CN102503813A - Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue - Google Patents

Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue Download PDF

Info

Publication number
CN102503813A
CN102503813A CN2011102826807A CN201110282680A CN102503813A CN 102503813 A CN102503813 A CN 102503813A CN 2011102826807 A CN2011102826807 A CN 2011102826807A CN 201110282680 A CN201110282680 A CN 201110282680A CN 102503813 A CN102503813 A CN 102503813A
Authority
CN
China
Prior art keywords
acid
cobalt
manganese
cobalt manganese
filtrating
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.)
Granted
Application number
CN2011102826807A
Other languages
Chinese (zh)
Other versions
CN102503813B (en
Inventor
曹善文
李朝晖
周波
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.)
Zhejiang Lixing Technology Co.,Ltd.
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN2011102826807A priority Critical patent/CN102503813B/en
Publication of CN102503813A publication Critical patent/CN102503813A/en
Application granted granted Critical
Publication of CN102503813B publication Critical patent/CN102503813B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/584Recycling of catalysts

Abstract

The invention belongs to a technology for recovering organic acid and catalyst in terephthalic acid oxidation residue, namely, controlling the solid content of high-temperature oxidation residue discharged from a terephthalic acid (PTA for short) production device to be within the range of 20-45%, and carrying out first-stage filtration separation at the temperature of 55-90 ℃, wherein the separated solid is directly sold for manufacturing resin or paint monomer or returned to an oxidation reactor for use; the first filtrate is treated according to the following process: adding oxalic acid to obtain cobalt manganese oxalate precipitate, filtering to separate cobalt manganese oxalate, further cooling, filtering and separating filtrate, extracting benzoic acid from the separated solid, and sending the filtrate to a wastewater treatment device; or (II) directly cooling the primary filtrate for secondary filtration and separation, wherein the separated solid is used for extracting benzoic acid, oxalic acid is added into the secondary filtrate to obtain cobalt manganese oxalate precipitate, the cobalt manganese oxalate is separated by filtration, and the filtrate is sent to a wastewater treatment device; reacting cobalt manganese oxalate obtained in the process (I) or (II) with oxidant hydrogen peroxide, peracetic acid, bromine, manganate, permanganate, manganese dioxide or/and hydrobromic acid, using aqueous solution of cobalt acetate, aqueous solution of cobalt bromide, aqueous solution of manganese acetate, aqueous solution of manganese bromide, acetic acid or/and pure water as solvent, after cobalt manganese oxalate is completely dissolved, reacting with metal cobalt, metal manganese or/and hydrobromic acid to remove impurities, and filtering to obtain homogeneous solution containing cobalt manganese bromide ions, wherein the mixed solution can be directly mixed with cobalt acetate, manganese acetate, cobalt bromide, manganese bromide, acetic acid or water to be used as an oxidation catalyst of terephthalic acid.

Description

The recovery method of organic acid and Co-Mn metal in a kind of terephthalic acid oxidation residua
Technical field
The present invention relates to organic acid and Co-Mn metal recovery and reutilization technology method field in a kind of terephthalic acid (being called for short PTA) oxidation residua.The residue that contains organic acid and Co-Mn metal that PTA device mother liquid evaporation device is got rid of of saying so in more detail filters to isolate water-insoluble organic acid solids, and filtrating warp further processing reclaims organic acid, Co-Mn compound and the Co-Mn compound that reclaims carried out the homogeneous phase processing return the field that the PTA oxidation system recycles again.
Background technology
At present, the working method of PTA is to adopt the compound of cobalt manganese bromine as catalyzer p-Xylol to be processed through the oxidation of air high-temperature liquid-phase, and the compound of these cobalt manganese bromines comprises Cobaltous diacetate, cobaltous bromide, manganese acetate, Manganese dibromide, Hydrogen bromide, tetrabromoethane etc.For guaranteeing the PTA quality, in the PTA production process, must 10~20% the mother liquor slurry that contains catalyzer be extracted out, after thin-film evaporator reclaims a large amount of acetic acid, remaining for containing the residue slurries of Cobaltous diacetate, manganese acetate, aromatic acid, acetic acid etc.One cover is produced the production equipment of 1,200,000 tons of PTA per year; Annual to discharge contain organic acid and catalyzer the oxidation residua slurries above 1.5 ten thousand tons; Wherein contain cobalt 0.5 ~ 1.2%, contain manganese 0.5 ~ 1.2%, contain organic acid 30 ~ 42%, if can organic acid, cobalt, the Mn catalyst in this part residue slurries be reclaimed, return mechanism uses or utilizes; Not only reduce environmental pollution, and direct economic benefit is above 4,000 ten thousand yuan.
The Mitsui chemistry once provided a kind of recovery and treatment method of PTA oxidation residua; This method is to reclaim acetic acid through thin-film evaporator; Under 45 ℃, extract with vaal water; Obtain Cobaltous diacetate and manganese acetate extraction liquid and after concentrating, directly return the use of PTA device, the granulation of residue organic acid residue is discharged and is sent incinerator, and this method has application on the PTA device of Jinan chemical fibre, Oil of Shanghai Petrochemical Company and Plant of Tianjin Petrochemical Company head factory; Also there is patent that the method that reclaims cobalt manganese in the PTA residue through IX is provided, like Chinese patent 98113765.2,99121153.7,200410030379.7.
The PTA device of E.I.Du Pont Company's technology then adopts oxalate to reclaim the cobalt-manganese catalyst in the residue, and residue organic acid waste liquid is directly discharged burning.
The disadvantage that the method for Mitsui Chemicals exists is: have only about 70% cobalt, Mn catalyst to obtain reclaiming, and energy consumption is high, equipment is many, and pipeline is prone to stop up, and the water waste is big; There is the accumulation of foreign ions such as iron, nickel in the cobalt-manganese catalyst that reclaims, defectives such as the unstable and active reduction of cobalt and manganese valence state; Organic acid is all sent to burning disposal, contaminate environment in addition; The IX rule exists treatment unit and complex disposal process, introduces a large amount of other chemical substances, has increased defectives such as waste discharge, wastewater treatment capacity increase, cost height; The instability that the PTA residue is formed has increased difficulty and complexity also for the IX pre-treatment, and the not mentioned organic acid of this method reclaims.
The defective that the oxalate way of recycling that E.I.Du Pont Company adopts exists is; It is that the oxalic acid or the aqueous solution are directly added from the mother liquor that the PTA device is extracted out; Deposition that oxalic acid and cobalt manganese generate and the insoluble organic acid in the residue liquid mix and form a kind of dope; And through finned whizzer separation, this dope sticks on the separating device not easily separated easily, and pipeline and equipment also very easily stop up; Isolating need more isolated liquid more than 90% being returned simultaneously washed; Therefore the actual efficiency of separating device is very low, and to obtain be cobalt oxalate manganese and organic acid solid mixture, and this mixture is dispersed in and returns what mix formation with live catalyst when using in the aqueous acetic acid is heterogeneous solution; Can only reach through the internal circulating load that improves PTA oxidizing reaction actuator temperature and reduction recovery dispersion liquid during application and utilize purpose again; This also is the reason that the present PTA of Du Pont technology adopts high temperature oxidation, but the raising of temperature can make that raw materials used PX (abbreviation of p-Xylol) significantly increases with acetic acid consumption when making PTA, and the side reaction aggravation is obvious; In addition, this technology is still burning to the residue treatment mode of isolating behind cobalt oxalate manganese and the acetic acid, has environmental pollution.
Summary of the invention
The object of the invention is exactly to overcome the disadvantage that prior art exists, and adopts new technical characterictic, provides in a kind of PTA oxidation residua organic acid and cobalt-manganese catalyst to reclaim to reach and utilizes novel method again, and be applicable to different PTA devices.
In order to reach the object of the invention; The present invention at first carries out one-level while hot with the PTA oxidation raffinate of extracting out and filters to isolate solids wherein; This solids staple is water-insoluble organic acids such as terephthalic acid, 4-carboxyl benzaldehyde, p-methylbenzoic acid, and this solids is returned oxidation system or sells the raw material that is used for synthetic resins; Filtrating is handled by following process: (I) adds oxalic acid in one-level filtrating, and the filtrating temperature is controlled at 60~100 ℃, and the mol ratio of the cobalt manganese total amount in oxalic acid and the filtrating is 0.75~1.2: 1; Obtain cobalt manganese oxalate precipitation; Filter to isolate cobalt oxalate manganese, filtrating further is cooled to 30~5 ℃, carries out filtering separation again; Solids after the separation is used to extract phenylformic acid, and filtrating is sent wastewater treatment equipment; Perhaps (II) directly is cooled to 30~5 ℃ with one-level filtrating, carries out second stage filtering separation, and the solids after the separation is used to extract phenylformic acid; In secondary filtrating, add oxalic acid; Controlled temperature is 30 ~ 100 ℃, and the mol ratio of the cobalt manganese total amount in oxalic acid and the filtrating is 0.75~1.2: 1, obtains cobalt oxalate manganese deposition; Filter to isolate cobalt oxalate manganese, filtrating is sent wastewater treatment equipment; With above-mentioned (I) perhaps the cobalt oxalate manganese that obtains of (II) process and oxidants hydrogen peroxide, Peracetic Acid, bromine, permanganic acid, mangaic acid, Manganse Dioxide or/and Hydrogen bromide carries out the homogeneous phase processing reaction; And use the Cobaltous diacetate aqueous solution, the cobaltous bromide aqueous solution, the manganese acetate aqueous solution, the Manganese dibromide aqueous solution, acetic acid or/and pure water as solvent; After solids all dissolves; In reactor drum, add cobalt metal, manganese metal or/and Hydrogen bromide continues heating 30 ~ 60min, filter; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine; This mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide, acetic acid or water, and wherein, the mol ratio of cobalt manganese oxalate and hydrogen peroxide or Peracetic Acid is 1: 1.0~1.2; The mol ratio of cobalt manganese oxalate and bromine or Manganse Dioxide or permanganic acid or mangaic acid is a stoichiometric ratio; Cobalt manganese oxalate and hydrobromic mol ratio are 1: 2.05~10.0.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention is considered and has been studied the residue component differences influence that causes owing to the oxidation technology of different PTA oxidizer units source is different, or rather; The solid content that different PTA oxidizer units are discharged residue is different; Even widely different, and also can there be very big difference in the residue that same device was discharged in some in stage, but usually all in 30 ~ 42% scopes; Cobalt manganese content is then respectively between 0.5 ~ 1.2%; For this reason, the present invention is directed to this scope and study in great detail, also studied simultaneously some dehydration back solid contents and surpassed 45% residue and thin up and be lower than 20% residue separating effect and influence factor to solid content; Experiment shows: when solid content surpasses 45%; Though still can direct filtration separate, residue thickness, filtration velocity are slow, and water soluble organic substance and catalyst residue obviously raise in the isolated solids; Also significantly increase the washing water consumption; Preferably refilter separation behind the thin up this moment, and water yield increase also helps to change the phenylformic acid in the solids and Co-Mn compound over to aqueous phase, makes the water soluble organic substance ratio minimizing in the solids that flash trapping stage goes out; Experiment shows that when below adding water adjusting solid content to 20%, filtering, the increase of water consumption is no longer obvious for the effect of extracting phenylformic acid and Co-Mn compound; But increase with the water yield,, have to use hot water or outer heating is provided for keeping filtration temperature; This increases the process energy consumption; Also increase later stage wastewater treatment expense, therefore, the present invention's control and selection solid content carry out first step filtering separation in 20 ~ 45% scopes; For cobalt manganese, when cobalt and manganese concentration was low to moderate 0.05% respectively in the waste liquid, the recovery that still can make cobalt through the present invention was greater than 98%.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention; Be the residue temperature to be controlled at implement first step filtering separation in 55~90 ℃ of scopes; Filter to isolate solids wherein; TR when this TR is equal to the residue discharge basically, both energy-conservation, can avoid the big filtration velocity that influences of residue fluid viscosity again; When temperature is lower than 55 ℃, separate benzoic acid content rising in the solids that obtains, be unfavorable for returning again oxidation; When temperature was higher than 90 ℃, when particularly reaching 95 ~ 100 ℃, one deck thickness oily matter can appear in the filtrating top layer, and the cooling crisp shape thing of back overstrike is also still carried dope secretly, disturbs cobalt manganese and solubility organic acid to reclaim.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention, be that the processing mode of filtrating can be divided into following dual mode after flash trapping stage is deviate from insoluble organic acid solids: (I) adds oxalic acid in filtrating; The filtrating temperature is controlled at 60~100 ℃; The soluble substances such as phenylformic acid that contain in the solution this moment still are dissolved in the aqueous solution, can not influence the deposition and the filtration of cobalt oxalate manganese, and filtered while hot is promptly isolated cobalt manganese oxalate compound; Filtrating after the separation further is cooled to 30~5 ℃; Dissolved organic matters such as phenylformic acid will separate out, and carry out filtering separation again, and filtrating is sent wastewater treatment equipment; Solids is crude benzol formic acid, and purifying through the high temperature distillation to obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; Perhaps (II) directly is cooled to 30~5 ℃ with one-level filtrating; Dissolved organic matters such as phenylformic acid are separated out and carry out filtering separation, add oxalic acid in the filtrating after the separation again, controlled temperature is 30 ~ 100 ℃; The oxalate particle of the favourable cobalt manganese of high temperature increases and is convenient to and filters; The solution of isolating cobalt manganese oxalate is delivered to wastewater treatment equipment again, and in above-mentioned dual mode, the mol ratio of the cobalt manganese total amount in oxalic acid and the filtrating is 0.75~1.2: 1.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention, oxalic acid both can directly add with solid form, also can directly add the aqueous solution that contains oxalic acid 10~50%, and minimum with cost is principle.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention; Be that the cobalt manganese oxalate that separation obtains is carried out the homogeneous phase processing; Be about to cobalt manganese oxalate and oxidants hydrogen peroxide, Peracetic Acid, bromine, permanganic acid, mangaic acid, Manganse Dioxide or/and Hydrogen bromide reacts dissolving; And use the Cobaltous diacetate aqueous solution, the cobaltous bromide aqueous solution, the manganese acetate aqueous solution, the Manganese dibromide aqueous solution, acetic acid or/and pure water obtains a kind of homogeneous phase solution that contains cobalt manganese bromide anion as solvent and adjusting cobalt and manganese concentration, the mol ratio of cobalt manganese oxalate and hydrogen peroxide or Peracetic Acid is 1: 1.0~1.2 in the reaction process; The mol ratio of cobalt manganese oxalate and bromine or Manganse Dioxide or permanganic acid or mangaic acid is a stoichiometric ratio; Cobalt manganese oxalate and hydrobromic mol ratio are 1: 2.05~10.0.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention; Be cobalt manganese oxalate solution that dissolving is obtained further with cobalt, manganese or/and the Hydrogen bromide reaction, to eliminate free bromine residual in the solution, to reduce impurity such as free acid, iron.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention is 40~130 ℃ to the homogeneous phase treatment temp of cobalt manganese oxalate; When temperature was lower than 40 ℃, the decomposition rate of cobalt manganese oxalate was slow and decomposition is incomplete, can not get the solution of complete homogeneous phaseization; When temperature was higher than 130 ℃, although still can improve the speed of homogeneous phaseization, the corrodibility increase of bromine, pressure etc. required all will improve to the manufacturing of equipment and technology controlling and process, thus the present invention to select the homogeneous phase treatment temp be 40~130 ℃.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention, what obtain contains cobalt (Co 2+), manganese (Mn 2+), bromine (Br -) homogeneous phase solution can directly be mixed for allocating the catalyzer for preparing terephthalic acid by p-Xylol through oxidation through pumping and live catalyst or aqueous acetic acid etc.
The recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua of the present invention is directly to send PTA waste water reclamation treatment plant to handle the waste water behind separation of cobalt manganese oxalate and the organic acid.
Embodiment
Further specify the present invention through embodiment below:
Embodiment 1:
Get the oxidation residua 1000g of PTA oxidation (first) device, wherein cobalt contents is 0.92%, and manganese content is 0.95%; Solid content is 40.6%; Attemperation is at 65 ~ 70 ℃, and filtered while hot is separated solids wherein, and usefulness pact and the isopyknic 70 ℃ of hot washes of solids are once again; Be weighed as 181.4g after the solids drying, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; In filtrating, add solid oxalic acid (concentration of oxalic acid >=99.5%, down together) 41.67g, the mol ratio of cobalt manganese is 1: 1 in oxalic acid and the filtrating; Stirring is warming up to 80 ~ 85 ℃; Filtered while hot, isolated pink solid thing are cobalt manganese oxalate compound, and dry back quality is 56.51g; Wherein cobalt manganese content is respectively 16.14%, 15.32%, and the recovery of cobalt manganese is respectively 99.1% and 91.2%; Filtrating after the separation further is cooled to 10 ~ 5 ℃; Have a large amount of whites and faint yellow solid thing to separate out in the solution this moment, when no solids is separated out, and filtering separation; Filtrating is sent wastewater treatment equipment; Solids is crude benzol formic acid etc., is weighed as 203.1g through dehydrating, with this solids again high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; The cobalt manganese oxalate 20g that above-mentioned separation is obtained adds in the 250ml reactor drum, adds and contains cobalt 4% Cobaltous diacetate aqueous solution 120g, adds bromine 17.68g; The mol ratio of cobalt oxalate manganese and bromine is a stoichiometric ratio, and stirring heating is warming up to 85 ~ 90 ℃, notices that cooling for reflux is to prevent the bromine volatilization; After solids all dissolves; The Hydrogen bromide that in reactor drum, adds 20g cobalt metal and 10g48% again continues heating 30min, filters; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
Embodiment 2:
Embodiment 1 is separated the cobalt manganese oxalate 20g that obtains add in the 250ml reactor drum, add and contain manganese 6% manganese acetate aqueous solution 100g, adding 20g concentration is 48% Hydrogen bromide and slowly adds the 16.4g27.5% hydrogen peroxide; The mol ratio of cobalt oxalate manganese and hydrogen peroxide is about 1: 1.2, and stirring heating is warming up to 95 ~ 100 ℃, notes the bromine volatilization of cooling for reflux to produce in preventing to react; After solids all dissolves; In reactor drum, add the 20g cobalt metal again, continue the about 50min of heating, filter; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Embodiment 3:
Get the oxidation residua 500g of PTA oxidation (first) device; One times of thin up; Attemperation is at 85 ~ 90 ℃, and filtered while hot is separated solids wherein, and usefulness pact and the isopyknic 90 ℃ of hot washes of solids are once again; Be weighed as 81.5g after the solids drying, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; In filtrating, add oxalic acid 25.0g; The mol ratio of cobalt manganese is 1.2: 1 in oxalic acid and the filtrating, stirs and is warming up to 80 ~ 85 ℃, filtered while hot; Isolated pink solid thing is cobalt manganese oxalate compound; Dry back quality is about 29.57g, and wherein cobalt manganese content is respectively 15.48%, 15.95%, and the recovery of cobalt manganese is respectively 99.5% and 99.3%; Filtrating after the separation further is cooled to 20 ~ 15 ℃, and adularescent and faint yellow solid thing are separated out in the solution at this moment, and a small amount of brown oil appears in the solution upper strata; When no solids is separated out, filtering separation, filtrating is sent wastewater treatment equipment; Solids is crude benzol formic acid etc.; Its middle and upper part is weighed as 110.7g through dehydrating with a small amount of brown dope, with this solids again the high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; The cobalt manganese oxalate 20g that above-mentioned separation is obtained adds in the 250ml reactor drum; Add the Cobaltous diacetate aqueous solution 100g that contains cobalt 3%, manganese acetate aqueous solution 50g, the Glacial acetic acid min. 99.5 20g that contains manganese 6%; The stirring at normal temperature state drip down proven concentration be 98.12% permanganic acid 5.41g to reactor drum, the mol ratio of cobalt oxalate manganese and permanganic acid is 1: 0.4, dropwises post-heating and is warming up to 40 ~ 45 ℃; This moment, solids all dissolved; In reactor drum, add 20g cobalt metal and 20g concentration again and be 48% Hydrogen bromide, continue the about 30min of heating, filtration; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Embodiment 4:
Get the oxidation residua 750g behind the partly dehydrating of PTA oxidation (first) device; Add water 250g dilution; Attemperation is at 55 ~ 60 ℃, and filtered while hot is separated solids wherein, and usefulness pact and the isopyknic 60 ℃ of hot washes of solids are once again; Be weighed as 131.7g after the solids drying, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; Filtrating is cooled to 30 ~ 25 ℃, filters to isolate the solids of separating out, be weighed as 155.2g through dehydrating, with this solids again high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; Filtrating is heated to 40 ~ 45 ℃ also adds the aqueous solution 93.7g that contains 25% oxalic acid; The mol ratio of cobalt manganese is 0.75: 1 in oxalic acid and the filtrating, stirs, and promptly has a large amount of pink throw outs to separate out; Filtering separation is cobalt manganese oxalate compound; Dry back quality is 31.07g, and wherein cobalt manganese content is respectively 21.96%, 9.77%, and the recovery of cobalt manganese is respectively 98.9% and 42.6%; Filtrating after the separation is directly sent wastewater treatment equipment; The cobalt manganese oxalate 20g that above-mentioned separation is obtained adds in the 250ml reactor drum; Add the Cobaltous diacetate aqueous solution 100g that contains cobalt 3%, manganese acetate aqueous solution 100g, the Glacial acetic acid min. 99.5 20g that contains manganese 6%; The stirring at normal temperature state drip down proven concentration be 98.06% mangaic acid 6.78g to reactor drum, the mol ratio of cobalt oxalate manganese and mangaic acid is 1: 0.5, dropwises post-heating and is warming up to 60-65 ℃; This moment, solids all dissolved; In reactor drum, add 20g cobalt metal and 20g concentration again and be 48% Hydrogen bromide, continue the about 30min of heating, filtration; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Embodiment 5:
Get the oxidation residua 1000g of PTA oxidation (first) device, at air drying, make its solid content reach 45% after; Attemperation is at 85 ~ 90 ℃, and filtered while hot is separated solids wherein, finds solution thickness this moment; Filtration velocity is slower than embodiment 1 speed, and after having filtered, usefulness pact and isopyknic 90 ~ 95 ℃ of hot washes of solids are once again; Be weighed as 176.6g after the solids drying, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; In filtrating, add the aqueous solution 91.68g that contains 50% oxalic acid; The mol ratio of cobalt manganese is 1.1: 1 in oxalic acid and the filtrating, stirs and is warming up to 95 ~ 100 ℃, filtered while hot; Isolated pink solid thing is cobalt manganese oxalate compound; Dry back quality is 57.87g, and wherein cobalt manganese content is respectively 15.82%, 15.63%, and the recovery of cobalt manganese is respectively 99.5% and 95.2%; Filtrating after the separation further is cooled to 10 ~ 5 ℃, and have a large amount of whites and faint yellow solid thing to separate out in the solution this moment, and there is skim brown dope on the solution upper strata; When no solids is separated out; Filtering separation, filtrating send wastewater treatment equipment, solids to be crude benzol formic acid etc.; Be weighed as 206.9g through dehydrating, with this solids again high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; The cobalt manganese oxalate 20g that above-mentioned separation is obtained adds in the 100ml reactor drum, and adding concentration is 48% Hydrogen bromide 38.26g, and cobalt oxalate manganese and hydrobromic mol ratio are 1: 2.05; Be heated with stirring to 120 ~ 125 ℃, after the solids dissolving, be cooled to normal temperature; Filter; The solids oxalic acid that obtains recycles, and in filtrating, adds the 10g cobalt metal again, is heated to 100 ~ 105 ℃ and continues the about 60min of reaction; Filtrating is the homogeneous phase solution that contains cobalt manganese bromine, and this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Embodiment 6:
Embodiment 5 is separated the cobalt manganese oxalate 20g that obtains add in the 250ml reactor drum, add and contain cobalt 10%, brominated 28% cobaltous bromide solution 50g, contain manganese 6% manganese acetate aqueous solution 100g; Slowly adding 42.5g concentration is 20% Peracetic Acid; The mol ratio of cobalt oxalate manganese and Peracetic Acid is about 1: 1, and stirring heating is warming up to 95 ~ 100 ℃, notes the bromine volatilization of cooling for reflux to produce in preventing to react; After solids all dissolves; In reactor drum, add 2g manganese metal and 12g Hydrogen bromide again, continue reaction 50min, filter; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Embodiment 7:
Get the oxidation residua 1000g of PTA oxidation (second) device; Wherein solid content is 33.6%, and cobalt contents is 0.65%, and manganese content is 0.70%; Attemperation is at 65 ~ 70 ℃; Filtered while hot separate wherein solids and with approximately with the isopyknic 70 ℃ of hot washes of solids once, be weighed as 125.9g after the solids drying, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; In filtrating, add the aqueous solution 301.5g that contains 10% oxalic acid; The mol ratio of cobalt manganese is about 1: 1 in oxalic acid and the filtrating; Stirring is warming up to 80 ~ 90 ℃, and filtered while hot is isolated pink cobalt manganese oxalate, and dry back quality is 40.90g; Wherein cobalt manganese content is respectively 15.78%, 15.66%, and the recovery of cobalt manganese is respectively 99.3% and 91.5%; Filtrating after the separation further is cooled to 10 ~ 5 ℃; Have a large amount of whites and faint yellow solid thing to separate out in the solution this moment, when no solids is separated out, and filtering separation; Filtrating is sent wastewater treatment equipment; Solids is crude benzol formic acid etc., is weighed as 192.2g through dehydrating, with this solids again high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; The 40.90g cobalt manganese oxalate that above-mentioned separation is obtained all adds in the 500ml reactor drum, and adding concentration is 48% Hydrogen bromide 381.5g, and cobalt oxalate manganese and hydrobromic mol ratio are 1: 10; Be heated with stirring to 120 ~ 125 ℃, after the solids dissolving, be cooled to normal temperature; Filter; The solids oxalic acid that obtains recycles, and in filtrating, adds 30g cobalt metal and 5g manganese metal again, is heated to 120 ~ 125 ℃ and continues the about 60min of reaction; Filtrating is the homogeneous phase solution that contains cobalt manganese bromine, and the oxide catalyst that this mixed solution can directly mix with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide as PTA perhaps send reactor drum and cobalt metal or/and manganese metal further reacts.
 
Embodiment 8:
Get the oxidation residua 1000g of PTA oxidation (second) device; Attemperation is at 55 ~ 60 ℃; Filtered while hot is separated solids wherein; Usefulness pact and the isopyknic 60 ℃ of hot washes of solids once are weighed as 128.2g after the solids drying again, directly return oxidation system and reoxidize or sell the raw material that is used for synthetic resins; Filtrating is cooled to 10 ~ 5 ℃, filters to isolate the solids of separating out, be weighed as 191.1g through dehydrating, with this solids again high temperature distillation purify and can obtain meeting the purified petroleum benzin formic acid of pharmaceutical grade standard; Filtrating is heated to 50 ~ 55 ℃ and add solid oxalic acid 36g; The mol ratio of cobalt manganese is about 1.2: 1 in oxalic acid and the filtrating, stirs, and pink throw out cobalt manganese oxalate is separated out; Filtering separation; Dry back quality is 42.63g, and wherein cobalt manganese content is respectively 15.16%, 16.26%, and the recovery of cobalt manganese is about 99.4% and 99.0% respectively; Filtrating after the separation is directly sent wastewater treatment equipment; The cobalt manganese oxalate 30g that above-mentioned separation is obtained adds in the 250ml reactor drum, adds the manganese acetate aqueous solution 30g that contains the aqueous acetic acid 50g of cobalt 3% and contain manganese 6%, and adding concentration is 48% Hydrogen bromide 84g; Cobalt oxalate manganese and hydrobromic mol ratio are 1: 3; Be heated with stirring to boiling, after the solids dissolving, be cooled to normal temperature; Filter; The solids oxalic acid that obtains recycles, and filtrating is the homogeneous phase solution that contains cobalt manganese bromine, and this mixed solution can directly mix with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide as the oxide catalyst of PTA perhaps to be sent to cobalt metal or/and manganese metal further reacts.
Embodiment 9:
Get the oxidation residua 1000g of PTA oxidation (second) device; Repeat the preceding two-stage sepn process of embodiment 6, contain washing and obtain about 820g altogether and do not add oxalic acid filtrating, get 2 parts of preceding filtratings respectively; Wherein 1 part is 41g; Thin up is to 650g, makes wherein that cobalt contents is about 0.05%, and this moment, manganese content was about 0.054%; In addition 1 part be 410g, heats to be concentrated into 216g, makes wherein that concentration of cobalt ions is about 1.5%, and manganese content is about 1.62% at this moment; The 1st part of solution is heated to 40 ~ 45 ℃ adds oxalic acid again; The 2nd part of solution concentration directly added oxalic acid after intact therein; The oxalic acid add-on is produced as benchmark to no longer include deposition in the solution; The 1st part and the 2nd part of solution consumption oxalic acid are respectively 1.82g and 16.16g, and according to cobalt manganese content meter in the PTA residue liquid, the 1st part and the 2nd part oxalic acid and the mol ratio of cobalt manganese are about 1.2: 1 respectively and 1.1: 1; The oxalate precipitation that obtains is merged filtering separation, and dry back quality is 23.49g, and wherein cobalt manganese content is respectively 15.14%, 16.28%, and the recovery of cobalt manganese is about 99.5% and 99.3% respectively; The cobalt manganese oxalate that above-mentioned separation is obtained all adds in the 250ml reactor drum; Adding 50g contains cobalt 10%, brominated 28% the cobaltous bromide aqueous solution, 50g to contain manganese 10%, brominated 30% the Manganese dibromide aqueous solution and 20g concentration is 48% Hydrogen bromide; Adding content again is 99.82% Manganse Dioxide 11.32g, and the mol ratio of cobalt oxalate manganese and Manganse Dioxide is 1: 1, and stirring heating is warming up to 125 ~ 130 ℃; Note the bromine volatilization of cooling for reflux to produce in preventing to react; After the pink solid dissolving, in reactor drum, add the 20g cobalt metal again, continue heating 50min; Filter the homogeneous phase solution that promptly obtains containing cobalt manganese bromine, this mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide.
 
Use nomenclature among the present invention:
%: mass percent; G: gram; Min: minute.
The measuring method of solid content is that the PTA oxidation residua is carried out weighing after the dehydration fully of atmospheric low-temperature slow-drying among the present invention.
Cobalt manganese Determination on content is to adopt volumetry among the present invention.
Employed permanganic acid, mangaic acid are demarcated to confirm content through the oxalate volumetry before use among the present invention; The content of Manganse Dioxide is through iodine and Sulfothiorine volumetric determination.
The recovery calculation formula of cobalt manganese is among the present invention:
The cobalt of measuring in the original residue of quality ÷ of cobalt or manganese in the oxalate that the recovery %=recovery of cobalt or manganese obtains or quality * 100% of manganese.
The stoichiometric equation of chemical reaction that relates among the present invention is:
(1)Co 2++H 2C 2O 4·2H 2O(S)=CoC 2O 4·2H 2O(S)+?2H +
(2)Mn 2++H 2C 2O 4·2H 2O(S)=MnC 2O 4·2H 2O(S)?+2H +
(3)CoC 2O 4(S)+Br 2(L)=CoBr 2(L)+2CO 2(g)
(4)MnC 2O 4(S)+Br 2(L)=MnBr 2(L)+2CO 2(g)
(5)CoC 2O 4(S)+CH 3COOOH(L)+2HBr(L)=CoBr 2(L)+2CO 2(g)+CH 3COOH(L)+H 2O(L)?(6)MnC 2O 4(S)+CH 3COOOH(L)+2HBr(L)=MnBr 2(L)+2CO 2(g)+CH 3COOH(L)+H 2O(L)
(7)CoC 2O 4(S)+2HBr(L)+H 2O 2(L)=CoBr 2(L)+2CO 2(g)+2H 2O(L)
(8)MnC 2O 4(S)+2HBr(L)+H 2O 2(L)=MnBr 2(L)+2CO 2(g)+2H 2O(L)
(9)?CoC 2O 4(S)+2HBr(L)=CoBr 2(L)+H 2C 2O 4(S)
(10)MnC 2O 4(S)+2HBr(L)=MnBr 2(L)+H 2C 2O 4(S)
(11)2CoC 2O 4(S)+H 2MnO 4(L)+6H +=2Co 2+(L)+Mn 2+(L)+4CO 2(g)+4H 2O(L)?(12)2MnC 2O 4(S)+H 2MnO 4(L)+6H +=3Mn 2+(L)+4CO 2(g)+4H 2O(L)
(13)5CoC 2O 4(S)+2HMnO 4(L)+14H +=5Co 2+(L)+2Mn 2+(L)+10CO 2(g)+8H 2O(L)
(14)5MnC 2O 4(S)+2HMnO 4(L)+14H +=7Mn 2+(L)+10CO 2(g)+8H 2O(L)
(15)?CoC 2O 4(S)+MnO 2(s)+4HBr=CoBr 2(L)+MnBr 2(L)+2CO 2(g)+2H 2O(L)
(16)?MnC 2O 4(S)+MnO 2(s)+4HBr=2MnBr 2(L)+2CO 2(g)+2H 2O(L)
(17)?Co(S)+Br 2(L)=CoBr 2(L)
(18)?Mn(S)+Br 2(L)=MnBr 2(L)
(19)?2Fe 2++Br 2(L)=2Fe 3++2Br -(L)
(20)?2Fe 2++H 2O 2(L)?+2H +=2Fe 3++2H 2O
(21)Fe 2++CH 3COOOH(L)+H +=Fe 3++H 2O+CH 3COO -
S represents solid in the equation bracket; L represents liquid.
Can find out that from the foregoing description 1 to 9 compared with prior art, the present invention has following characteristics:
⑴ the present invention has made full use of the waste heat of PTA residue directly carrying out filtering separation more than 55 ℃, has both utilized the residue energy, has reduced the residue viscosity when filtering again, has made things convenient for filtration.
⑵ the present invention has made full use of the water-soluble characteristic of organic acid and has filtered, and makes the organism of recovery obtain convenient the utilization, has increased added value.
⑶ the cobalt manganese that the present invention will reclaim from residue has directly changed into catalyzer, and the recovery is high, has saved PTA catalyzer cost.
⑷ the present invention is to the recovery method of organic acid in the residue and Co-Mn metal, and technology is simple, flow process is short, energy consumption is low.
⑸ the present invention has reduced environmental pollution to the recovery method of organic acid in the residue and Co-Mn metal.

Claims (6)

1. the recovery method of organic acid and Co-Mn metal in the terephthalic acid oxidation residua; It is characterized in that the high temperature oxidation residue that will from terephthalic acid (be called for short PTA) production equipment, discharge, the control solid content is implemented first step filtering separation in 20~45% scopes and in 55~90 ℃ of scopes of temperature, and isolated solids sells and is used to make the monomer of resin or paint or returns the use of PTA oxidation reactor; One-level filtrating is handled by following process: (I) adds oxalic acid in one-level filtrating; The filtrating temperature is controlled at 60~100 ℃, obtains cobalt manganese oxalate precipitation, filters to isolate cobalt manganese oxalate; Filtrating further is cooled to 30~5 ℃; Carry out filtering separation again, the solids after the separation is used to extract phenylformic acid, and filtrating is sent wastewater treatment equipment; Perhaps (II) directly is cooled to 30~5 ℃ with one-level filtrating; Carry out second stage filtering separation, the solids after the separation is used to extract phenylformic acid, in secondary filtrating, adds oxalic acid; Controlled temperature is 30 ~ 100 ℃; Obtain cobalt manganese oxalate precipitation, filter to isolate cobalt manganese oxalate, filtrating is sent wastewater treatment equipment; With above-mentioned (I) perhaps the cobalt manganese oxalate that obtains of (II) process and oxidants hydrogen peroxide, Peracetic Acid, bromine, permanganic acid, mangaic acid, Manganse Dioxide or/and Hydrogen bromide react; And use the Cobaltous diacetate aqueous solution, the cobaltous bromide aqueous solution, the manganese acetate aqueous solution, the Manganese dibromide aqueous solution, acetic acid or/and pure water as solvent; After solids all dissolves; In reactor drum, add cobalt metal, manganese metal or/and Hydrogen bromide continues heating 30 ~ 60min, filter; Promptly obtain containing the homogeneous phase solution of cobalt manganese bromine; This mixed solution can directly mix the oxide catalyst as PTA with Cobaltous diacetate, manganese acetate, cobaltous bromide, Manganese dibromide, acetic acid or water, and wherein, the mol ratio of cobalt manganese oxalate and hydrogen peroxide or Peracetic Acid is 1: 1.0~1.2; The mol ratio of cobalt manganese oxalate and bromine or Manganse Dioxide or permanganic acid or mangaic acid is stoichiometric ratio; Cobalt manganese oxalate and hydrobromic mol ratio are 1: 2.05~10.0.
2. according to the recovery method of organic acid and Co-Mn metal in the described a kind of terephthalic acid oxidation residua of claim l, oxalic acid both can directly add with solid form, also can be made into the aqueous solution that contains oxalic acid 10~50% and added.
3. according to the recovery method of organic acid and Co-Mn metal in the described a kind of terephthalic acid oxidation residua of claim l, the mol ratio of the cobalt manganese total amount in it is characterized in that oxalic acid and filtrating is 0.75~1.2: 1.
4. according to the recovery method of organic acid and Co-Mn metal in the described a kind of terephthalic acid oxidation residua of claim l, it is characterized in that the homogeneous phase treatment temp to cobalt manganese oxalate is 40 ~ 130 ℃.
5. according to the recovery method of organic acid and Co-Mn metal in the described a kind of terephthalic acid oxidation residua of claim l, the homogeneous phase processing of cobalt manganese deposition and cobalt manganese oxalate all is under normal pressure, to carry out.
6. according to the recovery method of organic acid and Co-Mn metal in the described a kind of terephthalic acid oxidation residua of claim l; Cobalt manganese oxalate solution that it is characterized in that dissolving is obtained and cobalt, manganese are or/and the Hydrogen bromide reaction, to eliminate free bromine residual in the solution, to reduce impurity such as free acid, iron.
CN2011102826807A 2011-09-22 2011-09-22 Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue Active CN102503813B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011102826807A CN102503813B (en) 2011-09-22 2011-09-22 Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011102826807A CN102503813B (en) 2011-09-22 2011-09-22 Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue

Publications (2)

Publication Number Publication Date
CN102503813A true CN102503813A (en) 2012-06-20
CN102503813B CN102503813B (en) 2013-12-25

Family

ID=46215964

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011102826807A Active CN102503813B (en) 2011-09-22 2011-09-22 Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue

Country Status (1)

Country Link
CN (1) CN102503813B (en)

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104844445A (en) * 2015-03-27 2015-08-19 中国昆仑工程公司 Method for recycling acetic acid from blanking residues of PTA (purified terephthalic acid) film evaporator
CN105274345A (en) * 2015-11-27 2016-01-27 江苏理工学院 Method for separating cobalt and manganese in cobalt-manganese waste
CN105688990A (en) * 2016-01-22 2016-06-22 福建洋屿环保科技股份有限公司 Method for regenerating cobalt and manganese acetate compound catalyst from PTA (Pure Terephthalic Acid) oxidization residues
CN106432622A (en) * 2016-09-27 2017-02-22 辽阳合成催化剂有限公司 Method for preparing unsaturated polyester resin from reclaimed material containing saturated binary acid
CN107176745A (en) * 2016-03-09 2017-09-19 王仲甫 The method for biologically treating wastewater of polybasic carboxylic acid residue
CN107597170A (en) * 2017-10-28 2018-01-19 浙江上虞利星化工有限公司 Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN107617445A (en) * 2017-10-28 2018-01-23 浙江上虞利星化工有限公司 Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN107652177A (en) * 2017-10-28 2018-02-02 浙江上虞利星化工有限公司 A kind of preparation method of cobalt or/and manganese acetate
CN107803211A (en) * 2017-10-28 2018-03-16 浙江上虞利星化工有限公司 Preparation method of cobalt or/and manganese bromide
CN108367942A (en) * 2015-12-31 2018-08-03 Bp北美公司 The method for recycling heavy metal ion
CN109592715A (en) * 2018-12-21 2019-04-09 陕西师范大学 A method of using two hydration terephthalic acid (TPA) manganese as presoma controllable preparation different structure manganese oxide
CN113292498A (en) * 2021-06-16 2021-08-24 浙江工业大学 3-peroxybenzoic acid-1-methylimidazole chloride salt and preparation and application thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4490297A (en) * 1981-12-24 1984-12-25 Dynamit Nobel Ag Method for the recovery and reuse of cobalt and/or manganese components of catalysts
CN101177394A (en) * 2006-11-08 2008-05-14 美琪玛国际股份有限公司 Crude terephthalic acid (CTA) residue recovery and catalyst purification regeneration system and method

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4490297A (en) * 1981-12-24 1984-12-25 Dynamit Nobel Ag Method for the recovery and reuse of cobalt and/or manganese components of catalysts
CN101177394A (en) * 2006-11-08 2008-05-14 美琪玛国际股份有限公司 Crude terephthalic acid (CTA) residue recovery and catalyst purification regeneration system and method

Cited By (21)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104844445B (en) * 2015-03-27 2017-06-20 中国昆仑工程有限公司 The method of recovery of acetic acid from PTA thin film evaporator blanking residues
CN104844445A (en) * 2015-03-27 2015-08-19 中国昆仑工程公司 Method for recycling acetic acid from blanking residues of PTA (purified terephthalic acid) film evaporator
CN105274345A (en) * 2015-11-27 2016-01-27 江苏理工学院 Method for separating cobalt and manganese in cobalt-manganese waste
CN105274345B (en) * 2015-11-27 2017-09-29 江苏理工学院 The method of cobalt and manganese in separating and recovering cobalt manganese waste material
CN107828965B (en) * 2015-11-27 2019-04-23 江苏理工学院 A kind of method of cobalt and manganese in separating and recovering cobalt manganese waste material
CN107828965A (en) * 2015-11-27 2018-03-23 江苏理工学院 A kind of method of cobalt and manganese in separating and recovering cobalt manganese waste material
CN108367942A (en) * 2015-12-31 2018-08-03 Bp北美公司 The method for recycling heavy metal ion
CN105688990A (en) * 2016-01-22 2016-06-22 福建洋屿环保科技股份有限公司 Method for regenerating cobalt and manganese acetate compound catalyst from PTA (Pure Terephthalic Acid) oxidization residues
CN105688990B (en) * 2016-01-22 2019-02-26 福建洋屿环保科技股份有限公司 A method of regenerating cobalt acetate manganese composite catalyst from PTA oxidation residua
CN107176745A (en) * 2016-03-09 2017-09-19 王仲甫 The method for biologically treating wastewater of polybasic carboxylic acid residue
CN106432622A (en) * 2016-09-27 2017-02-22 辽阳合成催化剂有限公司 Method for preparing unsaturated polyester resin from reclaimed material containing saturated binary acid
CN106432622B (en) * 2016-09-27 2019-01-01 辽阳合成催化剂有限公司 A method of reclaimed materials containing monounsaturated dicarboxylic acid prepares unsaturated polyester resin
CN107803211A (en) * 2017-10-28 2018-03-16 浙江上虞利星化工有限公司 Preparation method of cobalt or/and manganese bromide
CN107652177A (en) * 2017-10-28 2018-02-02 浙江上虞利星化工有限公司 A kind of preparation method of cobalt or/and manganese acetate
CN107617445A (en) * 2017-10-28 2018-01-23 浙江上虞利星化工有限公司 Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN107597170A (en) * 2017-10-28 2018-01-19 浙江上虞利星化工有限公司 Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN107803211B (en) * 2017-10-28 2019-06-28 浙江上虞利星化工有限公司 Preparation method of cobalt or/and manganese bromide
CN107617445B (en) * 2017-10-28 2019-12-27 浙江上虞利星化工有限公司 Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN109592715A (en) * 2018-12-21 2019-04-09 陕西师范大学 A method of using two hydration terephthalic acid (TPA) manganese as presoma controllable preparation different structure manganese oxide
CN113292498A (en) * 2021-06-16 2021-08-24 浙江工业大学 3-peroxybenzoic acid-1-methylimidazole chloride salt and preparation and application thereof
CN113292498B (en) * 2021-06-16 2022-11-25 浙江工业大学 3-peroxybenzoic acid-1-methylimidazole chloride salt and preparation and application thereof

Also Published As

Publication number Publication date
CN102503813B (en) 2013-12-25

Similar Documents

Publication Publication Date Title
CN102503813B (en) Method for recovering organic acid and cobalt manganese metal in terephthalic acid oxidation residue
CN105017022A (en) Method for methyl esterification recovery and recycle of PTA oxidation residue
CN105688990A (en) Method for regenerating cobalt and manganese acetate compound catalyst from PTA (Pure Terephthalic Acid) oxidization residues
CN102199082A (en) Recovery of aromatic carboxylic acids and oxidation catalyst
CN103183607B (en) A kind of production method mixing fragrant dioctyl phthalate
CN105274345A (en) Method for separating cobalt and manganese in cobalt-manganese waste
CN101365673B (en) Method for high-purity terephthalic acid preparation
CN112441907A (en) Method for co-producing mono-substituted methyl benzoic acid and mono-substituted phthalic acid
CN110078601A (en) The method that polyoxometallate efficient catalytic paraxylene prepares p-tolyl aldehyde
CN102381947B (en) Synthesis method of chiral 2,2 '- di-alkoxy-1, 1'-binaphthyl
CN105110537B (en) A kind for the treatment of of DSD acid oxidized waste water and its recovery method as resource
CN112340706A (en) Method for separating and purifying 2-methylanthraquinone from sulfuric acid
CN108530326A (en) A kind of preparation method of 2- nitryl-4-thiamphenicol benzoic acids
CN105111074B (en) A kind of alkali decrement waste water solid residue esterification recoverying and utilizing method
CN104086462B (en) 5-sodium sulfo isophthalate method is extracted in a kind of three monomer factory effluents
CN102137707A (en) Process and equipment for recovery of valuable materials from terephthalic acid manufacture
CN105349790A (en) Method of separating and recycling cobalt and manganese in low-cobalt high-manganese waste by ammonia-ammonium bicarbonate
WO2009064037A1 (en) Recovery of catalysts, benzoic acid and aromatic acid
CN107617445B (en) Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN107597170B (en) Method for preparing cobalt-manganese-bromine aqueous solution by utilizing recovered cobalt and manganese
CN205216527U (en) Processing apparatus of manganese acetate production tail gas
CN103319383A (en) Preparation method of p-methylsulfonylbenzoic acid
CN103566979A (en) Regeneration method for cobalt-manganese catalyst in p-xylene oxidation mother liquor
CN114591165B (en) Method for preparing plasticizer by purifying PTA residues
US4876385A (en) Batch or semicontinuous pseudocumene oxidation and catalyst recovery and recycle

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20180416

Address after: 312369 No. 15 Wei five road, Hangzhou Bay Economic and Technological Development Zone, Shangyu District, Shaoxing, Zhejiang

Co-patentee after: JINAN ZHAOHUI TECHNOLOGY Co.,Ltd.

Patentee after: ZHEJIANG SHANGYU LIXING CHEMICAL CO.,LTD.

Address before: 250100 Room 102, unit 50, 50 building, 5 Huayuan Road, Licheng District, Ji'nan, Shandong

Patentee before: Cao Shanwen

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20220512

Address after: 312369 No. 15, Weiwu Road, Hangzhou Bay Economic and Technological Development Zone, Shangyu, Shaoxing City, Zhejiang Province

Patentee after: ZHEJIANG SHANGYU LIXING CHEMICAL CO.,LTD.

Address before: 312369 No. 15 Wei five road, Hangzhou Bay Economic and Technological Development Zone, Shangyu District, Shaoxing, Zhejiang

Patentee before: ZHEJIANG SHANGYU LIXING CHEMICAL CO.,LTD.

Patentee before: JINAN ZHAOHUI TECHNOLOGY Co.,Ltd.

CP01 Change in the name or title of a patent holder
CP01 Change in the name or title of a patent holder

Address after: 312369 No. 15, Weiwu Road, Hangzhou Bay Economic and Technological Development Zone, Shangyu, Shaoxing City, Zhejiang Province

Patentee after: Zhejiang Lixing Technology Co.,Ltd.

Address before: 312369 No. 15, Weiwu Road, Hangzhou Bay Economic and Technological Development Zone, Shangyu, Shaoxing City, Zhejiang Province

Patentee before: ZHEJIANG SHANGYU LIXING CHEMICAL CO.,LTD.