EP3802435A1 - Verfahren zum recycling von extraktwasser bei der polyamid 6-herstellung - Google Patents
Verfahren zum recycling von extraktwasser bei der polyamid 6-herstellungInfo
- Publication number
- EP3802435A1 EP3802435A1 EP18729922.7A EP18729922A EP3802435A1 EP 3802435 A1 EP3802435 A1 EP 3802435A1 EP 18729922 A EP18729922 A EP 18729922A EP 3802435 A1 EP3802435 A1 EP 3802435A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- extract water
- cation
- unit
- ion
- exchanger
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/02—Column or bed processes
- B01J47/026—Column or bed processes using columns or beds of different ion exchange materials in series
- B01J47/028—Column or bed processes using columns or beds of different ion exchange materials in series with alternately arranged cationic and anionic exchangers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J39/00—Cation exchange; Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
- B01J39/04—Processes using organic exchangers
- B01J39/05—Processes using organic exchangers in the strongly acidic form
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J39/00—Cation exchange; Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
- B01J39/04—Processes using organic exchangers
- B01J39/07—Processes using organic exchangers in the weakly acidic form
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/02—Column or bed processes
- B01J47/04—Mixed-bed processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
- C02F1/004—Processes for the treatment of water whereby the filtration technique is of importance using large scale industrial sized filters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
- C02F2001/422—Treatment of water, waste water, or sewage by ion-exchange using anionic exchangers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
- C02F2001/425—Treatment of water, waste water, or sewage by ion-exchange using cation exchangers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
- C02F2001/427—Treatment of water, waste water, or sewage by ion-exchange using mixed beds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature 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
- C02F2103/38—Polymers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/02—Temperature
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/04—Flow arrangements
- C02F2301/043—Treatment of partial or bypass streams
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
Definitions
- the present invention relates to a process for the recycling of extract water resulting from the production of polyamide 6 or its copolymers (PA6 / 66), an apparatus for recycling in the production of
- Polyamide or its copolymers (PA6 / 66) accumulating extract water and the use of this device for recycling of resulting in the production of polyamide 6 or its copolymers (PA6 / 66) extracting water.
- caprolactam present in the crude product after the polymerization and cyclic and linear oligomers of caprolactam must be removed after the polymerization. This usually happens with hot water.
- the resulting extract waters typically contain from 5 to 20 percent by weight of organic fractions which must be reused from an economic point of view. These are these concentrated and recycled as raw material of the polyamide 6 synthesis, while the condensed distillate is used again for the extraction.
- additives such as titanium dioxide as matting agent for textile applications can be added already during the polymerization. Consequently, these additives come in contact with water during the subsequent extraction in the process and foreign matter such as e.g. Minerals from the coating of titanium dioxide are washed out.
- the difficulty lies in the fact that the dissolved oligomers of caprolactam can precipitate at temperatures below 80 ° C and block lines. However, if the temperature is kept above 80 ° C., no anion exchangers can be used, since they rapidly degrade at temperatures above 80 ° C. and tend to liberate odorous compounds, in particular amines, and contaminate the recirculating streams ,
- No. 5,245,029 relates to an ion exchange process for purifying water caprolactam solutions in a process for the preparation of caprolactam and laurolactam, in which a mixture of cyclohexanone oxime and cyclodeodecanoxime in the presence of sulfuric acid and fuming sulfuric acid is subjected to a Beckman reaction. Rearrangement is subjected. The process comprises, after neutralization of the reaction products from the rearrangement, a first extraction with an organic solvent and a second extraction of the first extract with water to obtain a second extract of an aqueous caprolactam solution.
- aqueous caprolactam solution obtained by extraction with a water immiscible organic solvent is treated with a strongly acidic cation exchange resin followed by a weakly basic anion exchange resin or further with a strongly basic anion exchange resin to remove surfactants such as alkyl sulfate , GB 762,879 describes a process for the removal of organic impurities from lactams, which describes the conduction of lactam in aqueous solution via anion and cation exchangers, which can be arranged in any order.
- GB 1 175,279 relates to processes for the purification of e-caprolactam obtained by nitrosation of cyclohexyl compounds and containing volatile amide-based bases.
- the e-caprolactam is treated with an alkaline reagent in the presence of water and a halogen or an alkali metal hypohalide to convert the volatile amide-based bases to amine compounds.
- These amine compounds are separated from the e-caprolactam, for example by a cation exchanger.
- No. 5,225,524 relates to a process for rendering odorless polymer solutions containing amino groups.
- a solution of terpolymers of vinylpyrrolidone, vinylcaprolactam and dimethylaminoethyl methacrylate is treated with from 0.1 to 10% by weight of an acidic compound or an acidic anion exchange resin in order to render it predominantly odorless.
- a further object of the present invention is to provide a device for the purification of extract water resulting from the production of polyamide 6 or its copolymers. This object is achieved by the method according to independent claim 1, which comprises the following steps:
- ion exchanger module comprising at least the following ion exchanger units: i) at least one cation exchanger unit, ii) at least one anion exchanger unit, wherein the extract water contains the ion exchanger units in c) deodorizing the extract water from step b) by iii) at least one cation exchanger unit or a mixed ion exchanger unit which comprises at least one anion exchanger and at least one cation exchanger, and wherein the extract water during the entire process Method has a temperature in the range of 80 to 100 ° C.
- the independent claim 12 relates to a device for cleaning and deodorization of Kapolactam-containing extract water obtained in the polyamide 6 preparation, comprising an extractor upstream and downstream of this an evaporation plant, between which in the flow path at least one filtration unit and an ion exchange module are positioned, wherein the ion exchange module contains at least the following ion exchange units: i) at least one cation exchanger unit, ii) at least one anion exchanger unit, iii at least one cation exchanger unit or a mixed ion exchanger unit which comprises at least one anion exchanger and at least one cation exchanger, the ion exchanger units being arranged in the flow direction of the extract water in the order i-ii-ii ,
- a preferred embodiment of the device according to the invention is specified in dependent claim 13.
- Claims 14 to 16 relate to uses of the device according to the invention for the recycling of extracting water resulting from the production of polyamide 6.
- Recycling of extract water in the context of the present invention is understood to mean that a concentrate of the extract water is returned to the polymerization reactor for the production of polyamide 6.
- the "purification” in the context of the present invention relates to the removal of soluble and insoluble impurities from the extract water.
- deodorization is understood to mean the removal of odor-intensive substances from the extract water which have arisen during the "purification” or which have not been removed during the purification step.
- Ion exchange resins have functional groups such as, for example, sulfonic acid groups, trimethylammonium groups or amino groups.
- a functional group-based ion exchange resin is understood to mean that the functionality of the ion exchange resin is based on this group.
- a preferred embodiment according to the present invention provides that the extract water caprolactam in monomeric form and / or cyclic and / or linear oligomers of caprolactam and impurities preferably selected from the group consisting of titanium compounds, silicon compounds, manganese compounds, aluminum compounds, sodium - compounds, potassium compounds, calcium compounds, in particular calcium sulfate, calcium polyphosphates, calcium oligophosphates and mixtures thereof.
- the proportion of cyclic and / or linear oligomers of caprolactam in the extract water is 5 to 20 wt .-%, preferably 10 to 15 wt .-%, based on the total mass of the extract water.
- a particularly preferred embodiment according to the present inven tion provides that the extract water caprolactam in monomeric form and / or cyclic and / or linear oligomers of caprolactam and impurities preferably selected from the group consisting of Titanver- compounds, silicon compounds, manganese compounds, aluminum compound compounds, sodium compounds, potassium compounds, calcium compounds, in particular calcium sulfate, calcium polyphosphates, calcium oligophosphates and mixtures thereof and the proportion of cyclic and / or linear oligomers of caprolactam in the extract water 5 to 20% by weight, preferably 10 to 15 wt .-%, based on the total mass of the extract water is.
- the proportion of caprolactam in the extract water is 5 to 20 wt .-%, preferably 10 to 15 wt .-% based on the total mass of the extract water.
- the proportion of impurities in the extract water is less than 1 wt .-%, preferably less than 0.5 wt .-% based on the total mass of the extract water.
- the extract water has a temperature in the range of 83 to 95 ° C, preferably in the range of 85 to 90 ° C during the entire process. If lower temperatures were used oligomers of caprolactam would precipitate and blockage of lines would be expected.
- the filtration unit a has a filter with a pore size in the range of 0.1 to 100 ⁇ m, preferably 5 to 50 ⁇ m.
- the filtration unit allows to remove insoluble impurities and suspended solids from the extract water.
- the at least one cation exchange unit i) is formed in the form of a resin bed.
- the at least one cation exchanger unit i) contains a sulfonic acid group-based cation exchange resin.
- Cation-exchange resins based on sulfonic acid groups are highly acidic.
- the at least one anion exchange unit ii) is in the form of a resin bed.
- the at least one anion exchanger unit ii) contains a trimethylammonium-based anion exchange resin.
- Anion exchange resins based on trimethylammonium groups are counted among the type I exchangers, are strongly basic and have an increased thermal stability compared to the type II exchangers.
- Amino group-based anion exchange resins are counted among the weakly basic anion exchange resins.
- a further preferred embodiment of the present invention provides that the at least one cation exchanger unit or mixed ion exchanger unit iii) used in step c) for deodorization is formed in the form of a resin bed.
- a mixed bed is used in which the cation and anion exchange resins are distributed almost homogeneously.
- a preferred ratio of cation exchange resin to anion exchanger is 1.9: 1.3 based on the active groups.
- the ion exchanger unit iii) is present in an ion exchange module with the ion exchanger units i) and ii).
- the at least one mixed ion exchanger unit comprises a mixture of a sulfonic acid group-based cation exchange resin and an trimethylammonium group-based anion exchange resin.
- the deodorization according to step c) is ensured by at least one container filled with a cation exchange resin or mixtures of at least one cation exchange resin and at least one anion exchange resin.
- this container is preferably installed behind the ion exchanger module in the extra water circuit.
- the odorizing step c) serves to neutralize odor-intensive substances which have been newly formed by the ion exchange module, in particular the ion exchange unit ii).
- the cation exchange resin in this container is preferably based on sulfonic acid groups and the anion exchange resin on trimethylammonium groups.
- the at least one container between the ion exchanger module and the evaporation plant is attached.
- a further preferred embodiment of the present invention provides that the at least one container for deodorization between the evaporation plant and the extractor is arranged. It is particularly preferred to install the container in the condensate of the evaporation plant, since there are lower temperatures of 20 to 70 ° C, preferably 40 to 60 ° C, are present. This has the advantage that the ion exchange resins are exposed to a lower thermal load and thus longer periods of use are possible. Another reason for the preferred mounting of the container in the condensate of the evaporation plant is in the accumulation of the volatile amines, which are the odorous substances, at this position, since they evaporate with the water.
- the water which is recycled from the evaporation plant into the extractor does not constitute extract water in the sense of the present invention, since it contains no organic constituents such as caprolactam or its oligomers.
- Another preferred embodiment of the present invention provides that at least one of the ion exchanger units i), ii) and / or those for deodorization iii), preferably all ion exchanger units, contain at least one protective filter.
- At least one, preferably all, of the ion exchange units i), ii) and iii) is bridgeable with a bypass.
- At least one, preferably all, of the ion exchanger units i), ii) and / or iii) is / are a second ion exchanger unit, which is / are preferably the same as the first ion exchanger unit in terms of construction and ion exchange material , interchangeable by a circuit.
- the temporary bridging with a bypass or the replacement by a second container or a second ion exchanger unit allows to replace the ion exchange resin without having to interrupt the operation.
- the container has at least one protective filter, wherein it is particularly preferred if both the inlet and the outlet of the container are provided with a protective filter.
- the purpose of the protective filters is to prevent the introduction of foreign substances into the ion exchange resin. Furthermore, it is particularly preferred that the last ion exchanger unit has a protective filter in the direction of flow on the outlet side, so that mechanical abrasion can be retained from the ion exchanger resin bed and its introduction into the process cycle can be prevented.
- the conductivity of the extract water after step c), which is carried out between the ion exchange module containing i) and ii) and the evaporation plant is less than 10 pS / cm, preferably is less than 5 pS / cm, more preferably less than 1 pS / cm.
- the device is designed such that the at least one cation exchange unit i) is in the form of a resin bed and / or contains a sulfonic acid group-based cation exchange resin, and / or the at least one anion exchange unit ii) is formed in the form of a resin bed and / or contains an anion exchange resin based on trimethylammonium groups, and / or contains a mixture of a sulfonic acid group-based cation exchange resin and a trimethylammonium-based anion exchange resin.
- the device according to the present invention is particularly suitable for recycling extract water resulting from polyamide 6 production.
- the apparatus is used for recycling of extract water, caprolactam in monomeric form and / or cyclic and / or linear oligomers of caprolactam and impurities preferably selected from the group consisting of titanium compounds, silicon compounds, manganese compounds , Aluminum compounds, sodium compounds, potassium compounds, calcium compounds, in particular calcium sulfate, calcium polyphosphates, calcium oligophosphates and mixtures thereof.
- the proportion of cyclic and / or linear oligomers of caprolactam is 5 to 20 wt .-%, preferably 10 to 15 wt .-%, based on the total mass of the extract water.
- the proportion of caprolactam is 5 to 20 wt .-%, preferably 10 to 15 wt .-% based on the total mass of the extract water.
- the proportion of impurities in the extract water is less than 1 wt .-%, preferably less than 0.5 wt .-% based on the total mass of the extract water.
- the device is used for recycling of extract water having a temperature in the range of 80 to 100 ° C, preferably 83 to 95 ° C and particularly preferably 85 to 90 ° C.
- FIGS. 1 to 3 serve to illustrate the invention better, but should not be construed as limiting in any way.
- FIG. 1 shows the schematic sequence of the polyamide 6 production process including the extract water cycle.
- the filtration unit (6) and the ion exchange module (7) comprising a cation ion exchanger unit i) and an anion exchange unit ii) are positioned between the extractor (4) and the evaporation plant (9).
- the units (6) and (7) ensure the filtration and purification according to process steps a) and b).
- the container (8) filled with ion exchange resin comprising a cation exchange unit or mixed ion exchanger unit iii) for the desorption according to process step c) can be arranged between the ion exchanger module (7) and the evaporation plant (8 '). However, it is preferable to position this container between the evaporation plant and the extractor. kidney, particularly preferably in the condensate of the evaporation plant (8 "). Furthermore, several containers can be used for deodorization.
- FIG. 2 schematically shows the flow of the mineral-containing extract water (15), which successively receives a filtration unit (6), a cation exchanger (7a) i) an anion exchanger (7b) ii), after which low-mineral extract water (16) is obtained which is again polyamide 6 Manufacturing process can be supplied.
- the ion exchanger unit (8) iii) comprising a mixed ion exchanger unit can be installed directly behind the ion exchange units (7a) and (7b).
- FIG. 3 a shows the bypass variant for the container for deodorization (8)
- FIG. 3 b illustrates the embodiment with a switchable second container
- FIG. 3c illustrates the embodiment with switchable identical ion exchanger units for the cation exchanger unit i), the anion exchanger unit ii) and the ion exchanger unit for the deodorizing iii).
- the ion exchange resins used in the examples were regenerated prior to use or are commercially available directly.
- a strong base Type I anion exchange resin (100 g) was refluxed overnight in water (200 g). The water subsequently smelled unpleasantly fishy and trime- thylamine was detected by gas chromatography. The resulting water was treated for 5 minutes with a mixed bed consisting of a strongly acidic and a strongly basic ion exchange resin (3 parts water to 1 part mixed bed) (duration 5 minutes), after which the odor disappeared and no trimethylamine was detectable ,
- aqueous solution with a conductivity of 32 pS / cm passed in succession through a resin bed of a strongly acidic cation exchanger and a strongly basic type I anion exchanger.
- the conductivity of the solution was reduced to 3 to 4 pS / cm.
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Polyamides (AREA)
Abstract
Description
Claims
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| PCT/EP2018/064503 WO2019228651A1 (de) | 2018-06-01 | 2018-06-01 | Verfahren zum recycling von extraktwasser bei der polyamid 6-herstellung |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| EP3802435A1 true EP3802435A1 (de) | 2021-04-14 |
Family
ID=62563127
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| EP18729922.7A Pending EP3802435A1 (de) | 2018-06-01 | 2018-06-01 | Verfahren zum recycling von extraktwasser bei der polyamid 6-herstellung |
Country Status (3)
| Country | Link |
|---|---|
| EP (1) | EP3802435A1 (de) |
| CN (1) | CN111527051B (de) |
| WO (1) | WO2019228651A1 (de) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114368869A (zh) * | 2022-01-27 | 2022-04-19 | 大连海新工程技术有限公司 | 一种pa6聚合萃取水的处理装置、系统及工艺 |
| CN118955378A (zh) * | 2024-07-29 | 2024-11-15 | 福建永荣锦江股份有限公司 | 一种提升回收己内酰胺品质的生产工艺 |
| CN119750713A (zh) * | 2025-02-19 | 2025-04-04 | 杭州逸宸化纤有限公司 | 净化处理装置及方法 |
Family Cites Families (15)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3145198A (en) * | 1964-08-18 | piija | ||
| GB762879A (en) | 1952-11-15 | 1956-12-05 | Stamicarbon | Process for purifying lactams |
| GB867741A (en) * | 1959-02-14 | 1961-05-10 | Stamicarbon | Method of removing impurity from aqueous solutions of caprolactam containing lactam oligomers |
| CH525887A (it) | 1966-07-27 | 1972-07-31 | Snia Viscosa | Procedimento di purificazione di caprolattame, in particolare ottenuto per nitrosazione di composti cicloesilici |
| GB1235351A (en) * | 1968-01-01 | 1971-06-16 | Permutit Co Ltd | Fibrous cross-linked polymers |
| US4380590A (en) * | 1978-09-19 | 1983-04-19 | Rohm And Haas Company | Emulsion copolymer cation exchange resins |
| JP2559903B2 (ja) * | 1990-11-21 | 1996-12-04 | 宇部興産株式会社 | カプロラクタム水溶液のイオン交換樹脂精製方法 |
| US5225524A (en) | 1992-07-02 | 1993-07-06 | Isp Investments Inc. | Process for rendering amino-group-containing polymer solutions substantially odorless |
| JPH08276180A (ja) * | 1995-04-06 | 1996-10-22 | Ngk Insulators Ltd | イオン交換純水の脱臭精製方法 |
| JP2000262893A (ja) * | 1999-03-16 | 2000-09-26 | Takuma Co Ltd | 陰イオン除去剤及び陰イオン除去ケミカルフィルタ |
| TW200812960A (en) * | 2006-09-04 | 2008-03-16 | China Petrochemical Dev Corp | A system and method for purification carprolactam from raw solution |
| JP5720138B2 (ja) * | 2010-08-06 | 2015-05-20 | 栗田工業株式会社 | 酢酸含有排水の処理方法 |
| CN103663792A (zh) * | 2013-12-12 | 2014-03-26 | 长乐恒申合纤科技有限公司 | 一种锦纶回收萃取水的过滤系统及其工艺 |
| CN105801841A (zh) * | 2016-04-20 | 2016-07-27 | 温州邦鹿化工有限公司 | 一种尼龙6生产工艺及系统 |
| CN105948333A (zh) * | 2016-06-30 | 2016-09-21 | 杭州聚合顺新材料股份有限公司 | 尼龙6切片萃取水中无机离子的去除方法及其去除装置 |
-
2018
- 2018-06-01 WO PCT/EP2018/064503 patent/WO2019228651A1/de not_active Ceased
- 2018-06-01 CN CN201880084887.3A patent/CN111527051B/zh active Active
- 2018-06-01 EP EP18729922.7A patent/EP3802435A1/de active Pending
Also Published As
| Publication number | Publication date |
|---|---|
| CN111527051B (zh) | 2023-03-24 |
| WO2019228651A1 (de) | 2019-12-05 |
| CN111527051A (zh) | 2020-08-11 |
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