[go: up one dir, main page]

CN115710031A - Method for treating photoresist developer wastewater containing 1,4-dioxane - Google Patents

Method for treating photoresist developer wastewater containing 1,4-dioxane Download PDF

Info

Publication number
CN115710031A
CN115710031A CN202211205996.0A CN202211205996A CN115710031A CN 115710031 A CN115710031 A CN 115710031A CN 202211205996 A CN202211205996 A CN 202211205996A CN 115710031 A CN115710031 A CN 115710031A
Authority
CN
China
Prior art keywords
dioxane
tower
pressure
water
photoresist developer
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.)
Pending
Application number
CN202211205996.0A
Other languages
Chinese (zh)
Inventor
汪元博
杨倪
王爱军
朱相红
刘学东
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.)
Jiangsu Haichuan Petrochemical Engineering Technology Co ltd
Original Assignee
Jiangsu Haichuan Petrochemical Engineering Technology 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 Jiangsu Haichuan Petrochemical Engineering Technology Co ltd filed Critical Jiangsu Haichuan Petrochemical Engineering Technology Co ltd
Priority to CN202211205996.0A priority Critical patent/CN115710031A/en
Publication of CN115710031A publication Critical patent/CN115710031A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)

Abstract

The invention discloses a method for treating photoresist developer wastewater containing 1,4-dioxane, wherein the wastewater is distilled from a rectifying tower under normal pressure, the distillate at the top of the tower is high-concentration 1,4-dioxane-containing aqueous solution, part of the aqueous solution is fed into a high-pressure rectifying tower, the liquid discharged from the bottom of the tower is high-purity water, part of the distillate at the top of the high-pressure rectifying tower is circularly returned to the normal-pressure rectifying tower, and the liquid discharged from the bottom of the tower is high-concentration 1,4-dioxane. The invention has the advantages that: after the photoresist developer wastewater containing 1,4-dioxane is treated, the high-purity 1,4-dioxane can be obtained, can be directly recycled after subsequent resin adsorption, can discharge high-purity water, and the purified wastewater meets the industrial environment-friendly requirement, can be directly discharged, and realizes win-win of economic benefit and environmental-friendly benefit; the wastewater treatment has the characteristics of large scale and continuity, the wastewater treatment capacity is large, a third component is not required to be introduced, secondary pollutants are not generated, and a large amount of energy can be saved.

Description

含1,4-二氧六环的光刻胶显影剂废水处理方法Method for treating photoresist developer wastewater containing 1,4-dioxane

技术领域technical field

本发明涉及一种废水处理方法,特别是涉及一种含1,4-二氧六环的光刻胶显影剂废水处理方法。The invention relates to a wastewater treatment method, in particular to a photoresist developer wastewater treatment method containing 1,4-dioxane.

背景技术Background technique

电子级1,4-二氧六环(1,4-Dioxane)是生产光刻胶显影剂的重要原料。目前国内尚无批量生产该原料的厂商,相关的生产工艺也为日韩等跨国公司所垄断,国内芯片行业只能以高价向国外求购。另一方面,1,4-二氧六环具有致癌性,不能直接排放。因此,从原料利用和环保方面讲,从含1,4-二氧六环的光刻胶显影剂废水中回收1,4-二氧六环具有极大的经济意义和环保意义。Electronic grade 1,4-Dioxane (1,4-Dioxane) is an important raw material for producing photoresist developer. At present, there is no domestic manufacturer that mass-produces this raw material, and the related production technology is monopolized by multinational companies such as Japan and South Korea. The domestic chip industry can only buy from foreign countries at high prices. On the other hand, 1,4-dioxane is carcinogenic and cannot be emitted directly. Therefore, in terms of raw material utilization and environmental protection, the recovery of 1,4-dioxane from photoresist developer wastewater containing 1,4-dioxane has great economic and environmental significance.

对含1,4-二氧六环的光刻胶显影剂废水处理需要综合考虑1,4-二氧六环回收和水净化两个方面。目前,传统的含1,4-二氧六环废水的处理方法是以环己烷为夹带剂,采用共沸精馏法经过预浓缩、加入夹带剂、再生夹带剂、提纯精制等5个塔的精馏流程回收得到高纯1,4-二氧六环。该工艺流程长,导致能耗较大;采用夹带剂,系统引入额外化学物质,既增加处理成本又增加处理过程的复杂性,导致环保方面的二次污染。The treatment of photoresist developer wastewater containing 1,4-dioxane requires comprehensive consideration of 1,4-dioxane recovery and water purification. At present, the traditional treatment method of wastewater containing 1,4-dioxane uses cyclohexane as the entrainer, and adopts the azeotropic distillation method to pre-concentrate, add entrainer, regenerate the entrainer, and purify five towers. High-purity 1,4-dioxane is recovered through the rectification process. The process is long, resulting in high energy consumption; the use of entrainer, the system introduces additional chemical substances, which not only increases the treatment cost but also increases the complexity of the treatment process, resulting in secondary pollution in terms of environmental protection.

发明内容Contents of the invention

发明目的:本发明的目的是提供一种含1,4-二氧六环的光刻胶显影剂废水处理方法,既可得到高纯度1,4-二氧六环,又可排出高纯度水。Purpose of the invention: The purpose of the invention is to provide a treatment method for photoresist developer wastewater containing 1,4-dioxane, which can not only obtain high-purity 1,4-dioxane, but also discharge high-purity water .

技术方案:一种含1,4-二氧六环的光刻胶显影剂废水处理方法,包括以下步骤:Technical solution: a method for treating photoresist developer wastewater containing 1,4-dioxane, comprising the following steps:

步骤100,废水送入常压精馏塔,常压精馏塔的塔顶馏出液为高浓度含1,4-二氧六环水溶液,塔釜排出液为高纯度水;高浓度含1,4-二氧六环水溶液部分回流送入常压精馏塔,其余送入高压精馏塔;Step 100, the waste water is sent to the atmospheric rectification tower, the overhead distillate of the atmospheric rectification tower is a high-concentration aqueous solution containing 1,4-dioxane, and the discharge liquid from the tower kettle is high-purity water; the high-concentration 1,4-dioxane , Part of the 4-dioxane aqueous solution is refluxed into the atmospheric rectification tower, and the rest is sent into the high-pressure rectification tower;

步骤200,高压精馏塔的塔顶馏出液部分回流送入高压精馏塔,其余循环返回至常压精馏塔,塔釜排出液为高浓度1,4-二氧六环。In step 200, part of the overhead distillate of the high-pressure rectification tower is refluxed into the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower, and the liquid discharged from the bottom of the tower is high-concentration 1,4-dioxane.

具体的,废水的组成为2~5%的1,4-二氧六环和95~98%的水,质量百分含量。Specifically, the composition of the waste water is 2-5% of 1,4-dioxane and 95-98% of water, in mass percent.

进一步的,常压精馏塔的操作条件:常压,塔釜温度100~105℃,理论板数20~50块,回流比0.5~5。Furthermore, the operating conditions of the atmospheric distillation tower are: normal pressure, the temperature of the bottom of the tower is 100-105°C, the number of theoretical plates is 20-50, and the reflux ratio is 0.5-5.

进一步的,高压精馏塔的操作条件:800~1000kpa,塔釜温度165~205℃,理论板数16~30块,回流比1~3。Furthermore, the operating conditions of the high-pressure rectification tower are: 800-1000kpa, the temperature of the tower bottom is 165-205°C, the number of theoretical plates is 16-30, and the reflux ratio is 1-3.

具体的,步骤100中,高浓度含1,4-二氧六环水溶液的组成为75~81%的1,4-二氧六环和19~25%的水,质量百分含量;高纯度水的质量纯度高于99.99%。Specifically, in step 100, the composition of the high-concentration 1,4-dioxane-containing aqueous solution is 75-81% of 1,4-dioxane and 19-25% of water, in mass percent; high-purity The mass purity of water is higher than 99.99%.

具体的,步骤200中,塔顶馏出液的组成为65~74%的1,4-二氧六环和26~30%的水,质量百分含量;高浓度1,4-二氧六环的质量纯度为99.99~99.998%。Specifically, in step 200, the composition of the overhead distillate is 65-74% of 1,4-dioxane and 26-30% of water, in mass percentage; high concentration 1,4-dioxane The mass purity of the ring is 99.99-99.998%.

本发明的原理是:根据1,4-二氧六环、水二元物系对压力的敏感性,采用变压精馏,利用共沸物组成比例随压力变化而显著变化的特性,对低浓度的含1,4-二氧六环的光刻胶显影剂废水经变压精馏分离,实现从中回收提取电子级1,4-二氧六环。The principle of the present invention is: according to the sensitivity of 1,4-dioxane and water binary systems to pressure, pressure swing rectification is adopted, and the characteristic that the composition ratio of azeotrope changes significantly with pressure changes is used, and the low The photoresist developer wastewater containing 1,4-dioxane in high concentration is separated by pressure swing rectification, so as to realize recovery and extraction of electronic grade 1,4-dioxane therefrom.

有益效果:本发明的优点是:含1,4-二氧六环的光刻胶显影剂废水经处理后,既可得到高纯度1,4-二氧六环,其经后续的树脂吸附后可直接循环利用,又可排出高纯度水,提纯后的废水满足行业环保要求,可直接排放,实现经济效益和环保效益双赢;废水处理具有大规模、连续化的特点,废水处理量大,不需要引入第三组分,不产生二次污染物,同时可节约大量能量。Beneficial effect: the advantage of the present invention is that after the photoresist developer wastewater containing 1,4-dioxane is treated, high-purity 1,4-dioxane can be obtained, which is absorbed by the subsequent resin It can be directly recycled, and can also discharge high-purity water. The purified wastewater meets the environmental protection requirements of the industry and can be discharged directly to achieve a win-win situation of economic and environmental benefits. The third component needs to be introduced, no secondary pollutants will be generated, and a large amount of energy can be saved at the same time.

附图说明Description of drawings

图1为本发明方法流程图。Fig. 1 is a flow chart of the method of the present invention.

具体实施方式Detailed ways

下面结合附图和具体实施例,进一步阐明本发明。The present invention will be further explained below in conjunction with the accompanying drawings and specific embodiments.

实施例1Example 1

一种含1,4-二氧六环的光刻胶显影剂废水处理方法,具体包括以下步骤:A method for treating photoresist developer wastewater containing 1,4-dioxane, specifically comprising the following steps:

步骤100:将废水以1000kg/h的流速送入常压精馏塔,废水中1,4-二氧六环的质量百分含量为2%,其余为水。Step 100: Send the waste water into the atmospheric rectification tower at a flow rate of 1000 kg/h. The mass percentage of 1,4-dioxane in the waste water is 2%, and the rest is water.

常压精馏塔中进行常压精馏,常压精馏塔的操作条件为常压、塔釜温度102℃、理论板数20块、回流比3。Atmospheric rectification is carried out in the atmospheric rectification tower, and the operating conditions of the atmospheric rectification tower are normal pressure, 102° C. in the bottom of the tower, 20 theoretical plates, and 3 reflux ratios.

塔顶馏出液为高浓度含1,4-二氧六环水溶液,经冷凝器冷凝后,部分回流送入常压精馏塔,其余以113kg/h的流速送入高压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为76%,其余为水。塔釜排出液为高纯度水,以980kg/h的流速流出常压精馏塔,高纯度水中的1,4-二氧六环的质量百分含量小于0.0001%。The distillate at the top of the tower is a high-concentration 1,4-dioxane-containing aqueous solution. After being condensed by the condenser, part of it is refluxed and sent to the atmospheric rectification tower, and the rest is sent to the high-pressure rectification tower at a flow rate of 113kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 76%, and the rest is water. The liquid discharged from the tower kettle is high-purity water, which flows out of the atmospheric distillation tower at a flow rate of 980kg/h, and the mass percentage of 1,4-dioxane in the high-purity water is less than 0.0001%.

步骤200:高压精馏塔中进行高压精馏,高压精馏塔的操作条件为800kpa、塔釜温度188℃、理论板数16块、回流比1。Step 200: Carry out high-pressure rectification in a high-pressure rectification tower. The operating conditions of the high-pressure rectification tower are 800 kPa, the temperature of the tower bottom is 188° C., the number of theoretical plates is 16, and the reflux ratio is 1.

塔顶馏出液经冷凝器冷凝后,部分回流送入高压精馏塔,其余以93kg/h的流速循环返回至常压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为70%,其余为水。塔釜排出液为质量纯度为99.996%高浓度1,4-二氧六环,以20kg/h的流速流出高压精馏塔。After the overhead distillate is condensed by the condenser, part of the reflux is sent to the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower at a flow rate of 93kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 70%, and the rest is water. The liquid discharged from the tower kettle is 1,4-dioxane with a mass purity of 99.996% and high concentration, and flows out of the high-pressure rectification tower at a flow rate of 20 kg/h.

实施例2Example 2

一种含1,4-二氧六环的光刻胶显影剂废水处理方法,具体包括以下步骤:A method for treating photoresist developer wastewater containing 1,4-dioxane, specifically comprising the following steps:

步骤100:将废水以1000kg/h的流速送入常压精馏塔,废水中1,4-二氧六环的质量百分含量为5%,其余为水。Step 100: Send the waste water into the atmospheric rectification tower at a flow rate of 1000 kg/h. The mass percentage of 1,4-dioxane in the waste water is 5%, and the rest is water.

常压精馏塔中进行常压精馏,常压精馏塔的操作条件为常压、塔釜温度102℃、理论板数20块、回流比0.7。Atmospheric rectification is carried out in the atmospheric rectification tower. The operating conditions of the atmospheric rectification tower are atmospheric pressure, tower bottom temperature 102°C, theoretical plate number 20, and reflux ratio 0.7.

塔顶馏出液为高浓度含1,4-二氧六环水溶液,经冷凝器冷凝后,部分回流送入常压精馏塔,其余以143kg/h的流速送入高压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为80%,其余为水。塔釜排出液为高纯度水,以950kg/h的流速流出常压精馏塔,高纯度水中的1,4-二氧六环的质量百分含量小于0.0001%。The distillate at the top of the tower is a high-concentration 1,4-dioxane-containing aqueous solution. After being condensed by the condenser, part of it is refluxed and sent to the atmospheric rectification tower, and the rest is sent to the high-pressure rectification tower at a flow rate of 143kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 80%, and the rest is water. The liquid discharged from the tower kettle is high-purity water, which flows out of the atmospheric distillation tower at a flow rate of 950kg/h, and the mass percentage of 1,4-dioxane in the high-purity water is less than 0.0001%.

步骤200:高压精馏塔中进行高压精馏,高压精馏塔的操作条件为800kpa、塔釜温度166℃、理论板数16块、回流比1。Step 200: Carry out high-pressure rectification in a high-pressure rectification tower. The operating conditions of the high-pressure rectification tower are 800 kPa, 166° C. tower bottom temperature, 16 theoretical plates, and 1 reflux ratio.

塔顶馏出液经冷凝器冷凝后,部分回流送入高压精馏塔,其余以93kg/h的流速循环返回至常压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为72%,其余为水。塔釜排出液为质量纯度为99.995%高浓度1,4-二氧六环,以50kg/h的流速流出高压精馏塔。After the overhead distillate is condensed by the condenser, part of the reflux is sent to the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower at a flow rate of 93kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 72%, and the rest is water. The liquid discharged from the bottom of the tower is high-concentration 1,4-dioxane with a mass purity of 99.995%, and flows out of the high-pressure rectification tower at a flow rate of 50 kg/h.

实施例3Example 3

一种含1,4-二氧六环的光刻胶显影剂废水处理方法,具体包括以下步骤:A method for treating photoresist developer wastewater containing 1,4-dioxane, specifically comprising the following steps:

步骤100:将废水以1000kg/h的流速送入常压精馏塔,废水中1,4-二氧六环的质量百分含量为5%,其余为水。Step 100: Send the waste water into the atmospheric rectification tower at a flow rate of 1000 kg/h. The mass percentage of 1,4-dioxane in the waste water is 5%, and the rest is water.

常压精馏塔中进行常压精馏,常压精馏塔的操作条件为常压、塔釜温度102℃、理论板数20块、回流比0.7。Atmospheric rectification is carried out in the atmospheric rectification tower. The operating conditions of the atmospheric rectification tower are atmospheric pressure, tower bottom temperature 102°C, theoretical plate number 20, and reflux ratio 0.7.

塔顶馏出液为高浓度含1,4-二氧六环水溶液,经冷凝器冷凝后,部分回流送入常压精馏塔,其余以143kg/h的流速送入高压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为80%,其余为水。塔釜排出液为高纯度水,以950kg/h的流速流出常压精馏塔,高纯度水中的1,4-二氧六环的质量百分含量小于0.0001%。The distillate at the top of the tower is a high-concentration 1,4-dioxane-containing aqueous solution. After being condensed by the condenser, part of it is refluxed and sent to the atmospheric rectification tower, and the rest is sent to the high-pressure rectification tower at a flow rate of 143kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 80%, and the rest is water. The liquid discharged from the tower kettle is high-purity water, which flows out of the atmospheric distillation tower at a flow rate of 950kg/h, and the mass percentage of 1,4-dioxane in the high-purity water is less than 0.0001%.

步骤200:高压精馏塔中进行高压精馏,高压精馏塔的操作条件为1000kpa、塔釜温度200℃、理论板数16块、回流比1。Step 200: Carry out high-pressure rectification in the high-pressure rectification tower. The operating conditions of the high-pressure rectification tower are 1000 kPa, the temperature of the bottom of the tower is 200° C., the number of theoretical plates is 16, and the reflux ratio is 1.

塔顶馏出液经冷凝器冷凝后,部分回流送入高压精馏塔,其余以93kg/h的流速循环返回至常压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为69%,其余为水。塔釜排出液为质量纯度为99.995%高浓度1,4-二氧六环,以50kg/h的流速流出高压精馏塔。After the overhead distillate is condensed by the condenser, part of the reflux is sent to the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower at a flow rate of 93kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 69%, and the rest is water. The liquid discharged from the bottom of the tower is high-concentration 1,4-dioxane with a mass purity of 99.995%, and flows out of the high-pressure rectification tower at a flow rate of 50 kg/h.

实施例4Example 4

一种含1,4-二氧六环的光刻胶显影剂废水处理方法,具体包括以下步骤:A method for treating photoresist developer wastewater containing 1,4-dioxane, specifically comprising the following steps:

步骤100:将废水以1000kg/h的流速送入常压精馏塔,废水中1,4-二氧六环的质量百分含量为5%,其余为水。Step 100: Send the waste water into the atmospheric rectification tower at a flow rate of 1000 kg/h. The mass percentage of 1,4-dioxane in the waste water is 5%, and the rest is water.

常压精馏塔中进行常压精馏,常压精馏塔的操作条件为常压、塔釜温度102℃、理论板数20块、回流比1.4。Atmospheric rectification is carried out in the atmospheric rectification tower, and the operating conditions of the atmospheric rectification tower are atmospheric pressure, tower bottom temperature 102°C, theoretical plate number 20, and reflux ratio 1.4.

塔顶馏出液为高浓度含1,4-二氧六环水溶液,经冷凝器冷凝后,部分回流送入常压精馏塔,其余以143kg/h的流速送入高压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为80%,其余为水。塔釜排出液为高纯度水,以950kg/h的流速流出常压精馏塔,高纯度水中的1,4-二氧六环的质量百分含量小于0.0007%。The distillate at the top of the tower is a high-concentration 1,4-dioxane-containing aqueous solution. After being condensed by the condenser, part of it is refluxed and sent to the atmospheric rectification tower, and the rest is sent to the high-pressure rectification tower at a flow rate of 143kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 80%, and the rest is water. The liquid discharged from the tower kettle is high-purity water, which flows out of the atmospheric distillation tower at a flow rate of 950kg/h, and the mass percentage of 1,4-dioxane in the high-purity water is less than 0.0007%.

步骤200:高压精馏塔中进行高压精馏,高压精馏塔的操作条件为1000kpa、塔釜温度200℃、理论板数16块、回流比3。Step 200: Carry out high-pressure rectification in the high-pressure rectification tower. The operating conditions of the high-pressure rectification tower are 1000 kPa, the temperature of the bottom of the tower is 200° C., the number of theoretical plates is 16, and the reflux ratio is 3.

塔顶馏出液经冷凝器冷凝后,部分回流送入高压精馏塔,其余以93kg/h的流速循环返回至常压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为69%,其余为水。塔釜排出液为质量纯度为99.997%高浓度1,4-二氧六环,以50kg/h的流速流出高压精馏塔。After the overhead distillate is condensed by the condenser, part of the reflux is sent to the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower at a flow rate of 93kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 69%, and the rest is water. The liquid discharged from the tower kettle is 1,4-dioxane with a mass purity of 99.997% and high concentration, and flows out of the high-pressure rectification tower at a flow rate of 50 kg/h.

实施例5Example 5

一种含1,4-二氧六环的光刻胶显影剂废水处理方法,具体包括以下步骤:A method for treating photoresist developer wastewater containing 1,4-dioxane, specifically comprising the following steps:

步骤100:将废水以1000kg/h的流速送入常压精馏塔,废水中1,4-二氧六环的质量百分含量为5%,其余为水。Step 100: Send the waste water into the atmospheric rectification tower at a flow rate of 1000 kg/h. The mass percentage of 1,4-dioxane in the waste water is 5%, and the rest is water.

常压精馏塔中进行常压精馏,常压精馏塔的操作条件为常压、塔釜温度102℃、理论板数30块、回流比0.7。Atmospheric rectification is carried out in the atmospheric rectification tower, and the operating conditions of the atmospheric rectification tower are normal pressure, tower bottom temperature 102°C, 30 theoretical plates, and reflux ratio 0.7.

塔顶馏出液为高浓度含1,4-二氧六环水溶液,经冷凝器冷凝后,部分回流送入常压精馏塔,其余以143kg/h的流速送入高压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为80%,其余为水。塔釜排出液为高纯度水,以950kg/h的流速流出常压精馏塔,高纯度水中的1,4-二氧六环的质量百分含量小于0.00008%。The distillate at the top of the tower is a high-concentration 1,4-dioxane-containing aqueous solution. After being condensed by the condenser, part of it is refluxed and sent to the atmospheric rectification tower, and the rest is sent to the high-pressure rectification tower at a flow rate of 143kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 80%, and the rest is water. The liquid discharged from the tower kettle is high-purity water, which flows out of the atmospheric rectification tower at a flow rate of 950kg/h, and the mass percentage of 1,4-dioxane in the high-purity water is less than 0.00008%.

步骤200:高压精馏塔中进行高压精馏,高压精馏塔的操作条件为1000kpa、塔釜温度200℃、理论板数24块、回流比1。Step 200: Carry out high-pressure rectification in the high-pressure rectification tower. The operating conditions of the high-pressure rectification tower are 1000 kPa, the temperature of the tower bottom is 200° C., the number of theoretical plates is 24, and the reflux ratio is 1.

塔顶馏出液经冷凝器冷凝后,部分回流送入高压精馏塔,其余以93kg/h的流速循环返回至常压精馏塔。塔顶馏出液中1,4-二氧六环的质量百分含量为69%,其余为水。塔釜排出液为质量纯度为99.998%高浓度1,4-二氧六环,以50kg/h的流速流出高压精馏塔。After the overhead distillate is condensed by the condenser, part of the reflux is sent to the high-pressure rectification tower, and the rest is circulated back to the atmospheric rectification tower at a flow rate of 93kg/h. The mass percent content of 1,4-dioxane in the overhead distillate is 69%, and the rest is water. The liquid discharged from the bottom of the tower is high-concentration 1,4-dioxane with a mass purity of 99.998%, and flows out of the high-pressure rectification tower at a flow rate of 50 kg/h.

附图1所示为本发明进行废水处理的流程图。Accompanying drawing 1 shows that the present invention carries out the flow chart of wastewater treatment.

含1,4-二氧六环的光刻胶显影剂废水中,1,4-二氧六环和水在常压下形成含水19.4%的共沸物,共沸温度87.74℃。本发明的废水处理方法,根据1,4-二氧六环、水二元物系对压力的敏感性,采用变压精馏,利用共沸物组成比例随压力变化而显著变化的特性,对低浓度的含1,4-二氧六环的光刻胶显影剂废水经变压精馏分离,实现从中回收提取电子级1,4-二氧六环,既可得到高纯度1,4-二氧六环,其经后续的树脂吸附后可直接循环利用,又可排出高纯度水,提纯后的废水满足行业环保要求,可直接排放,实现经济效益和环保效益双赢。In photoresist developer wastewater containing 1,4-dioxane, 1,4-dioxane and water form an azeotrope with a water content of 19.4% under normal pressure, and the azeotropic temperature is 87.74°C. According to the sensitivity of 1,4-dioxane and water binary system to pressure, the waste water treatment method of the present invention adopts pressure swing rectification, and utilizes the characteristic that the composition ratio of azeotrope changes significantly with the change of pressure. The low-concentration photoresist developer wastewater containing 1,4-dioxane is separated by pressure swing rectification to realize the recovery and extraction of electronic grade 1,4-dioxane, which can obtain high-purity 1,4-dioxane Dioxane, after subsequent resin adsorption, can be directly recycled, and high-purity water can be discharged. The purified wastewater meets the environmental protection requirements of the industry and can be discharged directly, achieving a win-win situation of economic and environmental benefits.

该废水处理方法具有大规模、连续化的特点,废水处理量大,不需要引入第三组分,不产生二次污染物,同时可节约大量能量。The wastewater treatment method has the characteristics of large-scale and continuous operation, a large amount of wastewater treatment, no need to introduce a third component, no secondary pollutants, and can save a lot of energy at the same time.

Claims (6)

1. A method for treating photoresist developer wastewater containing 1,4-dioxane is characterized by comprising the following steps:
step 100, feeding the wastewater into an atmospheric distillation tower, wherein the distillate at the top of the atmospheric distillation tower is a high-concentration 1,4-dioxane-containing aqueous solution, and the liquid discharged from the tower bottom is high-purity water; part of the high-concentration 1,4-dioxane-containing aqueous solution is refluxed and sent to the atmospheric distillation tower, and the rest is sent to the high-pressure distillation tower;
200, refluxing part of the tower top distillate of the high-pressure rectifying tower to be sent into the high-pressure rectifying tower, and circularly returning the rest to the normal-pressure rectifying tower, wherein the tower bottom discharge liquid is high-concentration 1,4-dioxane.
2. The method of claim 1 wherein the photoresist developer wastewater treatment process comprises 1,4-dioxane, wherein the method comprises: the composition of the waste water is 2-5% of 1,4-dioxane and 95-98% of water by mass percentage.
3. The method of claim 1 wherein the photoresist developer wastewater treatment process comprises 1,4-dioxane, wherein the method comprises: the operating conditions of the atmospheric distillation column are as follows: normal pressure, tower temperature 100-105 deg.c, theoretical plate number 20-50, reflux ratio 0.5-5.
4. The method of claim 1 wherein the method comprises treating the photoresist developer wastewater containing 1,4-dioxane: operating conditions of the high-pressure rectification column: 800-1000 kpa, the temperature of the tower kettle is 165-205 ℃, the number of theoretical plates is 16-30, and the reflux ratio is 1-3.
5. The method of claim 1 wherein the photoresist developer wastewater treatment process comprises 1,4-dioxane, wherein the method comprises: in the step 100, the high-concentration 1,4-dioxane aqueous solution comprises 75-81% of 1,4-dioxane and 19-25% of water by mass percentage; the high-purity water has a mass purity of greater than 99.99%.
6. The method of claim 1 wherein the photoresist developer wastewater treatment process comprises 1,4-dioxane, wherein the method comprises: in the step 200, the composition of the distillate at the top of the tower is 65-74 percent of 1,4-dioxane and 26-30 percent of water by mass percentage; the mass purity of the high-concentration 1,4-dioxane is 99.99-99.998%.
CN202211205996.0A 2022-09-30 2022-09-30 Method for treating photoresist developer wastewater containing 1,4-dioxane Pending CN115710031A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202211205996.0A CN115710031A (en) 2022-09-30 2022-09-30 Method for treating photoresist developer wastewater containing 1,4-dioxane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202211205996.0A CN115710031A (en) 2022-09-30 2022-09-30 Method for treating photoresist developer wastewater containing 1,4-dioxane

Publications (1)

Publication Number Publication Date
CN115710031A true CN115710031A (en) 2023-02-24

Family

ID=85230916

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202211205996.0A Pending CN115710031A (en) 2022-09-30 2022-09-30 Method for treating photoresist developer wastewater containing 1,4-dioxane

Country Status (1)

Country Link
CN (1) CN115710031A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116478123A (en) * 2023-03-17 2023-07-25 扬州贝尔新环境科技有限公司 Dioxa-hexacyclic liquid waste purification process

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107200680A (en) * 2016-03-19 2017-09-26 青岛科技大学 A kind of variable-pressure rectification separation method of phenolic waste water
CN107311832A (en) * 2017-08-01 2017-11-03 青岛科技大学 Variable-pressure rectification Separation of Benzene and isobutanol mixtures technique and dynamic control scheme
CN110835289A (en) * 2018-08-17 2020-02-25 中国石油化工股份有限公司 Method for recovering ethanol and co-producing ethylene glycol
CN212269760U (en) * 2020-05-06 2021-01-01 杭州格林达电子材料股份有限公司 Device for recovering organic solvent and photoresist from stripping liquid waste liquid

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107200680A (en) * 2016-03-19 2017-09-26 青岛科技大学 A kind of variable-pressure rectification separation method of phenolic waste water
CN107311832A (en) * 2017-08-01 2017-11-03 青岛科技大学 Variable-pressure rectification Separation of Benzene and isobutanol mixtures technique and dynamic control scheme
CN110835289A (en) * 2018-08-17 2020-02-25 中国石油化工股份有限公司 Method for recovering ethanol and co-producing ethylene glycol
CN212269760U (en) * 2020-05-06 2021-01-01 杭州格林达电子材料股份有限公司 Device for recovering organic solvent and photoresist from stripping liquid waste liquid

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
洪素芬: ""四氢呋喃-水体系变压共沸精馏模拟"", 《化学工程与装备》, no. 11, 15 November 2018 (2018-11-15), pages 47 - 49 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116478123A (en) * 2023-03-17 2023-07-25 扬州贝尔新环境科技有限公司 Dioxa-hexacyclic liquid waste purification process

Similar Documents

Publication Publication Date Title
CN101570318B (en) Method for producing electronic-stage hydrofluoric acid
CN101569817B (en) Tail gas recycling method in trichlorosilane production
CN108640844B (en) Method for recovering triethylamine from industrial wastewater
CN115710031A (en) Method for treating photoresist developer wastewater containing 1,4-dioxane
WO2021129404A1 (en) Device and method for recycling waste acid liquid for polycrystalline silicon texturing
CN105753649B (en) A kind of method that isooctanol is reclaimed from the solvent slop of isooctyl thioglycolate production process
CN104447275A (en) Method for purifying acetic acid from acetic acid wastewater
CN101709025A (en) Compound cross-flow liquid-liquid extraction separation method of methylal-methanol azeotropic system
CN104086363B (en) The energy-saving reclaiming process of N-BUTYL ACETATE and butanols in waste acid water
CN107200680B (en) Pressure swing distillation separation method of phenol wastewater
CN104860465A (en) Double-tower catalysis thermal-coupling reflux deamination method and deamination device thereof
CN104496100B (en) The ammonia nitrogen waste water recovery and treatment method produced in nitric acid/Ammonium Nitrate
CN112090235B (en) A purification system and purification process for hydrochloric acid by-product of chlorination reaction
CN102285697A (en) Unsaturated polyester resin industry wastewater recycling process
CN103708571A (en) Technology for treating dilute hydrochloric acid waste liquid generated in production process of ADC (azodicarbonamide) foaming agent
CN103819042B (en) A kind of hydrochloride waste purifying treatment method
CN104016352A (en) Method and system for treating polysilicon tail gas
CN212532807U (en) Equipment for producing methyl acrylate by anhydrous gas-phase formaldehyde
CN221940142U (en) A waste hydrochloric acid treatment system for VCM production room
CN115028526A (en) Method for treating secondary waste acid generated after evaporation of waste etching solution
CN111995518B (en) Method for producing chlorinated fatty acid methyl ester by resource utilization of byproduct hydrochloric acid
CN1307109C (en) Method for recovering aromatic carboxylic acid in waste water
CN223818644U (en) A system for preparing high-purity tetrahydrofuran from 1,4-butanediol waste liquid
CN104761433B (en) Equipment and technique for glycerine method ECH recycling dichlorohydrins and catalyst
CN223042177U (en) Butyl acrylate catalytic reaction recovery system

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