CN101234295B - Processing method for reducing NaCl removal rate of nano filter membrane - Google Patents

Processing method for reducing NaCl removal rate of nano filter membrane Download PDF

Info

Publication number
CN101234295B
CN101234295B CN2007100567055A CN200710056705A CN101234295B CN 101234295 B CN101234295 B CN 101234295B CN 2007100567055 A CN2007100567055 A CN 2007100567055A CN 200710056705 A CN200710056705 A CN 200710056705A CN 101234295 B CN101234295 B CN 101234295B
Authority
CN
China
Prior art keywords
nacl
concentration
temperature
membrane
processing method
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.)
Expired - Fee Related
Application number
CN2007100567055A
Other languages
Chinese (zh)
Other versions
CN101234295A (en
Inventor
叶明�
邹剑昆
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.)
TIANJIN WEIDETAIKE PETRIFICATION SCIENCE AND TECHNOLOGY DEVELOPMENT Co Ltd
Original Assignee
TIANJIN WEIDETAIKE PETRIFICATION SCIENCE AND TECHNOLOGY DEVELOPMENT 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 TIANJIN WEIDETAIKE PETRIFICATION SCIENCE AND TECHNOLOGY DEVELOPMENT Co Ltd filed Critical TIANJIN WEIDETAIKE PETRIFICATION SCIENCE AND TECHNOLOGY DEVELOPMENT Co Ltd
Priority to CN2007100567055A priority Critical patent/CN101234295B/en
Publication of CN101234295A publication Critical patent/CN101234295A/en
Application granted granted Critical
Publication of CN101234295B publication Critical patent/CN101234295B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention relates to a processing method for improving the separating effect of the nanofiltration membrane, in particular to a processing method of decreasing the NaCl removal rate by the nanofiltration membrane. The nanofiltration membrane is immersed at room temperature by sodium hydroxide solution with pH value of 8 to 10 and concentration of 100 to 5,000mg/L, then is cleaned by the deionization water and then is immersed by hydrogen peroxide aqueous solution of 100 to 5,000mg/L with the immersing temperature of 25 DEG C to 40 DEG C, operation pressure of 100psi to 500psi and immersing time of 4 to 12 hours. The invention also includes the steps that the solution provided by the invention immerses the nanofiltration membrane, thus changing the separating effect of the nanofiltration membrane.

Description

Reduce the processing method of NF membrane to the NaCl removal efficiency
Technical field
The present invention relates to improve the processing method of NF membrane separating effect, especially reduce the processing method of NF membrane the NaCl removal efficiency.
Background technology
At present, the raw materials used sodium chloride major part of China's chlor-alkali enterprise is sea salt and bittern.Sea salt and bittern all contain certain sulfate radical, constantly accumulate in production system, and the operation of electrolytic cell is had side effect.The advanced method that removes sulfate ion is to utilize the stalling characteristic of film that sulfate ion is removed from salt solution and keep sodium chloride.
But NF membrane is being handled sodium chloride and sodium sulphate mixed solution, in the time of to the high rejection of sulfate ion, to the rejection of sodium chloride also more than 10%.This situation when handling the sulfuric acid acid group, has also been handled raw material sodium chloride for chlor-alkali industry, is irrational, and is also uneconomic.
Therefore, the present invention has designed a kind of processing method of improving the NF membrane separating effect, at sodium sulfate concentration 10~70g/L, under the situation of sodium chloride concentration 50~300g/L, when making NF membrane remain on more than 90% to the rejection of sulfate ion, reduce the rejection of NF membrane, reach below 5% sodium chloride.
Summary of the invention
The object of the invention is to improve the processing method of NF membrane separating effect.Reduce the processing method of NF membrane to the NaCl removal efficiency
The invention provides the processing method of improving the NF membrane separating effect, step is as follows:
To the NF membrane soaking at room temperature, use the washed with de-ionized water warp with pH is 8~10, concentration is 100~5000mg/L sodium hydroxide solution then; Aqueous hydrogen peroxide solution with 100~5000mg/L soaks again, and soaking temperature is 25 ℃~40 ℃, and operating pressure is 100psi~500psi, and soak time is 4~12 hours.
The pH of sodium hydroxide solution of the present invention is preferably 9~9.5.Concentration of sodium hydroxide solution is 2000~3000mg/L.
Described NF membrane is the NF membrane of polyamide material.
The method that is used to dispose described sodium hydroxide solution and hydrogenperoxide steam generator is the conventional method of chemistry.
The present invention also comprises and will soak the step of NF membrane with above-mentioned solution, thereby changes the separating effect of described NF membrane.
The specific embodiment
Embodiment 1
With polyamide nanofiltration membrane pH is 8,25 ℃ NaOH solution, under the operating pressure of 150psi, soaked 6 hours, take out, with 20 ℃ washed with de-ionized water, under the operating pressure of 150psi, use 1000mg/L again, temperature is that 25 ℃ hydrogenperoxide steam generator soaked 8 hours, take out, with 20 ℃ washed with de-ionized water.The NF membrane of above-mentioned processing is positioned on the film properties tester, and under the operating pressure of 220psi, under 25 ℃, this film is handled 1000mg/L, and pH is 7.5 NaCl solution, and its NaCl rejection is 31%; It is 100g/L that this film is handled NaCl concentration, and SO42-concentration is 10g/L, and pH is 7.1 mixed-salt aqueous solution, and operating pressure is 360psi, and under 30 ℃, its NaCl rejection is 2.6%, and the SO42-rejection is 97%.
Embodiment 2, embodiment 3 are as following table:
Change pH value, the time of soak, the operating pressure when soaking of handing over the sodium hydroxide solution among the embodiment 1, other
Identical with embodiment 1, as to be improved NF membrane, the film properties test under different test conditions.
The molten H of real NaOH 2O 2Molten
Treatment fluid immersion condition dip time takes off NaCl and takes off SO 4 2-Testing conditions
Example
Liquid pH value liquid concentration
NaCl concentration is 1000mg/L, and temperature is 28 ℃,
9 1000 temperature are 25 5 27
The NaCl solution pressure of pH value 10.1 is 218psi
℃,
2 NaCl concentration are 200g/L, and pressure is that temperature is 28 ℃,
SO 4 2-Concentration is 20g/L, and pH 9 1,000 5 1.4 97.8
100psi pressure is 290psi
The mixed-salt aqueous solution of value 10.1
NaCl concentration is 500mg/L, and temperature is 28 ℃,
10 1000 temperature are 25 6 30
The NaCl solution pressure of pH value 10.0 is 220psi
℃,
3 NaCl concentration are 150g/L, and pressure is that temperature is 29 ℃,
SO 4 2-Concentration is 30g/L, and pH 10 1,000 6 1.8 96.9
150psi pressure is 290psi
The mixed-salt aqueous solution of value 10.0
Embodiment 4
With the polyamide nanofiltration membrane concentration of treatment is 1000mg/L, and pH is 7.5 NaCl solution, and under the operating pressure of 220psi, under 25 ℃, its NaCl rejection is 42.1%; It is 200g/L that this film is handled NaCl concentration, SO 4 2-Concentration is 10g/L, is 7.1 mixed-salt aqueous solution with pH, and operating pressure is 360psi, and under 29 ℃, its NaCl rejection is 10%, SO 4 2-Rejection is 99%.
With above-mentioned untapped NF200-400 NF membrane pH is 10,25 ℃ NaOH solution soaked 5 hours, take out, washed with de-ionized water with 20 ℃, under the operating pressure of 150psi, use 500mg/L again, temperature is that 25 ℃ hydrogenperoxide steam generator soaked 8 hours, takes out, with 20 ℃ washed with de-ionized water.The NF membrane of above-mentioned processing is positioned on the film properties tester, and under the operating pressure of 220psi, under 25 ℃, this film is handled 1000mg/L, and pH is 7.5 NaCl solution, and its NaCl rejection is 26.3%; It is 200g/L that this film is handled NaCl concentration, SO 4 2-Concentration is 10g/L, and pH is 7.1 mixed-salt aqueous solution, and operating pressure is 360psi, and under 30 ℃, its NaCl rejection is 1.1%, SO 4 2-Rejection is 98.2%.
Embodiment 5-12, as following table:
The concentration of the hydrogenperoxide steam generator among the change embodiment 4, the time of soak, the operating pressure when soaking, the temperature of soak, the NF membrane that other are identical with embodiment 4, as to be improved, the film properties test under different test conditions
Real H 2O 2During solution impregnation
The treatment fluid immersion condition takes off NaCl and takes off SO 4 2-Testing conditions
H between example concentration
NaCl concentration is 1000mg/L, and temperature is 25 ℃,
500 8 26.3
The NaCl solution pressure of pH value 7.5 is 220psi
Temperature is 25 ℃,
5 NaCl concentration are 200g/L, SO 4 2-
Pressure is 30 ℃ for the 150psi temperature,
Concentration is 10g/L, pH value 7.1 500 8 1.1 98.2
Mixed-salt aqueous solution pressure be 360psi
NaCl concentration is 1000mg/L, and temperature is 28 ℃,
1000 12 22
The NaCl solution pressure of pH value 10.1 is 218psi
Temperature is 25 ℃,
6 NaCl concentration are 200g/L, SO 4 2-
Pressure is 28 ℃ for the 100psi temperature,
Concentration is 20g/L, pH value 10.1 1,000 12 0.53 97.9
Mixed-salt aqueous solution pressure be 290psi
NaCl concentration is 500mg/L, and the pH temperature is 28 ℃,
1000 10 23
The NaCl solution pressure of value 10.0 is 220psi
Temperature is 25 ℃,
7 NaCl concentration are 150g/L, SO 4 2-
Pressure is 29 ℃ for the 150psi temperature,
Concentration is 30g/L, pH value 10.01000 10 0.86 98.2
Pressure is 290psi
Mixed-salt aqueous solution
NaCl concentration is 750mg/L, and the pH temperature is 28 ℃,
3000 8 3
The NaCl solution pressure of value 10.0 is 220psi
Temperature is 27 ℃,
8 NaCl concentration are 100g/L, SO 4 2-
Pressure is 31 ℃ for the 210psi temperature,
Concentration is 20g/L, pH value 9.0 3,000 80 82.6
Pressure is 290psi
Mixed-salt aqueous solution
NaCl concentration is 2000mg/L, and temperature is 29 ℃,
3000 4 21.4
The NaCl solution pressure of pH value 10.0 is 220psi
Temperature is 27 ℃,
9 NaCl concentration are 100g/L, SO 4 2-
Pressure is 25 ℃ for the 500psi temperature,
Concentration is 50g/L, pH value 7.8 3,000 4 0.49 97.4
Pressure is 290psi
Mixed-salt aqueous solution
NaCl concentration is 1000mg/L, and temperature is 29 ℃,
2000 7 20.4
The NaCl solution pressure of pH value 10.0 is 210psi
Temperature is 37 ℃,
10 NaCl concentration are 150g/L, SO 4 2-
Pressure is 30 ℃ for the 180psi temperature,
Concentration is 60g/L, pH value 6.2 2,000 7 0.34 97.2
Pressure is 290psi
Mixed-salt aqueous solution
NaCl concentration is 3000mg/L, and temperature is 29 ℃,
2500 6 19.8
The NaCl solution pressure of pH value 10.0 is 210psi
Temperature is 27 ℃,
11 NaCl concentration are 200g/L, SO 4 2-
Pressure is 29 ℃ for the 190psi temperature,
Concentration is 70g/L, pH value 8.1 2,500 6 0.26 96.5
Pressure is 270psi
Mixed-salt aqueous solution
NaCl concentration is 1000mg/L, and temperature is 28 ℃,
2500 5 20.5
The NaCl solution pressure of pH value 10.0 is 230psi
Temperature is 30 ℃,
12 NaCl concentration are 100g/L, SO 4 2-
Pressure is 26 ℃ for the 160psi temperature,
Concentration is 70g/L, pH value 9.7 2,500 5 0.31 97.4
Pressure is 280psi
Mixed-salt aqueous solution

Claims (3)

1. processing method that reduces NF membrane to the NaCl removal efficiency is characterized in that: with pH be 8~10 sodium hydroxide solution NF membrane soaking at room temperature to the polyamide material, and clean with washed with de-ionized water then; Aqueous hydrogen peroxide solution with 100~5000mg/L soaks again, and soaking temperature is 25 ℃~40 ℃, and operating pressure is 100psi~500psi, and soak time is 4~12 hours.
2. the described reduction NF membrane of claim 1 is characterized in that to the processing method of NaCl removal efficiency described concentration of sodium hydroxide solution is 2000~3000mg/L.
3. reduction NF membrane as claimed in claim 1 is characterized in that to the processing method of NaCl removal efficiency described sodium hydroxide solution pH value is 9~9.5.
CN2007100567055A 2007-02-02 2007-02-02 Processing method for reducing NaCl removal rate of nano filter membrane Expired - Fee Related CN101234295B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2007100567055A CN101234295B (en) 2007-02-02 2007-02-02 Processing method for reducing NaCl removal rate of nano filter membrane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2007100567055A CN101234295B (en) 2007-02-02 2007-02-02 Processing method for reducing NaCl removal rate of nano filter membrane

Publications (2)

Publication Number Publication Date
CN101234295A CN101234295A (en) 2008-08-06
CN101234295B true CN101234295B (en) 2010-10-27

Family

ID=39918354

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2007100567055A Expired - Fee Related CN101234295B (en) 2007-02-02 2007-02-02 Processing method for reducing NaCl removal rate of nano filter membrane

Country Status (1)

Country Link
CN (1) CN101234295B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AR084006A1 (en) * 2010-12-01 2013-04-17 Toray Industries PROCEDURE FOR THE SEPARATION AND RECOVERY OF A PURIFIED ALCALINE METAL SALT
CN106830191B (en) * 2017-01-20 2020-08-28 苏州新能环境技术股份有限公司 Isoelectric point identification-based nanofiltration salt separation process confirmation method
CN113398781B (en) * 2021-06-18 2022-07-19 中国农业科学院农业质量标准与检测技术研究所 Microporous filter membrane material and preparation method and application thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1288776A (en) * 2000-09-21 2001-03-28 华东理工大学 Preparation of sulfonated polyether sulfone filtering film
CN1415540A (en) * 2002-11-19 2003-05-07 华东理工大学 Method for removing sulfate ion from solution containing sodium chloride with high concentration
US7001518B1 (en) * 2000-11-28 2006-02-21 Hydranautics Low pressure reverse osmosis and nanofiltration membranes and method for the production thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1288776A (en) * 2000-09-21 2001-03-28 华东理工大学 Preparation of sulfonated polyether sulfone filtering film
US7001518B1 (en) * 2000-11-28 2006-02-21 Hydranautics Low pressure reverse osmosis and nanofiltration membranes and method for the production thereof
CN1415540A (en) * 2002-11-19 2003-05-07 华东理工大学 Method for removing sulfate ion from solution containing sodium chloride with high concentration

Also Published As

Publication number Publication date
CN101234295A (en) 2008-08-06

Similar Documents

Publication Publication Date Title
CN108178240A (en) Desalination mixed bed regeneration method
CN102459096A (en) Method for recovering water and metals from plating wastewater resulting from washing
CN110605027B (en) Alkaline cleaning solution, acidic cleaning solution and ultrafiltration membrane cleaning method
CN101234295B (en) Processing method for reducing NaCl removal rate of nano filter membrane
CN111268834A (en) Desulfurization wastewater treatment system and method capable of recycling resources
JP2017113729A (en) Membrane cleaning agent, membrane cleaning liquid and cleaning method of membrane
CN111672326A (en) Method for cleaning membrane pollution in process of treating paper-making reconstituted tobacco extract liquor by electrodialysis
JP6815394B2 (en) Etching bath treatment
CN111495203A (en) Method for converting waste reverse osmosis membrane into membrane for nanofiltration or ultrafiltration
CN212247228U (en) Contain salt waste water recycling apparatus based on electrolysis hydrogen manufacturing technique
Muñoz et al. Hydrofluoric acid treatment for improved performance of a nanofiltration membrane
CN111003779A (en) Fine treatment regeneration system and wastewater classified collection method
CN217676840U (en) System for waste acid and waste alkali in recovery aluminium and aluminum alloy treatment process
CN103072947A (en) Method for extracting iodine from kelp
CN110787512A (en) Pickling process for metal filter element
CN113351023B (en) MBR (Membrane biological reactor) membrane offline cleaning and repairing method for sewage treatment workshop
CN114411157A (en) Cleaning method for residual chloride ions in aluminum foil and application of cleaning method
CN109652805B (en) Deplating liquid for removing copper-nickel coating and using method thereof
CN108060452A (en) The electrobrightening processing method of aluminium
TWI715974B (en) Method for removing chlorine-containing salt from industrial wastewater and apparatus thereof
CN111302384A (en) Zero-emission process for treating alkaline copper etching waste liquid
CN101922012A (en) Method for cleaning positive plate after formation of lead-acid battery plates
CN111636073A (en) Device and process for recycling salt-containing wastewater
CN206395967U (en) Plating and chemical plating waste water processing and online reclamation set
JP2000144490A (en) Surface treating method for aluminum material

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
C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20101027

Termination date: 20130202