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CN102344219A - Method of total halogenated caustic production - Google Patents

Method of total halogenated caustic production Download PDF

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Publication number
CN102344219A
CN102344219A CN2011101851036A CN201110185103A CN102344219A CN 102344219 A CN102344219 A CN 102344219A CN 2011101851036 A CN2011101851036 A CN 2011101851036A CN 201110185103 A CN201110185103 A CN 201110185103A CN 102344219 A CN102344219 A CN 102344219A
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brine
light salt
salt brine
perhalogeno
sulfate radical
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CN2011101851036A
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CN102344219B (en
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张华�
张平俊
肖明富
姜永红
蔡邦雄
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Fuhua Tongda Chemical Co ltd
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SICHUAN LESHAN FUHUA TONGDA PESTICIDE TECHNOLOGY Co Ltd
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Abstract

The invention relates to a method of total halogenated caustic production, and belongs to the chemical field. In order to solve the problem of high cost of dilute brine recovery in the prior art, the invention provides a method of total halogenated caustic production; secondary brine is obtained by free chlorine removal, sulfite and sulfate removal, evaporation concentration, and resin treatment, and thus the purpose of dilute brine recovery is reached. Based on integrated innovation, the invention provides a set of industrial production process, adopts reasonable process steps and process parameter design, solves the recovery and utilization problem of dilute brine generated in caustic production by an ion-exchange membrane method, decreases the cost, reduces process outflanking of producing salts by brine and then dissolving the salts in water, saves a lot of energy consumption in salt production, and also protect the environment.

Description

A kind of method of perhalogeno system alkali
Technical field
The present invention relates to a kind of method of industry system alkali, more particularly, the present invention relates to a kind of method of ionic membrane method perhalogeno system alkali.
Background technology
Traditional chlor-alkali production technology is that salt is soluble in water, removes impurity such as calcium, magnesium, sulfate radical, ammonia nitrogen.The input electrolyzer carries out electrolysis and makes chlorine, hydrogen and sodium hydroxide.Adopt the water-soluble production energy consumption that causes salt of salt, 140 yuan of the production costs of one ton of salt of every production in the technology.Wherein, energy consumption folding standard coal is 0.25 ton.Adopt energy consumption and cost that perhalogeno system alkali can saving salt production.
Ionic membrane method alkali-making process process is:
1, removal of impurities: bittern adds soda ash and removes Ca 2+, Sr 2+, Ba 2+, Al 3+, Hg 2+Etc. most ion, get into the baffling groove, add the NaClO of some amount, in removing the ammonia react groove, accomplish reaction and generate monochloramine;
2, stripping is handled: and Xiang Tazhong is blown into pressurized air and carries out stripping and handle, and monochloramine is taken out of system by air;
3, system alkali: after removing most metal ion and total amine; Remove nitre technology removal sulfate radical with embrane method and obtain primary brine; Primary brine further removes metallic cations such as calcium-magnesium removing through Ao's resin complexing absorption; Secondary brine after resin tower is handled reaches ion-exchange membrane electrolyzer to the brinish quality standard; Secondary brine gets into electrolyzer and under the effect of electric current, reacts, and makes caustic soda, chlorine and hydrogen.
The qualified secondary brine of being processed into the light salt brine that produces in the ion-exchange membrane electrolyzer (salts contg is at 15-21%) reclaims that to be used for electrolyzer be the key that can perhalogeno system alkali be realized; There is enterprise's employing to re-inject salt mine on the industry and handles, but be subjected to the mine to be directed at the increase of energy consumption and the rising of cost apart from the production that produces transportation cost or salt with the method that adds solid salt.So it is most economical and method for saving energy that light salt brine is directly handled reuse.
Summary of the invention
The present invention is intended to solve the high problem of light salt brine cost recovery in the prior art; Realize a kind of method of ionic membrane method perhalogeno system alkali; Present method efficiently solves and adopts the technical problem that reclaims light salt brine in the bittern direct production caustic soda; Being applied in the state-of-the-art ionic membrane method perhalogeno system alkali of success reaches economic, energy-conservation effect.
In order to realize the foregoing invention purpose, concrete technical scheme of the present invention is following:
A kind of method of perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The S-WAT that in light salt brine, adds light salt brine quality 0.1-2%; Adding the salt acid for adjusting pH value again is 8-9; Circulating reaction 1-8 hour, remove the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; The light salt brine of removing free chlorine and inferior sulfate radical gets into embrane method and removes the nitre device; Remove behind the sulfate radical light salt brine with get into vapo(u)rization system in the lump without the light salt brine that removes nitre; Remove portion water; Improve salts contg and obtain reclaiming light salt brine to advancing the groove concentration requirement; Get into resin processing system in the lump with primary brine; Make that to meet into the refined brine of slot standard be secondary brine (secondary brine continues into groove electrolysis system alkali, and cost is practiced thrift in recycle).
Above-mentioned circulating reaction is to mix from flowing, and need not heat exchange, and it is 60-75 ℃ that light salt brine goes out the groove temperature.
The pressurized air of above-mentioned adding is the pressurized air of 0.15-0.3MPa.
The compressed-air actuated amount of above-mentioned feeding is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:8-12.
Above-mentioned entering embrane method is removed the light salt brine of removing free chlorine and inferior sulfate radical of nitre device, accounts for the 25-100% of the light salt brine total amount of removing free chlorine and inferior sulfate radical.
The above-mentioned light salt brine of removing behind the sulfate radical gets into vapo(u)rization system and removes portion water, and salts contg is increased to 250-320g/l.
The standard of the above-mentioned recovery secondary brine that makes is:
NaCl=290-310g/l、I -≤0.1ppm、Ca 2++Mg 2+<20ppb、Ba 2+<0.1ppm、Fe 2++Fe 3+<0.15ppm、Al 3+?<0.1ppm、Sr 2+?<0.1ppm、Mn 2+?<0.05ppm、Ni 2+?<0.01ppm。
The above-mentioned material that is used for the used container of spissated vapo(u)rization system is titanium or titanium alloy.
The useful technique effect that the present invention brings:
The present invention is based on integrated innovation one cover industrialized producing technology is provided; Utilization reasonable technology step and process parameters design; Solved the recycling problem of ionic membrane legal system alkali generation light salt brine; Reduced cost; Having reduced bittern, to process salt circuitous by the water-soluble technology of salt again; Save the mass energy consumption of salt manufacturing, also protected environment.
Description of drawings
Fig. 1 is a Total Halogenated Caustic Production schema of the present invention.
Embodiment
Embodiment 1
The ionic membrane method perhalogeno system alkali that light salt brine is reclaimed:
A kind of method of ionic membrane method perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The excessive S-WAT that in light salt brine, adds light salt brine quality 0.1%; Adding the salt acid for adjusting pH value again is 8; Circulating reaction 1 hour is removed the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; The light salt brine of removing free chlorine and inferior sulfate radical gets into embrane method and removes the nitre device; The light salt brine of removing behind the sulfate radical gets into vapo(u)rization system; Remove portion water; Improve salts contg and obtain reclaiming light salt brine to advancing the groove concentration requirement; Get into resin processing system in the lump with primary brine, make and meet into that the refined brine of slot standard is a secondary brine.
Embodiment 2
The ionic membrane method perhalogeno system alkali that light salt brine is reclaimed:
A kind of method of ionic membrane method perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The excessive S-WAT that in light salt brine, adds light salt brine quality 2%; Adding the salt acid for adjusting pH value again is 9; Circulating reaction 8 hours is removed the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; The light salt brine of removing free chlorine and inferior sulfate radical gets into embrane method and removes the nitre device; The light salt brine of removing behind the sulfate radical gets into vapo(u)rization system; Remove portion water; Improve salts contg and obtain reclaiming light salt brine to advancing the groove concentration requirement; Get into resin processing system in the lump with primary brine, make and meet into that the refined brine of slot standard is a secondary brine.
Embodiment 3
The ionic membrane method perhalogeno system alkali that light salt brine is reclaimed:
A kind of method of ionic membrane method perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The excessive S-WAT that in light salt brine, adds light salt brine quality 0.6%; Adding the salt acid for adjusting pH value again is 8.5; Circulating reaction 4 hours is removed the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; Remove 1/3rd of free chlorine and inferior sulfate radical light salt brine and get into embrane methods and remove the nitre device, the light salt brine of removing behind the sulfate radical gets into vapo(u)rization system.Two of its excess-three branch also gets into vapo(u)rization system and removes portion water, improves salts contg and obtains reclaiming light salt brine to advancing the groove concentration requirement, gets into resin processing system in the lump with primary brine, makes to meet into that the refined brine of slot standard is a secondary brine.
Embodiment 4
The ionic membrane method perhalogeno system alkali that light salt brine is reclaimed:
A kind of method of ionic membrane method perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The excessive S-WAT that in light salt brine, adds light salt brine quality 1.6%; Adding the salt acid for adjusting pH value again is 8.8; Circulating reaction 2 hours is removed the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; The light salt brine 1/2nd of removing free chlorine and inferior sulfate radical gets into embrane method and removes the nitre device; The light salt brine of removing behind the sulfate radical gets into vapo(u)rization system; All the other also entering vapo(u)rization systems of 1/2nd; Remove portion water; Improve salts contg and obtain reclaiming light salt brine to advancing the groove concentration requirement; Get into resin processing system in the lump with primary brine, make and meet into that the refined brine of slot standard is a secondary brine.
Embodiment 5
On the basis of embodiment 1-4, further preferred version is:
The pressurized air that in removing the step of excessive inferior sulfate radical, adds is the pressurized air of 0.15MPa; The amount of bubbling air is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:8;
Account for 25% of the light salt brine total amount that produces in the electrolysis system alkali step getting into light salt brine that embrane method removes the nitre device;
Remove light salt brine behind the sulfate radical and get into vapo(u)rization system and remove portion water, salts contg is increased to 250g/l, obtain reclaiming light salt brine;
Reclaim light salt brine and primary brine and get into resin processing system in the lump, make secondary brine.
The material that is used for the used container of spissated vapo(u)rization system is titanium or titanium alloy.
Embodiment 6
On the basis of embodiment 1-4, further preferred version is:
The pressurized air that in removing the step of excessive inferior sulfate radical, adds is the pressurized air of 0.3MPa; The amount of bubbling air is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:12;
Account for 100% of the light salt brine total amount that produces in the electrolysis system alkali step getting into light salt brine that embrane method removes the nitre device;
Remove light salt brine behind the sulfate radical and get into vapo(u)rization system and remove portion water, salts contg is increased to 320g/l, obtain reclaiming light salt brine;
Reclaim light salt brine and primary brine and get into resin processing system in the lump, make secondary brine.
The material that is used for the used container of spissated vapo(u)rization system is titanium or titanium alloy.
Embodiment 7
On the basis of embodiment 1-4, further preferred version is:
The pressurized air that in removing the step of excessive inferior sulfate radical, adds is the pressurized air of 0.25MPa; The amount of bubbling air is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:10;
Account for 63% of the light salt brine total amount that produces in the electrolysis system alkali step getting into light salt brine that embrane method removes the nitre device;
Remove light salt brine behind the sulfate radical and get into vapo(u)rization system and remove portion water, salts contg is increased to 280g/l, obtain reclaiming light salt brine;
Reclaim light salt brine and primary brine and get into resin processing system in the lump, make secondary brine.
The material that is used for the used container of spissated vapo(u)rization system is titanium or titanium alloy.
Embodiment 8
On the basis of embodiment 1-4, further preferred version is:
The pressurized air that in removing the step of excessive inferior sulfate radical, adds is the pressurized air of 0.17MPa; The amount of bubbling air is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:11;
Account for 90% of the light salt brine total amount that produces in the electrolysis system alkali step getting into light salt brine that embrane method removes the nitre device;
Remove light salt brine behind the sulfate radical and get into vapo(u)rization system and remove portion water, salts contg is increased to 260g/l, obtain reclaiming light salt brine;
Reclaim light salt brine and primary brine and get into resin processing system in the lump, make secondary brine.
The material that is used for the used container of spissated vapo(u)rization system is titanium or titanium alloy.
Embodiment 9
According to Figure of description Fig. 1 perhalogeno system alkali method is described:
1500 cubic metres of bittern are preheating to 55 ℃ through plate-type heat exchangers, get into the baffling groove and add 25 kilograms of 4.5 tons in 30% sodium hydroxide and clorox, reactive tank before getting into stirs.Pump into pressurized tank and on pipeline, feed the empty fully sudden and violent gas (0.18MPa, 2.5 ten thousand mark sides) of compression.(this process is got rid of organic amine in the bittern and ammonia nitrogen with the mode of ammonia),
After removing denitrification; Be mixed into settling bowl 1 with iron trichloride; The upper clear supernate overflow gets into the divalent cation treater; 880 kilograms of the sodium carbonate solutions of adding 15%; Fully stir; Get into settling bowl 2; The pressurization of upper clear supernate pump gets into film filter; (brine quality per-cent is thousandth to see through liquid adding S-WAT; Excessive 4%) and hydrochloric acid; Regulate pH value 8-9 and remove that excessive free chlorine is laggard goes into resin tower secondary treatment salt solution, further remove divalent cation, reach into groove salt water quality standard (in calcium≤20ppb).
Qualified refined brine after secondary treatment gets into ion-exchange membrane electrolyzer, current density 5.5A/CM 2, under the effect of electric current, produce 840 tons in 32% sodium hydroxide and produce 1100 tons of light salt brines simultaneously.
Add S-WAT in 1100 tons of light salt brines and remove the free chlorine that produces in the electrolysis with hydrochloric acid adjusting pH8.5; Feed the sudden and violent gas (0.18MPA of pressurized air; 1.5 make inferior sulfate radical be converted into sulfate radical ten thousand mark sides); Remove nitre through embrane method and change (settling bowl 2 outlets of two effect concentration systems over to; Get into resin tower secondary treatment salt solution; Further remove divalent cation, reached groove salt water quality standard (20PPB).After making concentration bring up to 275g/l, get into embrane method and remove nitre system removal sulfate radical, incorporate the salt solution of secondary settlement again into.

Claims (8)

1. the method for a perhalogeno system alkali; Comprise that removal of impurities, stripping processing amine and ammonia nitrogen, preparation primary brine, resin system prepare secondary brine and electrolysis system alkali; It is characterized in that: detect the free chlorine in the light salt brine of described electrolysis system alkali generating step; The S-WAT that in light salt brine, adds light salt brine quality 0.1-2%; Adding the salt acid for adjusting pH value again is 8-9; Circulating reaction 1-8 hour, remove the free chlorine that produces in the electrolytic process; Feed pressurized air again, excessive inferior sulfate radical is oxidized to sulfate radical; The light salt brine of removing free chlorine and inferior sulfate radical gets into embrane method and removes the nitre device; The light salt brine of removing behind the sulfate radical gets into vapo(u)rization system; Remove portion water; Improve salts contg and obtain reclaiming light salt brine to advancing the groove concentration requirement; Get into resin processing system in the lump with primary brine, make and meet into that the refined brine of slot standard is a secondary brine.
2. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: described circulating reaction is for mixing from flowing, and it is 60-75 ℃ that light salt brine goes out the groove temperature.
3. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: the pressurized air of described adding is the pressurized air of 0.15-0.3MPa.
4. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: the compressed-air actuated amount of described feeding is that light salt brine and the volume ratio of air of removing behind the free chlorine are 1:8-12.
5. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: described entering embrane method accounts for the 25-100% of its total amount except that the light salt brine of removing free chlorine and inferior sulfate radical of nitre device.
6. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: the described light salt brine of removing behind the sulfate radical gets into vapo(u)rization system and removes portion water, is meant salts contg is increased to 250-320g/l.
7. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: the standard of the described secondary brine that makes is:
NaCl=290-310g/l、I -≤0.1ppm、Ca 2++Mg 2+<20ppb、Ba 2+<0.1PPm、Fe 2++Fe 3+<0.15PPm、Al 3+?<0.1PPm、Sr 2+?<0.1PPm、Mn 2+?<0.05PPm、Ni 2+?<0.01PPm。
8. the method for a kind of perhalogeno system alkali according to claim 1 is characterized in that: described vapo(u)rization system is for adopting the vapo(u)rization system of titanium or titanium alloy container.
CN 201110185103 2011-07-04 2011-07-04 Method of total halogenated caustic production Active CN102344219B (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102851684A (en) * 2012-09-17 2013-01-02 广州新普利节能环保科技有限公司 Process and device for preparing alkali by full-brine mechanical steam recompression method
CN104532283A (en) * 2014-12-17 2015-04-22 济宁金威煤电有限公司 Method and device for producing caustic soda through electrolysis by replacing part of fine brine with light salt brine
CN104695252A (en) * 2015-02-13 2015-06-10 中盐金坛盐化有限责任公司 Method for preparing dyeing accelerant from high liquid glauber salt
CN106906485A (en) * 2017-03-31 2017-06-30 四川永祥股份有限公司 A kind of total Halogenated Caustic Production
CN107366005A (en) * 2016-05-11 2017-11-21 江苏井神盐化股份有限公司 A kind of process of sodium sulphate type bittern perhalogeno ionic membrane caustic soda by-product glauber salt
CN110723742A (en) * 2019-11-26 2020-01-24 江西富达盐化有限公司 Novel process for producing liquid salt by using sodium carbonate distillate

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4839003A (en) * 1986-11-07 1989-06-13 Metallgesellschaft Aktiengesellschaft Process for producing alkali hydroxide, chlorine and hydrogen by the electrolysis of an aqueous alkali chloride solution in a membrane cell
CN1107903A (en) * 1994-03-03 1995-09-06 湖南化学工业设计院 Method for preparing sodium hydroxide by brine electrolysis
CN101694000A (en) * 2009-09-30 2010-04-14 莫新来 Method for concentrating dilute brine
JP2010180445A (en) * 2009-02-04 2010-08-19 Nippon Rensui Co Ltd Method of electrolyzing alkaline metal chloride

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4839003A (en) * 1986-11-07 1989-06-13 Metallgesellschaft Aktiengesellschaft Process for producing alkali hydroxide, chlorine and hydrogen by the electrolysis of an aqueous alkali chloride solution in a membrane cell
CN1107903A (en) * 1994-03-03 1995-09-06 湖南化学工业设计院 Method for preparing sodium hydroxide by brine electrolysis
JP2010180445A (en) * 2009-02-04 2010-08-19 Nippon Rensui Co Ltd Method of electrolyzing alkaline metal chloride
CN101694000A (en) * 2009-09-30 2010-04-14 莫新来 Method for concentrating dilute brine

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王正新等: "关于全卤离子膜烧碱的探讨", 《中国氯碱》, no. 5, 31 May 2006 (2006-05-31), pages 6 - 8 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102851684A (en) * 2012-09-17 2013-01-02 广州新普利节能环保科技有限公司 Process and device for preparing alkali by full-brine mechanical steam recompression method
CN102851684B (en) * 2012-09-17 2015-08-05 广州新普利节能环保科技有限公司 A kind of perhalogeno water function of mechanical steam recompression method alkali-making process and device
CN104532283A (en) * 2014-12-17 2015-04-22 济宁金威煤电有限公司 Method and device for producing caustic soda through electrolysis by replacing part of fine brine with light salt brine
CN104532283B (en) * 2014-12-17 2016-01-13 济宁金威煤电有限公司 A method and device for producing caustic soda by electrolysis of light brine instead of part of refined brine
CN104695252A (en) * 2015-02-13 2015-06-10 中盐金坛盐化有限责任公司 Method for preparing dyeing accelerant from high liquid glauber salt
CN104695252B (en) * 2015-02-13 2016-06-29 中盐金坛盐化有限责任公司 A kind of method adopting high glass gall to prepare accelerant
CN107366005A (en) * 2016-05-11 2017-11-21 江苏井神盐化股份有限公司 A kind of process of sodium sulphate type bittern perhalogeno ionic membrane caustic soda by-product glauber salt
CN107366005B (en) * 2016-05-11 2019-03-26 江苏苏盐井神股份有限公司 A kind of process of sodium sulphate type bittern perhalogeno ionic membrane caustic soda by-product anhydrous sodium sulphate
CN106906485A (en) * 2017-03-31 2017-06-30 四川永祥股份有限公司 A kind of total Halogenated Caustic Production
CN110723742A (en) * 2019-11-26 2020-01-24 江西富达盐化有限公司 Novel process for producing liquid salt by using sodium carbonate distillate

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Denomination of invention: Method of total halogenated caustic production

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Denomination of invention: A method of alkali production by total bittern

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Registration number: Y2020510000109

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Address after: 614803 Jinsu Town, Wutongqiao District, Leshan City, Sichuan Province

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Address before: Wutongqiao Qiao Gou Zhen 614800 Sichuan city of Leshan Province

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Registration number: Y2020510000109