KR100722942B1 - Ethanolamine recovery method with physicochemical process - Google Patents

Ethanolamine recovery method with physicochemical process Download PDF

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KR100722942B1
KR100722942B1 KR1020060071411A KR20060071411A KR100722942B1 KR 100722942 B1 KR100722942 B1 KR 100722942B1 KR 1020060071411 A KR1020060071411 A KR 1020060071411A KR 20060071411 A KR20060071411 A KR 20060071411A KR 100722942 B1 KR100722942 B1 KR 100722942B1
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ethanolamine
tower
exchange resin
wastewater
distillation step
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이인형
조대철
박병기
안현경
정현준
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Priority to PCT/KR2007/003384 priority patent/WO2008013370A1/en

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    • 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
    • C02F1/048Purification of waste water by 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • 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
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • C02F2001/425Treatment of water, waste water, or sewage by ion-exchange using cation exchangers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/08Corrosion inhibition
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters

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

Abstract

본 발명은 원자력 및 화력 발전소에서 사용된 에탄올아민을 회수하는 방법에 관한 것으로, 좀 더 구체적으로는 유입된 폐수는 양이온교환수지를 이용한 에탄올아민포획농축단계와; 상기 양이온교환수지에 의해 에탄올아민이 포획농축된 폐수를 60~100℃로 가열하는 1차 증류단계와; 상기 1차 증류단계를 거친 폐수를 100~200℃로 가열하는 2차 증류단계;를 거쳐 에탄올아민을 함유한 폐수에서 고가의 에탄올아민을 회수하는 것을 그 주요 구성으로 한다.The present invention relates to a method for recovering ethanolamine used in nuclear and thermal power plants, more specifically, the wastewater introduced is an ethanolamine capture concentration step using a cation exchange resin; A first distillation step of heating the wastewater in which the ethanolamine is concentrated by the cation exchange resin to 60 to 100 ° C .; The second distillation step of heating the wastewater passed through the first distillation step to 100 ~ 200 ℃; and recovering the expensive ethanolamine from the wastewater containing ethanol amine as the main configuration.

에탄올아민, 원전 폐수처리, 이온교환, 증류, 냉각 Ethanolamine, Nuclear Wastewater Treatment, Ion Exchange, Distillation, Cooling

Description

물리화학적 공정에 의한 에탄올아민 회수방법{ETHANOLAMINE RECOVERY METHOD WITH PHYSICOCHEMICAL PROCESS}Ethanolamine recovery by physicochemical process {ETHANOLAMINE RECOVERY METHOD WITH PHYSICOCHEMICAL PROCESS}

제 1도는 본 발명에 따른 복합공정에 의한 에탄올아민 폐수의 회수공정을 나타낸 블록도1 is a block diagram showing a process for recovering ethanolamine wastewater by a complex process according to the present invention

제 2도는 본 발명의 일 실시예가 적용되는 시스템을 도시한 개략도2 is a schematic diagram showing a system to which an embodiment of the present invention is applied.

* 도면의 주요부호에 대한 설명 *Explanation of the main symbols in the drawings

1: 이온교환수지탑 2: 양이온교환수지 3: 가성소다 탱크1: ion exchange resin tower 2: cation exchange resin 3: caustic soda tank

4: 가성소다액 5: 공기 6: 흡착탑4: caustic soda solution 5: air 6: adsorption tower

7: 흡착제 8: 증발탑 9: 가열장치7: sorbent 8: evaporation tower 9: heater

10:냉각장치 11:회수탱크10: cooling unit 11: recovery tank

본 발명은 원자력 및 화력 발전소에서 사용된 에탄올아민을 함유한 폐수를 양이온교환수지를 이용한 에탄올아민포획농축단계와; 상기 양이온교환수지에 의해 에탄올아민이 포획농축된 폐수를 60~100℃로 가열하는 1차 증류단계와; 상기 1차 증류단계를 거친 폐수를 100~200℃로 가열하는 2차 증류단계;를 거쳐 유입된 폐수 에서 고가의 에탄올아민을 회수하는 방법에 관한 것이다.The present invention comprises an ethanolamine capture concentration step using a cation exchange resin for wastewater containing ethanolamine used in nuclear and thermal power plants; A first distillation step of heating the wastewater in which the ethanolamine is concentrated by the cation exchange resin to 60 to 100 ° C .; It relates to a method for recovering expensive ethanolamine from the wastewater introduced through the second distillation step of heating the wastewater passed through the first distillation step to 100 ~ 200 ℃.

원자력 및 화력 발전소는 원자력에너지 또는 화석연료로부터 전기에너지를 얻기 위하여 에너지 전달매체로서 물을 사용하는데, 일반적으로 발전소에서의 물/증기 순환계통은 물을 기화하여 터빈을 회전시켜 전기를 생산한 후 증기를 다시 물로 응축시켜 재순환한다. Nuclear and thermal power plants use water as an energy transfer medium to obtain electrical energy from nuclear energy or fossil fuels. In general, the water / steam circulation system in a power plant vaporizes water, rotates a turbine to produce electricity, and then produces steam. Recycle again by condensing with water.

이때 응축된 물에서 각종 구성기기는 부식되어 손상될 수 있으므로, pH 제어제 및 화학전위 조절제 등 화학약품을 주입한다. 이는 전기화학적으로 각종 금속의 부식을 억제할 수 있기 때문이다.At this time, since various components in the condensed water may be damaged by corrosion, chemicals such as pH control agent and chemical potential control agent are injected. This is because corrosion of various metals can be suppressed electrochemically.

이러한 원자력 및 화력 발전소의 물/증기 순환계통에는 이온교환수지탑이 설치되어 있어 미량의 불순물은 물론 부식억제를 위해 주입하는 화학약품도 제거되므로 물/증기 순환주기마다 반복적으로 화학약품을 이온교환수지로 제거하고 외부에서 다시 주입하는 과정을 반복한다. Ion exchange resin towers are installed in the water / steam circulation system of nuclear and thermal power plants to remove trace impurities as well as chemicals injected for corrosion inhibition. Repeat the process of removing and reinjecting from the outside.

상기 화학약품이 과거에는 휘발성 강한 물질로 사용되어 처리도중에 대기로 방출되므로 발전소에서 배출되는 중금속 등을 간단한 물리화학적 공정으로 처리할 수 있었으나, 현재 pH 제어제로 에탄올아민이 채택되면서 COD 및 총질소 성분이 포함된 재생폐수가 다량으로 배출되어 더 이상 방류수 방출허용기준을 만족할 수 없 게 되었다. In the past, since the chemical was used as a volatile substance and released into the atmosphere during processing, it was possible to treat heavy metals discharged from the power plant by a simple physicochemical process, but the ethanolamine as a pH control agent is now adopted to reduce COD and total nitrogen components. The contained wastewater discharged in large quantities can no longer meet the discharge limit.

상기 에탄올아민은 화학구조가 NH2CH2CH2OH으로, 탄소, 수소, 산소, 질소로 구성되어 있어 폐수에 존재할 경우 환경배출허용기준에 규정된 생물학적산소요구량, 생화학적산소요구량 및 질소농도의 증가를 유발하는 고가의 물질로 이 에탄올아민의 처리가 시급한 실정이다. The ethanolamine has a chemical structure of NH 2 CH 2 CH 2 OH, and consists of carbon, hydrogen, oxygen, and nitrogen, and when present in wastewater, the biological oxygen demand, biochemical oxygen demand, and nitrogen concentration specified in the environmental emission allowance standard. As an expensive substance causing an increase, it is urgent to treat this ethanolamine.

따라서, 원자력 및 화력 발전소에서 배출되는 에탄올아민의 폐수를 환경기준이하로 처리, 방류할 수 있는 기술이 요구되고 있다. Therefore, there is a demand for a technology capable of treating and discharging ethanolamine wastewater discharged from nuclear and thermal power plants below environmental standards.

상기와 같은 문제점을 해결하기 위해, 본 발명은 원자력 및 화력 발전소에서 배출되는 에탄올아민의 폐수를 에탄올아민이 방출되지 않도록 할 뿐만 아니라 고가의 에탄올아민을 회수하여 재이용할 수 있게 하여 산업적 이용가치를 높일 수 있는 에탄올아민 회수방법을 제공하는 것을 목적으로 한다.In order to solve the above problems, the present invention not only prevents ethanolamine from being discharged from wastewater of ethanolamine discharged from nuclear and thermal power plants, but also recovers and reuses expensive ethanolamine to increase industrial use value. An object of the present invention is to provide a method for recovering ethanolamine.

전술한 목적을 달성하기 위하여, 본 발명은 유입된 폐수를 양이온교환수지(2)가 충진된 이온교환수지탑(1)에 통과시켜, 상기 양이온교환수지(2)를 통해 에탄올아민을 포획농축한 후, 에탄올아민이 포획농축된 폐수를 증발탑(8)으로 이송하는 에탄올아민포획농축단계와;In order to achieve the above object, the present invention passes the introduced waste water through the ion exchange resin tower (1) filled with the cation exchange resin (2), to capture and concentrate the ethanolamine through the cation exchange resin (2) Thereafter, the ethanolamine capture concentration step of transferring the waste water in which the ethanolamine is concentrated in the evaporation tower (8);

상기 증발탑(8)으로 유입된 폐수에 60 ~ 100℃로 1차 가열하여 발생된 기체를 제올라이트가 충진된 흡착탑(6)에 통과시켜 에탄올아민을 흡착하고, 상기 에탄올아민이 제거된 증기를 대기중으로 방출하는 1차 증류단계와;The gas generated by first heating the wastewater introduced into the evaporation tower 8 at 60 to 100 ° C. is passed through an adsorption tower 6 filled with zeolite to adsorb ethanolamine, and the vapor from which the ethanolamine is removed is air. A first distillation step of discharging to the inside;

상기 1차 증류단계를 거친 폐수에 100 ~ 200℃로 2차 가열하여 발생된 증기와 에탄올아민을 냉각탑(10)으로 이송시키고, 상기 냉각탑(10)에서 10~25℃의 온도로 응축하는 2차 증류단계;를 거쳐 에탄올아민이 회수되는 에탄올아민의 회수방법을 그 주요구성으로 한다.Steam and ethanolamine generated by the second heating to 100 ~ 200 ℃ to the wastewater passed through the first distillation step to the cooling tower 10, the secondary condensing at a temperature of 10 ~ 25 ℃ in the cooling tower (10) The main structure is a method for recovering ethanolamine in which ethanolamine is recovered through a distillation step.

이하, 본 발명의 구성 및 작용을 첨부된 예시도면을 참조하여 상세하게 설명한다.Hereinafter, the configuration and operation of the present invention will be described in detail with reference to the accompanying drawings.

도 1은 본 발명의 에탄올아민 회수과정을 그린 순서도로, 폐수는 양이온교환수지로 통과되어 에탄올아민이 포획되고, 상기 에탄올아민이 포획된 양이온교환수지에 가성소다와 공기를 주입하여 에탄올아민을 용출시켜 폐수를 농축한 후, 폐수를 증발탑으로 이송하는 에탄올아민포획농축단계(S10)와,Figure 1 is a flow chart illustrating the ethanolamine recovery process of the present invention, waste water is passed through the cation exchange resin is trapped ethanolamine, the caustic soda and air is injected into the cation exchange resin trapped by the ethanol amine eluted ethanolamine After concentrating the wastewater, the ethanolamine capture concentration step of transferring the wastewater to the evaporation tower (S10),

상기 증발탑으로 유입된 폐수를 1차 가열하여 발생된 기체를 제올라이트가 충진된 흡착탑에 통과시켜, 에탄올아민을 흡착하고, 상기 에탄올아민이 제거된 증기는 대기중으로 방출하는 1차 증류단계(S20)와,The first distillation step (S20) of adsorbing ethanolamine and the vapor from which the ethanolamine is removed is adsorbed by passing the gas generated by first heating the wastewater introduced into the evaporation tower through a zeolite-filled adsorption tower. Wow,

상기 1차 증류단계를 거친 폐수를 2차 가열하여 발생된 기체를 냉각탑으로 이송시키고, 상기 냉각탑에서 응축하여 에탄올아민을 응축하는 2차 증류단계(S30)를 거쳐 처리된다.Secondary heating of the wastewater passed through the first distillation step is transferred to a cooling tower, and is treated through a second distillation step (S30) condensing in the cooling tower to condense ethanolamine.

도 2는 본 발명의 에탄올아민을 회수하는 공정의 개략도를 나타낸 것으로, 폐수가 통과되는 이온교환수지탑(1)과, 상기 이온교환수지탑(1) 내부에는 양이온교환수지(2)가 충진되고, 상기 이온교환수지탑(1)의 내부로 가성소다탱크(3)에서 유입되는 가성소다액(4)과 공기(5)를 주입함으로써, 양이온교환수지(2)의 교반이 이루어져 에탄올아민이 농축되는 에탄올아민포획농축단계와;Figure 2 shows a schematic diagram of a process for recovering the ethanolamine of the present invention, the ion exchange resin tower (1) through which the waste water is passed, and the cation exchange resin (2) is filled inside the ion exchange resin tower (1) By injecting caustic soda solution 4 and air 5 introduced from the caustic soda tank 3 into the ion exchange resin tower 1, the cation exchange resin 2 is stirred to concentrate ethanolamine. Ethanolamine capture concentration step;

상기 에탄올아민이 포획농축된 폐수를 증발탑(8)으로 이송하고,상기 증발탑(8)으로 유입된 폐수를 가열장치(9)를 이용해 60 ~ 100℃로 1차 가열하여 발생된 기체를 흡착제(7)가 충진된 흡착탑(6)에 통과시켜, 에탄올아민을 흡착하고, 상기 에탄올아민이 제거된 증기는 대기중으로 방출하는 1차 증류단계와;The wastewater containing the concentrated ethanolamine is transferred to the evaporation tower (8), and the wastewater introduced into the evaporation tower (8) is first heated to 60 to 100 ° C using a heating device (9) to adsorb the gas generated. Passing through the adsorption tower (6) filled with (7), adsorbing ethanolamine and discharging the ethanolamine-removed vapor into the atmosphere;

상기 1차 가열하여 이물질이 제거된 폐수를 100 ~ 200℃로 2차 가열하여 발생된 증기를 냉각탑(10)으로 이송시키고, 상기 냉각탑(10)에서 10~25℃의 온도로 응축하여 회수탱크(11)에서 에탄올아민을 회수하는 2차 증류단계;로 구성된다.The waste water from which the foreign matter is removed by the first heating is secondarily heated to 100 to 200 ° C., and the vapor generated by the second heating is transferred to the cooling tower 10, and condensed at a temperature of 10 to 25 ° C. in the cooling tower 10 to recover a recovery tank ( It is composed of; secondary distillation step to recover the ethanolamine in 11).

상기 에탄올아민포획농축단계에서는 강염기성에서 부식이 발생하지 않는 고분자 물질 또는 스텐인레스강과 같은 금속으로 구성된 이온교환수지탑(1)에 충진된 양이온교환수지(2)를 통해 폐수의 에탄올아민이 포획되는데, 상기 양이온교환수지(2)로서는 디비닐렌젠-스틸렌 공중합체를 모체로 하는 설폰산형이 사용되며, 이와 같은 양이온교환수지(2)의 이온교환 능력이 상실되면 가성소다 탱크(3)의 가성소다액(4)과, 공기(5)를 주입하여 양이온교환수지(2)를 교반한다. In the ethanolamine capture concentration step, the ethanolamine of the wastewater is captured through the cation exchange resin (2) filled in the ion exchange resin tower (1) made of a high molecular material or a metal such as stainless steel, which does not generate corrosion. As the cation exchange resin 2, a sulfonic acid type based on a divinylene-styrene copolymer is used. When the ion exchange capacity of the cation exchange resin 2 is lost, a caustic soda solution of the caustic soda tank 3 is used. (4) and air (5) are injected to stir the cation exchange resin (2).

또한, 에탄올아민포획농축단계는 이온교환수지탑(1)에서 재생폐수가 생산되는 과정을 의미하며, 가성소다탱크(3)의 가성소다액(4)과 공기(5)를 이온교환수지층에 통과시켜 얻어진다. 이 과정에서 초기 유입된 에탄올아민 폐수의 농도는 1/10,000~1/20,000 정도로 고농축되며 폐수의 감량화가 이루어지며 부피가 감소된다.In addition, the ethanolamine capture concentration step refers to a process in which regeneration wastewater is produced in the ion exchange resin tower (1), and the caustic soda solution (4) and air (5) of the caustic soda tank (3) are transferred to the ion exchange resin layer. Obtained by passing. In this process, the concentration of ethanolamine wastewater initially introduced is concentrated to about 1 / 10,000 to 1 / 20,000, and the wastewater is reduced and its volume is reduced.

상기 이온교환수지탑(1)의 일측에는 에탄올아민이 대기중으로 방출되는 것을 차단하기 위하여 흡착탑(6)이 설치되고, 상기 흡착탑(6) 내부에 흡착제(7)가 충진되며, 상기 흡착제(7)로는 제올라이트가 사용되는데, 이는 상기 제올라이트는 결정구조적으로 내부에 존재하는 미세 공간에 화학물질을 물리 또는 화학적으로 결합할 수 있으므로, 공기와 함께 기체상의 물 및 에탄올아민이 통과되면서 흡착되기 때문이다.At one side of the ion exchange resin tower (1), an adsorption tower (6) is installed to block ethanolamine from being released into the atmosphere, and an adsorbent (7) is filled in the adsorption tower (6), and the adsorbent (7) As the zeolite is used, since the zeolite can physically or chemically bind a chemical substance to the microcavity existing within the crystal structure, the zeolite is adsorbed while passing gaseous water and ethanolamine together with air.

이상과 같이 에탄올아민포획농축단계를 통과해 수거된 감량폐수는 증발탑(8)으로 이송되는데, 이 증발탑(8)은 이온교환수지탑(1)의 재생폐액을 1단계와 2단계로 증발하는 역할을 하며, 상기 증발탑(8)은 강염기성에서 부식이 발생하지 않으며, 열전달이 우수한 스테인레스강 또는 알루미늄제 재질로 구성된다. As described above, the weight loss wastewater collected through the ethanolamine capture concentration step is transferred to the evaporation tower (8), which evaporates the regeneration wastewater of the ion exchange resin tower (1) in the first and second stages. The evaporation tower (8) does not generate corrosion in the strong base and is made of stainless steel or aluminum material having excellent heat transfer.

상기 1차 증류단계는 60~100℃로 가열하며 이때 발생된 증기와 소량의 에탄올아민은 흡착탑(6)을 통과시켜 대기로 방출하는데, 상기 1차 증류단계의 온도는 60~100℃로 한다. 이는 에탄올아민이 포함된 물을 가열하면 믈과 에탄올아민이 기체로 되는데, 물의 끓는 온도가 100℃, 에탄올아민이 170℃이므로, 100℃ 까지는 물과, 극미량의 에탄올아민이 증발되기 때문이다. 따라서 상기 1차 증류단계의 온도는 60~100℃가 바람직하다.The first distillation step is heated to 60 ~ 100 ℃ and the generated steam and a small amount of ethanolamine is passed through the adsorption tower (6) to release to the atmosphere, the temperature of the first distillation step is 60 ~ 100 ℃. This is because when the water containing the ethanolamine is heated gas and ethanolamine becomes a gas, since the boiling temperature of the water is 100 ℃, ethanol amine 170 ℃, water and a very small amount of ethanol amine is evaporated up to 100 ℃. Therefore, the temperature of the first distillation step is preferably 60 ~ 100 ℃.

또한, 1차 증류단계에서 증발하는 물과 에탄올아민의 기체는 증발탑(8)과 냉각탑(9)의 사이의 흡착탑(6)에 충진되어 있는 흡착제(7)로 흡착하여 에탄올아민이 대기중으로 방출되는 것을 차단하고, 상기 에탄올아민이 흡착된 흡착제(7)를 순수에 침지시켜 흡착제(7)를 재생시키는데, 상기 흡착제(7)로는 결정구조적으로 내부에 존재하는 미세 공간에 기체상의 물 및 에탄올아민을 흡착할 수 있는 제올라이트가 사용된다. In addition, the gas of water and ethanolamine evaporated in the first distillation step is adsorbed by the adsorbent (7) filled in the adsorption tower (6) between the evaporation tower (8) and the cooling tower (9) to release the ethanolamine into the atmosphere. The ethanolamine adsorbed adsorbent (7) is immersed in pure water to regenerate the adsorbent (7). The adsorbent (7) is a gaseous water and ethanolamine in a microcavity that is internally crystalline. Zeolites capable of adsorbing are used.

상기 2차 증류단계는 100~200℃로 가열하는데, 이는 100℃이상으로 가열하면더 이상 물은 없고 에탄올아민만 증발되기 때문이다. 이때 발생된 에탄올아민은 냉각탑(10)으로 이송되며, 증발이 끝나면 내부를 순수로 세척한다. 이러한 증발탑(8)의 내부에는 탄소로 구성되어 있으며 내부에 미세 공간이 존재하는 활성탄을 채워 재생폐액에 존재하는 유기물 및 고형물이 캐리오버되어 기상에 포함되는 것을 방지할 수 있다.The second distillation step is heated to 100 ~ 200 ℃, because when heated to more than 100 ℃ no water and no ethanolamine is evaporated. The ethanolamine generated at this time is transferred to the cooling tower 10, and after the evaporation is finished, the inside is washed with pure water. The inside of the evaporation tower (8) is made of carbon and filled with activated carbon having a microcavity therein, and organic materials and solids present in the regeneration waste liquid may be carried over to prevent inclusion in the gas phase.

상기의 캐리오버는 휘발성이 없는 유기물 또는 무기물이 존재하는 물을 끓이면, 물은 증기로 되어 대기로 날아가고, 유기물 또는 무기물은 끓지 않으므로 물속에 남아 있어야 하나 증기 또는 거품과 함께 대기중으로 날아가는 현상을 말한다.Carryover refers to a phenomenon in which, when boiling water in which organic or inorganic substances which are not volatile are boiled, water flows into the atmosphere as steam, and organic or inorganic matters remain in water because they do not boil, but fly into the atmosphere together with steam or foam.

상기 냉각탑(10)은 증발탑(8)에서 넘어온 증기와 기체상 에탄올아민을 응축시키는 역할을 하며, 냉각온도가 10℃이하일 경우는 에탄올아민의 어는점이 10℃이므로 에탄올아민의 회수가 어려워지며, 수돗물, 지하수 및 바닷물의 어는점은 일반적으로 25℃이하이므로 상기 냉각탑(10)의 냉각온도는 10~25℃가 적당하다.The cooling tower 10 serves to condense the vapor and gaseous ethanolamine from the evaporation tower (8), when the cooling temperature is less than 10 ℃ ethanol amine is difficult to recover because the freezing point of 10 ℃, Since the freezing point of tap water, ground water and sea water is generally 25 ° C. or less, the cooling temperature of the cooling tower 10 is preferably 10 to 25 ° C.

또한, 냉각탑(10)은 강염기성에서 부식이 발생하지 않으며, 열전달이 우수한 구리성분이 포함되지 않은 철 등의 금속 재질로 구성되고, 상기 냉각탑(10)의 열 제거원으로 공기, 물, 냉매를 사용할 수 있다.In addition, the cooling tower 10 is formed of a metal material such as iron does not contain corrosion in the strong base, and does not contain a copper component excellent in heat transfer, air, water, refrigerant as a heat removal source of the cooling tower 10 Can be used.

이렇게 냉각탑(10)을 통하여 응축된 에탄올아민이 회수탱크(11)에 모이게 됨으로써 에탄올아민 수용액은 회수된다. 그리고, 회수된 에탄올아민 수용액은 증발탑에 주입하여 처리한다.The ethanolamine condensed through the cooling tower 10 is collected in the recovery tank 11, the ethanolamine aqueous solution is recovered. The recovered ethanolamine aqueous solution is injected into an evaporation tower and treated.

이상과 같이 본 발명은 에탄올아민포획농축단계와 1차 증류단계 및 2차 증류단계를 통해 에탄올아민을 함유한 폐수는 환경배출기준인 생화학적산소요구량 및 질소 함량을 만족하며 방류됨과 동시에 고가의 에탄올아민은 회수하게 된다. As described above, according to the present invention, the wastewater containing ethanolamine through the ethanolamine capture concentration step, the first distillation step and the second distillation step satisfies the biochemical oxygen demand and nitrogen content, which is an environmental emission standard, and is discharged at the same time as the expensive ethanol. The amine is recovered.

상기에서 설명한 바와 같이, 본 발명에 따라 원자력 및 화력 발전소의 폐수에서 생화학적산소요구량 및 총질소 발생원인 에탄올아민을 발생 시점인 이온교환 수지 재생시 근본적으로 처리함으로서 기존 폐수처리장의 부하 증가를 유발하지 않을 뿐만 아니라 설비 개선의 필요성도 제거할 수 있다. As described above, according to the present invention, by treating ethanolamine, a source of biochemical oxygen demand and total nitrogen, in the wastewater of nuclear and thermal power plants during regeneration of the ion exchange resin at the time of generation, it does not cause an increase in load of the existing wastewater treatment plant. Not only that, but it also eliminates the need for facility improvements.

또한, 원자력 및 화력 발전소의 물/증기 순환계통에 부식 예방을 위해 계속적으로 주입하는 에탄올아민을 회수하여 재이용함으로서 발전소의 경제성을 제고할 수 있다. In addition, it is possible to improve the economics of the power plant by recovering and reusing ethanolamine continuously injected to the water / steam circulation system of nuclear and thermal power plants to prevent corrosion.

Claims (4)

유입된 폐수를 양이온교환수지(2)가 충진된 이온교환수지탑(1)에 통과시켜, 상기 양이온교환수지(2)를 통해 에탄올아민을 포획농축한 후, 에탄올아민이 포획농축된 폐수를 증발탑(8)으로 이송하는 에탄올아민포획농축단계(S10)와;The wastewater introduced is passed through an ion exchange resin tower (1) filled with a cation exchange resin (2) to capture and concentrate the ethanolamine through the cation exchange resin (2), and then evaporate the wastewater containing the concentrated ethanolamine. Ethanolamine capture concentration step (S10) to be transferred to the tower (8); 상기 증발탑(8)으로 유입된 폐수에 60 ~ 100℃로 1차 가열하여 발생된 증기를 제올라이트가 충진된 흡착탑(6)에 통과시켜 에탄올아민을 흡착하고, 상기 에탄올아민이 제거된 증기를 대기중으로 방출하는 1차 증류단계(S20)와;The steam generated by first heating the wastewater introduced into the evaporation tower 8 at 60 to 100 ° C. is passed through the adsorption tower 6 filled with zeolite to adsorb ethanolamine, and the vapor from which the ethanolamine is removed is air. A first distillation step (S20) to be released into the; 상기 1차 증류단계를 거쳐 이물질이 제거된 폐수에 100 ~ 200℃로 2차 가열하여 발생된 증기를 냉각탑(10)으로 이송시키고, 상기 냉각탑(10)에서 10~25 ℃ 온도로 냉각처리하는 2차 증류단계(S30);를 거쳐 에탄올아민이 회수됨을 특징으로 하는 에탄올아민의 회수방법.The steam generated by the second heating to 100 ~ 200 ℃ in the waste water from which the foreign matter is removed through the first distillation step is transferred to the cooling tower 10, the cooling treatment to 10 ~ 25 ℃ temperature in the cooling tower 10 Second distillation step (S30); Ethanolamine recovery method characterized in that the ethanolamine is recovered. 제 1항에 있어서, The method of claim 1, 에탄올아민포획농축단계(S10)는 에탄올아민을 함유한 폐수를 양이온교환수지(2)로 포획한 후, 이온교환수지탑(1)의 일측에 구비되어 있는 가성소다 탱크(3)로부터 주입되는 가성소다(4)를 이용하여 용출시켜 에탄올아민 폐수의 부피를 감소시키는 것을 특징으로 하는 에탄올아민의 회수방법.The ethanolamine capture concentration step (S10) captures wastewater containing ethanolamine with a cation exchange resin (2), and then caustic injected from the caustic soda tank (3) provided on one side of the ion exchange resin tower (1). Elution using soda (4) to reduce the volume of the ethanolamine waste water, characterized in that for recovering ethanolamine. 제 1항에 있어서, The method of claim 1, 에탄올아민포획농축단계에서 기상으로 방출되는 에탄올아민은 이온교환수지탑(1) 일측에 구비된 흡착탑(6)에 충진되어 있는 제올라이트로 흡착하여 에탄올아민이 대기중으로 방출되는 것을 차단하고, 상기 에탄올아민이 흡착된 제올라이트를 순수에 침지시켜 제올라이트를 재생시키는 과정이 더 포함됨을 특징으로 하는 에탄올아민의 회수방법.The ethanolamine released in the gas phase in the ethanolamine capture concentration step is adsorbed by the zeolite packed in the adsorption tower 6 provided on one side of the ion exchange resin tower 1 to block the release of ethanolamine into the atmosphere, and the ethanolamine A method for recovering ethanolamine, further comprising the step of regenerating the zeolite by immersing the adsorbed zeolite in pure water. 제 1항에 있어서, The method of claim 1, 증발탑(8)은 폐수에 존재하는 유기물 및 고형물이 캐리오버되어 기상에 포함되는 것을 방지하기 위해 활성탄을 충진하는 것을 특징으로 하는 에탄올아민의 회수방법.The evaporation tower (8) is a method for recovering ethanolamine, characterized in that the activated carbon is filled in order to prevent the organic matter and solids present in the waste water is carried over to the gas phase.
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WO2009145372A1 (en) * 2008-05-28 2009-12-03 Soonchunhyang University Industry Academy Cooperation Foundation Method for recovering amine from amine-containing waste water
KR101182544B1 (en) 2010-07-27 2012-09-12 순천향대학교 산학협력단 Method and apparatus for recovery of amine from amine-containing waste water and regeneration of amine-form cation exchange resin

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