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CN110451679B - Method for recovering sodium sulfate and removing potassium chloride ions from alkali ash separation filtrate - Google Patents

Method for recovering sodium sulfate and removing potassium chloride ions from alkali ash separation filtrate Download PDF

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CN110451679B
CN110451679B CN201910645242.9A CN201910645242A CN110451679B CN 110451679 B CN110451679 B CN 110451679B CN 201910645242 A CN201910645242 A CN 201910645242A CN 110451679 B CN110451679 B CN 110451679B
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sodium sulfate
alkali ash
mother liquor
filtrate
alkali
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杨刚
秦冬玲
孙朋飞
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Jiangsu Liboxing Water Technology Co ltd
Nanjing Tech University
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Nanjing Tech University
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    • 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
    • C01D5/16Purification
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F2001/5218Crystallization
    • 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
    • C02F2103/26Nature of the water, waste water, sewage or sludge to be treated from the processing of plants or parts thereof
    • C02F2103/28Nature of the water, waste water, sewage or sludge to be treated from the processing of plants or parts thereof from the paper or cellulose industry

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  • Inorganic Chemistry (AREA)
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  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

本发明提供了一种碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,包括以下步骤:a.恒温结晶:将碱灰析滤滤液在‑10‑15℃下进行恒温结晶,然后在此温度下进行固液分离,得到十水硫酸钠晶体及结晶母液;b.对步骤a获得的结晶母液进行pH值调节,将pH值调到3‑8;c.活性炭吸附,将调节完pH值的结晶母液用活性炭吸附其中的COD;d.将步骤c处理后的结晶母液送入纳滤膜系统,进行纳滤浓缩,纳滤浓缩液进入碱灰析滤液进行循环回收。本发明提供的碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,硫酸根离子的回收率达90%以上,而且工艺条件简单稳定,能够回收得到的高纯度的硫酸钠,实现了废水的资源化利用,去除了废水中可能富集的有机物,使废水处理可持续进行。

Figure 201910645242

The invention provides a method for recovering sodium sulfate and removing potassium chloride ions from alkali ash analysis filtrate, comprising the following steps: a. constant temperature crystallization: carrying out constant temperature crystallization of alkali ash analysis filtrate at -10-15°C, and then Carry out solid-liquid separation at this temperature to obtain sodium sulfate decahydrate crystals and crystallization mother liquor; b. adjust the pH value of the crystallization mother liquor obtained in step a, and adjust the pH value to 3‑8; Use activated carbon to absorb the COD in the crystalline mother liquor; d. Send the crystalline mother liquor treated in step c to the nanofiltration membrane system for nanofiltration and concentration, and the nanofiltration concentrated solution enters the alkali ash analysis filtrate for recycling. In the method for recovering sodium sulfate and removing potassium chloride ions from alkali ash analysis filtrate provided by the present invention, the recovery rate of sulfate ions is more than 90%, and the process conditions are simple and stable, and the obtained high-purity sodium sulfate can be recovered, realizing waste water The utilization of resources removes the organic matter that may be enriched in the wastewater, making wastewater treatment sustainable.

Figure 201910645242

Description

一种碱灰析滤液回收硫酸钠并脱除氯钾离子的方法A kind of alkali ash analysis filtrate reclaims the method for sodium sulfate and removes potassium chloride ion

技术领域technical field

本发明属于一种水处理领域,涉及一种碱灰析滤液回收硫酸钠并脱除氯钾离子的方法。The invention belongs to the field of water treatment, and relates to a method for recovering sodium sulfate and removing potassium chloride ions from alkali ash analysis filtrate.

背景技术Background technique

造纸工业作为我国国民经济发展的重要产业之一,近年来发展迅速。碱回收作为造纸废液处理及能量回收的主要方式被广泛采用。作为碱回收炉中黑液的燃烧产物之一的碱灰,其主要成分为钠,钾,硫酸根,氯离子,碳酸根等离子组成的无机盐。其中氯离子和钾离子会降低积灰的融化温度,造成管路堵塞,缩短碱炉的运行周期,并且对碱炉金属材料有腐蚀作用。一般采用析滤法对碱灰进行处理,即把碱灰溶解于热水中,使溶液达到饱和,利用硫酸钠的溶解性低的原理回收碱灰中的硫酸钠,并去除氯钾离子,此溶液即为碱灰析滤液。但碱灰析滤液中仍含有部分硫酸钠,导致析滤过程中硫酸钠回收效率低,大量硫酸钠都被丢弃。As one of the important industries of my country's national economic development, the paper industry has developed rapidly in recent years. Alkali recovery is widely used as the main way of papermaking waste liquid treatment and energy recovery. Soda ash, one of the combustion products of black liquor in the alkali recovery furnace, is mainly composed of inorganic salts such as sodium, potassium, sulfate, chloride, and carbonate. Among them, chloride ions and potassium ions will reduce the melting temperature of accumulated ash, cause pipeline blockage, shorten the operating cycle of the alkali furnace, and have a corrosive effect on the metal materials of the alkali furnace. The soda ash is generally treated by the analysis and filtration method, that is, the soda ash is dissolved in hot water to make the solution saturated, and the sodium sulfate in the soda ash is recovered by using the principle of low solubility of sodium sulfate, and potassium chloride ions are removed. The solution is the alkali ash analysis filtrate. However, some sodium sulfate is still contained in the soda ash analysis filtrate, which leads to low recovery efficiency of sodium sulfate in the analysis and filtration process, and a large amount of sodium sulfate is discarded.

发明内容Contents of the invention

1、所要解决的技术问题:1. Technical problems to be solved:

现有的析滤法对碱灰进行处理,最终得到的碱灰析滤液仍含有部分硫酸钠,导致析滤过程中硫酸钠回收效率低,大量硫酸钠都被丢弃。The existing analysis and filtration method processes soda ash, and the finally obtained soda ash analysis filtrate still contains part of sodium sulfate, which leads to low recovery efficiency of sodium sulfate in the analysis and filtration process, and a large amount of sodium sulfate is discarded.

2、技术方案:2. Technical solution:

为了解决以上问题,本发明提供了一种碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,包括以下步骤:a.恒温结晶:将碱灰析滤滤液在-10-15℃下进行恒温结晶,然后在此温度下进行固液分离,得到十水硫酸钠晶体及结晶母液,所述十水硫酸钠晶体干燥所得无水硫酸钠进行回收;b.对步骤a获得的结晶母液进行pH值调节,将pH值调到3-8;c.活性炭吸附,将调节完pH值的结晶母液用活性炭吸附其中的COD;d.将步骤c处理后的结晶母液送入纳滤膜系统,进行纳滤浓缩,浓缩侧浓缩液进入碱灰析滤液进行循环回收,回到步骤a继续参与恒温结晶,渗透液作为电解行业电解液回收。In order to solve the above problems, the present invention provides a method for recovering sodium sulfate and removing potassium chloride ions from alkali ash analysis filtrate, comprising the following steps: a. constant temperature crystallization: carrying out alkali ash analysis filtrate at -10-15°C constant temperature crystallization, and then carry out solid-liquid separation at this temperature to obtain sodium sulfate decahydrate crystals and crystallization mother liquor, and the sodium sulfate decahydrate obtained by drying the sodium sulfate decahydrate crystals is recovered; b. the pH of the crystallization mother liquor obtained in step a Adjust the pH value to 3-8; c. Activated carbon adsorption, use activated carbon to adsorb the COD in the crystallization mother liquor after adjusting the pH value; d. Send the crystallization mother liquor treated in step c into the nanofiltration membrane system for Concentrated by nanofiltration, the concentrated liquid on the concentrated side enters the alkali ash analysis filtrate for recycling, returns to step a to continue to participate in constant temperature crystallization, and the permeate is recovered as the electrolyte in the electrolysis industry.

在步骤b中对结晶母液PH值是通过盐酸或硫酸来进行调节pH值。In step b, the pH value of the crystallization mother liquor is adjusted by hydrochloric acid or sulfuric acid.

在步骤c中 所使用的活性炭为木质活性炭获果壳活性炭或煤质活性炭。The activated carbon used in step c is wood activated carbon, fruit shell activated carbon or coal-based activated carbon.

在步骤d中所述纳滤膜为有机膜,平均孔径为0.5-5nm,膜元件为卷式膜或者平板膜。In step d, the nanofiltration membrane is an organic membrane with an average pore size of 0.5-5 nm, and the membrane element is a roll membrane or a flat membrane.

在步骤d中,所述渗透液为氯化钠、氯化钾混合溶液。In step d, the permeate is a mixed solution of sodium chloride and potassium chloride.

3、有益效果:3. Beneficial effects:

本发明提供的碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,硫酸根离子的回收率达90%以上,而且工艺条件简单稳定,便于工业化推广,能够回收得到的高纯度的硫酸钠,实现了废水的资源化利用,去除了废水中可能富集的有机物,使废水处理可持续进行。In the method for recovering sodium sulfate and removing potassium chloride ions from the alkali ash analysis filtrate provided by the present invention, the recovery rate of sulfate ions is more than 90%, and the process conditions are simple and stable, which is convenient for industrialization and can recycle the obtained high-purity sodium sulfate , Realize the resource utilization of wastewater, remove the organic matter that may be enriched in the wastewater, and make the wastewater treatment sustainable.

附图说明Description of drawings

图1为发明的工艺流程图。Fig. 1 is the process flow chart of invention.

具体实施方式Detailed ways

下面通过实施例来对本发明进行详细说明。The present invention will be described in detail below by way of examples.

实施例1Example 1

所用碱灰析滤液成分如下所示:The used alkali ash analysis filtrate composition is as follows:

成分Element Na<sup>+</sup>Na<sup>+</sup> K<sup>+</sup>K<sup>+</sup> CO<sub>3</sub><sup>2-</sup>CO<sub>3</sub><sup>2-</sup> SO<sub>4</sub><sup>2-</sup>SO<sub>4</sub><sup>2-</sup> Cl<sup>-</sup>Cl<sup>-</sup> CODCOD 浓度 g/LConcentration g/L 100-130100-130 30-6030-60 15-3015-30 150-250150-250 20-5020-50 0.3-0.60.3-0.6

碱灰析滤液经过-10 ℃结晶后,结晶母液中Na+为32.1 g/L, SO4 2-为35.9 g/L,CO3 2-为44.1 g/L, Cl-为67.3 g/L, K+为61.6 g/L,体积分数降为34 %。用浓盐酸调节结晶母液的pH值为3。调节完pH的溶液用活性炭吸附COD,COD降为54mg/L。活性炭吸附后液体进入纳滤浓缩系统处理,纳滤系统采用平均孔径为1-5nm的平板有机膜,渗透液体积分数为44%,其中SO4 2-为0.2 g/L, Cl-为66.4 g/L ,Na+为31.5 g/L,K+为62.1 g/L,COD为20mg/L,可作为电解工业原材料使用。浓缩侧体积分数为22 %,其中SO4 2-为37.5 g/L, Cl-为59.1 g/L,Na+为33.7 g/L,K+为62.8 g/L。将浓缩侧浓缩液直接返回碱灰析滤液中,继续参与恒温结晶过程。经过上述步骤处理后,碱灰析滤液中SO4 2-的回收率为93%,所得无水Na2SO4符合GB/T6009-2014工业无水硫酸钠Ⅰ类一等品标准。After the soda ash analysis filtrate was crystallized at -10 ℃, Na + in the crystallization mother liquor was 32.1 g/L, SO 4 2- was 35.9 g/L, CO 3 2- was 44.1 g/L, Cl - was 67.3 g/L, K + is 61.6 g/L, and the volume fraction is reduced to 34%. Adjust the pH value of the crystallization mother liquor to 3 with concentrated hydrochloric acid. After adjusting the pH of the solution, activated carbon was used to absorb COD, and the COD was reduced to 54mg/L. After activated carbon adsorption, the liquid enters the nanofiltration concentration system for treatment. The nanofiltration system adopts a flat organic membrane with an average pore size of 1-5nm, and the permeation liquid fraction is 44%, of which SO 4 2- is 0.2 g/L, and Cl - is 66.4 g /L, Na + is 31.5 g/L, K + is 62.1 g/L, COD is 20mg/L, it can be used as raw material for electrolysis industry. The concentrated side volume fraction is 22%, among which SO 4 2- is 37.5 g/L, Cl - is 59.1 g/L, Na + is 33.7 g/L, and K + is 62.8 g/L. The concentrated liquid on the concentrated side is directly returned to the soda ash analysis filtrate, and continues to participate in the constant temperature crystallization process. After the above steps, the recovery rate of SO 4 2- in the soda ash analysis filtrate was 93%, and the obtained anhydrous Na 2 SO 4 met the standard of GB/T6009-2014 Industrial Anhydrous Sodium Sulfate Class I First-Class Product.

实施例2Example 2

所用碱灰析滤液成分同实施例1。The used alkali ash analysis filtrate composition is the same as embodiment 1.

碱灰析滤液经过-5 ℃结晶后,结晶母液中Na+为46.3 g/L, SO4 2-为44.1 g/L,CO3 2-为42.3 g/L, Cl-为63.7 g/L, K+为57.2 g/L,体积分数降为41 %。用浓硫酸调节结晶母液的pH值为5。调节完pH的溶液用活性炭吸附COD,COD降为83 mg/L。活性炭吸附后液体进入纳滤浓缩系统处理,纳滤系统采用平均孔径为1-5nm的卷式有机膜,渗透液体积分数为47%,其中SO4 2-为0.5 g/L, Cl-为62.1 g/L ,Na+为46.1 g/L,K+为58.6 g/L,COD为17 mg/L,可作为电解工业原材料使用。浓缩侧体积分数为12%,其中SO4 2-为57.6g/L, Cl-为54.8 g/L,Na+为47.5 g/L,K+为57.0g/L。将浓缩侧浓缩液直接返回碱灰析滤液中,继续参与恒温结晶过程。经过上述步骤处理后,碱灰析滤液中SO4 2-的回收率为92%,所得无水Na2SO4符合GB/T6009-2014工业无水硫酸钠Ⅰ类一等品标准。After the alkali ash analysis filtrate was crystallized at -5 °C, the Na + in the crystallization mother liquor was 46.3 g/L, the SO 4 2- was 44.1 g/L, the CO 3 2- was 42.3 g/L, and the Cl - was 63.7 g/L. K + is 57.2 g/L, and the volume fraction is reduced to 41%. Adjust the pH value of the crystallization mother liquor to 5 with concentrated sulfuric acid. Activated carbon was used to absorb COD in the pH-adjusted solution, and the COD was reduced to 83 mg/L. After activated carbon adsorption, the liquid enters the nanofiltration concentration system for treatment. The nanofiltration system adopts a roll-type organic membrane with an average pore size of 1-5nm, and the permeation liquid fraction is 47%, of which SO 4 2- is 0.5 g/L, Cl - is 62.1 g/L, Na + is 46.1 g/L, K + is 58.6 g/L, COD is 17 mg/L, it can be used as raw material for electrolysis industry. The volume fraction of the concentrated side is 12%, of which SO 4 2- is 57.6g/L, Cl - is 54.8 g/L, Na + is 47.5 g/L, and K + is 57.0g/L. The concentrated liquid on the concentrated side is directly returned to the soda ash analysis filtrate, and continues to participate in the constant temperature crystallization process. After the above steps, the recovery rate of SO 4 2- in the soda ash analysis filtrate was 92%, and the obtained anhydrous Na 2 SO 4 complied with the standard of GB/T6009-2014 Industrial Anhydrous Sodium Sulfate Class I First Class.

实施例3Example 3

所用碱灰析滤液成分同实施例1。The used alkali ash analysis filtrate composition is the same as embodiment 1.

碱灰析滤液经过10℃结晶后,结晶母液中Na+为58.2 g/L, SO4 2-为50.8 g/L,CO3 2-为38.2 g/L, Cl-为56.3 g/L, K+为50.6 g/L,体积分数降为50 %。用浓盐酸调节结晶母液的pH值为7。调节完pH的溶液用活性炭吸附COD,COD降为47 mg/L。活性炭吸附后液体进入纳滤浓缩系统处理,纳滤系统采用平均孔径为1-5nm的卷式有机膜,渗透液体积分数为40%,其中SO4 2-为0.6 g/L, Cl-为53.4 g/L ,Na+为57.1 g/L,K+为47.3 g/L,COD为24 mg/L,可作为电解工业原材料使用。浓缩侧体积分数为10%,其中SO4 2-为58.6 g/L, Cl-为58.1 g/L,Na+为56.1 g/L,K+为54.2 g/L。将浓缩侧浓缩液直接返回碱灰析滤液中,继续参与恒温结晶过程。经过上述步骤处理后,碱灰析滤液中SO4 2-的回收率为90%,所得无水Na2SO4符合GB/T6009-2014工业无水硫酸钠Ⅰ类一等品标准。After the alkali ash analysis filtrate was crystallized at 10°C, Na + in the crystallization mother liquor was 58.2 g/L, SO 4 2- was 50.8 g/L, CO 3 2- was 38.2 g/L, Cl - was 56.3 g/L, K + is 50.6 g/L, and the volume fraction is reduced to 50%. The pH value of the crystallization mother liquor was adjusted to 7 with concentrated hydrochloric acid. After adjusting the pH of the solution, activated carbon was used to absorb COD, and the COD was reduced to 47 mg/L. After activated carbon adsorption, the liquid enters the nanofiltration concentration system for treatment. The nanofiltration system adopts a roll-type organic membrane with an average pore size of 1-5nm, and the permeation liquid fraction is 40%, of which SO 4 2- is 0.6 g/L, Cl - is 53.4 g/L, Na + is 57.1 g/L, K + is 47.3 g/L, and COD is 24 mg/L, which can be used as raw materials for electrolysis industry. The volume fraction of the concentrated side is 10%, of which SO 4 2- is 58.6 g/L, Cl - is 58.1 g/L, Na + is 56.1 g/L, and K + is 54.2 g/L. The concentrated liquid on the concentrated side is directly returned to the soda ash analysis filtrate, and continues to participate in the constant temperature crystallization process. After the above steps, the recovery rate of SO 4 2- in the soda ash analysis filtrate is 90%, and the obtained anhydrous Na 2 SO 4 meets the standard of GB/T6009-2014 Industrial Anhydrous Sodium Sulfate Class I First-Class.

虽然本发明已以较佳实施例公开如上,但它们并不是用来限定本发明的,任何熟习此技艺者,在不脱离本发明之精神和范围内,自当可作各种变化或润饰,因此本发明的保护范围应当以本申请的权利要求保护范围所界定的为准。Although the present invention has been disclosed as above with preferred embodiments, they are not intended to limit the present invention. Any skilled person can make various changes or modifications without departing from the spirit and scope of the present invention. Therefore, the protection scope of the present invention should be defined by the protection scope of the claims of the present application.

Claims (3)

1.一种碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,所述碱灰析滤液是造纸工业中,黑液经碱回收炉燃烧后所产生的碱灰经溶解和析滤法回收硫酸钠后的溶液,碱灰析滤液中的Na+浓度为100-130 g/L,K+浓度为30-60 g/L,CO3 2-浓度为15-30 g/L,SO4 2-浓度为150-250 g/L,Cl-浓度为20-50 g/L,COD浓度为0.3-0.6 g/L;1. a kind of method that alkali ash analyzes filtrate and reclaims sodium sulfate and removes potassium chloride ion, and described alkali ash analyzes filtrate is in the papermaking industry, and the alkali ash that black liquor produces after alkali recovery furnace burns is through dissolving and analysis filtration method The solution after recovering sodium sulfate, the Na + concentration in the alkali ash analysis filtrate is 100-130 g/L, the K + concentration is 30-60 g/L, the CO 3 2- concentration is 15-30 g/L, SO 4 2- The concentration is 150-250 g/L, the Cl - concentration is 20-50 g/L, and the COD concentration is 0.3-0.6 g/L; 所述方法包括以下步骤:The method comprises the steps of: a.恒温结晶:将碱灰析滤滤液在-10-15℃下进行恒温结晶,然后在此温度下进行固液分离,得到十水硫酸钠晶体及结晶母液,所述十水硫酸钠晶体干燥所得无水硫酸钠进行回收;a. Constant temperature crystallization: carry out constant temperature crystallization at -10-15°C for the alkali ash analysis filtrate, and then carry out solid-liquid separation at this temperature to obtain sodium sulfate decahydrate crystals and crystallization mother liquor, and the sodium sulfate decahydrate crystals are dried Gained anhydrous sodium sulfate reclaims; b. 通过盐酸或硫酸对步骤a获得的结晶母液进行pH值调节,将pH值调到3-8;b. adjust the pH value of the crystallization mother liquor obtained in step a by hydrochloric acid or sulfuric acid, and adjust the pH value to 3-8; c.活性炭吸附,将调节完pH值的结晶母液用活性炭吸附其中的COD;c. Activated carbon adsorption, use activated carbon to adsorb the COD in the crystallization mother liquor after adjusting the pH value; d.将步骤c处理后的结晶母液送入纳滤膜系统,进行纳滤浓缩,浓缩侧浓缩液进入碱灰析滤液进行循环回收,回到步骤a继续参与恒温结晶,渗透液作为电解行业电解液回收,所述渗透液为氯化钠、氯化钾混合溶液。d. Send the crystallization mother liquor treated in step c into the nanofiltration membrane system for nanofiltration concentration, the concentrated liquid on the concentrated side enters the alkali ash analysis filtrate for recycling, returns to step a to continue to participate in constant temperature crystallization, and the permeate is used as electrolysis in the electrolysis industry Liquid recovery, the permeate is sodium chloride, potassium chloride mixed solution. 2.如权利要求1所述的碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,其特征在于:在步骤c中所使用的活性炭为木质活性炭,或果壳活性炭,或煤质活性炭。2. the method that alkali ash analyzes filtrate as claimed in claim 1 reclaims sodium sulfate and removes potassium chloride ion, it is characterized in that: the activated carbon used in step c is woody activated carbon, or fruit shell activated carbon, or coal-based activated carbon . 3.如权利要求1所述的碱灰析滤液回收硫酸钠并脱除氯钾离子的方法,其特征在于:在步骤d中所述纳滤膜为有机膜,平均孔径为0.5-5nm,膜元件为卷式膜或者平板膜。3. the method that alkali ash analyzes filtrate as claimed in claim 1 reclaims sodium sulfate and removes potassium chloride ion, it is characterized in that: the nanofiltration membrane described in step d is an organic membrane, and average aperture is 0.5-5nm, membrane The element is a roll film or a flat film.
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CN109851124A (en) * 2018-12-13 2019-06-07 新疆环境工程技术有限责任公司 For the coupling method for crystallising of weaving Thermal Power Generation Industry high concentration salt water

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