KR940011824B1 - Waste water treatment system - Google Patents

Waste water treatment system Download PDF

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KR940011824B1
KR940011824B1 KR1019910019727A KR910019727A KR940011824B1 KR 940011824 B1 KR940011824 B1 KR 940011824B1 KR 1019910019727 A KR1019910019727 A KR 1019910019727A KR 910019727 A KR910019727 A KR 910019727A KR 940011824 B1 KR940011824 B1 KR 940011824B1
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incinerator
wastewater
ammonium sulfate
gas
waste water
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KR1019910019727A
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Korean (ko)
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KR930009935A (en
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이규남
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이규남
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material

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

Abstract

The waste water sprayed by a nozzle (2) installed on top of spray/dry apparatus (4) is dryed by hot air (B) at 150 deg.C and ammonium sulfate that is materials of fertilizer is recovered as solid state (D). The gas of low temperature (150 deg.C) that ammonium sulfate in waste water is perfectly removed is decomposed in an incinerator at 482 deg.C and changed to a hot gas. The hot gas is passed into a thermal exchanging machine (8) and recovered heat capacity is used as other energy source.

Description

합성수지제조시 발생되는 폐수처리시스템Wastewater Treatment System in Synthetic Resin Manufacturing

제1도는 본 발명에 따른 실시예시도.1 is an exemplary embodiment according to the present invention.

제2도는 본 발명에 의한 폐수처리에 따른 흐름도.2 is a flow chart according to the wastewater treatment according to the present invention.

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

1 : 폐수탱크 2 : 노즐1: waste water tank 2: nozzle

3 : 열풍발생기 4 : 분무건조장치3: hot air generator 4: spray drying apparatus

5 : 여과집진기 6 : 소각로5: bag filter 6: incinerator

7 : 연도 8 : 열교환기7: year 8: heat exchanger

9 : 가스세정기 10 : 조작댐퍼9: gas cleaner 10: operation damper

A : 펌프수단A: Pump means

본 발명은 합성수지제조 과정에서 발생되는 폐수(황산암모늄, 피라딘등이 함유됨)에 대한 처리 시스템에 관한 것으로, 특히, 폐수를 자연환경이 오염되지 않도록 안전하게 처리하는 과정에서 비교원료인 황산암모늄을 고형화상태로 회수하는 기능과, 폐가스의 잔여열량을 회수하여 재활용할 수 있도록 개발된 합성수지 제조시 발생되는 폐수처리 시스템에 관한 것이다.The present invention relates to a treatment system for wastewater (containing ammonium sulfate, pyridin, etc.) generated during the manufacture of synthetic resins. In particular, the present invention relates to ammonium sulfate, a comparative raw material, in the process of safely treating wastewater to prevent contamination of the natural environment. The present invention relates to a wastewater treatment system generated during the production of a synthetic resin developed to recover a solidified state and to recover and recycle residual heat of waste gas.

일반적으로 합성수지 제조과정에서 발생되는 폐수중에는 황산암모늄(약 35%), 파라딘(약 0.5%), 물(64.5%) 등이 혼합되어 있는데, 종래의 경우, 상기와 같은 폐수처리 방식은 직화염에 의한 소각 처리방법이 사용되고 있다.In general, wastewater generated during the production of synthetic resin is mixed with ammonium sulfate (about 35%), paradine (about 0.5%), water (64.5%), etc. In the conventional case, the wastewater treatment method is a direct flame Incineration treatment by is used.

그러나 이와 같은 폐수처리 과정에서는 폐수에 함유된 황산암모늄의 분해를 위해서 고온(약 780℃) 상태를 유지하는 소각로가 필요하기 때문에, 경제적인 손실이 초래되었음은 물론 대기중으로 배출되는 배기가스중에도 황산화물(SOx), 질소산화물(NOx)이 함유되어 있어 대기오염의 주요인이 되었다.However, such wastewater treatment requires an incinerator that maintains a high temperature (about 780 ° C) for the decomposition of ammonium sulfate in the wastewater, resulting in economic losses and sulfur oxides in the exhaust gases to the atmosphere. It contains (SO x ) and nitrogen oxides (NO x ), which are the main causes of air pollution.

또한, 폐수처리과정에서 이에 함유된 비교원료인 황산암모늄의 재회수가 요구되었다.In addition, the wastewater treatment was required to recover the ammonium sulfate, a comparative material contained therein.

이에 본 발명은 상기와 같은 종래의 문제점을 해결하기 위해서 폐수를 분사시키면서, 분사되는 폐수에 대해 약 150℃ 정도의 열풍에 의한 저온으로 증발 건조시켜 처리케함과, 그 과정에서 폐수에 함유된 황산암모늄을 고형화상태로 분리회수하면서 피라딘을 완전 분해시킴과 더불어 고온의 폐가스중에 잔여하는 열량을 회수하여 재활용할 수 있도록 된 것으로, 그 실시예를 첨부된 도면에 의거하여 상세히 설명하면 다음과 같다.In order to solve the above problems, the present invention injects wastewater, and treats the wastewater to be evaporated to dryness at a low temperature by hot air at about 150 ° C., and the ammonium sulfate contained in the wastewater in the process. While completely recovering pyridin while separating and recovering it in a solidified state, it is possible to recover and recycle heat remaining in high-temperature waste gas, which will be described in detail with reference to the accompanying drawings.

합성수지 제조과정에서 발생된 폐수가 집수상태로 교반되는 폐수탱크(1)와, 펌프수단(A)이 펌핑력으로 폐수가 공급로로 유도되어 노즐(2)에 분사되고 열풍발생기(3)에서 저온(130-150℃)상태의 열풍이 유도되어 분사되는 페수를 가열증발시켜 폐수에 함유된 황산암모늄을 고형화상태로 분리하는 분무건조장치(4)와, 상기 분무건조장치로부터 유도되는 가스에 잔여하고 있는 황산암모늄 고형분을 완전히 여과하는 여과집진기(5)와, 상기 여과집진기(5)에서 가스가 유도되어 잔여하고 있는 피라딘을 완전연소시켜 분해시키는 소각로(6)와, 상기 소각로(6)의 배기구쪽으로 연도(7)에 연통되게 설치되고 순차적으로 연동되는 폐열회수수단인 열교환기(8) 및 가스세정기(9)와, 상기 소각로(6) 배기측 일측에는 연도(7)와 연통설치되며, 전기적인 제어에 의해 조작되는 조작댐퍼(10)로 이루어져서 된 것이다. 여기서, 열풍발생기(3) 및 소각로(6)에는 가열수단(B)(B1)과 연료 및 연소공기공급수단(C)(C1)이 부설연결된다.Wastewater tank (1) in which wastewater generated in the synthetic resin manufacturing process is agitated in a collecting state, and pump means (A) is pumped into the wastewater supply path by the pumping force and injected into the nozzle (2), and the low temperature in the hot air generator (3). A spray drying apparatus 4 for separating the ammonium sulfate contained in the waste water into a solidified state by heating and evaporating the waste water injected by hot air in a state of (130-150 ° C.), and remaining in the gas derived from the spray drying apparatus. A bag filter (5) for completely filtering solid ammonium sulfate solids, an incinerator (6) for completely burning and decomposing pyridines which are induced by gas in the bag filter (5), and an exhaust port of the incinerator (6) It is installed in communication with the flue (7) toward the heat exchanger (8) and the gas cleaner (9), which is a waste heat recovery means sequentially interlocked with the flue (7) is installed in communication with the flue (7) on one side of the incinerator (6), Manipulated by manual control It consists of the operation damper (10). Here, the heating means (B) (B1) and the fuel and combustion air supply means (C) (C1) are attached to the hot air generator (3) and the incinerator (6).

또, 분무건조장치(4) 및 여과집진기(5)에서 분리되는 고형화상태의 황산암모늄은 회수수단(컨베어등을 채용함)(D)에 낙하시켜 회수한다. 본 발명의 폐수처리시스템은 제어수단(E)으로 제어동작된다. 미설명부호 F는 모터와 휀으로 된 교반수단인 것이다.In addition, the ammonium sulfate in the solidified state separated by the spray drying apparatus 4 and the bag filter 5 is collected by dropping it into a recovery means (using a conveyor or the like) D. The wastewater treatment system of the present invention is controlled by the control means (E). Reference numeral F is a stirring means consisting of a motor and a fan.

이와 같은 본 발명의 실시예를 상세히 설명하면 다음과 같다.When explaining the embodiment of the present invention in detail as follows.

합성수지 제조과정에서 발생된 폐수를 처리하기 위해서는 먼저, 본 발명에 의한 시스템의 폐수탱크(1)내로 집수시켜 교반수단(F)로서 교반케한 상태에서, 시스템제어수단(E)에서 송출된 제어신호에 의해 시스템을 가동시키게되면, 폐수탱크(1)내의 폐수가 펌프수단(A)의 펌핑작용으로 공급로를 따라 분무건조장치(4)의 상측에 위치부설된 노즐(2)로 유도되어 분무건조장치(4)내로 분사되는데, 이때, 연료 및 연소공기공급수단(C)으로부터 연료 및 연소공기를 공급받아 가동되는 가열수단(B)의 가동으로 저온(150℃)상태의 열풍이 분무건조장치(4)로 유도되므로 저온상태를 유지하게되며, 이와 같은 상태의 분무건조장치(4)내로 분사되는 폐수는 증발건조 되면서 함유하고 있던 비료의 원료인 황산암모늄은 고형화 상태로 분리되어 분무건조장치(4)의 출구를 통해 회수수단(D)으로 낙하되어 회수된다.In order to treat the wastewater generated in the synthetic resin manufacturing process, first, the control signal sent out from the system control means (E) while collecting the wastewater tank (1) of the system according to the present invention and agitated as the stirring means (F) When the system is operated by the waste water, the waste water in the waste water tank 1 is guided to the nozzle 2 positioned above the spray drying apparatus 4 along the supply path by the pumping action of the pump means A and spray dried. It is injected into the apparatus 4, where hot air in a low temperature (150 ° C.) state is spray-dried by the operation of the heating means B, which is operated by receiving fuel and combustion air from the fuel and combustion air supply means C. 4) it is induced to maintain a low temperature state, and the waste water sprayed into the spray drying apparatus 4 in this state is evaporated to dryness, while ammonium sulfate, which is a raw material of the fertilizer contained, is separated into a solidified spray drying apparatus (4). Through the exit of Is dropped to the collection means (D) is recovered.

계속해서, 분무건조장치(4)에서 배기된 저온가스(소량의 고형 황산암모늄이 잔여하고 있음)가 연통되게 장치된 여과집진기(5)로 유도되어져 고온가스에 잔여하고 있는 황산암모늄을 완전히 여과하여 회수수단(D)으로 낙하하여 회수하게 된다.Subsequently, the low temperature gas exhausted from the spray drying apparatus 4 (a small amount of solid ammonium sulfate remains) is introduced into the filter dust collector 5, which is in communication, to completely filter the ammonium sulfate remaining in the hot gas. It will fall to collect | recovery means D, and it will collect | recover.

또한, 상기와 같은 황산암모늄 회수공정에서 황산암모늄이 완전히 제거된 저온가스는 가스유도로를 따라 소각로(6) 내부로 유도되어 통과하게 되는데, 이때, 소각로(6)의 상측에 연료 및 연소공기 공급수단(C1)과 연결된 상태로 장치된 가열수단(B1)의 가동으로 소각로(6) 내부는 피라딘의 열분해온도(약 482℃) 이상을 유지하게되며, 이 상태의 내부를 가스가 통과하면서 가스에 잔여하고 있던 피라딘은 열분해온도에 의해 완전분해되어져 소각로(6)의 배기구쪽으로 장치된 조작댐퍼(10)쪽으로 고온의 열량을 지닌상태로 배기된다.In addition, in the ammonium sulfate recovery process as described above, the low-temperature gas from which ammonium sulfate is completely removed is led to the inside of the incinerator 6 along the gas flow path, and at this time, fuel and combustion air are supplied to the upper side of the incinerator 6. By operating the heating means B1 connected to the means C1, the inside of the incinerator 6 maintains pyrodine pyrolysis temperature (about 482 ° C) or more, and the gas passes through the interior of this state. The pyridine remaining in the gas is completely decomposed by the pyrolysis temperature and is exhausted with a high amount of heat toward the operation damper 10 installed toward the exhaust port of the incinerator 6.

여기서, 조작댐퍼(10)쪽으로 배기되는 가스는 분무건조장치(4) 및 여과집진기(5)와 소각로(6)를 순차적으로 거치는 동안 황산암모늄과 피라딘을 완전히 제거된 상태이다.Here, the gas exhausted toward the operation damper 10 is in a state of completely removing ammonium sulfate and pyridine while sequentially passing through the spray drying apparatus 4, the bag filter 5, and the incinerator 6.

한편, 소각로(6)의 배기구에는 전기적인 제어에 의해 조작되는 조작댐퍼(10)가 장치되어있어 작업자의 선택적인 조작에 의해 폐열을 회수하고자 할때에는 연도(7)쪽으로 가스가 배출되지 못하도록 조작댐퍼(10)를 가동시켜 소각로(6)의 배기구와 연도(7) 사이를 차단하면 소각로(6)를 통과한 고온상태의 가스가 열교환기(8)쪽으로 유도되어지며, 열교환기(8)를 통과한 가스는 가스세정기(9)를 통해 여과세정되면서 연도(7)를 통해 대기중으로 방출하게 된다.On the other hand, the exhaust port of the incinerator (6) is equipped with an operation damper 10 which is operated by electrical control, so that when the waste heat is to be recovered by the operator's selective operation, the operation damper does not discharge to the flue (7) By operating (10) to cut off between the exhaust port of the incinerator (6) and the flue (7), the high temperature gas passing through the incinerator (6) is led to the heat exchanger (8), and passes through the heat exchanger (8). One gas is filtered through a gas cleaner (9) and released into the atmosphere through the flue (7).

이때, 열교환기(8)를 통과하게되는 고온의 가스에 의해서 얻어지는 회수열량을 에너지원으로 하여 온수(난방) 또는 기타의 산업분야에 적용할 수 있게 되었고, 또한 조작댐퍼(10)는 작업자의 선택적인 적기적인 제어에 의해 열교환기(8)의 가동 즉, 폐열회수를 필요로 하지 않을때에는 조작댐퍼(10)를 개방시켜줌으로서 소각로(6) 배기구쪽으로부터 방출되는 가스는 조작댐퍼(10)를 거쳐 연도(7)를 통해 대기중으로 방출하게 된다.At this time, the amount of heat recovered by the hot gas passing through the heat exchanger 8 can be applied to hot water (heating) or other industrial fields as an energy source, and the operation damper 10 is selected by the operator. When the heat exchanger 8 is operated by timely control, that is, when the waste heat recovery is not required, the operation damper 10 is opened so that the gas discharged from the exhaust port side of the incinerator 6 passes through the operation damper 10. It will be released into the atmosphere through year (7).

이상에서 본 바와 같이 본 발명은 합성수지제조 과정에서 발생되는 폐수를 처리하는데 있어서, 폐수에 함유되어있는 황산암모늄을 분사건조장치 및 여과집진기로 이루어진 황산암모늄 회수공정에서 고형화상태로 분리회수토록함과, 아울러 소각로에서 열분해방식으로 피라딘성분을 완전제거하여 처리함과 폐가스의 잔여열량을 회수하여 별도의 용도로 사용할 수 있도록 된것으로서, 폐수처리와 동시에 비료원료인 황산암모늄을 회수사용할 수 있으며, 또, 소각로의 분해온도가 낮은 상태로 시스템이 운전되므로 경제적인 효과를 얻을 수 있을 뿐만 아니라 페수처리에 의한 제반 자연환경 오염요인을 해소시킬 수 있도록 된것이다.As described above, in the present invention, in treating wastewater generated in a synthetic resin manufacturing process, the ammonium sulfate contained in the wastewater is recovered in a solidified state in an ammonium sulfate recovery process consisting of a spray dryer and a bag filter, In addition, by treating pyrodine in the incinerator with pyrolysis completely, it can be used for separate purposes by recovering the residual heat of waste gas, and it can recover and use ammonium sulfate as a fertilizer as well as waste water treatment. The system is operated with the decomposition temperature of the incinerator at low temperature, so that economical effects can be obtained and the natural environmental pollution factors caused by wastewater treatment can be eliminated.

Claims (1)

합성수지제조과정에서 발생된 페수가 집수상태로 교반되는 폐수탱크(1)와, 펌프수단(A)의 펌핑력으로 폐수가 공급로로 유도되어 노즐(2)에 분사되고 열풍발생기(3)에서 저온상태의 열풍이 유도되어 분사되는 폐수를 가열증발시켜 페수에 함유된 황산암모늄을 고형화상태로 분리되는 분무건조장치(4)와, 상기 분무건조장치로부터 유도되는 가스에 잔여하고 있는 황산암모늄을 완전히 여과분리하는 여과집진기(5)와, 상기 여과집진기(5)에서 가스가 유도되어 잔여하고 있는 파라딘을 완전연소시켜 분해시키는 소각로(6)와, 상기 소각로(6)의 배기구쪽으로 연도(7)에 연통되게 설치되고 순차적으로 연동되는 폐열회수수단인 열교환기(8) 및 가스세정기(9)와, 상기 소각로(6) 배기측 일측에는 연도(7)와 연통설치되며, 전기적인 제어에 의해 조작되는 조작댐퍼(10)로 이루어져서 된것을 특징으로 하는 합성수지제조시 발생되는 폐수처리시스템.Wastewater tank (1) in which wastewater generated in the synthetic resin manufacturing process is agitated in a collecting state, and wastewater is guided to the supply path by the pumping force of the pump means (A), injected into the nozzle (2), and the low temperature in the hot air generator (3). The spray drying apparatus 4 which separates the ammonium sulfate contained in the waste water into the solidified state by heating and evaporating the wastewater injected by the hot air of the state, and the ammonium sulfate remaining in the gas derived from the spray drying apparatus is completely filtered. The bag filter 5 to be separated, the incinerator 6 to completely burn and decompose the remaining paradine induced by gas in the bag filter 5, and the flue 7 toward the exhaust port of the incinerator 6; The heat exchanger 8 and the gas cleaner 9, which are installed in communication and sequentially interlocked with each other, are connected to the flue 7 on one side of the exhaust side of the incinerator 6, and are operated by electrical control. Operation Damper (10) Yirueojyeoseo waste water treatment system that occur during manufacturing the synthetic resin according to claim to become.
KR1019910019727A 1991-11-07 1991-11-07 Waste water treatment system KR940011824B1 (en)

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KR100389652B1 (en) * 2000-12-04 2003-06-27 주식회사 한국카본 waste water treatment method for wet type special fiber paper manufacturing process and apparatus thereof
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