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CN109776307A - A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit - Google Patents

A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit Download PDF

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Publication number
CN109776307A
CN109776307A CN201910235452.0A CN201910235452A CN109776307A CN 109776307 A CN109776307 A CN 109776307A CN 201910235452 A CN201910235452 A CN 201910235452A CN 109776307 A CN109776307 A CN 109776307A
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liquid
unit
acid
treatment
phthalic acid
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李玉宽
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Baishibang Water Treatment Environmental Protection Technology (dalian) Co Ltd
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Baishibang Water Treatment Environmental Protection Technology (dalian) Co Ltd
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Priority to CN201910235452.0A priority Critical patent/CN109776307A/en
Publication of CN109776307A publication Critical patent/CN109776307A/en
Priority to CN201910591654.9A priority patent/CN110128266B/en
Priority to CN202211011056.8A priority patent/CN116444364A/en
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    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C51/00Preparation of carboxylic acids or their salts, halides or anhydrides
    • C07C51/42Separation; Purification; Stabilisation; Use of additives
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B7/00Halogens; Halogen acids
    • C01B7/09Bromine; Hydrogen bromide
    • C01B7/093Hydrogen bromide
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    • 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
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    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C51/00Preparation of carboxylic acids or their salts, halides or anhydrides
    • C07C51/41Preparation of salts of carboxylic acids
    • C07C51/412Preparation of salts of carboxylic acids by conversion of the acids, their salts, esters or anhydrides with the same carboxylic acid part
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    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C51/00Preparation of carboxylic acids or their salts, halides or anhydrides
    • C07C51/42Separation; Purification; Stabilisation; Use of additives
    • C07C51/47Separation; Purification; Stabilisation; Use of additives by solid-liquid treatment; by chemisorption
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    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C67/00Preparation of carboxylic acid esters
    • C07C67/08Preparation of carboxylic acid esters by reacting carboxylic acids or symmetrical anhydrides with the hydroxy or O-metal group of organic compounds
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
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    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/206Manganese or manganese compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F2101/30Organic compounds
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • C02F2103/38Polymers
    • 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

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  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit, belong to field of industrial waste water treatment, process flow are as follows: oxidation mother liquor Extract is by acetic acid recovery unit or the partially recycled unit of terephthalic acid (TPA), reduction temperature solid-liquid separation unit processing.Separating liquid passes through impurity removing unit, resin adsorption cobalt manganese unit Call Provision manganese, except bromine unit recycles bromine, and waste liquid is finally directly discharged to integrated wastewater processing unit;Solid first passes through washing, and water lotion is delivered to Call Provision manganese in resin adsorption cobalt manganese unit, and terephthalic acid (TPA) therein is extracted and purified in remaining solid recycling, benzoic acid generates economic value.The concentration for reducing the benzene homologues such as bromine, benzoic acid and the phthalic acid in oxidation mother liquor Extract, avoids to the active adverse effect of biochemical sludge, reduces the processing difficulty of waste water, improves the efficiency of later period integrated wastewater processing;The consumption for reducing alkaline matter, saves resource, reduces entreprise cost and increases utilization rate.

Description

A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit
Technical field
The invention belongs to field of industrial waste water treatment, and in particular to a kind of mother for p-phthalic acid's oxidation unit The treatment process of liquid Extract.
Background technique
P-phthalic acid is a kind of important production of polyester raw material, therefore very extensive in industrial application.Essence is to benzene two The oxidation unit of formic acid has one liquor abstraction liquid, and the more conventional way of this class factory is to recycle this liquor abstraction liquid at present Acetic acid, or using the partially recycled processing unit of terephthalic acid (TPA) after, addition alkaline matter (be normally applied carbonate, carbonic acid Hydrogen salt, hydroxide) dissolve the benzene homologues such as phthalic acid, benzoic acid;Precipitating removes de-iron, chromium ion;Precipitate cobalt, manganese recycling (cobalt, Manganese is the catalyst of the oxidation unit of p-phthalic acid).But so handle, the bromine in oxidation mother liquor Extract does not remove It goes, the integrated wastewater treatment process for entering back segment can impact reduction activity to biochemical sludge, reduce its biochemical effect; Wherein the processing difficulty of biochemical sludge still has been aggravated containing benzene homologues such as a large amount of benzoic acid, phthalic acids;Alkalinity is added simultaneously The process of substance dissolution benzene homologues and Call Provision, manganese also consumes a large amount of alkaline matter.Therefore technological design can be after entering Before the integrated wastewater treatment process of section, extract and purify recycling bromine therein, benzoic acid, terephthalic acid (TPA), that is, produce through Ji value reduces the adverse effect to biochemical sewage sludge activity again;Solid-liquid separation benzene homologues reduce sewage alkaline matter Consumption.The technique separated and recovered using the technology generations of resin adsorption cobalt, manganese for a large amount of addition alkaline matter precipitate cobalts, manganese, The consumption of alkaline matter can also be reduced again.The effective newly-increased transformation of process route, can extract beneficial from sewage source Substance is turned waste into wealth, while being achieved energy-saving and emission reduction purposes again, and the operating cost of enterprise is reduced, while being also beneficial to environment Protection.
Summary of the invention
The invention patent purpose solves alkaline matter dosage in the prior art by handling oxidation mother liquor Extract Greatly, the entreprise cost is caused to increase and the defect of the wasting of resources, and in particular to a kind of for p-phthalic acid's oxidation unit The treatment process of liquor abstraction liquid.
The invention patent is achieved in the following ways a kind of liquor abstraction for p-phthalic acid's oxidation unit The treatment process of liquid, process flow are as follows:
Step a: oxidation mother liquor Extract passes through acetic acid recovery processing unit or the partially recycled processing unit of terephthalic acid (TPA), obtains Sewage;
Step b: it by the sewage of step a by reducing temperature and solid-liquid separation treatment, obtains containing phthalic acid and benzoic acid solid Mixture and separating liquid.
It is that will walk to be precipitated and obtaining another method of the solid mixture containing phthalic acid and benzoic acid and separating liquid The sewage of rapid a adds again after passing through current prior art common " addition alkaline matter dissolves benzene homologues, Call Provision manganese unit " Acid out goes out and is separated by solid-liquid separation.But not only the method increases sour consumption without reducing the consumption of alkaline matter again, compare by The sewage of step a directly cools down and is separated by solid-liquid separation that acid and alkali consumption is big, operating cost is high;
Step c: being delivered to impurity removing unit for separating liquid, using addition alkaline matter Crystallization Separation route, precipitated iron, chromium etc. from Son removal;
Step d: and then the liquid of step c is delivered to resin adsorption cobalt manganese unit, cobalt therein, manganese are adsorbed, adsorbed Water outlet filtering afterwards, removes broken resin therein;
Step e: the water outlet of step d is delivered to except bromine unit, carries out absorption bromine by selectively adsorbing resin to bromine, is inhaled Attached water outlet filtering emission;
Step f: sewage is finally directly discharged to integrated wastewater processing unit;
Step g: the mixture containing phthalic acid and benzoic acid solid in step b is first passed through into washing, water lotion is delivered to step d Carry out adsorption of cobalt, manganese;
Solid after step h: step g washing is recycled.
After resin adsorption saturation in preferred resin adsorption cobalt manganese unit, desorption and regeneration is carried out by hydrobromic acid solution, Solution reuse after desorption and regeneration is to oxidation reactor.
After the preferred absorption resin saturation except in bromine unit, desorption and regeneration is carried out by alkaline solution, restores its absorption Volume adsorbs use in turn again.Solution after desorption and regeneration carries out the crystallization of film concentration and evaporation and is used as fixed-end forces;Or it uses Bipolar Membrane method or electrolysis method are extracted recycle hydrobromic acid therein after again reuse to oxidation reactor.Exist into the sewage except bromine step By in the adsorption process to the selective absorption resin of bromine, the organic matters such as most benzene homologues are not adsorbed with this resin Water outlet enter next step, i.e., retained the organic matters such as the benzene homologues of sub-fraction on this resin, can be in desorption and regeneration liquid Desorption and regeneration during and bromine desorption dissociates from this resin together, so resin be one bromine extracted and be concentrated, The process for separating the organic matters such as bromine and most benzene homologues, used desorption and regeneration liquid use Bipolar Membrane method or electrolysis method again Recycle bromine processing.It except another method of bromine is direct progress Bipolar Membrane method or electrolysis method recycling bromine processing, but compares: to bromine Sewage handled by much smaller than this resin one operation adsorption saturation period of desorption and regeneration liquid product of selective absorption resin The small operating cost of equipment of volume, i.e., the desorption and regeneration liquid that need to be handled Bipolar Membrane method or electrolysis method small in size, used is low;To bromine The organic matters such as adsorption process major part benzene homologues of selective absorption resin be not adsorbed and directly with this resin be discharged into Enter next step, i.e., the content of organics such as total benzene homologues contained in desorption and regeneration liquid are less than one operation adsorption saturation week of this resin The content of organics such as total benzene homologues in sewage handled by the phase, the organic matters such as benzene homologues grasp the equipment of Bipolar Membrane method or electrolysis method Work can have an impact, therefore it is small on the influence of the equipment of Bipolar Membrane method or electrolysis method to handle desorption and regeneration liquid.
Solid carries out recovery processing unit after preferred washing, concrete mode first is that use part alcohols such as ethyl alcohol as Solvent dissolves M-phthalic acid therein, phthalic acid, benzoic acid, is separated by solid-liquid separation later, solid is to be not readily dissolved in ethyl alcohol Terephthalic acid (TPA), washing or evaporating ethanol after obtain terephthalic acid (TPA) finished product;Liquid evaporation recycles ethyl alcohol and is recycled, knot Partial crystallization go out containing M-phthalic acid, phthalic acid, benzoic acid mixture.Mode second is that use part ethers such as ether as Solvent dissolves benzoic acid therein, is separated by solid-liquid separation later, liquid evaporation recycle ether be recycled, crystallization be precipitated benzoic acid at Product;It is the mixture containing phthalic acid for being not readily dissolved in ether in solid.Two ways is individually implemented, and reality can also be successively carried out It applies.
Procedure described above d and step e can individually be implemented, and sequence also can be interchanged and implemented.
The invention patent the utility model has the advantages that reducing the benzene series such as bromine, benzoic acid and phthalic acid in oxidation mother liquor Extract The concentration of object is avoided to the active adverse effect of biochemical sludge, reduces the processing difficulty of waste water, improves later period integrated wastewater The efficiency of processing;More therefrom extract and purified out the substance that hydrobromic acid, terephthalic acid (TPA), benzoic acid have economic value;Entirely Technique considerably reduces the consumption of alkaline matter, saves resource, reduces entreprise cost and increases utilization rate.
The purpose of different step designed by the present invention is different and mutually indepedent, each step can both be used alone or Selection and the combination of different order can be carried out by actual demand, only selection can also be applied a part of technique therein, be existed In the range of present patent application protection.
Detailed description of the invention
Fig. 1 is process flow diagram.
Specific embodiment
A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit, process flow are as follows:
Step a: oxidation mother liquor Extract passes through acetic acid recovery processing unit or the partially recycled processing unit of terephthalic acid (TPA), obtains Sewage;
Step b: it by the sewage of step a by reducing temperature and solid-liquid separation treatment, obtains containing phthalic acid and benzoic acid solid Mixture and separating liquid;
Step c: separating liquid is delivered to impurity removing unit, removes iron and chromium ion in separating liquid;
Step d: and then the liquid of step c is delivered to resin adsorption cobalt manganese unit, cobalt therein, manganese are adsorbed, adsorbed Water outlet filtering afterwards;
Step e: the water outlet of step d is delivered to except bromine unit, carries out absorption bromine by selectively adsorbing resin to bromine, is inhaled Attached water outlet filtering emission;
Step f: sewage is finally directly discharged to integrated wastewater processing unit;
Step g: step b is obtained to first pass through washing containing the mixture of phthalic acid and benzoic acid solid, water lotion is delivered to step Rapid d carries out adsorption of cobalt, manganese;
Solid after step h: step g washing is recycled.
After resin adsorption saturation in preferred resin adsorption cobalt manganese unit, desorption and regeneration is carried out by hydrobromic acid solution, Solution reuse after desorption and regeneration is to oxidation reactor.
After the preferred absorption resin saturation except in bromine unit, desorption and regeneration is carried out by alkaline solution, restores its absorption Volume adsorbs use in turn again.Solution after desorption and regeneration carries out the crystallization of film concentration and evaporation as fixed-end forces or using double Pole embrane method or electrolysis method are extracted recycle hydrobromic acid therein after again reuse to oxidation reactor.Solid is returned after preferred washing Receive processing unit, concrete mode first is that use part alcohols such as ethyl alcohol as solvent, dissolve M-phthalic acid therein, neighbour's benzene Dioctyl phthalate, benzoic acid, are separated by solid-liquid separation later, and solid is the terephthalic acid (TPA) for being not readily dissolved in ethyl alcohol, washing or evaporating ethanol After obtain terephthalic acid (TPA) finished product;Liquid evaporation recycles ethyl alcohol and is recycled, and crystallization, which is precipitated, contains M-phthalic acid, O-phthalic The mixture of acid, benzoic acid.Mode second is that use ethers such as ether in part as solvent, dissolve benzoic acid therein, later It is separated by solid-liquid separation, liquid evaporation recycles ether and is recycled, and benzoic acid finished product is precipitated in crystallization;Solid be not readily dissolved in ether containing benzene The mixture of dioctyl phthalate.Two ways is individually implemented, and can also successively be implemented.
Experiment 1
The experiment handled in step e with resin is selectively adsorbed to bromine.The separating liquid 10L after step d is collected, Bromine content is 2612ppm, and experiment resin volume 100ml (flows after adsorbing resin by the flow velocity of 2 times of resin volumes Speed control 200ml/H), the concentration of bromine is as follows in water outlet:
Sample time Water outlet 15 minutes Water outlet 2 hours Water outlet 3 hours Water outlet 4 hours
Handle water volume 0.5 times of resin 4 times of resins 6 times of resins 8 times of resins
It is discharged bromine concentration 19.1ppm 185.3 ppm 228 ppm 480 ppm
Sample time 5 hours 6 hours 7 hours 8 hours
Handle water volume 10 times of resins 12 times of resins 14 times of resins 16 times of resins
It is discharged bromine concentration 799ppm 1218ppm 1381ppm 1610ppm
With to bromine selective absorption resin, being for this water can normal selective absorption bromine for experimental verification.With 4% hydrogen Sodium oxide molybdena impregnates 1 hour, and washing is neutral to water outlet later, then carries out absorption test, flow control 100ml/H:
Sample time Water outlet 15 minutes Water outlet 2 hours Water outlet 3 hours Water outlet 4 hours
Handle water volume 0.25 times of resin 2 times of resins 3 times of resins 4 times of resins
It is discharged bromine concentration 433ppm 443 ppm 673ppm 753ppm
Sample time 5 hours 6 hours 7 hours
Handle water volume 5 times of resins 6 times of resins 7 times of resins
It is discharged bromine concentration 918ppm 1051ppm 1248ppm
Conclusion: after desorption and regeneration, the adsorption capacity of resin is risen explanation, illustrates that resin can utilize again first. Production design should be with the amount of resin needed for the resin adsorption Capacity design after desorption and regeneration, by the absorption volume after desorption and regeneration Actual motion technique can be designed.
Experiment 2
The solid of step g dissolves recycling test with alcohols: solid being first washed with water, remaining solid is heated to 105 DEG C after washing It maintains reach drying within 24 hours, grinds broken rear sampling 10.0612g later, excessive addition absolute ethyl alcohol and stirring dissolves 0.5 hour simultaneously Filtrate and filter paper are gone out ethyl alcohol in heating evaporation respectively, are heated to by filtering, then rinse the insoluble matter on filter paper with dehydrated alcohol 105 DEG C maintain 24 hours, measure solid i.e. terephthalic acid (TPA) 3.7431g on filter paper, solid is precipitated after filtrate ethanol evaporation and contains Benzoic acid, M-phthalic acid, phthalic acid mixture 6.2511g.
Conclusion: benzoic acid therein, M-phthalic acid, phthalic acid can be dissolved with ethyl alcohol, by being separated by solid-liquid separation After can isolate terephthalic acid (TPA).
Test the test of 3 alkaline matter dosages
As former state: sampling oxidation mother liquor Extract is by Reclaim Process of Acetic Acid, the water outlet sewage of the partially recycled technique of terephthalic acid (TPA) 0.23Kg, referred to as former state.
It separately takes as former state, separating liquid sampling 0.23Kg, PH=3.1, this experiment drop is obtained after cooling filtering is separated by solid-liquid separation Temperature arrives 18 DEG C of laboratory room temperature.
The aqueous solution that sodium carbonate is configured to 9% concentration is used.
Table one is the consumption test of alkaline matter used in original sample, and table two is the separating liquid institute as former state after cooling is separated by solid-liquid separation It is tested with the consumption of alkaline matter:
PH Original sample PH=3.1 Adjust PH=5.7 Adjust PH=9.4
Procedure declaration Phenomenon: the benzene homologues such as phthalic acid, benzoic acid all dissolve;The Precipitations such as iron, chromium Phenomenon: cobalt, manganese all precipitate
Sodium carbonate liquor amount dosage 150ml 300ml
Pure sodium carbonate consumption 13.5g 27g
Table one
PH Original sample PH=3.1 Adjust PH=5.7 Adjust PH=9.4
Phenomenon: the Precipitations such as iron, chromium Phenomenon: cobalt, manganese all precipitate
Sodium carbonate liquor amount 80ml 200ml
Pure sodium carbonate consumption 7.2g 18g
Table two
Conclusion:
From above table as can be seen that the consumption of the separating liquid alkaline matter after application separation of solid and liquid is obviously relatively as former state with alkalinity The consumption of substance decreases.

Claims (7)

1. a kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit, which is characterized in that process flow Are as follows:
Step a: oxidation mother liquor Extract passes through acetic acid recovery processing unit or the partially recycled processing unit of terephthalic acid (TPA), obtains Sewage;
Step b: it by the sewage of step a by reducing temperature and solid-liquid separation treatment, obtains containing phthalic acid and benzoic acid solid Mixture and separating liquid;
Step c: separating liquid is delivered to impurity removing unit, removes iron and chromium ion in separating liquid;
Step d: and then the liquid of step c is delivered to resin adsorption cobalt manganese unit, cobalt therein, manganese are adsorbed, adsorbed Water outlet filtering afterwards;
Step e: the water outlet of step d is delivered to except bromine unit, carries out absorption bromine by selectively adsorbing resin to bromine, is inhaled Attached water outlet filtering emission;
Step f: sewage is finally directly discharged to integrated wastewater processing unit;
Step g: step b is obtained to first pass through washing containing the mixture of phthalic acid and benzoic acid solid, water lotion is delivered to step Rapid d carries out adsorption of cobalt, manganese;
Solid after step h: step g washing is recycled.
2. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 1, It is characterized in that, carrying out desorption and regeneration after the resin adsorption in the resin adsorption cobalt manganese unit is saturated by acid solution, taking off Solution reuse after attached regeneration is to oxidation reactor.
3. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 1, It is characterized in that, desorption and regeneration is carried out by alkaline solution or salting liquid after the absorption resin saturation removed in bromine unit, The hydrobromic acid solution reuse that solution after desorption and regeneration is generated by separating treatment is to oxidation reactor.
4. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 1, It is characterized in that, it includes that alcohols separated and dissolved extraction terephthalic acid (TPA) and ethers are molten that the solid after the washing, which carries out recovery processing, Solve separation and Extraction benzoic acid.
5. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 2, It is characterized in that, the acid solution is hydrobromic acid solution.
6. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 3, It is characterized in that, the alkaline solution is hydroxide solution or salting liquid is chloride solution.
7. a kind for the treatment of process of liquor abstraction liquid for p-phthalic acid's oxidation unit according to claim 3, It is characterized in that, the separating treatment uses Bipolar Membrane method or electrolysis method processing mode.
CN201910235452.0A 2019-03-27 2019-03-27 A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit Pending CN109776307A (en)

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Application Number Priority Date Filing Date Title
CN201910235452.0A CN109776307A (en) 2019-03-27 2019-03-27 A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit
CN201910591654.9A CN110128266B (en) 2019-03-27 2019-07-02 Treatment process of mother liquor extract for purified terephthalic acid oxidation unit
CN202211011056.8A CN116444364A (en) 2019-03-27 2019-07-02 Treatment process for mother liquor extract of refined terephthalic acid oxidation unit

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CN201910235452.0A CN109776307A (en) 2019-03-27 2019-03-27 A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit

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CN110128266A (en) * 2019-03-27 2019-08-16 佰仕邦水处理环保科技(大连)有限公司 A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit
CN110255769A (en) * 2019-07-02 2019-09-20 佰仕邦水处理环保科技(大连)有限公司 A kind for the treatment of process of the aqueous solution for terephthalic acid production plant
CN110548311A (en) * 2019-09-18 2019-12-10 佰仕邦水处理环保科技(大连)有限公司 Treatment process for mixed solution containing benzoic acid and acid radical thereof and/or phthalic acid and acid radical thereof
CN111217333A (en) * 2020-02-25 2020-06-02 佰仕邦水处理环保科技(大连)有限公司 Process for recovering bromine from mother liquor extract of oxidation process of terephthalic acid production device
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CN110128266A (en) * 2019-03-27 2019-08-16 佰仕邦水处理环保科技(大连)有限公司 A kind for the treatment of process of the liquor abstraction liquid for p-phthalic acid's oxidation unit
CN110128266B (en) * 2019-03-27 2022-12-27 佰仕邦水处理环保科技(大连)有限公司 Treatment process of mother liquor extract for purified terephthalic acid oxidation unit
CN110255769A (en) * 2019-07-02 2019-09-20 佰仕邦水处理环保科技(大连)有限公司 A kind for the treatment of process of the aqueous solution for terephthalic acid production plant
CN110548311A (en) * 2019-09-18 2019-12-10 佰仕邦水处理环保科技(大连)有限公司 Treatment process for mixed solution containing benzoic acid and acid radical thereof and/or phthalic acid and acid radical thereof
CN111217333A (en) * 2020-02-25 2020-06-02 佰仕邦水处理环保科技(大连)有限公司 Process for recovering bromine from mother liquor extract of oxidation process of terephthalic acid production device
CN111575486A (en) * 2020-05-20 2020-08-25 杨文辉 PTA oxidation mother liquor recycling method
CN111646892A (en) * 2020-06-01 2020-09-11 佰仕邦水处理环保科技(大连)有限公司 Process for separating and recovering materials from slurry of solvent recovery unit in oxidation process of terephthalic acid production device
CN113087081A (en) * 2021-04-14 2021-07-09 南京依柯卡特排放技术股份有限公司 PTA refining mother liquor recovery method based on ceramic membrane technology
CN113087081B (en) * 2021-04-14 2022-04-26 南京依柯卡特排放技术股份有限公司 PTA refining mother liquor recovery method based on ceramic membrane technology
CN115282939A (en) * 2022-08-04 2022-11-04 南京大学 Method and system for recycling cobalt and manganese catalysts in high-selectivity iron-removing resin and PTA wastewater

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Application publication date: 20190521