109231632A (en) The processing method and system of a kind of highly mineralized mine water reuse and resource utilization
CN109912118A (en) Waste water reclaiming Zero discharging system and method are spun in a kind of color separation with high salt
CN105523676A (en) High-salt wastewater zero-discharge evaporation crystallization salt substance-division method
CN105923704A (en) Forward osmosis draw fluid recycling method, wastewater treatment method and treatment device
CN109205960A (en) A kind of highly salt containing organic waste water processing system and method
CN102139983A (en) Waste water treatment method and system
CN112499863A (en) Method for resource comprehensive utilization of high-concentration wastewater and waste salt
CN102311193B (en) Method for treating filter cake filter-press filtrate in polyolefin catalyst production
CN110550802A (en) High-salinity aqueous solution zero-emission treatment system and method
CN212954702U (en) Zero discharging equipment of power plant's high salt waste water
CN114105349A (en) Zero-emission resource utilization system and process method of fracturing flow-back fluid
CN206985964U (en) A kind of processing system of textile waste
CN108423903A (en) Dyeing waste water zero-discharge treatment system
CN108147604A (en) A kind of desulfurization wastewater Zero-discharge treating process
CN109574366B (en) High-salinity waste water salt concentration treatment system and process
CN205635216U (en) Concentrated processing apparatus of desulfurization waste water
CN111661886A (en) MVR evaporation salt separation system
CN209411998U (en) A kind of processing system of highly mineralized mine water reuse and resource utilization
CN206156979U (en) High processing apparatus who contains salt difficult degradation saccharin industrial waste water waste gas

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20180821