CN117623339A - Method for preparing chlor-alkali by treating wastewater with purified graphite tail gas - Google Patents

Method for preparing chlor-alkali by treating wastewater with purified graphite tail gas Download PDF

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Publication number
CN117623339A
CN117623339A CN202311592135.7A CN202311592135A CN117623339A CN 117623339 A CN117623339 A CN 117623339A CN 202311592135 A CN202311592135 A CN 202311592135A CN 117623339 A CN117623339 A CN 117623339A
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China
Prior art keywords
alkali
tail gas
chlor
wastewater
preparing
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CN202311592135.7A
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Chinese (zh)
Inventor
张芋
杨建明
尹文刚
邹国华
聂兵
吴昕忆
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Panzhihua Steel Enterprises Xinyu Chemical Co ltd
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Panzhihua Steel Enterprises Xinyu Chemical Co ltd
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Priority to CN202311592135.7A priority Critical patent/CN117623339A/en
Publication of CN117623339A publication Critical patent/CN117623339A/en
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    • 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
    • C01D3/04Chlorides
    • C01D3/06Preparation by working up brines; seawater or spent lyes
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D5/00Sulfates or sulfites of sodium, potassium or alkali metals in general
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/18Nature of the water, waste water, sewage or sludge to be treated from the purification of gaseous effluents

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention discloses a method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas, which comprises the following steps: adding acid into tail gas treatment wastewater of graphite purification by a chlorination method, adjusting the pH value to 3-6, adding soluble ferrous salt, adding alkali to adjust the pH value of the mixed solution to 7-9, performing ultrafiltration and/or multistage reverse osmosis treatment on the mixed solution, separating sodium chloride brine by nanofiltration, further separating, purifying and concentrating, and directly delivering chlor-alkali corporate salt as a raw material for use, recycling sodium chloride in the wastewater, simultaneously saving energy consumption of sodium chloride evaporation and wastewater treatment cost.

Description

Method for preparing chlor-alkali by treating wastewater with purified graphite tail gas
Technical Field
The invention belongs to the technical field of wastewater treatment, and particularly relates to a method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas.
Background
The waste gas from graphite purification mainly contains chlorine, sulfur dioxide, metal chloride and other pollutants, and waste water is produced by the waste gas treatment through the absorption of an alkaline washing tower. The waste brine produced by the process of chloridizing roasting and purifying graphite contains sodium chloride, sodium hypochlorite, sodium carbonate, sodium chlorate, vanadium, titanium, chromium and other impurities, and the waste water can produce environmental pollution if directly discharged. The main substances of the waste brine are sodium chloride and sodium carbonate, wherein the content of the sodium chloride is about 150g/L, and the waste brine can be recycled in a chlor-alkali plant after removing metal impurities such as vanadium, titanium, chromium and the like and sodium hypochlorite, so that the raw material cost of the chlor-alkali plant can be reduced, and the environmental pollution problem caused by wastewater discharge can be reduced.
At present, many domestic enterprises mainly adopt reclaimed water recycling or evaporation crystallization to obtain mixed salt, concentrate the waste water, recycle the water, discharge strong brine, or treat hazardous waste in the form of sludge, salt mud and mixed salt, and the solid waste causes secondary soil pollution or water body pollution at the same time of zero water discharge. Although there are methods related to recycling waste water in the prior art, it is generally aimed at treating a specific problem in waste water, and there is no method related to recycling all water and salts of different prices in waste water.
Disclosure of Invention
The invention aims to solve the technical problems that: the method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas is provided, so that the technical aim that water and salt in the wastewater can be fully recycled and the wastewater treatment cost is reduced is fulfilled.
In order to achieve the above purpose, the invention adopts the following technical scheme: the method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas comprises the following steps:
s1: adjusting the pH value of the purified graphite tail gas treatment wastewater to 3-6 by using acid, adding soluble ferrous salt, and then adding alkali to adjust the pH value of the mixed solution to 7-9;
s2: subjecting the mixed solution to ultrafiltration and/or multistage reverse osmosis treatment; then the monovalent salt and the high-valence salt are separated by nanofiltration;
s3: the monovalent salt separated by nanofiltration is further separated, converted and concentrated to prepare sodium chloride strong brine, and the brine can be used for chlor-alkali primary brine and is normally produced by a common chlor-alkali production process;
s4: adding potassium chloride into the mixed brine containing the high valence ions and the monovalent ions, which is separated by nanofiltration, and then obtaining potassium sulfate and sodium chloride respectively through freezing crystallization and high-temperature evaporation crystallization.
The beneficial effects of the technical scheme adopted by the invention are as follows: the sodium chloride brine separated by nanofiltration is further separated, purified and concentrated and then directly sent to chlor-alkali company salt to be used as a raw material, so that the energy consumption of sodium chloride evaporation is saved while the sodium chloride in the wastewater is recycled. The mixed brine containing high valence ions and monovalent ions, which is obtained by nanofiltration separation, is sent to a high valence salt conversion device, potassium chloride is added for double decomposition reaction to generate potassium sulfate and sodium chloride, and the potassium sulfate and the sodium chloride are separated by low-temperature evaporation crystallization and high-temperature evaporation crystallization. The produced potassium sulfate is used as a raw material for producing chemical fertilizers, and the separated sodium chloride is sent to chlor-alkali company to be used as a raw material.
Based on the technical scheme, the invention can also be improved as follows:
further, the acid is hydrochloric acid or sulfuric acid.
Further, the soluble ferrous salt is ferrous sulfate and/or ferrous chloride, and the proportioning relation between the soluble ferrous salt and the purified graphite tail gas treatment wastewater is 10kg:1m 3
Further, the base is sodium hydroxide.
Further, the concentration in step S3 is high pressure reverse osmosis concentration.
Further, the free chlorine content of the residual water after the treatment in steps S3 and S4 is less than 2ppb, and the contents of vanadium, titanium and chromium elements are all less than 15ppb.
The beneficial effects of the invention are as follows:
1. by adopting the method of adding soluble ferrous salt for reduction and flocculation, free chlorine and vanadium, titanium and chromium in the tail gas treatment wastewater of the chloridizing and purifying graphite can be treated in one step, and the treatment process is simplified.
2. The method can solve the problem of wastewater generated in the treatment of the tail gas of the purified graphite by the chlorination process, is applied to the production of chlor-alkali, and can effectively reduce the treatment cost of the wastewater generated in the treatment of the tail gas of the purified graphite by the chlorination process.
3. The invention can realize the recycling and zero discharge treatment of materials in the wastewater, the wastewater is treated by the method of the invention, the evaporation loss of the system and the water carried away by the materials are removed by about 2%, the residual water is completely recovered, the water recycling rate is more than 98%, the inorganic salt recycling rate is more than 80%, the environment is protected, and the wastewater treatment cost is saved.
Detailed Description
The following description of the specific embodiments of the present invention is provided to facilitate understanding of the present invention by those skilled in the art, and the examples are not intended to be limiting, and the reagents or apparatus used are not intended to be limiting, and are conventional products available for commercial purchase. It should be understood that the invention is not limited to the specific embodiments, but is capable of numerous modifications within the spirit and scope of the invention as hereinafter defined and defined by the appended claims as will be apparent to those skilled in the art all falling within the true spirit and scope of the invention as hereinafter claimed.
Example 1:
a method for preparing chlor-alkali by treating wastewater with purified graphite tail gas comprises the following steps:
s1: adjusting the pH value of the purified graphite tail gas treatment wastewater to 5.5 by using hydrochloric acid or sulfuric acid, adding 10kg of ferrous chloride into each cubic meter of wastewater, and then adding sodium hydroxide to adjust the pH value of the mixed solution to 7.3;
s2: subjecting the mixed solution to ultrafiltration treatment; then the monovalent salt and the high-valence salt are separated by nanofiltration;
s3: the monovalent salt separated by nanofiltration is further separated and converted, and then concentrated by high-pressure reverse osmosis to prepare sodium chloride strong brine, wherein the brine can be used as chlor-alkali primary brine and is normally produced by a common chlor-alkali production process;
s4: adding potassium chloride into the mixed brine containing high valence ions and monovalent ions, which is separated by nanofiltration, to perform double decomposition reaction to generate potassium sulfate and sodium chloride, and then respectively obtaining the potassium sulfate and the sodium chloride by freezing crystallization and high-temperature evaporation crystallization, wherein the produced potassium sulfate is used as a raw material for producing chemical fertilizers, and the separated sodium chloride is used as a chlor-alkali production raw material.
The free chlorine content of the residual water after the treatment in steps S3 and S4 was 1ppb, the vanadium content was 3ppb, the titanium content was 10ppb, and the chromium content was 1ppb.
Example 2:
a method for preparing chlor-alkali by treating wastewater with purified graphite tail gas comprises the following steps:
s1: adjusting the pH value of the purified graphite tail gas treatment wastewater to 3 by using hydrochloric acid or sulfuric acid, adding 10kg of ferrous sulfate into each cubic meter of wastewater, and then adding sodium hydroxide to adjust the pH value of the mixed solution to 9;
s2: subjecting the mixed solution to multistage reverse osmosis treatment; then the monovalent salt and the high-valence salt are separated by nanofiltration;
s3: the monovalent salt separated by nanofiltration is further separated and converted, and then concentrated by high-pressure reverse osmosis to prepare sodium chloride strong brine, wherein the brine can be used as chlor-alkali primary brine and is normally produced by a common chlor-alkali production process;
s4: adding potassium chloride into the mixed brine containing high valence ions and monovalent ions, which is separated by nanofiltration, to perform double decomposition reaction to generate potassium sulfate and sodium chloride, and then respectively obtaining the potassium sulfate and the sodium chloride by freezing crystallization and high-temperature evaporation crystallization, wherein the produced potassium sulfate is used as a raw material for producing chemical fertilizers, and the separated sodium chloride is used as a chlor-alkali production raw material.
The free chlorine content of the residual water after the treatment in steps S3 and S4 was 2ppb, the vanadium content was 1ppb, the titanium content was 15ppb, and chromium was not detected.
Example 3:
a method for preparing chlor-alkali by treating wastewater with purified graphite tail gas comprises the following steps:
s1: adjusting the pH value of the purified graphite tail gas treatment wastewater to 6 by using hydrochloric acid or sulfuric acid, and adding 10kg of ferrous sulfate and ferrous chloride into each cubic meter of wastewater to 1:1, then adding sodium hydroxide to adjust the pH value of the mixed solution to 7;
s2: subjecting the mixed solution to ultrafiltration and multistage reverse osmosis treatment; then the monovalent salt and the high-valence salt are separated by nanofiltration;
s3: the monovalent salt separated by nanofiltration is further separated and converted, and then concentrated by high-pressure reverse osmosis to prepare sodium chloride strong brine, wherein the brine can be used as chlor-alkali primary brine and is normally produced by a common chlor-alkali production process;
s4: adding potassium chloride into the mixed brine containing high valence ions and monovalent ions, which is separated by nanofiltration, to perform double decomposition reaction to generate potassium sulfate and sodium chloride, and then respectively obtaining the potassium sulfate and the sodium chloride by freezing crystallization and high-temperature evaporation crystallization, wherein the produced potassium sulfate is used as a raw material for producing chemical fertilizers, and the separated sodium chloride is used as a chlor-alkali production raw material.
The free chlorine, vanadium and chromium elements of the residual water after the treatment in steps S3 and S4 were not detected, and the titanium content was 2ppb.

Claims (6)

1. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas is characterized by comprising the following steps of:
s1: adjusting the pH value of the purified graphite tail gas treatment wastewater to 3-6 by using acid, adding soluble ferrous salt, and then adding alkali to adjust the pH value of the mixed solution to 7-9;
s2: subjecting the mixed solution to ultrafiltration and/or multistage reverse osmosis treatment; then the monovalent salt and the high-valence salt are separated by nanofiltration;
s3: the monovalent salt separated by nanofiltration is further separated and converted, and concentrated to prepare sodium chloride concentrated brine;
s4: adding potassium chloride into the mixed brine containing the high valence ions and the monovalent ions, which is separated by nanofiltration, and then obtaining potassium sulfate and sodium chloride respectively through freezing crystallization and high-temperature evaporation crystallization.
2. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas according to claim 1, wherein the method comprises the following steps: the acid is hydrochloric acid or sulfuric acid.
3. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas according to claim 1, wherein the method comprises the following steps: the soluble ferrous salt is ferrous sulfate and/or ferrous chloride, and the proportioning relation between the soluble ferrous salt and the purified graphite tail gas treatment wastewater is 10kg:1m 3
4. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas according to claim 1, wherein the method comprises the following steps: the alkali is sodium hydroxide.
5. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas according to claim 1, wherein the method comprises the following steps: the concentration in the step S3 is high-pressure reverse osmosis concentration.
6. The method for preparing chlor-alkali by treating wastewater by utilizing purified graphite tail gas according to claim 1, wherein the method comprises the following steps: the free chlorine content of the residual water after the treatment in the steps S3 and S4 is lower than 2ppb, and the contents of vanadium, titanium and chromium elements are all lower than 15ppb.
CN202311592135.7A 2023-11-27 2023-11-27 Method for preparing chlor-alkali by treating wastewater with purified graphite tail gas Pending CN117623339A (en)

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