CN112079364B - Method for recycling fluorine-and iodine-containing waste material resources - Google Patents

Method for recycling fluorine-and iodine-containing waste material resources Download PDF

Info

Publication number
CN112079364B
CN112079364B CN202010936781.0A CN202010936781A CN112079364B CN 112079364 B CN112079364 B CN 112079364B CN 202010936781 A CN202010936781 A CN 202010936781A CN 112079364 B CN112079364 B CN 112079364B
Authority
CN
China
Prior art keywords
potassium iodide
potassium
solution
iodine
filtering
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.)
Active
Application number
CN202010936781.0A
Other languages
Chinese (zh)
Other versions
CN112079364A (en
Inventor
刘会军
刘亚琪
邢晓宇
周丽娜
于国清
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shandong Boyuan Pharmaceutical Chemical Co Ltd
Original Assignee
Shandong Boyuan Pharmaceutical Chemical Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shandong Boyuan Pharmaceutical Chemical Co Ltd filed Critical Shandong Boyuan Pharmaceutical Chemical Co Ltd
Priority to CN202010936781.0A priority Critical patent/CN112079364B/en
Publication of CN112079364A publication Critical patent/CN112079364A/en
Application granted granted Critical
Publication of CN112079364B publication Critical patent/CN112079364B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/12Iodides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/14Purification

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

The invention relates to a method for recycling fluorine-and iodine-containing waste materials, which comprises the steps of converting organic fluorine into potassium fluoride by using potassium hydroxide, carrying out aerobic incineration at 600-800 ℃ by using a converter, completely burning or completely carbonizing organic matters, and avoiding generating fluorine-containing toxic substances such as hydrofluoric acid, perfluoroisobutylene and the like; the method has the advantages that fluoride ions are removed by using calcium hydroxide, excessive calcium hydroxide is removed by using potassium carbonate, the pH value is adjusted by using formic acid, and potassium formate is converted into potassium iodide by using iodine, so that the potassium iodide is produced without recovering iodine simple substances, the cost is saved, and the utilization rate of iodine is improved. The potassium iodide finished product obtained by the invention has the potassium iodide content of more than 99 percent and the fluorine ion content of less than 1 ppm.

Description

Method for recycling fluorine-and iodine-containing waste material resources
Technical Field
The invention relates to a method for recycling fluorine-and iodine-containing waste materials, in particular to a method for recycling iodine-containing byproduct resources of perfluoroalkyl ethyl (meth) acrylate, which can be directly subjected to a series of treatments to obtain a potassium iodide product with qualified quality, and belongs to the field of waste recycling.
Background
The perfluoroalkyl ethyl (meth) acrylate is the most important and key intermediate for preparing a surfactant with excellent hydrophobic and oleophobic properties, air permeability, washing resistance, stain resistance and easy stain removal, and a fluorine-containing hydrophobic and oleophobic fabric finishing agent with high stability in various environments such as strong acid, strong alkali, high temperature, high radiation and the like, and can be used for industrially recovering iodine by producing a crude potassium iodide product with the byproduct content of 70-85% in the synthesis process, wherein the potassium iodide product contains 15-20% of organic matters and 1-3% of fluorine, the obtained iodine has poor quality, the content of the organic matters in the iodine is high, the iodine contains fluorine ions, the iodide cannot be directly prepared and can be used after being refined, and the residual organic matters are difficult to treat, thereby causing environmental pollution.
The existing potassium iodide purification method is a calcination method, namely, crude potassium iodide is directly added into a rotary kiln or an incinerator for high-temperature incineration, high-boiling-point organic matters in the potassium iodide are decomposed, and then the potassium iodide is dissolved, filtered and recrystallized. The process can generate a large amount of strong corrosive hydrofluoric acid to severely corrode equipment, and meanwhile, because the C-F bond energy is large, fluorine-containing organic matters can be remained in the system, and even highly toxic perfluoroisobutylene can be generated. Resulting in poor safety, high environmental protection pressure and poor product quality.
Patent CN103241747A discloses a method for purifying KI in perfluoroalkyl ethyl acrylate synthesis byproducts, which comprises the steps of adsorbing with an adsorbent, filtering with an ultrafiltration membrane to remove colloid and macromolecular organic matters in the solution, sending the filtrate to a reverse osmosis membrane for filtering, and enriching the micromolecular organic matters and water in the filtrate together, thereby realizing the enrichment of KI. But the ultrafiltration membrane can not remove low molecular weight fluorine-containing organic matters and finally remains in the product, the ultrafiltrate is treated by a reverse osmosis membrane, and fluorine ions in the solution can not be effectively removed, so that the fluorine ions in the product can reach 0.5 percent, the product quality is seriously influenced, the treatment cost is high, impurity ions such as F and the like are difficult to completely remove, and the purity of KI is still difficult to meet the requirement. Especially fluoride ions (in the form of potassium fluoride) are present in the product and cannot be used in food, feed additives and the like.
The patent CN110002470A discloses a method for purifying potassium iodide from a perfluoroalkyl ethyl acrylate byproduct, which comprises the steps of adding the perfluoroalkyl ethyl acrylate byproduct into a stirring kettle, and adding 1-2 times of anhydrous ethanol by weight to obtain a crude potassium iodide mixed solution; and cooling the mixed solution, and carrying out centrifugal filtration to obtain the refined potassium iodide. The method can not effectively remove organic impurities and completely remove fluorine ions, so that the product content is low, the fluorine ions in the product reach 0.5 percent, the product quality is seriously influenced, and particularly, the fluorine ions (in the form of potassium fluoride) exist in the product and can not be used for food, feed additives and the like.
The invention is mainly concerned with how to treat the fluorine and iodine-containing waste material, especially the perfluoroalkyl ethyl (meth) acrylate iodine-containing byproduct into qualified potassium iodide, and the harmless treatment of the residual waste material.
Disclosure of Invention
In view of the above problems, the present invention is directed to: (1) extracting potassium iodide from the waste material, and processing the potassium iodide into qualified potassium iodide; (2) and (4) performing harmless treatment on the residual waste. The invention provides a method for recycling fluorine-and iodine-containing waste materials, which comprises the steps of adding a proper amount of water into a reaction kettle, adding crude potassium iodide, adding a proper amount of potassium hydroxide, slowly heating to reflux, keeping the reflux for 2-4 hours to form paste, burning the paste in a converter at 600-800 ℃ with oxygen, completely burning or completely carbonizing organic matters, cooling the obtained potassium iodide melt to form blocks, dissolving the blocks in water, filtering to remove insoluble substances to obtain a colorless to light yellow solution, measuring the content of fluoride ions, removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide, filtering to remove the generated calcium fluoride to obtain a potassium iodide solution without the fluoride ions, and removing excessive calcium hydroxide by using potassium carbonate with the same mole as the calcium hydroxide. Adjusting the pH of the solution to 6-8 by using formic acid, controlling the temperature to 80-90 ℃, adding iodine for reaction, after the reaction is finished, adjusting the pH to about 8 by using potassium hydroxide solution, decoloring by using proper amount of activated carbon, filtering to obtain filtrate, distilling and concentrating the filtrate, cooling and crystallizing, centrifuging and filtering to obtain a potassium iodide wet product, and drying to obtain a potassium iodide finished product, wherein the content of the potassium iodide finished product is more than 99%, and the content of fluorine ions is less than 1 ppm.
The technical scheme of the invention is as follows:
the invention relates to a method for recycling fluorine-and iodine-containing waste materials, in particular to potassium iodide as a byproduct of perfluoroalkyl ethyl (meth) acrylate, wherein the potassium iodide content is 70-80%, 15-20% of organic matters contain 1-3% of fluorine, and the potassium iodide is subjected to alkali boiling, concentration, high-temperature incineration in a converter to form salt, dissolution, filtration, fluoride ion removal by calcium hydroxide, and removal of excessive calcium hydroxide by potassium carbonate with the same mol as that of the calcium hydroxide. And (3) obtaining a potassium iodide solution without fluoride ions, adjusting the pH of the solution by using formic acid, adding iodine for reaction, adjusting the pH by using a potassium hydroxide solution, decoloring by using proper amount of activated carbon, filtering to obtain a filtrate, distilling and concentrating the filtrate, cooling for crystallization, centrifuging and filtering to obtain a wet potassium iodide product, and drying to obtain a finished potassium iodide product with the content of more than 99% and the fluoride ions of less than 1 ppm.
The more specific technical scheme is as follows:
a method for recycling fluorine-and iodine-containing waste materials comprises the following steps:
(1) adding a proper amount of water into a reaction kettle, adding potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate while stirring, and adding a proper amount of potassium hydroxide solution, wherein the solution is strongly alkaline;
(2) slowly heating to reflux, and keeping the reflux for 2-4 hours;
(3) forming into paste;
(4) cooling to below 70 ℃;
(5) using a converter; carrying out aerobic incineration at 600-800 ℃, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering to remove insoluble substances to obtain colorless to light yellow solution;
(8) measuring the content of fluoride ions, and removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions;
(10) adjusting the pH value of the potassium iodide solution obtained in the step (9) to 6-8 by using formic acid;
(11) controlling the temperature to be 80-90 ℃ and adding iodine for reaction;
(12) after the reaction is finished, regulating the pH value to about 8 by using a potassium hydroxide solution, decoloring by using a proper amount of activated carbon, and filtering to obtain a filtrate; adjusting the pH value to 8, wherein potassium hydroxide is slightly excessive, potassium iodide is filtered out by distillation, concentration, temperature reduction and condensation, and a trace amount of potassium hydroxide is left in the mother liquor, so that the separation is realized; HI can be completely removed by adjusting the pH to 7.0, and the pH value of the product can be qualified by adjusting the pH to 8.0.
(13) Distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain potassium iodide product with content over 99% and fluorion less than 1 ppm.
The step 2 comprises the main reaction: R-F + KOH ═ KF + R-OH
Step 8, the main reaction F-+Ca2+=CaF2↓Ca2++CO3 2-=CaCO3
The 10 th step mainly comprises the following reaction: KOH + HCOOH ═ HCOOK + H2O
The main reaction in the 11 th step: HCOOK + I2=KI+HI+CO2
The main reaction in the 12 th step: HI + KOH ═ KI + H2O
The invention has the beneficial effects that:
(1) converting organic fluorine into potassium fluoride by adding potassium hydroxide, and carrying out aerobic incineration at 600-800 ℃ by using a converter to thoroughly burn out or thoroughly carbonize organic matters without generating fluorine-containing toxic substances such as hydrofluoric acid, perfluoroisobutylene and the like;
(2) removing various impurity ions step by step, firstly removing fluoride ions by using calcium hydroxide, and then removing excessive calcium hydroxide by using potassium carbonate; regulating the pH value with formic acid; converting the potassium formate into potassium iodide by using iodine, thereby realizing the purification of the potassium iodide and obtaining qualified potassium iodide;
(3) through the impurity removal design utilizing various impurity ions, qualified potassium iodide can be directly extracted from the waste, the recovery of iodine simple substances is not needed to reproduce the potassium iodide, the cost is saved, and the utilization rate of iodine is improved.
Detailed Description
The invention will be further illustrated with reference to the following specific examples. It should be understood that these examples are only for illustrating the present invention and are not intended to limit the scope of the present invention. Further, it should be understood that various changes and modifications can be made by those skilled in the art after reading the teaching of the present invention, and those equivalents also fall within the scope of the appended claims of the present application.
The fluorine-containing and iodine-containing waste materials used in the embodiment of the invention are all prepared from perfluoroalkyl ethyl (meth) acrylate iodine-containing byproducts, wherein the content of potassium iodide is 70-80%, 15-20% of organic matters are contained, and 1-3% of fluorine is contained.
Example 1:
(1) adding a proper amount of water into a reaction kettle, adding a proper amount of potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate under stirring, adding a proper amount of potassium hydroxide solution, and adjusting the pH to 12;
(2) slowly heating to reflux, and keeping reflux for 2 hours;
(3) concentrating into paste;
(4) cooling to 70 ℃;
(5) using a converter; carrying out aerobic incineration at 800 ℃, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering to remove insoluble substances to obtain colorless to light yellow solution;
(8) measuring the content of fluoride ions, and removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions; (ii) a
(10) Adjusting the pH value of the potassium iodide solution obtained in the step (9) with formic acid to 8;
(11) controlling the temperature to be 90 ℃ and adding iodine for reaction;
(12) after the reaction is finished, regulating the pH value to about 8 by using a potassium hydroxide solution, decoloring by using a proper amount of activated carbon, and filtering to obtain a filtrate;
(13) distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain potassium iodide product with potassium iodide content of 99.1% and fluorion content of 0.9 ppm.
Example 2:
(1) adding a proper amount of water into a reaction kettle, and adding potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate under stirring; adding a proper amount of potassium hydroxide solution, and adjusting the pH value to 12;
(2) slowly heating to reflux, and keeping reflux for 4 hours;
(3) concentrating into paste;
(4) cooling to 60 ℃;
(5) using a converter; carrying out aerobic incineration at 800 ℃, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering to remove insoluble substances to obtain colorless to light yellow solution;
(8) measuring the content of fluoride ions, and removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions; (ii) a
(10) Adjusting the pH value of the potassium iodide solution obtained in the step (9) with formic acid to 6;
(11) controlling the temperature to be 80 ℃ and adding iodine for reaction;
(12) after the reaction is finished, regulating the pH value to about 8 by using a potassium hydroxide solution, decoloring by using a proper amount of activated carbon, and filtering to obtain a filtrate;
(13) distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain potassium iodide product with potassium iodide content of 99.5% and fluorion content of 0.5 ppm.
Example 3:
(1) adding a proper amount of water into a reaction kettle, adding potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate while stirring, adding a proper amount of potassium hydroxide solution, and adjusting the pH to 11;
(2) slowly heating to reflux, and keeping reflux for 3 hours;
(3) concentrating into paste;
(4) cooling to 65 ℃;
(5) using a converter; carrying out aerobic incineration at 600 ℃, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering to remove insoluble substances to obtain colorless to light yellow solution;
(8) measuring the content of fluoride ions, and removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions; (ii) a
(10) Adjusting the pH value of the potassium iodide solution obtained in the step (9) with formic acid to 6;
(11) controlling the temperature to be 85 ℃, and adding iodine for reaction;
(12) after the reaction is finished, regulating the pH value to about 8 by using a potassium hydroxide solution, decoloring by using a proper amount of activated carbon, and filtering to obtain a filtrate;
(13) distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain potassium iodide product with potassium iodide content of 99.3% and fluoric ion content of 0.9 ppm.
Example 4:
(1) adding a proper amount of water into a reaction kettle, adding potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate while stirring, adding a proper amount of potassium hydroxide solution, and adjusting the pH to 9;
(2) slowly heating to reflux, and keeping reflux for 4 hours;
(3) concentrating into paste;
(4) cooling to 70 ℃;
(5) using a converter; carrying out aerobic incineration at 800 ℃, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering to remove insoluble substances to obtain colorless to light yellow solution;
(8) measuring the content of fluoride ions, and removing the fluoride ions by using 2-5 times of theoretical amount of calcium hydroxide;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions; (ii) a
(10) Adjusting the pH value of the potassium iodide solution obtained in the step (9) to 7.5 by using formic acid;
(11) controlling the temperature to be 90 ℃ and adding iodine for reaction;
(12) after the reaction is finished, regulating the pH value to about 8 by using a potassium hydroxide solution, decoloring by using a proper amount of activated carbon, and filtering to obtain a filtrate;
(13) distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain potassium iodide product with content over 99.2% and fluoride ion content of 1 ppm.
The materials treated by the method are not only limited to the byproduct potassium iodide of perfluoroalkyl ethyl (meth) acrylate, but also comprise iodine-containing materials with similar components, and belong to the protection scope of the patent.

Claims (6)

1. A method for recycling fluorine-and iodine-containing waste materials comprises the following steps:
(1) adding a proper amount of water into a reaction kettle, adding potassium iodide which is a byproduct of perfluoroalkyl ethyl (meth) acrylate while stirring, and adding a proper amount of potassium hydroxide solution, wherein the solution is strongly alkaline;
(2) slowly heating to reflux, and keeping the reflux for 2-4 hours;
(3) forming into paste;
(4) cooling to below 70 ℃;
(5) carrying out aerobic incineration at 600-800 ℃ by using a converter, completely burning out or completely carbonizing organic matters, and cooling and agglomerating the obtained potassium iodide melt to obtain potassium iodide salt blocks;
(6) dissolving potassium iodide salt blocks with water;
(7) filtering;
(8) adding calcium hydroxide to remove fluoride ions;
(9) filtering and removing the generated calcium fluoride to obtain a potassium iodide solution without fluoride ions, adding potassium carbonate with the same mole as that of calcium hydroxide into the solution, stirring for 30-60 minutes, and filtering to obtain a potassium iodide solution without fluoride ions and calcium ions;
(10) adjusting the pH value of the potassium iodide solution obtained in the step (9) to 6-8 by using formic acid;
(11) controlling the temperature to be 80-90 ℃ and adding iodine for reaction;
(12) after the reaction is finished, adjusting the pH value to 8 by using a potassium hydroxide solution, and filtering to obtain a filtrate;
(13) distilling and concentrating the filtrate;
(14) cooling and crystallizing;
(15) centrifuging and filtering to obtain a wet potassium iodide product;
(16) drying to obtain the potassium iodide finished product.
2. The method of claim 1, wherein: insoluble matter is removed by filtration in step (7), and a colorless to pale yellow solution is obtained.
3. The method of claim 1, wherein: in the step (8), the content of fluoride ions is measured, 2-5 times of theoretical amount of calcium hydroxide is used for removing fluoride ions, and excessive calcium hydroxide is removed by using potassium carbonate which is equimolar with calcium hydroxide.
4. The method of claim 1, wherein: in the step (12), a proper amount of activated carbon is used for decoloring.
5. The method of claim 1, wherein: and (3) the potassium iodide finished product obtained in the step (16) has the potassium iodide content of over 99 percent and the fluorine ion content of less than 1 ppm.
6. The method of claim 1, wherein: the byproduct potassium iodide of the perfluoroalkyl ethyl (meth) acrylate contains 70-80% of potassium iodide, 15-20% of organic matters and 1-3% of fluorine.
CN202010936781.0A 2020-09-08 2020-09-08 Method for recycling fluorine-and iodine-containing waste material resources Active CN112079364B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010936781.0A CN112079364B (en) 2020-09-08 2020-09-08 Method for recycling fluorine-and iodine-containing waste material resources

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010936781.0A CN112079364B (en) 2020-09-08 2020-09-08 Method for recycling fluorine-and iodine-containing waste material resources

Publications (2)

Publication Number Publication Date
CN112079364A CN112079364A (en) 2020-12-15
CN112079364B true CN112079364B (en) 2021-05-28

Family

ID=73732150

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010936781.0A Active CN112079364B (en) 2020-09-08 2020-09-08 Method for recycling fluorine-and iodine-containing waste material resources

Country Status (1)

Country Link
CN (1) CN112079364B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112557142B (en) * 2020-12-24 2024-05-31 广州博诺通技术股份有限公司 Sample pretreatment method, halogen content detection method and application
CN113526528A (en) * 2021-07-16 2021-10-22 自贡鸿鹤制药有限责任公司 Preparation method of medicinal potassium iodide

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3992510A (en) * 1974-09-18 1976-11-16 Harima Chemicals, Inc. Method for recovery of iodine
KR20120136739A (en) * 2011-06-10 2012-12-20 (주) 라미나 Polarizing film to waste recovery of potassium iodide
CN103224220A (en) * 2013-05-09 2013-07-31 四川西艾氟科技有限公司 Method for recovering iodine from perfluoroalkylethyl acrylate synthesis byproduct
CN103241747A (en) * 2013-05-09 2013-08-14 四川西艾氟科技有限公司 Method for purifying KI in perfluoroalkylethyl acrylate synthesized by-product
CN104986771A (en) * 2015-07-02 2015-10-21 苏州晶洲装备科技有限公司 Treatment method for multi-crystalline silicon texturization etching waste liquid
CN106517252A (en) * 2016-10-10 2017-03-22 无锡易水元资源循环科技有限公司 Analytical pure potassium iodide preparation method using waste liquid containing iodine
CN108947060A (en) * 2017-05-23 2018-12-07 世宗化学株式会社 The method of liquor kalii iodide is regenerated from the waste liquid generated in light polarizing film manufacturing process
CN209383391U (en) * 2018-12-21 2019-09-13 福建三农新材料有限责任公司 A kind of iodine recovery system of perfluor alkyl ethyl acrylate production tail gas
CN110563003A (en) * 2018-06-06 2019-12-13 笹仓机械工程有限公司 Method and apparatus for treating waste liquid from polarizing plate production

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3992510A (en) * 1974-09-18 1976-11-16 Harima Chemicals, Inc. Method for recovery of iodine
KR20120136739A (en) * 2011-06-10 2012-12-20 (주) 라미나 Polarizing film to waste recovery of potassium iodide
CN103224220A (en) * 2013-05-09 2013-07-31 四川西艾氟科技有限公司 Method for recovering iodine from perfluoroalkylethyl acrylate synthesis byproduct
CN103241747A (en) * 2013-05-09 2013-08-14 四川西艾氟科技有限公司 Method for purifying KI in perfluoroalkylethyl acrylate synthesized by-product
CN104986771A (en) * 2015-07-02 2015-10-21 苏州晶洲装备科技有限公司 Treatment method for multi-crystalline silicon texturization etching waste liquid
CN106517252A (en) * 2016-10-10 2017-03-22 无锡易水元资源循环科技有限公司 Analytical pure potassium iodide preparation method using waste liquid containing iodine
CN108947060A (en) * 2017-05-23 2018-12-07 世宗化学株式会社 The method of liquor kalii iodide is regenerated from the waste liquid generated in light polarizing film manufacturing process
CN110563003A (en) * 2018-06-06 2019-12-13 笹仓机械工程有限公司 Method and apparatus for treating waste liquid from polarizing plate production
CN209383391U (en) * 2018-12-21 2019-09-13 福建三农新材料有限责任公司 A kind of iodine recovery system of perfluor alkyl ethyl acrylate production tail gas

Also Published As

Publication number Publication date
CN112079364A (en) 2020-12-15

Similar Documents

Publication Publication Date Title
US20190023585A1 (en) Method and apparatus for the recovery and deep treatment of polluted acid
CN110844922B (en) Industrial waste salt recycling treatment method and equipment
CN112079364B (en) Method for recycling fluorine-and iodine-containing waste material resources
CN109665495B (en) Combined resource utilization method of high-salinity wastewater and bypass ash of washed fly ash
CN109336068B (en) Method for removing tellurium from crude selenium slag
CN109500061B (en) Method for combined utilization of incineration fly ash and bypass ash
CN110002649B (en) Method for resource utilization of graphene waste acid
CN101597032A (en) The preparation method of electron-grade high purity hydrofluoric acid
CN114804158A (en) Method for producing high-purity potassium carbonate by using fly ash washing byproduct potassium chloride
CN113264540A (en) Method for recovering sodium chloride from phosphorus-containing waste salt
CN111804704A (en) Method for treating tetrachloro sodium aluminate solid slag
CN113896208A (en) Method for treating industrial mixed waste salt by using sulfuric acid
JP2019131448A (en) Method for producing lithium hydroxide
CN103043823A (en) Method for recycling waste water containing ammonium chloride
CN116814957A (en) Method for synchronously decyanating overhaul slag and extracting lithium
CN110937742A (en) Method for treating and recycling high-fluorine high-ammonia nitrogen waste liquid
CN114409157B (en) Recycling method for preparing chlor-alkali by waste salt water electrolysis
CN106698783B (en) A kind for the treatment of process of epoxy grease plasticizer production waste water
CN1225303C (en) Method for controlling flue gas contaiing SO2 with NaCl and producing high concentratino SO2
CN111690266B (en) Production method of dye disperse blue B56#
CN1673107A (en) Recovering process of polyester dyeing modified SIPM waste water
CN108751229B (en) Method for recovering dicyclohexyl disulfide mother liquor
CN111960456A (en) Recycling and treating process for calcium-containing waste acid after acid leaching of fluorite
CN112028020A (en) Process for recovering iodine from iodine bromide-containing medical organic waste liquid
CN112479423B (en) Wastewater treatment method for producing amino-containing phenolic compounds

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP02 Change in the address of a patent holder

Address after: 262725 200m north of the intersection of Xinhai road and Dajiu Road, marine chemical park, Hou Town, Shouguang City, Weifang City, Shandong Province

Patentee after: Shandong Boyuan Pharmaceutical Chemical Co.,Ltd.

Address before: 262725 Xinsha Road North, 500m west of Dajiu Road, Houzhen project area, Shouguang City, Weifang City, Shandong Province

Patentee before: Shandong Boyuan Pharmaceutical Chemical Co.,Ltd.

CP02 Change in the address of a patent holder