CN110372012A - A kind of embrane method total halogenated caustic production method of no solid waste discharge - Google Patents
A kind of embrane method total halogenated caustic production method of no solid waste discharge Download PDFInfo
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- CN110372012A CN110372012A CN201910591512.2A CN201910591512A CN110372012A CN 110372012 A CN110372012 A CN 110372012A CN 201910591512 A CN201910591512 A CN 201910591512A CN 110372012 A CN110372012 A CN 110372012A
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D3/00—Halides of sodium, potassium or alkali metals in general
- C01D3/04—Chlorides
- C01D3/06—Preparation by working up brines; seawater or spent lyes
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D3/00—Halides of sodium, potassium or alkali metals in general
- C01D3/14—Purification
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- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
- C25B1/00—Electrolytic production of inorganic compounds or non-metals
- C25B1/01—Products
- C25B1/34—Simultaneous production of alkali metal hydroxides and chlorine, oxyacids or salts of chlorine, e.g. by chlor-alkali electrolysis
- C25B1/46—Simultaneous production of alkali metal hydroxides and chlorine, oxyacids or salts of chlorine, e.g. by chlor-alkali electrolysis in diaphragm cells
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Abstract
The present invention relates to a kind of embrane method total halogenated caustic production methods of no solid waste discharge, it includes the following steps: that brine is sent into organic tubular type membranous system after refining reaction and is filtered, filtered permeate is divided into two parts, and a portion permeate obtains low salt made from earth containing a comparatively high percentage of sodium chloride water and high salt made from earth containing a comparatively high percentage of sodium chloride water after denitration process;Another part permeate is mixed with the resulting low salt made from earth containing a comparatively high percentage of sodium chloride water of step S1, obtains primary brine;Caustic soda and light salt brine is made after adsorbing, then through ionic membrane alkaline system in primary brine.The application directly carries out denitration to saturated bittern using alkali resistant nanofiltration membrane, compared with tradition is first diluted with water again salt dissolving to the technique being saturated, has saved salt consumption, the steam consumption, water consume, has substantially reduced denitration cost;And by high salt made from earth containing a comparatively high percentage of sodium chloride water and Mg (OH)2、CaCO3Mud infuses well processing, solves high salt made from earth containing a comparatively high percentage of sodium chloride water problem of outlet, also thoroughly solves the problems, such as that salt slurry is subsequent intractable.
Description
Technical field
The invention belongs to salt refining technical fields, and in particular to a kind of embrane method total halogenated caustic production method of no solid waste discharge.
Background technique
Currently, domestic chlor-alkali industry mainly uses ionic membrane method alkaline, using saturated brine as raw material, electrolysis generates hydroxide
The products such as sodium, if containing the impurity such as a large amount of calcium, magnesium in salt water, calcium and magnesium ion can in electrolytic process with the OH on anode-Instead
Insoluble matter should be generated to be deposited on ionic membrane, seriously affect service life of ion-exchange membrane, therefore, salt refining is produced in ionic membrane method alkaline
It is particularly important in the process.
Traditional primary refined brine work of the country based on " barrel type reactor+dongle settling tank+sand filter " process route
Skill is eliminated substantially, currently, domestic chlor-alkali enterprises are mainly used to there is following two membrane filtration process: gore film, HVM film is generations
The organic microfiltration membrane process and ceramic membrane crossflow filtration technique of table.
New varieties of organic tubular membrane as membrane separation technique, the runner for having both tubular membrane is wide, cross-flow filtration and organic film
Mature preparation process the advantages that, since the advent of the world is concerned, be widely used at present juice clarification, external
MBR, processing, the reuse of spent acid lye and sewage treatment project of oil field reinjection water etc..Organic tubular membrane refined brine technique is one
Kind makes full use of tubular membrane to carry out the salt water electric process for refining of high efficient solid and liquid separation effect, is by being added in salt water first
Sodium hydroxide, sodium carbonate refining agent make the calcium ions and magnesium ions in salt water generate precipitating, then efficiently separating by tubular membrane component
Effect make sediment and water quickly, be completely separated, effluent quality is strengthened.
Country's salt water, which removes nitre conventional method, at present barium chloride method, calcium method, freezing, embrane method.Wherein embrane method denitration conduct
A kind of emerging denitration technology removes the sulfate ion in salt water, tool using nanofiltration membrane to divalent ion crown_interception
There is the advantages that operation energy consumption is low, occupied area is small, does not introduce third component, cleanliness without any pollution.Currently, domestic chlor-alkali enterprises only will
Embrane method is used for light salt brine denitration, and cannot be used for high concentration salt water (NaCl > 260g/L) denitration process.Therefore, de- for brine
Nitre, this requires must first add water from the saturated bittern of underground mining out to reduce wherein NaCl content, again through salt dissolving after denitration
Technique increases NaCl content, low efficiency.In addition, calcium ions and magnesium ions content is higher in brine, domestic chlor-alkali enterprises mainly use two alkali
Method removal, by the way that NaOH, Na are added into brine2CO3, reaction generation Mg (OH) 2、CaCO3Then solid matter is cut by film
Concentrate is stayed in, then salt slurry is extruded by filter press, salt slurry send to the external world and handles, but salt slurry subsequent processing is also more and more difficult.
Summary of the invention
The purpose of the present invention is to provide a kind of embrane method total halogenated caustic production methods of no solid waste discharge, and organic tubular membrane is gone
Removing calcium and magnesium and nanofiltration membrane denitration combine the total Halogenated Caustic Production for carrying out salt refining, which is directly used in nanofiltration full
With the denitration of brine, and thoroughly solve the problems, such as that salt slurry is intractable.
Specific technical solution is as follows:
A kind of embrane method total halogenated caustic production method of no solid waste discharge, includes the following steps:
S1, brine are sent into organic tubular type membranous system after refining reaction and are filtered, and filtered permeate is divided into two parts,
Middle a part of permeate obtains low salt made from earth containing a comparatively high percentage of sodium chloride water and high salt made from earth containing a comparatively high percentage of sodium chloride water after denitration process;
S2, another part permeate are mixed with the resulting low salt made from earth containing a comparatively high percentage of sodium chloride water of step S1, obtain primary brine;
Caustic soda and light salt brine is made after adsorbing, then through ionic membrane alkaline system in S3, primary brine.
Further scheme is sent into subsider, sedimentation through the filtered concentrate of organic tubular type membranous system in the step S1
After 0.5-2h, subsider middle and upper part clear liquid returns to organic tubular type membranous system reprocessing.
Further scheme, the mud of the sedimentation trench bottom infuse well after mixing with the high salt made from earth containing a comparatively high percentage of sodium chloride water, light salt brine.
Further scheme, NaCl content is 290~310g/L in brine described in step S1.
Further scheme, refining reaction described in step S1 is that brine to be processed is first sent into baffling slot, in baffling slot
In metered refining agent and degradation agent, when being then introduced into reaction container row react.
Further scheme, the refining agent are NaOH and Na2CO3, the degradation agent be NaClO, wherein NaClO plus
Entering amount is 10-50mg/L.
Specifically, NaOH, Na is added into the brine that NaCl content is 290~310g/L2CO3Refining agent, NaOH additional amount
For with Mg2+Excessive 0.1~0.3g/L, Na after reaction2CO3Additional amount is and Ca2+Excessive 0.3~0.5g/L after reaction;Degradation agent
The additional amount of NaClO is 10-50mg/L.
Further scheme, denitration process described in step S1 be first will transmit through liquid be adjusted to pH value be 7-9, ORP < 0mV,
Then the alkali resistant nanofiltration membrane that pH value is 7-9 is re-fed into be handled.
HCl, Na are added in the permeate for further scheme2SO3To adjust its pH value and ORP.
Further scheme, the content of sulfate radical reaches 5g/L in primary brine described in step S2.
Two parts will be divided into through organic filtered permeate of tubular type membranous system in the application, be due to after denitration process
Low glass gall sulfate radical content is low (generally less than 5g/L), and sulfate radical content height (generally higher than 5g/L) in permeate, and mixes
Primary brine will carry out resin adsorption afterwards, it requires that wherein sulfate radical content is 5-7g/L, so organic tubular type membranous system mistake
Permeate after filter will be divided into two parts and be blended.
Denitration process is using alkali resistant nanofiltration membrane, and operation pH range is 7-9, so will transmit through liquid is adjusted to pH value
It for 7-9, ORP < 0mV, is then re-fed into alkali resistant nanofiltration membrane and is handled, to meet into film requirement.
The present invention directly filters the salt water after refining reaction using organic tubular type membranous system, the Mg that reaction is generated
(OH)2Colloid, CaCO3The impurity such as the suspended matter carried in precipitating and salt water removal, through the refined brine of organic tubular type membranous system
Middle Ca2+、Mg2+Total content < 1mg/L, SS < 0.5mg/L.
Organic tubular membrane system structure in the application is made of as disclosed in CN109133112A 1~10 group of membrane stack,
Every group of membrane stack series connection 3-8 props up organic tubular membrane component, and filter type is interior press filtration, 0.1 ~ 0.6MPa of operating pressure, film surface stream
Fast 1m/s-3m/s.Membrane module diameter is 6 inches, 8 inches or 10 inches, and membrane module length is 3m or 4m.Organic tubular membrane component
It is encapsulated in putamina sealant and is formed by more organic tubular type membrane tube both ends, membrane channels diameter is 5mm or 8mm, membrane aperture 10-
50nm, membrane material are Kynoar, polyether sulfone, polysulfones or polyacrylonitrile.
Organic tubular membrane is applied to salt refining field as a kind of novel technology, has the advantages that filtering accuracy
Height, pore-size distribution are narrow, and obtained brine quality is higher, quality is more stable;Membrane tube is not broken, good airproof performance;It is logical with broader film
Road, channel will not block;Stronger contamination resistance, the chemical cleaning period is long, easy cleaning;
The application directly carries out denitration to saturated bittern using alkali resistant nanofiltration membrane, is first diluted with water again salt dissolving to saturation with tradition
Technique compare, saved salt consumption, the steam consumption, water consume, brine denitration cost substantially reduces;
Traditional nanofiltration denitrating system uses acid-resistant disintegration, needs that salt water pH is first adjusted to acidity, salt water pH is adjusted to alkali again after denitration
Property, to meet the requirement of resin adsorption condition, cause acid, alkali consumption big.And the application nanofiltration system uses alkali resistant nanofiltration membrane, fortune
Row pH range is 7-9, to save acid adding plus alkali expense.
By high salt made from earth containing a comparatively high percentage of sodium chloride water and Mg (OH) in the application 2、CaCO3Mud infuses well processing, solves high salt made from earth containing a comparatively high percentage of sodium chloride water problem of outlet,
Also thoroughly solve the problems, such as that salt slurry is subsequent intractable.
Specific embodiment
For a further understanding of the present invention, the preferred embodiment of the invention is described below with reference to embodiment, still
It should be appreciated that these descriptions are only further explanation the features and advantages of the present invention, rather than to the claims in the present invention
Limitation.
Embodiment 1
NaCl content 300g/L, SO from the brine that Jing Kuang is produced4 2-Content 12g/L, Ca2+Content 0.65g/L, Mg2+Content
0.07g/L is pumped directly into baffling slot, the metered sodium carbonate 2.1g/L, sodium hydroxide 0.35g/L, secondary in baffling slot
Then sodium chlorate 20mg/L flows into reaction container and carries out refining reaction;Wherein, the Mg in salt dissolving2+、Ca2+Respectively with NaOH, Na2CO3
Reaction generates Mg (OH)2、CaCO3Solid matter, the crude brine after refining reaction are sent into organic tubular type membranous system, organic tubular membrane
System is made of 2 groups of membrane stacks, organic tubular membrane component of 5 10 inches of diameters of every group of membrane stack series connection, length 4m, organic tubular membrane
Channel 5mm, aperture 30nm, membrane material are Kynoar;It controls operating pressure 0.3MPa, crossflow velocity 1.5m/s, instead
The Mg (OH) that should be generated2Colloid, CaCO3The impurity such as the suspended matter carried in precipitating and salt water are trapped, through organic tubular membrane
Ca in the refined brine of system2+、Mg2+Total content 0.65mg/L, SS=0.36mg/L;
HCl, Na is added in a part of permeate2SO3It adjusts pH=9, be sent into alkali resistant nanofiltration membrane system after ORP < 0mV, through receiving
SO in the low salt made from earth containing a comparatively high percentage of sodium chloride water of filter membrane4 2-Content 1.5g/L, SO in the high salt made from earth containing a comparatively high percentage of sodium chloride water being trapped4 2-Content 42g/L, low salt made from earth containing a comparatively high percentage of sodium chloride water and remainder
Permeate mixing after obtain primary brine, make wherein SO4 2-Content 7g/L adsorbs to obtain secondary brine using chelate resin,
It is sent into ionic membrane alkaline system, caustic soda and light salt brine is made;
The concentrate of organic tubular membrane retention is sent into subsider, residence time 1h, and upper part clear liquid returns to organic tubular type membranous system
Reprocessing, bottom mud (solid content 5%) infuse well after mixing with high salt made from earth containing a comparatively high percentage of sodium chloride water, light salt brine.
Embodiment 2
NaCl content 295g/L, SO from the brine that Jing Kuang is produced4 2-Content 18g/L, Ca2+Content 1.32g/L, Mg2+Content
0.18g/L is pumped directly into baffling slot, metered sodium carbonate 4g/L, sodium hydroxide 0.9g/L, sodium hypochlorite in baffling slot
Then 30mg/L flows into reaction container and carries out refining reaction;Wherein, the Mg in salt dissolving2+、Ca2+Respectively with NaOH, Na2CO3Reaction life
At Mg (OH)2、CaCO3Solid matter, the crude brine after refining reaction are sent into organic tubular type membranous system, and organic tubular type membranous system is by 4
Group membrane stack composition, organic tubular membrane component of 6 10 inches of diameters of every group of membrane stack series connection, length 4m, organic tubular type membrane channels
8mm, aperture 50nm, membrane material are Kynoar.Organic tubular membrane controls operating pressure 0.35MPa, crossflow velocity 2m/s,
React the Mg (OH) generated2Colloid, CaCO3The impurity such as the suspended matter carried in precipitating and salt water are trapped, through organic tubular type
Ca in the refined brine of membranous system2+、Mg2+Total content 0.65 mg/L, SS=0.43mg/L;
HCl, Na is added in a part of permeate2SO3It is sent into alkali resistant nanofiltration membrane system after adjusting pH=8.5, ORP < 0mV, is penetrated
SO in the low salt made from earth containing a comparatively high percentage of sodium chloride water of nanofiltration membrane4 2-Content 2g/L, SO in the high salt made from earth containing a comparatively high percentage of sodium chloride water being trapped4 2-Content 45g/L, low salt made from earth containing a comparatively high percentage of sodium chloride water and remainder
Permeate mixing after obtain primary brine, make wherein SO4 2-Content 5g/L adsorbs to obtain secondary brine using chelate resin,
It is sent into ionic membrane alkaline system, caustic soda and light salt brine is made;
The concentrate of organic tubular membrane retention is sent into subsider, residence time 0.5h, and upper clear supernate returns to organic tubular type membranous system
Reprocessing, bottom mud (solid content 6%) infuse well after mixing with high salt made from earth containing a comparatively high percentage of sodium chloride water, light salt brine.
Embodiment 3
NaCl content 295g/L, SO from the brine that Jing Kuang is produced4 2-Content 13g/L, Ca2+Content 0.86g/L, Mg2+Content
0.1g/L is pumped directly into baffling slot, metered sodium carbonate 2.7g/L, sodium hydroxide 0.53g/L, sodium hypochlorite in baffling slot
Then 20mg/L flows into reaction container and carries out refining reaction;Wherein, the Mg in salt dissolving2+、Ca2+Respectively with NaOH, Na2CO3Reaction life
At Mg (OH)2、CaCO3Solid matter, the crude brine after refining reaction are sent into organic tubular type membranous system, and organic tubular type membranous system is by 1
Group membrane stack composition, organic tubular membrane component of 48 inches of diameters of every group of membrane stack series connection, length 3m, organic tubular type membrane channels 5mm,
Aperture is 30nm, and membrane material is Kynoar.Operating pressure 0.3MPa is controlled, crossflow velocity 1.8m/s reacts the Mg of generation
(OH)2Colloid, CaCO3The impurity such as the suspended matter carried in precipitating and salt water are trapped, through the refined salt of organic tubular type membranous system
Ca in water2+、Mg2+Total content 0.74 mg/L, SS=0.38mg/L;
HCl, Na are added in a part of permeate2SO3It is sent into alkali resistant nanofiltration membrane system after adjusting pH=9, ORP < 0mV, thoroughly
Cross SO in the low salt made from earth containing a comparatively high percentage of sodium chloride water of nanofiltration membrane4 2-Content 1g/L, SO in the high salt made from earth containing a comparatively high percentage of sodium chloride water being trapped4 2-Content 40g/L, low salt made from earth containing a comparatively high percentage of sodium chloride water with it is remaining
Under permeate mixing after obtain primary brine, make wherein SO4 2-Content 5g/L adsorbs to obtain secondary salt using chelate resin
Water is sent into ionic membrane alkaline system, and caustic soda and light salt brine is made;
The concentrate of organic tubular membrane retention is sent into subsider, residence time 0.5h, and upper clear supernate returns to organic tubular type membranous system
Reprocessing, bottom mud (solid content 5%) infuse well after mixing with high salt made from earth containing a comparatively high percentage of sodium chloride water, light salt brine.
Comparative example
Former halogen NaCl content 300g/L, SO produced from Jing Kuang4 2-Content 12g/L, Ca2+Content 1.30g/L, Mg2+Content
0.32g/L is pumped directly into baffling slot, metered sodium carbonate 4g/L, sodium hydroxide 1.3g/L, sodium hypochlorite in baffling slot
Then 20mg/L flows into reaction container, wherein the Mg in salt dissolving2+、Ca2+Respectively with NaOH, Na2CO3Reaction generates Mg (OH)2、
CaCO3Solid matter, the crude brine after refining reaction are sent into ceramic membranous system, react the Mg (OH) of generation2Colloid, CaCO3Precipitating
And the impurity such as suspended matter carried in salt water are trapped, Ca in the refined brine of permeation ceramic membrane system2+、Mg2+Total content
1.24mg/L,SS=0.96mg/L;
Soft water is added in wherein a part of permeate, NaCl content is diluted to 260g/L and then plus HCl, Na2SO3Adjust pH
=6, it is sent into nanofiltration membrane system after ORP < 0mV, through SO in the low salt made from earth containing a comparatively high percentage of sodium chloride water of nanofiltration membrane4 2-Content 2g/L, the high salt made from earth containing a comparatively high percentage of sodium chloride being trapped
SO in water4 2-Content 40g/L, low glass gall is using being steam heated to 60 DEG C, then salt dissolving is to NaCl content 300g/L, salt dissolving water with it is remaining
Primary brine is obtained after lower transmission mixing, makes wherein SO4 2-Content 5g/L is adsorbed to obtain secondary brine using chelate resin, be sent
Enter ionic membrane alkaline system, caustic soda and light salt brine is made;
Ceramic membranous system concentrate carries out filters pressing processing, and salt slurry outward transport is used as fixed-end forces, and pressing filtering liquid returns to preamble workshop section and locates again
Reason.Well is infused after high salt made from earth containing a comparatively high percentage of sodium chloride water, light salt brine mixing.
Acid-resistant disintegration is used in comparative example, needs that salt water pH is first adjusted to acidity, salt water pH is adjusted to alkalinity again after denitration, with
Meet the requirement of resin adsorption condition, causes acid, alkali consumption big.The embodiment of the present application 1-3 is using alkali resistant nanofiltration membrane directly to full
Denitration is carried out with brine, compared with tradition is first diluted with water again salt dissolving to the technique being saturated, has saved salt consumption, the steam consumption, water consume, salt
Water denitration cost substantially reduces;In addition, the application simple process, and be by high salt made from earth containing a comparatively high percentage of sodium chloride water and Mg (OH) 2、CaCO3Mud note
Well processing, solves high salt made from earth containing a comparatively high percentage of sodium chloride water problem of outlet, also thoroughly solves the problems, such as that salt slurry is subsequent intractable.
Claims (9)
1. a kind of embrane method total halogenated caustic production method of no solid waste discharge, characterized by the following steps:
S1, brine are sent into organic tubular type membranous system after refining reaction and are filtered, and filtered permeate is divided into two parts,
Middle a part of permeate obtains low salt made from earth containing a comparatively high percentage of sodium chloride water and high salt made from earth containing a comparatively high percentage of sodium chloride water after denitration process;
S2, another part permeate are mixed with the resulting low salt made from earth containing a comparatively high percentage of sodium chloride water of step S1, obtain primary brine;
Caustic soda and light salt brine is made after adsorbing, then through ionic membrane alkaline system in S3, primary brine.
2. embrane method total halogenated caustic production method according to claim 1, it is characterised in that: through organic tubular membrane in the step S1
The filtered concentrate of system is sent into subsider, and after settling 0.5-2h, subsider middle and upper part clear liquid returns to organic tubular type membranous system
Reprocessing.
3. embrane method total halogenated caustic production method according to claim 2, it is characterised in that: the mud of the sedimentation trench bottom and institute
High salt made from earth containing a comparatively high percentage of sodium chloride water, the light salt brine stated infuse well after mixing.
4. embrane method total halogenated caustic production method according to claim 1, it is characterised in that: NaCl contains in brine described in step S1
Amount is 290~310g/L.
5. embrane method total halogenated caustic production method according to claim 1, it is characterised in that: refining reaction described in step S1 be by
Brine to be processed is first sent into baffling slot, metered refining agent and degradation agent in baffling slot, when being then introduced into reaction container
Row reaction.
6. embrane method total halogenated caustic production method according to claim 5, it is characterised in that: the refining agent is NaOH and Na2CO3,
The degradation agent is NaClO, and wherein the additional amount of NaClO is 10-50mg/L.
7. embrane method total halogenated caustic production method according to claim 1, it is characterised in that: denitration process described in step S1 is first
Will transmit through liquid and be adjusted to pH value is 7-9, ORP < 0mV, is then re-fed into the alkali resistant nanofiltration membrane that pH value is 7-9 and is handled.
8. embrane method total halogenated caustic production method according to claim 7, it is characterised in that: in the permeate be added HCl,
Na2SO3To adjust its pH value and ORP.
9. embrane method total halogenated caustic production method according to claim 1, it is characterised in that: in primary brine described in step S2
The content of sulfate radical reaches 5g/L.
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113753918A (en) * | 2021-09-24 | 2021-12-07 | 攀枝花钢企欣宇化工有限公司 | Method for reusing vanadium-chromium-titanium waste salt in chlor-alkali |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102627300A (en) * | 2012-04-20 | 2012-08-08 | 江苏凯米膜科技股份有限公司 | Double-membrane-method technology for refining brine and equipment for the same |
CN205346850U (en) * | 2015-12-30 | 2016-06-29 | 江苏九天高科技股份有限公司 | Two embrane method salt refining devices in perhalogeno system alkali |
CN105731495A (en) * | 2015-12-30 | 2016-07-06 | 江苏九天高科技股份有限公司 | Dual membrane method brine refining technology and device in whole bittern caustic soda production |
CN107022770A (en) * | 2017-04-28 | 2017-08-08 | 湖北可赛化工有限公司 | The process system and method for a kind of high caldo perhalogeno ionic membrane alkaline |
US20180119298A1 (en) * | 2015-03-11 | 2018-05-03 | Chemetics Inc. | Iodide removal from brine using ion retardation resins |
-
2019
- 2019-07-02 CN CN201910591512.2A patent/CN110372012A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102627300A (en) * | 2012-04-20 | 2012-08-08 | 江苏凯米膜科技股份有限公司 | Double-membrane-method technology for refining brine and equipment for the same |
US20180119298A1 (en) * | 2015-03-11 | 2018-05-03 | Chemetics Inc. | Iodide removal from brine using ion retardation resins |
CN205346850U (en) * | 2015-12-30 | 2016-06-29 | 江苏九天高科技股份有限公司 | Two embrane method salt refining devices in perhalogeno system alkali |
CN105731495A (en) * | 2015-12-30 | 2016-07-06 | 江苏九天高科技股份有限公司 | Dual membrane method brine refining technology and device in whole bittern caustic soda production |
CN107022770A (en) * | 2017-04-28 | 2017-08-08 | 湖北可赛化工有限公司 | The process system and method for a kind of high caldo perhalogeno ionic membrane alkaline |
Non-Patent Citations (1)
Title |
---|
孙春峰等: ""工艺条件确定"", 《化工生产技术》 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113753918A (en) * | 2021-09-24 | 2021-12-07 | 攀枝花钢企欣宇化工有限公司 | Method for reusing vanadium-chromium-titanium waste salt in chlor-alkali |
CN113753918B (en) * | 2021-09-24 | 2023-02-03 | 攀枝花钢企欣宇化工有限公司 | Method for reusing vanadium-chromium-titanium waste salt in chlor-alkali |
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Address after: 238200 First Floor of No.5 High-tech Enterprise Incubator Factory Building of Ma'anshan City and County Economic Development Zone, Anhui Province Applicant after: Anhui xingqida Membrane Technology Co.,Ltd. Address before: 238200 First Floor of No.5 High-tech Enterprise Incubator Factory Building of Ma'anshan City and County Economic Development Zone, Anhui Province Applicant before: Ma'anshan xingqida New Material Technology Co.,Ltd. |
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Application publication date: 20191025 |