KR100244971B1 - A waste water treating method using sodium chloride separation process - Google Patents

A waste water treating method using sodium chloride separation process Download PDF

Info

Publication number
KR100244971B1
KR100244971B1 KR1019970031335A KR19970031335A KR100244971B1 KR 100244971 B1 KR100244971 B1 KR 100244971B1 KR 1019970031335 A KR1019970031335 A KR 1019970031335A KR 19970031335 A KR19970031335 A KR 19970031335A KR 100244971 B1 KR100244971 B1 KR 100244971B1
Authority
KR
South Korea
Prior art keywords
waste liquid
distillation
tank
organic matter
incineration
Prior art date
Application number
KR1019970031335A
Other languages
Korean (ko)
Other versions
KR19990009070A (en
Inventor
윤해원
안영인
이병주
박형담
김해연
Original Assignee
박영구
삼성정밀화학주식회사
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 박영구, 삼성정밀화학주식회사 filed Critical 박영구
Priority to KR1019970031335A priority Critical patent/KR100244971B1/en
Publication of KR19990009070A publication Critical patent/KR19990009070A/en
Application granted granted Critical
Publication of KR100244971B1 publication Critical patent/KR100244971B1/en

Links

Images

Classifications

    • 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
    • C02F1/38Treatment of water, waste water, or sewage by centrifugal separation
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S159/00Concentrating evaporators

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Abstract

본 발명은 소금의 분리를 이용한 폐액의 처리방법에 관한 것으로써, 더욱 상세하게는 하이드록실프로필메틸셀룰로오스 제조공정에서 나오는 폐액을 다단계의 농축시스템에서 증류예열조의 저온에서 증발, 응축된 저비점 유기물은 소각로의 연료로 사용하고, 제1농축조, 제2농축조의 농축공정에서 발생하는 응축수는 생물학적 방법으로 처리하며, 최종적으로 생성되는 소금은 원심분리기를 통해 고체폐기물로 처리하고, 소금이 제거된 폐액만을 소각로에서 소각함으로써, 소각대상물질을 최소화하여 폐액의 처리비용을 절감시킬 수 있는 폐액의 처리공정에 관한 것이다.The present invention relates to a method for treating waste liquid using separation of salt. More specifically, the waste liquid from the hydroxylpropyl methylcellulose manufacturing process is evaporated at low temperature in a distillation preheating tank in a multi-stage condensing system, and the low-boiling organic matter condensed is incinerator. The condensate from the concentrations of the first and second concentration tanks is treated by biological method, and the resulting salt is treated as solid waste through a centrifuge. By incineration, it relates to a waste liquid treatment process that can minimize the incineration material to reduce the treatment cost of waste liquid.

Description

소금 분리공정을 이용한 폐액처리공정Wastewater Treatment Process Using Salt Separation Process

본 발명은 소금의 분리를 이용한 폐액의 처리방법에 관한 것으로써, 더욱 상세하게는 하이드록실프로필메틸셀룰로오스 제조공정에서 나오는 폐액을 다단계의 농축시스템에서 증류예열조의 저온에서 증발, 응축된 저비점 유기물은 소각로의 연료로 사용하고, 제1농축조, 제2농축조의 농축공정에서 발생하는 응축수는 생물학적 방법으로 처리하며, 최종적으로 생성되는 소금은 원심분리기를 통해 고체폐기물로 처리하고, 소금이 제거된 폐액만을 소각로에서 소각함으로써, 소각대상물질을 최소화하여 폐액의 처리비용을 절감시킬 수 있는 폐액의 처리공정에 관한 것이다.The present invention relates to a method for treating waste liquid using separation of salt. More specifically, the waste liquid from the hydroxylpropyl methylcellulose manufacturing process is evaporated at low temperature in a distillation preheating tank in a multi-stage condensing system, and the low-boiling organic matter condensed is incinerator. The condensate from the concentrations of the first and second concentration tanks is treated by biological method, and the resulting salt is treated as solid waste through a centrifuge. By incineration, it relates to a waste liquid treatment process that can minimize the incineration material to reduce the treatment cost of waste liquid.

하이드록실프로필메틸셀룰로오스 제조 공정에서 발생되는 폐액은 헤미셀룰로오스, 프로필렌글리콜 등의 -OH 작용기를 가지는 수용성 유기물 및 소금을 다량으로 함유한 악성폐액이다.The waste liquid generated in the hydroxylpropyl methyl cellulose manufacturing process is a malignant waste liquid containing a large amount of water-soluble organic substances and salts having -OH functional groups such as hemicellulose and propylene glycol.

종래에는 상기 폐액을 처리하기 위해 폐액 전량을 소각처리하였는데 폐액의 발생량이 많을 뿐 아니라 무기염의 함량이 약 10 중량%나 되므로 소각처리를 할 경우 분진발생등의 2차 환경문제를 야기시킬 수 있다. 따라서, 소각물량을 감소시키거나 분진을 제거하기 위한 집진장치의 추가설치등의 방법이 필요한 문제점이 있다.Conventionally, the entire waste solution was incinerated to treat the waste solution, but the amount of the waste solution is increased as well as the content of the inorganic salt is about 10% by weight, which may cause secondary environmental problems such as dust generation. Therefore, there is a problem in that a method such as additional installation of a dust collector for reducing the amount of incineration or removing dust is required.

이와 같은 폐액발생공정은 첨부된 도면 제1도에 도시하였으며, 그 공정을 상세히 설명하면 다음과 같다.Such waste liquid generating process is shown in Figure 1 of the accompanying drawings, the process will be described in detail as follows.

셀룰로오스의 주원료인 펄프를 펄프밀(1)에서 분쇄하고, 펄프필터(2)를 거쳐 펄프사일로(3)로 보낸 다음 반응기(4)로 투입한다. 반응기에서는 분쇄된 펄프와 가성소다등의 원료가 섞여 하이드록실프로필메틸셀룰로오스가 생성된다.The pulp, which is the main raw material of cellulose, is pulverized in the pulp mill (1), sent to the pulp silo (3) through the pulp filter (2), and then introduced into the reactor (4). In the reactor, pulverized pulp and raw materials such as caustic soda are mixed to produce hydroxylpropylmethylcellulose.

프레스필터(5)를 거치면서 여액은 폐액(11)으로 발생되고 나머지는 블렌더(6), 그레뉼러(7) 및 드라이어(8)를 거쳐 제품으로 만들어진다. 이때 프레스필터(5)에서 생긴 폐액은 바로 소각로로 보내져서 소각된다.The filtrate is generated as waste liquor 11 through the press filter 5 and the remainder is made into the product via the blender 6, the granulator 7 and the dryer 8. At this time, the waste liquid generated from the press filter 5 is directly sent to an incinerator for incineration.

이렇게 종래에는 발생되는 폐액을 바로 소각처리함으로써 폐액의 처리 비용의 과다지출뿐 아니라 소각후 배출가스내의 분진의 함유등의 2차 환경문제를 일으킬 수 있다. 따라서, 폐액의 처리비용절약과 2차 환경오염을 줄이기 위한 소각대상 물질을 최소화하는 기술의 확보가 절실히 필요하게 되었다.Thus, incineration of the waste liquid generated in the related art can cause secondary environmental problems such as excessive expenditure of waste treatment costs and the inclusion of dust in the exhaust gas after incineration. Therefore, there is an urgent need to secure a technology for minimizing incineration materials to reduce waste disposal costs and to reduce secondary environmental pollution.

따라서, 본 발명에서는 상기의 문제점을 개선하고자 하이드록실프로필메틸셀룰로오스 제조공정에서 발생되는 폐액을 증류, 농축시켜 여과하는 방법으로, 소각물량을 감소시키고, 소각대상물질에서 소금등의 무기염류를 제거함으로써 분진 등의 발생을 최소화하게 하는데 목적있다.Therefore, in the present invention, by distilling and concentrating the waste liquid generated in the hydroxylpropyl methyl cellulose manufacturing process to improve the above problems, by reducing the amount of incineration, by removing inorganic salts such as salt from the incineration target material The purpose is to minimize the occurrence of dust and the like.

제1도는 소금 분리공정의 도입전 하이드록실프로필메틸셀룰로오스 제조공정 개략도이다.1 is a schematic diagram of a hydroxylpropyl methyl cellulose production process before the introduction of the salt separation process.

제2도는 소금 분리공정의 도입후 하이드록실프로필메틸셀룰로오스 제조공정 개략도이다.2 is a schematic diagram of a hydroxylpropyl methyl cellulose production process after the introduction of a salt separation process.

* 도면의 주요부분에 대한 부호의 설명* Explanation of symbols for main parts of the drawings

1 : 펄프밀 2 : 펄프 필터1: pulp mill 2: pulp filter

3 : 펄프 사일로 4 : 반응기3: pulp silo 4: reactor

5 : 프레스필터 6 : 블렌더5: press filter 6: blender

7 : 그레뉼러 8 : 드라이어7: granular 8: dry

9 : 원료 10 : 제품9: raw material 10: product

11 : 폐액 12 : 증류예열조11: waste liquid 12: distillation preheating tank

13a : 제 1 증류농축조 13b : 제 2 증류농축조13a: first distillation tank 13b: second distillation tank

14 : 응축조 15 : 유기물 제거조14 condensing tank 15 organic matter removing tank

16 : 여과기 17 : 소금16: filter 17: salt

18 : 여액 19 : 호퍼18: Filtrate 19: Hopper

20 : 저비점 유기물 배출라인 21 : 소각로20: low boiling point organic matter discharge line 21: incinerator

22 : 생물학적 처리장행 폐수 23 : 재순환리인22: biological treatment plant wastewater 23: recycling

따라서 본 발명은 하이드록실프로필메틸셀룰로오스 제조공정시 발생되는 폐액을 처리함에 있어서, 폐액중 저비점 유기물을 증류예열조(12)에서 제거시키고, 저비점 유기물이 제거된 폐액을 제 1 증류농축조(13a)와 제 2 증류농축조(13b)에서 농축시킨 후 증류된 저비점 유기물을 유기물 제거조(15)에서 제거하고, 상기 농축된 폐액을 여과기(16)에서 여과시키며 이때 석출된 소금을 호퍼(19)로 회수하고 여 과된 폐액을 소각로(21)에서 소각시킴을 특징으로 하는 하이드록실프로필메틸셀룰로오스 제조공정에서 발생되는 폐액의 처리공정에 관한 것이다.Therefore, in the present invention, in treating the waste liquid generated during the hydroxylpropyl methyl cellulose manufacturing process, the low-boiling organic matter in the waste liquid is removed from the distillation preheating tank 12, and the waste liquid from which the low-boiling organic matter is removed is removed from the first distillation concentration tank 13a. After concentration in the second distillation tank (13b) and distilled low-boiling organic matter is removed in the organic material removal tank 15, the concentrated waste liquid is filtered through a filter (16) at this time the precipitated salt is recovered to the hopper (19) It relates to a waste liquid treatment process generated in the hydroxylpropyl methyl cellulose production process characterized by incineration of the filtered waste liquid in the incinerator (21).

또한 이때 증류예열조(12)에서는 저비점 유기물을 45∼65℃ 온도, 300∼500 mmHg 압력하에서 선택적으로 분리시켜 제거한 후 제거된 저비점 유기물을 소각로의 연료로 사용함을 특징으로 하고, 기타 제 1 증류농축조(13a)와 제 2 증류농축 조(13b)에서 증발 응축된 응축수에 포함된 저비점 유기물은 유기물 처리조(15)를 통과시켜 생물학적 처리시킴을 특징으로 한다.In this case, the distillation preheating tank 12 is characterized in that the low boiling point organic material is selectively separated and removed under 45 to 65 ° C. temperature and 300 to 500 mmHg pressure, and then used as the fuel of the incinerator. The low-boiling point organic matter contained in the condensed water evaporated and condensed in the 13a and the second distillation tank 13b is passed through the organic matter treatment tank 15 for biological treatment.

이하 본 발명을 더욱 상세히 설명하면 다음과 같다.Hereinafter, the present invention will be described in more detail.

본 발명의 구성을 설명하면, 하이드록실프로필메틸셀룰로오스 제조공정시 발생되는 폐액의 저비점 유기물을 제거하는 증류예열조(12)와; 저비점 유기물이 제거된 폐액을 1차 농축하는 제 1 증류농축조(13a) 및 제 2 증류농축조(13b)와; 제 1 및 제 2 증류농축조(13a, 13b)에서 증류되는 고비점 유기물을 제거하는 유기물 제거조(15)와; 상기 농축된 농축폐액을 여과시키는 여과기(16)와; 여과된 찌꺼기가 보내지는 호퍼(19)와; 그리고 여과된 폐액을 소각하는 소각로(21)를 포함하는 구성으로 이루어져서 상기 폐액(11)으로부터 소금을 분리하도록 구성되어 있다.When explaining the configuration of the present invention, distillation preheating tank 12 for removing the low-boiling point organic matter of the waste liquid generated during the hydroxylpropyl methyl cellulose manufacturing process; A first distillation tank (13a) and a second distillation tank (13b) for firstly concentrating the waste liquid from which the low boiling point organic matter has been removed; An organic material removing tank 15 for removing high-boiling organic matter distilled from the first and second distillation concentration tanks 13a and 13b; A filter (16) for filtering the concentrated concentrate; A hopper 19 through which filtered residue is sent; And it consists of a configuration including an incinerator 21 for incineration of the filtered waste liquid is configured to separate the salt from the waste liquid (11).

상기 프레스필터(5)에서 나오는 폐액(11)과 소각로(21)사이에 증류예열조 및 다단계 증류농축조, 여과기등을 가지는 것을 본 발명의 특징으로 한다.It is characterized by having a distillation preheating tank, a multi-stage distillation tank, a filter, etc., between the waste liquid 11 and the incinerator 21 coming out of the press filter 5.

이와 같은 본 발명의 소금의 분리를 이용한 폐액처리공정을 첨부도면 제2도에 의거하여 상세히 설명하면 다음과 같다.Referring to the waste liquid treatment process using the separation of salt of the present invention as described in detail based on Figure 2 as follows.

프레스필터(5)에서 나온 폐액은 폐액 주입라인을 통해 증류예열조(12)로 보 내어지고, 증류예열조(12)에서 비점이 60℃ 이하인 일부 저비점 유기물이 저비점 유기물 배출라인(20)을 통해 증류된 후, 폐액(11)을 제 1 증류농축조(13a)에서 농축시킨다. 제 1 증류농축조(13a)에서 농축된 폐액은 보다 나은 소각처리를 위하여 증류농축조간의 이동라인을 통해 제 2 증류농축조(13b)로 들어간 후 제 2 증류농축 조(13b)에서 재농축된다. 이때 증류농축을 원활히 하고, 효율을 높이기 위해서 감 압증류의 방법을 사용한다. 또한 포함되어 있는 물질이 온도가 높아지거나 감압을 할 경우 거품이 생길 수도 있으므로 이때는 소포제를 사용하는 것이 좋다. 제 1 증류농축조(13a) 및 제 2 증류농축조(13b)에서 증류된 물은 미량의저비점 유기물을 함유하므로 유기물 제거조(15)로 보내진다. 여기서는 제 1 증류농축조에서 증류된 유기물을 제거하는 방법과 동일한 공정으로 유기물을 가스상태로 저비점 유기물 배출라인(20)으로 보내 처리하고, 대부분의 나머지 응축수는 생물학적 처리장(22)으로 보낸다.The waste liquid from the press filter 5 is sent to the distillation preheating tank 12 through the waste liquid injecting line, and some low boiling organic matters having a boiling point of 60 ° C. or lower from the distillation preheating tank 12 are passed through the low boiling point organic matter discharge line 20. After distillation, the waste liquid 11 is concentrated in the first distillation tank 13a. The waste liquid concentrated in the first distillation tank 13a is re-concentrated in the second distillation tank 13b after entering the second distillation tank 13b through a moving line between the distillation tanks for better incineration treatment. At this time, in order to facilitate the distillation concentration and increase the efficiency, a pressure reduction distillation method is used. In addition, it is recommended to use an antifoaming agent at this time because the contained material may be foamed when the temperature is increased or reduced pressure. The water distilled in the first distillation tank 13a and the second distillation tank 13b is sent to the organic matter removal tank 15 because it contains a small amount of low boiling point organic matter. Here, the organic matter is sent to the low boiling point organic matter discharge line 20 in a gaseous state in the same process as the method of removing the organic matter distilled from the first distillation tank, and most of the remaining condensate water is sent to the biological treatment plant 22.

한편 제 2 증류농축조(13a)에서 유기물 제거조(15)로 증류되지 않고 남은 농축폐액은 여과기(16)로 보내져서 여과된다. 여과기에 주입된 여액은 소금의 석출이 일어난 상태이다. 순조로운 여과를 위해 강압여과하는 방법이나, 가압여과 또는 원심분리기를 사용한다. 여과된 소금(17)은 물에 쉽게 용해될 수 있는 가용성 물질이므로 호퍼(19)로 보내져 고체폐기물로 매립처리된다. 그러나, 여과기(16)를 통과한 여액은 다시 재순환라인(23)을 거쳐 제 2 증류농축조(13b)로 투입된 후 다시 농축된다. 재순환라인(23)을 통해 제 2 증류농축조(13b)로 투입된 폐액은 농축되고, 농축시 석출된 소금과 농축폐액은 다시 여과기(16)로 보낸다. 이렇게 농축된 폐액을 다시 여과기(16)에서 여과한 후, 여과한후의 소금은 호퍼(19)에서 고체 폐기물로 매립처리하고, 여과기(16)에서의 여액은 소각로(21)로 보내지게 된다.On the other hand, the concentrated waste liquid remaining without distillation from the second distillation concentration tank 13a to the organic matter removal tank 15 is sent to the filter 16 and filtered. The filtrate injected into the filter is a state of precipitation of salt. Pressure filtration, or pressure filtration or centrifugation, is used for smooth filtration. Since the filtered salt 17 is a soluble substance that can be easily dissolved in water, it is sent to the hopper 19 to be landfilled with solid waste. However, the filtrate passing through the filter 16 is fed back into the second distillation tank 13b via the recycle line 23 and then concentrated again. The waste liquid introduced into the second distillation tank 13b through the recirculation line 23 is concentrated, and the precipitated salt and the concentrated waste liquid are sent to the filter 16 again. After the concentrated waste liquid is filtered again in the filter 16, the salt after filtering is landfilled as solid waste in the hopper 19, and the filtrate in the filter 16 is sent to the incinerator 21.

본 발명에서는 하이드록실프로필메틸셀룰로오스 제조공정에서 발생되는 폐 액을 다단계 농축공정과 소금의 분리공정을 이용해서 소각물량을 감소시켰으므로, 소각시 발생하는 2차 환경오염을 줄일 수 있는 효과가 있다.In the present invention, since the incineration amount is reduced by using a multi-step concentration process and a salt separation process, the waste liquid generated in the hydroxylpropylmethylcellulose manufacturing process has an effect of reducing secondary environmental pollution generated during incineration.

상기 하이드록실프로필메틸셀룰로오스 제조공정 폐액의 처리과정에 있어서, 효과적으로 소각물량을 줄이는 중요한 과정은 폐액중의 80 중량%를 차지하는 물과 소량의 유기물은 증류로 제거하고, 소금은 석출시켜 따로 분리하는 과정에 있다. 농축과 분리가 잘 이루어질 경우 소각물량은 약 10 중량% 정도로 줄어든다. 대부분의 물이 증류되어 제거되면 소각처리법에 있어서 소각물량이 감소되고, 소금을 따로 분리하여 제거하면 분진발생등의 2차 환경오염을 방지할 수 있다.In the treatment of the wastewater of the hydroxylpropyl methyl cellulose manufacturing process, an important process for effectively reducing the amount of incineration is a process in which water and a small amount of organic matter, which occupy 80% by weight of the waste, are removed by distillation, and salts are separated and separated. Is in. When concentrated and separated well, the incineration amount is reduced to about 10% by weight. When most of the water is distilled off, the amount of incineration is reduced in the incineration method, and if the salt is separated and removed, it is possible to prevent secondary environmental pollution such as dust generation.

본 발명을 실시예에 의거하여 상세히 설명하면 다음과 같다. 본 발명이 실시예에 의한 한정되는 것은 아니다.Hereinafter, the present invention will be described in detail with reference to Examples. The present invention is not limited by the examples.

(실시예 )Example

하이드록실프로필메틸셀룰로오스 제조공정에서 나오는 폐액의 조성은 아래의 표 1과 같다. 이중 폐액이 다음의 표 2와 같은 조성을 가질 때 이 폐액을 첨부도 면 제 2도에 도시된 증류예열조(12)에 라인을 통해 투입한다. 여기에서 비점이 60℃ 이하인 물질을 60℃, 450mmHg의 조건하에서 증류한 다음, 가스상태로 날아가는 저비점 유기물을 저비점 유기물 배출라인(20)을 통해 소각로로 보내고, 저비점 유기물에 제거된 폐액은 제 1 증류농축조(13a)로 보낸다. 제 1 증류농축조(13a)에서는 70℃, 300mmHg의 조건하에서 약 30% 까지 농축시킨다. 이때 증류된 물은 생물학적 처리장(22)으로 보내지고, 농축된 액은 제 2 증류농축조(13b)로 넘어간다. 농축된 폐액은 제 2 증류농축조에서 65℃, 250mmHg의 조건으로 다시 농축되고, 소금을 석출시킨다. 제 1 증류농축조(13a)에서와 같은 공정으로 증류된 물은 생물학적 처리장(22)으로 가고, 소금이 석출되어 있는 농축액은 여과기(16)으로 보내진다. 여과기에서 원심분리를 사용하여 소금을 분리한다. 이때 소금이 과포화 되어 있는 여액은 재순환라인(23)을 통해 제 2 증류농축조(13b)로 다시 보내진다. 소금이 거의 완전히 제거되고 분리된 여액(18)은 소각로(21)로 보내져서 소각처리된다.The composition of the waste liquid from the hydroxylpropyl methyl cellulose manufacturing process is shown in Table 1 below. When the waste liquid has a composition as shown in Table 2 below, the waste liquid is added to the distillation preheating tank 12 shown in FIG. Here, the material having a boiling point of 60 ° C. or less is distilled under conditions of 60 ° C. and 450 mm Hg, and then low-boiling organics flying in a gaseous state are sent to the incinerator through the low-boiling organics discharge line 20, and the waste liquid removed from the low-boiling organics is first distilled. It is sent to the concentration tank 13a. In the first distillation tank (13a) is concentrated to about 30% under the conditions of 70 ℃, 300mmHg. At this time, the distilled water is sent to the biological treatment plant 22, and the concentrated liquid is passed to the second distillation concentration tank 13b. The concentrated waste liquid is concentrated again in the second distillation tank at the condition of 65 ° C. and 250 mm Hg to precipitate salt. The water distilled by the same process as in the first distillation concentration tank 13a goes to the biological treatment plant 22, and the concentrated liquid in which the salt is precipitated is sent to the filter 16. The salt is separated using centrifugation in the filter. At this time, the filtrate containing the supersaturated salt is sent back to the second distillation tank (13b) through the recycle line (23). The salt is almost completely removed and the separated filtrate 18 is sent to an incinerator 21 for incineration.

[표 1] 일반적 폐액의 조성[Table 1] Composition of General Waste Liquid

Figure kpo00002
Figure kpo00002

[표 2] 본 실시예의 폐액의 조성[Table 2] Composition of Waste Liquid in the Example

Figure kpo00003
Figure kpo00003

본 발명에서 전량 소각되던 폐액을 연속적인 증발농축과 소금의 분리공정을 이용함으로써 소각물량을 줄이고, 2차 환경오염문제를 해결하게 되었다. 상기 증발농축공정과 소금의 분리공정을 이용함으로써 소각물량을 원폐액의 약 10%까지 감소시키고, 소각으로 인한 2차 환경오염을 방지하는 것을 비롯하여 폐액의 생물학적 처리를 가능하게 함으로써 환경부하 감소효과 및 폐액처리비용 절감효과가 있음을 알 수 있다.Wastewater, which was completely incinerated in the present invention, was used to reduce the amount of incineration by using a continuous evaporation and salt separation process, thereby solving the secondary environmental pollution problem. By using the evaporation concentration process and the salt separation process, the incineration amount is reduced to about 10% of the original waste liquid, and the secondary environmental pollution due to incineration, including the biological treatment of the waste liquid by reducing the environmental load and effect It can be seen that there is an effect of reducing the waste disposal cost.

Claims (1)

폐액중 저비점 유기물을 45∼65℃ 온도 300∼500 mmHg 압력하에서 선택적으로 분리시켜 증류예열조(12)에서 제거시키고, 저비점 유기물이 제거괸 폐액을 제1 증류농축조(13a)와 제 2 증류농축조(13b)에서 증발 응축후 응축수에 포함된 저비점 유기물은 유기물 처리조(15)를 통과시켜 생물학적 처리시키고, 그 후 농축된 폐액을 여과기(16)에서 여과시키며 이때 석출된 소금을 호퍼(19)로 회수하고 여과된 폐액을 소각로(21)에서 소각시킴을 특징으로 하는 하이드록실프로필메틸셀룰로오스 제조공정에서 발생되는 폐액의 처리공정.The low-boiling organic matter in the waste liquid is selectively separated under a 45-65 ° C. temperature of 300-500 mmHg pressure to remove it from the distillation preheating tank 12, and the waste liquid from which the low-boiling organic matter is removed is removed from the first distillation concentration tank 13a and the second distillation concentration tank ( The low-boiling organic matter contained in the condensate after evaporation and condensation in 13b) is passed through the organic matter treatment tank 15 for biological treatment, and then the concentrated waste liquid is filtered through the filter 16, and the precipitated salt is recovered to the hopper 19. And injecting the filtered waste liquid in the incinerator (21).
KR1019970031335A 1997-07-07 1997-07-07 A waste water treating method using sodium chloride separation process KR100244971B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1019970031335A KR100244971B1 (en) 1997-07-07 1997-07-07 A waste water treating method using sodium chloride separation process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1019970031335A KR100244971B1 (en) 1997-07-07 1997-07-07 A waste water treating method using sodium chloride separation process

Publications (2)

Publication Number Publication Date
KR19990009070A KR19990009070A (en) 1999-02-05
KR100244971B1 true KR100244971B1 (en) 2000-02-15

Family

ID=19513589

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1019970031335A KR100244971B1 (en) 1997-07-07 1997-07-07 A waste water treating method using sodium chloride separation process

Country Status (1)

Country Link
KR (1) KR100244971B1 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101585620B (en) * 2009-06-26 2012-08-22 河北建新化工股份有限公司 Method for comprehensively treating high salt content organic industrial wastewater
CN104649496A (en) * 2015-02-13 2015-05-27 江苏中丹集团股份有限公司 Chemical industrial waste salt refining device
CN104671576A (en) * 2015-02-13 2015-06-03 江苏中丹集团股份有限公司 Waste salt refining device and process in chemical industry
CN110397940A (en) * 2019-07-23 2019-11-01 源创环境科技有限公司 A kind of technique of high temperature incineration processing landfill leachate

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4672113A (en) * 1983-09-05 1987-06-09 Hoechst Aktiengesellschaft Process for purifying aqueous distillation residues during the treatment of liquids in the preparation of cellulose ethers

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4672113A (en) * 1983-09-05 1987-06-09 Hoechst Aktiengesellschaft Process for purifying aqueous distillation residues during the treatment of liquids in the preparation of cellulose ethers

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101585620B (en) * 2009-06-26 2012-08-22 河北建新化工股份有限公司 Method for comprehensively treating high salt content organic industrial wastewater
CN104649496A (en) * 2015-02-13 2015-05-27 江苏中丹集团股份有限公司 Chemical industrial waste salt refining device
CN104671576A (en) * 2015-02-13 2015-06-03 江苏中丹集团股份有限公司 Waste salt refining device and process in chemical industry
CN110397940A (en) * 2019-07-23 2019-11-01 源创环境科技有限公司 A kind of technique of high temperature incineration processing landfill leachate

Also Published As

Publication number Publication date
KR19990009070A (en) 1999-02-05

Similar Documents

Publication Publication Date Title
US3342731A (en) Method for dewatering sludges
CN108503181B (en) Harmless integrated treatment method for oily sludge
CN105714590A (en) Method for separating lignin and hemicellulose from papermaking black liquor and recycling alkali liquor
US20070227979A1 (en) Black Liquor Treatment Method
CN110734164A (en) ship wastewater treatment system and treatment method thereof
CN211688260U (en) Full-automatic industrial sulfur purification system
KR100244971B1 (en) A waste water treating method using sodium chloride separation process
JP2002159953A (en) Process and equipment for treating waste
JP4235091B2 (en) Method and apparatus for treating manure and organic sludge
KR20020094421A (en) System and Process for Ozone-Enhanced Reduction and Recycling of Wastewater Sludge
JP2007000734A (en) Method for treating organic waste water, and system therefor
CN111778059A (en) Oil sludge sand pre-separation-oil recovery-post-treatment system and process
US5705073A (en) Method for the disposal of excess sludge
CN113060884B (en) Petrochemical oily sewage and oil sludge purifying and recycling system
JPH01218699A (en) Treatment of excessive activated sludge
CN1057512C (en) Harnessing method for papermaking waste water
CN106629961A (en) Method for extracting high-concentration phenol-containing wastewater by super-gravity
CN112028272A (en) Method for recovering crude oil in crude oil electric desalting wastewater
JP2000015228A (en) Method for fermenting organic waste
KR100217307B1 (en) The treatment of polymeric material in waste water in acid
JP4294540B2 (en) Organic sludge treatment method and treatment equipment
KR100243061B1 (en) A recycling method of low boiling point organic matter in waste water
KR101323277B1 (en) Wastewater treatment system and method thereof
KR100217305B1 (en) The continuous elimination equipment of polymeric material in waste water
JP3832808B2 (en) Method for recovering phosphorus in sludge

Legal Events

Date Code Title Description
A201 Request for examination
E902 Notification of reason for refusal
E701 Decision to grant or registration of patent right
GRNT Written decision to grant
FPAY Annual fee payment

Payment date: 20021125

Year of fee payment: 4

LAPS Lapse due to unpaid annual fee