CN114988435A - Harmless treatment method for saline water in polyphenylene sulfide resin production - Google Patents

Harmless treatment method for saline water in polyphenylene sulfide resin production Download PDF

Info

Publication number
CN114988435A
CN114988435A CN202210668084.0A CN202210668084A CN114988435A CN 114988435 A CN114988435 A CN 114988435A CN 202210668084 A CN202210668084 A CN 202210668084A CN 114988435 A CN114988435 A CN 114988435A
Authority
CN
China
Prior art keywords
evaporation
brine
polyphenylene sulfide
temperature
sulfide resin
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202210668084.0A
Other languages
Chinese (zh)
Inventor
李乃杰
刘秉臣
任冰涛
王志武
王鹏
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.)
Shandong Minghua New Material Co ltd
Original Assignee
Shandong Minghua New Material Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shandong Minghua New Material Co ltd filed Critical Shandong Minghua New Material Co ltd
Priority to CN202210668084.0A priority Critical patent/CN114988435A/en
Publication of CN114988435A publication Critical patent/CN114988435A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/14Purification
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Polymers With Sulfur, Phosphorus Or Metals In The Main Chain (AREA)

Abstract

The invention discloses a harmless treatment method of brine in polyphenylene sulfide resin production, which comprises the following steps: primary evaporation: carrying out primary evaporation crystallization on the washing strong brine to generate miscellaneous salt, cooling, crystallizing and centrifugally drying the evaporation mother liquor to obtain a product sodium acetate, and recycling the product sodium acetate system; pyrolyzing miscellaneous salt; dissolving the solution; membrane filtration; and (3) secondary evaporation, namely, performing multistage evaporation or MVR evaporation crystallization on the brine after membrane filtration, drying by a fluidized bed to obtain a product sodium chloride with the water content lower than 0.2%, and conveying the mother liquor to primary evaporation for recycling. The harmless treatment method of the brine in the production of the polyphenylene sulfide resin solves the difficult problems in the polyphenylene sulfide industry, reduces the industrial bottleneck again, reduces the environmental protection risk, has simple process, is easy to operate and control, has small equipment investment and high recovery rate.

Description

Harmless treatment method for saline water in polyphenylene sulfide resin production
Technical Field
The invention relates to the technical field of polyphenylene sulfide production, in particular to a harmless treatment method of saline water in polyphenylene sulfide resin production.
Background
Polyphenylene sulfide is a special engineering plastic with excellent mechanical properties, has excellent heat resistance, electrical properties and rigidity, and is widely applied to various material fields, such as automobiles and electronic and electrical parts. At present, the method for producing polyphenylene sulfide usually employs a condensation polymerization reaction of a dihalo-substituted aromatic compound and an alkali metal sulfide in a polar organic solvent, for example, p-dichlorobenzene and sodium sulfide are polymerized in an N-methyl-2-pyrrolidone solvent at high temperature and high pressure to prepare a slurry containing polyphenylene sulfide resin, and the slurry is filtered and recovered to obtain the polyphenylene sulfide resin. However, in the above-mentioned production process of polyphenylene sulfide resin, p-dichlorobenzene and sodium sulfide are polymerized to produce polyphenylene sulfide resin, and sodium chloride as a by-product is also produced, and the produced sodium chloride is insoluble in N-methyl-2-pyrrolidone solvent, and at the same time, a small amount of polyphenylene sulfide oligomer, that is, low molecular weight substances such as polyphenylene sulfide trimer, polyphenylene sulfide tetramer, etc. is also produced during the polymerization. In the existing production process of polyphenylene sulfide resin, a large amount of brine is generated, the brine contains sodium chloride, lithium carbonate, low-carbon chain organic matters and the like, and no effective utilization method is available for the brine so far, so that the environment is polluted.
Disclosure of Invention
The invention aims to provide a harmless treatment method of brine in polyphenylene sulfide resin production, which solves the difficult problems in the polyphenylene sulfide industry, reduces the industrial bottleneck again, reduces the environmental protection risk, has simple process, is easy to operate and control, has small equipment investment and high recovery rate.
In order to achieve the aim, the invention provides a harmless treatment method of brine in polyphenylene sulfide resin production, which comprises the following steps:
s1, primary evaporation: carrying out primary evaporation crystallization on the washing strong brine to generate mixed salt, cooling, crystallizing and centrifugally drying the evaporation mother liquor to obtain a product sodium acetate, and recycling the product sodium acetate system;
s2, pyrolyzing miscellaneous salts: continuously adding the miscellaneous salt into a special electric heating furnace through a spiral pusher, controlling the environment and the temperature in the electric heating furnace and keeping the retention time, and converting organic matters in the miscellaneous salt into crude salt;
s3, dissolving the solution: dissolving the pyrolyzed crude salt in a first reaction kettle by using an aqueous solution doped with hydrochloric acid, wherein the pH value is less than 2, overflowing the saline water dissolved in the first reaction kettle into a second reaction kettle, adding sodium hydroxide, and changing impurities dissolved in a liquid phase into solid impurities, wherein the pH value is 6.5 to obtain saline water;
s4, membrane filtration: separating solid impurities out of the system by the saline water through a multistage tubular membrane filter to be used as common solid waste filter residues;
and S5, secondary evaporation, namely, carrying out multistage evaporation or MVR evaporation crystallization on the brine filtered by the membrane in the S4, drying the brine by a fluidized bed to obtain a product sodium chloride with the water content of less than 0.2%, and conveying the mother liquor to primary evaporation for recycling.
Preferably, the primary evaporative crystallization in step S1 is specifically: the washing concentrated brine is directly introduced into a multi-stage countercurrent evaporator at 70 ℃ at 60 ℃, the mixed salt is taken out from the last stage at 110 ℃, and then centrifugal separation is carried out to keep impurities in the evaporation mother liquor.
Preferably, the cooling crystallization in step S1 specifically includes: and (3) putting the evaporation mother liquor into a cooling kettle, cooling the evaporation mother liquor to less than 10 ℃ through circulating water and low-temperature water, and then centrifugally drying and separating until the moisture content is less than 3% to obtain the product sodium acetate.
Preferably, the temperature of the circulating water is reduced to 60 ℃, and the temperature of the low-temperature water is reduced to 10 ℃.
Preferably, the environment of the special electric heating furnace in the miscellaneous salt pyrolysis of the step S2 is an oxygen-insulated environment, the temperature is 500-750 ℃, and the retention time is kept for 2-4 h.
Preferably, the temperature of the special electric heating furnace is lower than the melting temperature of sodium chloride and higher than the decomposition temperature of organic matters.
Preferably, the dissolution temperature of the first reaction kettle in the step S3 is 40-70 ℃.
Preferably, the membrane filtration temperature of the step S4 is 40-60 ℃.
Preferably, the temperature of the secondary evaporation in the step S5 is 120 ℃, and the reflux amount of the mother liquor conveyed to the primary evaporation is 0.5m 3 /h。
Therefore, the harmless treatment method for the brine in the production of the polyphenylene sulfide resin has the following beneficial effects:
(1) the process is simple, easy to operate and control, the equipment investment is small, the recovery rate is high, the product purity is high, no production wastewater is discharged, the requirement of environmental protection is met, and better economic and social benefits are achieved;
(2) the pyrolysis temperature is controlled to be 300-500 ℃, the calcination time is 1-3 hours, the time is reduced by 50% compared with the time of the existing process on the market, the organic matter removal rate is 99.5% higher than that of the existing process, the sodium acetate product is white in color and high in purity and can be recycled, and a tail gas treatment system is installed in the pyrolysis furnace, so that toxic and harmful substances in the smoke are eliminated, and the environment is protected;
(3) the purity of the refined sodium chloride product is more than or equal to 98.5 percent and the TOC is less than or equal to 30 after twice evaporation and crystallization, the purity is higher than the standards of T/CCT002-2019 coal chemical industry byproduct industrial sodium chloride and QBT5270-2018 ionic membrane caustic soda salt, and the economic value is high;
(4) no hazardous waste is generated, the filter residue is common solid waste, the difficult problem of the polyphenylene sulfide industry is thoroughly solved, the industrial bottleneck is reduced again, the environmental protection risk is reduced, and the industrial value is very high.
The technical solution of the present invention is further described in detail by the accompanying drawings and embodiments.
Drawings
FIG. 1 is a flow chart of an embodiment of the present invention, wherein the crude salt A is a mixed salt of sodium chloride and sodium acetate.
Detailed Description
The invention provides a harmless treatment method of brine in polyphenylene sulfide resin production, which comprises the following steps:
s1, primary evaporation: washing strong brine (brine to be treated) is subjected to primary evaporation crystallization, and the primary evaporation crystallization is specifically to be used for washing strong brineDirectly introducing the mixed salt into a 70 ℃ multistage countercurrent evaporator at 60 ℃, taking out the mixed salt from the last stage at 110 ℃, then performing centrifugal separation, retaining impurities in evaporation mother liquor, putting the evaporation mother liquor into a cooling kettle, cooling the evaporation mother liquor to less than 10 ℃ through circulating water and low-temperature water, then performing centrifugal drying separation until the moisture content is less than 3 percent to obtain a product sodium acetate, and recycling the product sodium acetate system, wherein the circulating water is cooled to 60 ℃, and the low-temperature water is cooled to 10 ℃. Primary evaporation crystallization procedure H is added into the solution separated from the water washing procedure 2 O 2 Adjusting and maintaining the pH value to be 7-8, evaporating and concentrating by 20-40 times, drying, screening, and producing crude sodium chloride. The preferred conditions are countercurrent evaporation and 120 deg.c high temperature discharge, and 98% organic matter is maintained in the evaporating mother liquid to the maximum.
S2, pyrolyzing miscellaneous salts: continuously adding the miscellaneous salt into a special electric heating furnace through a spiral pusher, controlling the environment of the electric heating furnace to be an anaerobic environment at the temperature of 500-; the temperature of the special electric heating furnace is lower than the melting temperature of sodium chloride and higher than the decomposition temperature of organic matters. Organic matters in the salt are removed, and a tail gas treatment system is arranged in the furnace, so that the smoke gas is discharged up to the standard. The electric furnace for pyrolysis has simple and safe structure compared with natural gas, convenient maintenance and temperature control precision of +/-0.5 ℃.
S3, dissolving the solution: dissolving the pyrolyzed crude salt in a first reaction kettle by using an aqueous solution doped with hydrochloric acid, wherein the dissolving temperature is 40-70 ℃, the pH value is less than 2, overflowing the saline water dissolved in the first reaction kettle into a second reaction kettle, adding sodium hydroxide, and changing impurities dissolved in a liquid phase into solid impurities, wherein the pH is 6.5, so as to obtain saline water; and washing crude lithium carbonate obtained in the water leaching filtration and precipitation filtration process by deionized water for several times, carrying out solid-liquid separation and drying to obtain a lithium carbonate product, and returning washing liquor to the solution in the evaporation crystallization process.
S4, membrane filtration: the salt water passes through a multi-stage tubular membrane filter to separate solid impurities out of the system to be used as common solid waste filter residues, and the membrane filtration temperature is 40-60 ℃. The membrane filtration process is that salt water enters a multi-stage tubular ultrafiltration membrane element after passing through a bag filter by a pump, clear liquid enters a collection tank, concentrated liquid returns to a raw material tank, the membrane precision is preferably 30nm, and the number of components is more than 8. In the washing procedure, hot deionized water is used for washing 3-5 times according to the solid-liquid ratio of 1: 0.5-1.5.
S5, secondary evaporation, namely, carrying out multistage evaporation or MVR evaporation crystallization on the salt water subjected to membrane filtration in the S4 at 120 ℃, drying the salt water by a fluidized bed to obtain a product sodium chloride with the water content of less than 0.2%, conveying the mother liquor to primary evaporation for recycling, and conveying the mother liquor to the primary evaporation with the reflux amount of 0.5m 3 /h。
The technical scheme of the invention is further explained by the attached drawings and the embodiment.
Examples
In the chemical production process of the chlor-alkali industry, a large amount of waste salt containing sodium chloride, lithium carbonate and a small amount of low-carbon chain organic matters is generated. The waste salt was calcined at 550 ℃ for 4h to give a white mixture. And (3) leaching the calcined mixture by using deionized water, and filtering insoluble substances to obtain a crude lithium carbonate product. Adding hydrochloric acid into the filtrate, adjusting the pH of the solution to 5-6, and evaporating and concentrating until Li is obtained + >20g/L, filtering, washing with deionized water at a solid-to-liquid ratio of 1:0.5-1.0 for 2-3 times, wherein the obtained sodium chloride product meets the quality requirement of GB/T5462-2016. And keeping the temperature of the filtrate to 80 ℃, precipitating lithium by using a hot sodium carbonate solution, carrying out solid-liquid separation to obtain a crude lithium carbonate product, and returning the obtained filtrate to the evaporation and crystallization process. Washing and drying the lithium carbonate product by using deionized water at 90 ℃ to the crude lithium carbonate product in five times according to the solid-to-liquid ratio of 1:1, and returning the washing liquid to the solution in the evaporation and crystallization process. The primary yield of lithium is more than or equal to 85 percent, and the product meets the GB/T11075-2013 quality requirement.
Therefore, the harmless treatment method for the brine in the production of the polyphenylene sulfide resin solves the difficult problems in the polyphenylene sulfide industry, reduces the industrial bottleneck again, reduces the environmental protection risk, and has the advantages of simple process, easy operation and control, small equipment investment and high recovery rate.
Finally, it should be noted that: the above embodiments are only for illustrating the technical solutions of the present invention and not for limiting the same, and although the present invention is described in detail with reference to the preferred embodiments, those of ordinary skill in the art should understand that: modifications and equivalents may be made to the disclosed embodiments without departing from the spirit and scope of the present invention.

Claims (9)

1. A harmless treatment method of saline water in polyphenylene sulfide resin production is characterized by comprising the following steps:
s1, primary evaporation: carrying out primary evaporation crystallization on the washing strong brine to generate mixed salt, cooling, crystallizing and centrifugally drying the evaporation mother liquor to obtain a product sodium acetate, and recycling the product sodium acetate system;
s2, pyrolyzing miscellaneous salts: continuously adding the miscellaneous salt into a special electric heating furnace through a spiral pusher, controlling the environment and the temperature in the electric heating furnace and keeping the retention time, and converting organic matters in the miscellaneous salt into crude salt;
s3, dissolving the solution: dissolving the pyrolyzed crude salt in a first reaction kettle by using an aqueous solution doped with hydrochloric acid, wherein the pH value is less than 2, overflowing the saline water dissolved in the first reaction kettle into a second reaction kettle, adding sodium hydroxide, and changing impurities dissolved in a liquid phase into solid impurities, wherein the pH value is 6.5 to obtain saline water;
s4, membrane filtration: separating solid impurities out of the system by the saline water through a multistage tubular membrane filter to be used as common solid waste filter residues;
and S5, secondary evaporation, namely, carrying out multistage evaporation or MVR evaporation crystallization on the brine filtered by the membrane in the S4, drying the brine by a fluidized bed to obtain a product sodium chloride with the water content of less than 0.2%, and conveying the mother liquor to primary evaporation for recycling.
2. The method for harmless treatment of brine in polyphenylene sulfide resin production as defined in claim 1, wherein said one-time evaporative crystallization in step S1 comprises: the washing concentrated brine is directly introduced into a multi-stage countercurrent evaporator at 70 ℃ at 60 ℃, the mixed salt is taken out from the last stage at 110 ℃, and then centrifugal separation is carried out to keep impurities in the evaporation mother liquor.
3. The method as claimed in claim 1, wherein the cooling crystallization in step S1 is specifically as follows: and putting the evaporation mother liquor into a cooling kettle, cooling the evaporation mother liquor to be less than 10 ℃ through circulating water and low-temperature water, and then centrifugally drying and separating until the moisture content is less than 3% to obtain the product sodium acetate.
4. The method for harmless treatment of the brine in the production of polyphenylene sulfide resin as claimed in claim 3, wherein: the temperature of the circulating water is reduced to 60 ℃, and the temperature of the low-temperature water is reduced to 10 ℃.
5. The method for the harmless treatment of the brine in the production of polyphenylene sulfide resin as claimed in claim 1, wherein the method comprises the following steps: the environment of the special electric heating furnace in the miscellaneous salt pyrolysis in the step S2 is an anaerobic environment, the temperature is 500-750 ℃, and the retention time is kept for 2-4 h.
6. The method for harmless treatment of brine in polyphenylene sulfide resin production as claimed in claim 5, wherein: the temperature of the special electric heating furnace is lower than the melting temperature of sodium chloride and higher than the decomposition temperature of organic matters.
7. The method for harmless treatment of brine in polyphenylene sulfide resin production as claimed in claim 1, wherein: the dissolution temperature of the first reaction kettle in the step S3 is 40-70 ℃.
8. The method for harmless treatment of brine in polyphenylene sulfide resin production as claimed in claim 1, wherein: the membrane filtration temperature of the step S4 is 40-60 ℃.
9. The method for harmless treatment of brine in polyphenylene sulfide resin production as claimed in claim 1, wherein: the temperature of the secondary evaporation in the step S5 is 120 ℃, and the reflux quantity of the mother liquor conveyed to the primary evaporation is 0.5m 3/h.
CN202210668084.0A 2022-06-14 2022-06-14 Harmless treatment method for saline water in polyphenylene sulfide resin production Pending CN114988435A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210668084.0A CN114988435A (en) 2022-06-14 2022-06-14 Harmless treatment method for saline water in polyphenylene sulfide resin production

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210668084.0A CN114988435A (en) 2022-06-14 2022-06-14 Harmless treatment method for saline water in polyphenylene sulfide resin production

Publications (1)

Publication Number Publication Date
CN114988435A true CN114988435A (en) 2022-09-02

Family

ID=83034894

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210668084.0A Pending CN114988435A (en) 2022-06-14 2022-06-14 Harmless treatment method for saline water in polyphenylene sulfide resin production

Country Status (1)

Country Link
CN (1) CN114988435A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115432720A (en) * 2022-10-09 2022-12-06 宜宾学院 Process for recovering byproduct salt in polyphenylene sulfide synthesis
CN116672797A (en) * 2023-07-19 2023-09-01 东莞市曼塔新材料科技有限公司 Purification and filtration device and method for polyphenylene sulfide melt

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106395862A (en) * 2016-08-29 2017-02-15 四川理工学院 Recovery method of by-product sodium chloride in production process of polyphenylene sulfide
CN106495190A (en) * 2016-09-12 2017-03-15 天津科技大学 A kind of calcining of abraum salt containing lithium recovery method
CN106565956A (en) * 2016-10-21 2017-04-19 天津科技大学 Method for comprehensive recycling of by-product slurry in polyphenylene sulfide productive process
CN106745076A (en) * 2016-11-21 2017-05-31 大唐国际化工技术研究院有限公司 A kind of method that Industrial Wastewater Treatment is produced carnallite resource
CN111574713A (en) * 2020-06-16 2020-08-25 四川明道和化学新材料有限公司 Method for recovering polyphenylene sulfide byproduct salt
CN112320822A (en) * 2020-10-20 2021-02-05 绍兴凤登环保有限公司 Waste salt recycling treatment method
CN113772692A (en) * 2021-09-03 2021-12-10 江苏海普功能材料有限公司 Method for treating and recycling waste salt
CN114349026A (en) * 2021-04-08 2022-04-15 李广柱 Treatment process of high-risk waste salt

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106395862A (en) * 2016-08-29 2017-02-15 四川理工学院 Recovery method of by-product sodium chloride in production process of polyphenylene sulfide
CN106495190A (en) * 2016-09-12 2017-03-15 天津科技大学 A kind of calcining of abraum salt containing lithium recovery method
CN106565956A (en) * 2016-10-21 2017-04-19 天津科技大学 Method for comprehensive recycling of by-product slurry in polyphenylene sulfide productive process
CN106745076A (en) * 2016-11-21 2017-05-31 大唐国际化工技术研究院有限公司 A kind of method that Industrial Wastewater Treatment is produced carnallite resource
CN111574713A (en) * 2020-06-16 2020-08-25 四川明道和化学新材料有限公司 Method for recovering polyphenylene sulfide byproduct salt
CN112320822A (en) * 2020-10-20 2021-02-05 绍兴凤登环保有限公司 Waste salt recycling treatment method
CN114349026A (en) * 2021-04-08 2022-04-15 李广柱 Treatment process of high-risk waste salt
CN113772692A (en) * 2021-09-03 2021-12-10 江苏海普功能材料有限公司 Method for treating and recycling waste salt

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115432720A (en) * 2022-10-09 2022-12-06 宜宾学院 Process for recovering byproduct salt in polyphenylene sulfide synthesis
CN116672797A (en) * 2023-07-19 2023-09-01 东莞市曼塔新材料科技有限公司 Purification and filtration device and method for polyphenylene sulfide melt
CN116672797B (en) * 2023-07-19 2024-05-24 威海旭日过滤器股份有限公司 Purification and filtration device and method for polyphenylene sulfide melt

Similar Documents

Publication Publication Date Title
CN114988435A (en) Harmless treatment method for saline water in polyphenylene sulfide resin production
CN106565956B (en) By-product slurry comprehensive reutilization method in a kind of polyphenylene sulfide production process
KR101283843B1 (en) Purification method of lithium carbonate
CN111100286A (en) Green high-purity polyarylether and preparation method thereof
CN115947486B (en) Desulfurization waste liquid recycling treatment process and system
CN101747173B (en) Method utilizing acetic acid in PTA oxidation residues to prepare sodium acetate trihydrate
JP6926010B2 (en) Method for producing lithium hydroxide
CN105036281A (en) Preparation of organic sulfur heavy metal capturing agent and recycling and treating method of filtrate thereof
CN112357967A (en) Process for purifying high-purity ferrous sulfate as titanium dioxide byproduct
CN115818671A (en) Method for crystallizing and purifying sodium carbonate of incineration product
CN111574713A (en) Method for recovering polyphenylene sulfide byproduct salt
CN113511662A (en) Purification method of waste salt containing sodium sulfate
CN115650256A (en) Industrial potassium chloride purification process and production system
KR101562263B1 (en) Method for preparing sodium nitrate using a waste solution containing nitric acid
CN110015796B (en) Zero-discharge treatment system and process for nickel hydrometallurgy wastewater of mixed high-salt system
CN114409157B (en) Recycling method for preparing chlor-alkali by waste salt water electrolysis
CN113274882B (en) Ammonium adipate waste liquid recovery method and device based on high-temperature bipolar membrane electrodialysis
CN113023751B (en) Method for recovering lithium, sodium, potassium, magnesium and calcium from chloride brine
CN114956126A (en) Method for recycling mother solution in sodium method iron phosphate production process
CN108217698B (en) Method for recovering lithium from PPS (polyphenylene sulfite) catalyst waste residue
JP3177755B2 (en) Method for producing lithium N-methylaminobutyrate
CN117303415B (en) Technology for preparing lithium carbonate from water leaching solution after lepidolite roasting
CN114959306B (en) Method for recycling lithium from lithium precipitation mother liquor by closed cycle method
CN102345014A (en) Method for preparing elementary copper, copper hydroxide and sodium chloride through dye waste residues
CN218357408U (en) Hydrazine hydrate refining desalination system

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
CB03 Change of inventor or designer information

Inventor after: Gao Jianping

Inventor after: Ren Bingtao

Inventor after: Wang Zhiwu

Inventor after: Liu Bingchen

Inventor after: Wang Peng

Inventor before: Li Naijie

Inventor before: Liu Bingchen

Inventor before: Ren Bingtao

Inventor before: Wang Zhiwu

Inventor before: Wang Peng

CB03 Change of inventor or designer information
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20220902

RJ01 Rejection of invention patent application after publication