KR102031920B1 - Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method - Google Patents

Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method

Info

Publication number
KR102031920B1
KR102031920B1 KR1020190066891A KR20190066891A KR102031920B1 KR 102031920 B1 KR102031920 B1 KR 102031920B1 KR 1020190066891 A KR1020190066891 A KR 1020190066891A KR 20190066891 A KR20190066891 A KR 20190066891A KR 102031920 B1 KR102031920 B1 KR 102031920B1
Authority
KR
South Korea
Prior art keywords
ammonium phosphate
waste liquid
gas
hot air
granules
Prior art date
Application number
KR1020190066891A
Other languages
Korean (ko)
Inventor
서시원
Original Assignee
(주)에코이노베이션
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 (주)에코이노베이션 filed Critical (주)에코이노베이션
Priority to KR1020190066891A priority Critical patent/KR102031920B1/en
Application granted granted Critical
Publication of KR102031920B1 publication Critical patent/KR102031920B1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B25/00Phosphorus; Compounds thereof
    • C01B25/16Oxyacids of phosphorus; Salts thereof
    • C01B25/26Phosphates
    • C01B25/28Ammonium phosphates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2/00Processes or devices for granulating materials, e.g. fertilisers in general; Rendering particulate materials free flowing in general, e.g. making them hydrophobic
    • B01J2/02Processes or devices for granulating materials, e.g. fertilisers in general; Rendering particulate materials free flowing in general, e.g. making them hydrophobic by dividing the liquid material into drops, e.g. by spraying, and solidifying the drops
    • B01J2/04Processes or devices for granulating materials, e.g. fertilisers in general; Rendering particulate materials free flowing in general, e.g. making them hydrophobic by dividing the liquid material into drops, e.g. by spraying, and solidifying the drops in a gaseous medium
    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/584Recycling of catalysts
    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/40Valorisation of by-products of wastewater, sewage or sludge processing

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Removal Of Specific Substances (AREA)
  • Treating Waste Gases (AREA)

Abstract

The present invention relates to an apparatus and a method for preparing granules of first ammonium phosphate for recycling ammonium phosphate waste liquid discharged from a semiconductor etching process, which are eco-friendly. The apparatus of the present invention comprises: a plurality of waste liquid collectors; a storage tank; a pH adjusting unit; a buffer; a hot air granulator; a filter dust collector; an oxidation catalyst combustor; and an air cooling heat exchanger.

Description

반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치 및 그 제조공법{Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method}Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method}

본 발명은 제1인산암모늄 과립 제조장치에 관한 것으로서, 특히 인산암모늄 폐액을 수거하여 pH를 조정한 후, 열풍과립기와 여과집진기를 통해 고체 상태로 결정화된 제1인산암모늄 과립을 추출하고, The present invention relates to a first ammonium phosphate granule manufacturing apparatus, in particular, after collecting the ammonium phosphate waste liquid to adjust the pH, the first ammonium phosphate granules crystallized in a solid state through hot air granules and bag filter,

이 과정에서 배출되는 암모니아 가스 및 초산 가스는 촉매산화연소기에서 고온 및 촉매층에 의해 분해한 후, 열교환기 또는 에코너마이저를 통해 폐열을 재이용하면서 가스 성분을 배출기로 외부 방출하는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치에 관한 것이다. The ammonia gas and acetic acid gas discharged in this process are decomposed by the high temperature and catalyst layer in the catalytic combustion furnace, and recycled the ammonium phosphate waste liquid which discharges the gas components to the discharger while reusing the waste heat through a heat exchanger or an economizer. It relates to a first ammonium phosphate granule production apparatus.

액상폐기물은 각종 생산품의 제조, 가공, 세척과정 등의 산업 활동에 따라 필연적으로 발생되어 배출되고 있으며, 그 중 산성 또는 염기성 액상폐기물(폐액)의 경우 국내의 전자산업 발달과 더불어 발생되는 양이 지속적으로 증가하고 있다.Liquid wastes are inevitably generated and discharged according to industrial activities such as manufacturing, processing and washing various products. Among them, acidic or basic liquid wastes (waste liquids) continue to be produced with the development of the domestic electronics industry. Is increasing.

전자산업에서 발생하는 산성 또는 염기성 폐액은 각종 부품의 세척공정, 반도체 및 LCD 에칭공정 등에서 발생되며, 여러 가지 유해한 물질을 다량 함유하고 있으므로, 이러한 산성 또는 염기성 폐액이 그 대로 배출될 경우 토양오염, 수질오염, 악취발생 등의 환경오염 문제를 일으킬 뿐만 아니라, 회수 가능한 자원의 낭비에 의한 경제적인 손실을 수반하게 되므로, 이의 해결을 위한 처리 및 재활용화 기술의 개발이 중요시되고 있다.Acidic or basic wastes generated in the electronics industry are generated in the process of washing various parts, semiconductor and LCD etching process, and contain a large amount of various harmful substances. So, if these acidic or basic wastes are discharged as it is, soil pollution, water quality In addition to the problem of environmental pollution such as pollution, odor generation, and accompanied by economic loss due to the waste of recoverable resources, the development of treatment and recycling technology for solving this is important.

특히, 인산암모늄 폐액은 반도체 식각(에칭) 공정에서 사용하는 불산, 인산, 초산, 질산 등이 유기산 등의 여러 산이 혼합된 산을 이용하여 반도체 제조원관인 웨이퍼(wafer)에 제어용 전극인 게이트를 만들기 위한 공정에서 산화규소부분을 깎아내기 위한 식각(에칭)액으로 사용된다. In particular, the ammonium phosphate waste solution is used to make a gate as a control electrode on a wafer, which is a semiconductor manufacturing tube, using an acid mixed with various acids such as organic acid such as hydrofluoric acid, phosphoric acid, acetic acid, and nitric acid used in a semiconductor etching (etching) process. It is used as an etching solution for scrapping silicon oxide parts in the process.

반도체 에칭용액 중 반응액의 배출방법에 따라 각기 다르나 대체로 인산, 질산, 초산이 혼합된 혼산 용액은 반도체 공업 분야의 중요약품으로 근래 반도체의 생산량이 증가함에 따라 에칭용액의 사용량도 증가되고 있고 따라서 반응폐액도 다량으로 부생되고 있으나 재활용하기 위한 기술은 현재까지 알려져 있는 바가 없다.The mixed acid solution mixed with phosphoric acid, nitric acid, and acetic acid is an important chemical in the semiconductor industry. Recently, the amount of etching solution is increasing as the production of semiconductor increases. Waste fluids are also produced in large quantities, but there is no known technique for recycling.

반도체의 식각(에칭)공정에서 배출되는 가스를 습식 세정시설에서 세정 후 반응된 폐액을 재활용하는 기술은 폐액으로 인한 환경오염 문제를 해소할 수 있고, 자원을 재활용할 수 있는 이점이 있다.The technology of recycling the waste liquid reacted after cleaning the gas discharged from the etching (etching) process of the semiconductor in a wet cleaning facility can solve the environmental pollution problem caused by the waste liquid and has the advantage of recycling resources.

제1인산암모늄은 분말 소화제 및 인산 유기질 비료 등의 원료로 사용된다. Ammonium monophosphate is used as a raw material for powdered extinguishing agents and organic phosphate fertilizers.

종래기술에는 순도 98% 이상의 제1인산암모늄 화합물을 에칭공정 폐액으로부터 제조하는 방법(한국등록특허 10-0436173), 인산계 혼합 폐액을 처리해 인산이수소암모늄의 분말을 얻는 방법(일본공개특허 2016-16375) 등이 선행문헌에 개시되었으나, 위 선행기술들은 고가의 순수 암모니아를 다량 사용하기 때문에 경제성이 떨어지는 문제점이 있었다. In the prior art, a method of preparing a first ammonium phosphate compound having a purity of 98% or more from an etching process waste solution (Korean Patent No. 10-0436173), and a method of treating a phosphoric acid-based mixed waste solution to obtain a powder of ammonium dihydrogen phosphate (Japanese Patent Laid-Open No. 2016- 16375) and the like are disclosed in the prior art, but the prior arts have a problem of low economic feasibility because they use a large amount of expensive pure ammonia.

이를 개선하기 제안된 특허등록 제 1935820호에서는 인산암모늄 폐액에 인산용액을 첨가하여 pH를 조절한 다음, 감압 농축하고 냉각시켜 침전을 유도하는 고순도의 인산이수소암모늄 제조 방법이 공지되었다. In the proposed Patent Registration No. 1935820, a method of preparing ammonium dihydrogen phosphate of high purity is known, in which a pH is adjusted by adding a phosphate solution to an ammonium phosphate waste solution, followed by concentration under reduced pressure and cooling.

그러나, 위 선행기술에서는 감압 농축하고 냉각 침전시키는 과정에 막대한 설비 비용이 소요되는 문제점이 있었다. However, in the above prior art, there is a problem in that enormous equipment costs are required for the process of concentration under reduced pressure and cooling.

본 발명은 상기와 같은 문제점을 해결하기 위한 것으로, 전용 차량에 의해 인산암모늄 폐액을 수거하여 pH를 조정한후, 열풍과립기와 여과집진기를 통해 고체 상태로 결정화된 제1인산암모늄 과립을 추출하고, 열풍과립기에서 분해 배출된 암모니아 가스 및 초산 가스는 촉매산화연소기에서 분해시킨 후, 열교환기 또는 에코노마이저를 통해 폐열을 재이용하여 배출기로 외부 방출하는 반도체 식각(에칭)공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치를 제공함에 그 목적이 있다. The present invention is to solve the above problems, and after collecting the ammonium phosphate waste liquid by a dedicated vehicle to adjust the pH, the first ammonium phosphate granules crystallized in a solid state through hot air granules and bag filter, and hot air The ammonia gas and acetic acid gas decomposed and discharged from the granulator are decomposed in the catalytic oxidation furnace, and the ammonium phosphate waste solution discharged from the semiconductor etching (etching) process, which is discharged to the discharger by recycling waste heat through a heat exchanger or an economizer, is used. It is an object to provide a first ammonium phosphate granule manufacturing apparatus for recycling.

또한, 전처리단계(S10)와, 숙성단계(S20)와, 제1인산암모늄 과립생성단계(S30)와, 가스배출단계(S40)의 간단한 단계별 공정을 통해 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조공법을 제공함에 다른 목적이 있다. In addition, the ammonium phosphate waste solution discharged from the semiconductor etching process through a simple step-by-step process of the pre-treatment step (S10), the aging step (S20), the first ammonium phosphate granules production step (S30), and the gas discharge step (S40). Another object is to provide a manufacturing method of recycling the first ammonium phosphate granules.

본 발명에 의한 다수의 반도체 식각공정에서 획득된 인산암모늄 폐액을 전용 운송차량에 의해 집액하는 복수의 폐액수거기와; 상기 복수의 폐액수거기를 통해 집액된 인산암모늄 폐액을 저장하는 저장탱크와; 상기 저장탱크의 pH를 조정하기 위해 일정량의 알칼리성 물질 또는 산성 물질로 이루어지는 조정성분을 투입하는 pH조정부와; 상기 저장탱크에서 인산암모늄 폐액에 조정성분이 투입된 혼합액을 이송하면서 분할 저장하여 일정시간 대기하는 버퍼와; 상기 버퍼로부터 공급된 혼합액을 분무기(atomizer) 노즐을 통해 초미립자로 분무하면서 열교환기에서 공급되는 열풍에 의해 고온 건조하는 열풍과립기와; 상기 열풍과립기에서 배출되는 가스에서 잔존하는 미세한 제1인산암모늄 과립을 필터를 통해 취득하는 여과집진기와; 상기 열풍과립기에서 고온의 열풍에 의해 분해된 암모니아 가스 및 초산 가스를 직접 연소 및 촉매 분해하여 악취가 제거된 가스를 열교환기로 이송하는 촉매산화연소기와; 상기 촉매산화연소기(80)에서 발생된 가스의 열을 열풍과립기로 전달하여 재활용하고, 냉각된 잔존 가스를 배출기로 이송하는 외기 흡입에 의한 공냉식 열교환기를 포함하여 구성된 것을 그 기술적 특징으로 한다. A plurality of waste liquid collectors for collecting ammonium phosphate waste liquids obtained in a plurality of semiconductor etching processes by a dedicated transport vehicle; A storage tank for storing the ammonium phosphate waste liquid collected through the plurality of waste liquid collectors; A pH adjusting unit for inputting an adjustment component made of a predetermined amount of an alkaline substance or an acidic substance to adjust the pH of the storage tank; A buffer for dividing and storing the mixed liquid in which the adjustment component is added to the ammonium phosphate waste liquid in the storage tank and waiting for a predetermined time; A hot air granulator for hot drying by hot air supplied from a heat exchanger while spraying the mixed liquid supplied from the buffer into ultra-fine particles through an atomizer nozzle; A bag filter for obtaining fine ammonium phosphate granules remaining in the gas discharged from the hot air granulator through a filter; A catalytic oxidation burner which directly burns and catalytically decomposes ammonia gas and acetic acid gas decomposed by hot hot air in the hot air granulator and transfers the gas from which the odor is removed to a heat exchanger; The technical features of the present invention include an air-cooled heat exchanger by intake of outside air which transfers the heat of the gas generated by the catalytic oxidation burner 80 to the hot air granules and recycles it, and transfers the cooled residual gas to the discharger.

또한, 본 발명에 의한 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조방법은 폐액수거기를 통해 인산암모늄 폐액을 집액하여 저장탱크에 저장하고, 인산암모늄 폐액의 pH를 조정하기 위해 pH조정부를 통해 일정량의 알칼리성 물질 또는 산성 물질을 포함하는 조정성분을 투하하여 pH를 6∼7로 조정하는 전처리단계(S10)와; 상기 인산암모늄 폐액에 조정성분이 투입된 혼합액을 복수의 버퍼로 이송하면서 분할 저장하여 일정시간 대기하는 숙성단계(S20)와; 숙성된 혼합액을 열풍과립기를 통해 고온 건조하여 결정화된 제1인산암모늄 과립을 추출하고, 여과집진기에서 필터를 통해 열풍과립기에서 미처 추출되지 못한 제1인산암모늄 과립을 재추출하면서 암모니아 가스 및 초산 가스를 배출하는 제1인산암모늄 과립 생성단계(S30)와; 상기 여과집진기(70)에서 배출된 암모니아 가스 및 초산 가스를 촉매산화연소기에서 고온으로 직접 연소 및 촉매분해하여 악취성분을 제거한 깨끗한 가스(clean gas)를 배출기(100)을 통해 외부로 방출하는 가스배출단계(S40)가 순차적으로 진행되는 것을 그 기술적 특징으로 한다. In addition, the first method for producing ammonium phosphate granules for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process according to the present invention collects the ammonium phosphate waste liquid through a waste liquid collector and stores it in a storage tank to adjust the pH of the ammonium phosphate waste liquid. A pretreatment step (S10) of adjusting the pH to 6 to 7 by dropping a control component containing a predetermined amount of an alkaline substance or an acidic substance through a pH adjusting unit; A maturation step (S20) of dividing and storing the mixed solution in which the adjustment component is added to the ammonium phosphate waste liquid and waiting for a predetermined time; The matured mixed liquor was dried at high temperature through a hot air granulator to extract the crystallized ammonium phosphate granules, and the ammonia gas and the acetic acid gas were reextracted the first ammonium phosphate granules which were not extracted from the hot air granulator through a filter in a filter bag. First ammonium phosphate granules producing step (S30) and the discharge; Ammonia gas and acetic acid gas discharged from the bag filter 70 are directly discharged and catalytically decomposed to a high temperature in a catalytic oxidizer to remove odor components and clean gas discharged to the outside through the discharger 100. It is a technical feature that step S40 proceeds sequentially.

본 발명에 의한 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치는 인산암모늄 폐액을 수거하여 pH를 조정한후, 열풍과립기와 여과집진기를 통해 고체 상태로 결정화된 제1인산암모늄 과립을 간단하게 추출할 수 있으므로, 2단계의 추출공정을 통해 제1인산암모늄 과립의 추출율을 대폭적으로 향상시킬 수 있으며, 잔여 가스성분은 촉매산화연소기를 통해 고온에서 직접 연소 및 촉매분해하여 악취성분인 암모니성 가스 및 초산 가스를 제거한 후 배출기로 외부 방출하므로 친환경적인 효과와 함께 열교환기를 통한 폐열 재활용의 효과가 있다.The first ammonium phosphate granules manufacturing apparatus for recycling the ammonium phosphate waste liquid according to the present invention collects the ammonium phosphate waste liquid and adjusts its pH, and then simply extracts the first ammonium phosphate granules crystallized in a solid state through hot air granules and a bag filter. Therefore, the extraction rate of the first ammonium phosphate granules can be greatly improved through the two-step extraction process, and the residual gas component is directly burned and catalytically decomposed at a high temperature through a catalytic oxidizer to produce ammonia gas, which is an odor component, and Since acetic acid is removed and then discharged to the discharger, there is an eco-friendly effect and waste heat recycling through a heat exchanger.

도 1은 본 발명에 의한 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치의 블록도,
도 2는 본 발명의 일 실시예로서, 폐액수거기와 저장탱크의 구성도,
도 3은 본 발명의 일 실시예로서, 버퍼의 구성도,
도 4는 본 발명의 일 실시예로서, 인사과립을 추출하는 열풍과립기 및 여과집진기와, 암모니아 가스 및 초산 가스를 연소 및 촉매분해하는 촉매산화연소기 및 열교환기를 개략적으로 나타낸 구성도,
도 5는 본 발명에 의한 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조방법을 개략적으로 나타낸 공정 단계도.
1 is a block diagram of a first ammonium phosphate granule manufacturing apparatus for recycling ammonium phosphate waste liquid discharged from a semiconductor etching process according to the present invention;
2 is an embodiment of the present invention, the configuration of the waste liquid collector and the storage tank,
3 is a block diagram of a buffer according to an embodiment of the present invention;
4 is a configuration diagram schematically showing a hot air granulator and bag filter for extracting human granules, a catalytic oxidation burner and a heat exchanger for burning and catalytic decomposition of ammonia gas and acetic acid gas, as an embodiment of the present invention;
Figure 5 is a process step schematically showing a first ammonium phosphate granules manufacturing method for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process according to the present invention.

본 발명의 바람직한 실시 예를 첨부된 도면을 통해 상세히 설명한다.Preferred embodiments of the present invention will be described in detail with reference to the accompanying drawings.

본 발명에 의한 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치는 도 1에 도시된 바와 같이, 인산암모늄 폐액을 수거하여 소정의 처리과정을 거치는 공정을 위해 폐액수거기(10)와 저장탱크(20)와 pH조정부(30) 및 버퍼(40)가 구비되고, 열풍건조 및 기필터에 의해 고체 결정화된 제1인산암모늄 과립을 추출하기 위해 열풍과립기(50)와 제1인산암모늄 과립포집기(60) 및 여과집진기(70)가 구비되고, 깨끗한 가스(clean gas)를 배출하기 위해 촉매산화연소기(80)와 폐열을 재활용하는 열교환기(90) 및 배출기(100)을 포함하는 다수의 설비장치들이 연계되어 있다. The first ammonium phosphate granule manufacturing apparatus for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process according to the present invention, as shown in Figure 1, the waste liquid collector for the process of collecting the ammonium phosphate waste liquid through a predetermined treatment process 10, a storage tank 20, a pH adjusting unit 30 and a buffer 40, and hot air granulator 50 to extract solid ammonium phosphate granules crystallized by hot air drying and a gas filter. A first ammonium phosphate granular collector (60) and a bag filter (70) are provided, and the heat exchanger (90) and the discharger (100) for recycling the catalytic oxidation furnace (80) and waste heat to discharge clean gas (clean gas). A plurality of installations, including a is connected.

먼저, 폐액수거기(10)에서는 도 2의 'Ⅰ'의 공정으로 도시된 바와 같이, 반도체 식각공정에서 획득된 인산암모늄 폐액을 전용 운송차량에 의해 집액하고, 상기 복수의 폐액수거기(10)를 통해 집액된 인산암모늄 폐액은 저장탱크(20)에 저장된다. First, in the waste liquid collector 10, the ammonium phosphate waste liquid obtained in the semiconductor etching process is collected by a dedicated transport vehicle, as shown by the process of 'I' of FIG. 2, and the plurality of waste liquid collectors 10 are collected. The ammonium phosphate waste liquid collected through is stored in the storage tank 20.

상기 저장탱크(20)의 pH를 조정하기 위해 pH조정부(30)에서는 일정량의 알칼리성 물질 또는 산성 물질로 이루어지는 조정성분을 저장탱크(20)의 내부로 투입하게 된다. In order to adjust the pH of the storage tank 20, the pH adjusting unit 30 is introduced into the storage tank 20 of the adjustment component consisting of a predetermined amount of an alkaline substance or an acidic substance.

본 발명의 일 실시예로, 상기 pH조정부(30)에서는 알칼리성 물질로서 가성 소다를 사용하고, 산성 물질로서 황산을 사용하여, 인산암모듐 폐액과의 혼합액 pH를 6 ∼7로 조정한다. In one embodiment of the present invention, the pH adjuster 30 adjusts the pH of the mixed liquid with the ammonium phosphate waste liquid to 6-7 using caustic soda as the alkaline substance and sulfuric acid as the acidic substance.

또한, 상기 저장탱크(20)에서 인산암모늄 폐액에 조정성분이 투입된 혼합액은 도 3의 'Ⅱ'의 공정으로 도시된 바와 같이, 복수의 버퍼(40)로 이송되어 분할 저장되고, 일정시간 대기하여 숙성된다. In addition, the mixed liquid in which the adjustment component is added to the ammonium phosphate waste liquid in the storage tank 20 is transferred to a plurality of buffers 40, divided and stored as shown in the process of 'II' of FIG. It is aged.

이는 혼합액이 충분한 화학반응을 일으켜서, 후술하는 열풍 건조시 보다 효율적으로 고체 결정화되도록 하는 것으로서, 4시간 정도 숙성되는 것이 바람직하다. This allows the mixed solution to cause sufficient chemical reaction, so that the solid crystallization more efficiently during hot air drying described later, and preferably aged for about 4 hours.

상기 버퍼(40)에서는 공급된 혼합액은 도 4의 'Ⅲ'의 공정으로 도시된 바와 같이, 열풍과립기(50)에서 분무기(atomizer) 노즐을 통해 초미립자로 분무하면서 열교환기(90)에서 공급되는 300∼350℃의 고온 열풍에 의해 건조되어 과립상태의 분말로 결정화되며, 고체 결정화된 제1인산암모늄 과립은 하부에 구비된 제1인산암모늄 과립포집기(60)로 추출된다. The mixed liquid supplied from the buffer 40 is supplied from the heat exchanger 90 while spraying the ultrafine particles through the atomizer nozzle in the hot air granulator 50 as shown in the process of 'III' of FIG. 4. It is dried by high temperature hot air of 300-350 ° C. to crystallize into granular powder, and the solid crystallized first ammonium phosphate granules are extracted by the first ammonium phosphate granular collector 60 provided below.

이때, 열풍 건조(과립)과정에서 발생한 가스중에는 미세한 제1인산암모늄 분말이 잔존하고 있으므로, 다시 여과집진기(70)로 전송된다. At this time, since the fine ammonium phosphate powder remains in the gas generated during the hot air drying (granulation) process, it is transmitted to the bag filter 70 again.

상기 여과집진기(70)에서는 필터를 통해 고체성분인 제1인산암모늄 과립을 하부에 구비된 제1인산암모늄 과립포집기(60)로 추출하며, 제1인산암모늄 성분이 전부 제거된 가스를 다시 촉매산화연소기(80)로 이송한다. In the bag filter 70, the first ammonium phosphate granules, which are solid components, are extracted through a filter into the first ammonium phosphate granulator collector 60 provided below, and the catalyst is completely catalytically oxidized. Transfer to the combustor (80).

상기 촉매산화연소기(80)에서는 상기 열풍과립기(50)에서 발생된 암모니아 가스 및 초산 가스를 다시 450℃ 이상의 고온으로 촉매 산화분해하면서 악취성분을 제거하고, 악취성분이 제거된 깨끗한 가스는 열교환기(90)로 이송된다.
상기 암모니아(NH3) 가스 및 초산(CH3COOH) 가스는 폐액에 함유되어 있는 암모니아 성분 및 초산 성분이 초 미립자상태로 분사된 후, 열풍에 의해 가스형태로 배출되는 가스를 의미하며, 이와 같은 암모니아 가스 및 초산 가스는 설비주변에 악취오염의 주원인이 되므로, 본 발명에서는 촉매산화연소기(80)에서 제거하여 대기로 깨끗한 공기를 배출하고자 제안된 것이다.
The catalytic oxidation burner (80) removes the odor component while catalytic oxidative decomposition of the ammonia gas and the acetic acid gas generated in the hot air granulator (50) at a high temperature of 450 ℃ or more, and the clean gas from which the odor component is removed is a heat exchanger. Is transferred to 90.
The ammonia (NH 3 ) gas and acetic acid (CH 3 COOH) gas refers to a gas which is discharged in the form of gas by hot air after the ammonia component and the acetic acid component contained in the waste liquid are injected into the superfine particle state. Since ammonia gas and acetic acid gas are the main causes of odor pollution around the equipment, the present invention is proposed to remove clean air from the catalytic oxidizer 80 to discharge clean air to the atmosphere.

상기 열교환기(90)는 공냉식에 의해 고온의 가스를 냉각하게 되며, 상온의 외부공기를 가스의 폐열로 약 300∼350℃ 정도로 승온시켜 열풍과립기(50)로 전달하는 방식으로 폐열을 재활용하게 하며, 냉각된 깨끗한 가스는 연돌이 구비된 배출기(100)를 통해 외부로 방출된다. The heat exchanger 90 cools the gas at high temperature by air cooling, and heats the ambient air at room temperature to about 300 to 350 ° C. with the waste heat of the gas to recycle the waste heat to the hot air granulator 50. In addition, the cooled clean gas is discharged to the outside through the ejector 100 having the stack.

상기 연돌(chimney)(煙突)은 연소설비에 의해서 통풍 배연 및 배기가스의 확산, 희석을 목적으로 하는 부속설비로서, 본 발명에서는 송풍기와 소음기를 구비하여 깨끗한 가스를 소음없이 효과적으로 방출하도록 설계되었다. The chimney is an accessory device for the purpose of diffusion and dilution of ventilation flue gas and exhaust gas by a combustion facility. In the present invention, a blower and a silencer are provided to effectively discharge clean gas without noise.

본 발명의 다른 실시예로, 상기 열교환기(90)의 후단에는 별도로 에코노마이저(economizer)(91)가 부가될 수 있다. In another embodiment of the present invention, an economizer 91 may be separately added to the rear end of the heat exchanger 90.

상기 에코노마이저는(91)는 보일러의 열손실의 가장 많은 부분을 차지하는 연도 가스의 열을 이용해서 급수를 예열하는 장치로서, 온수를 이용하는 시설에 제공할 수 있다.The economizer 91 is a device for preheating the water supply using the heat of the flue gas that occupies the most part of the heat loss of the boiler, it can be provided to the facility using hot water.

한편, 본 발명에 의한 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치의 인사과립 제조공법은 도 5에 도시된 바와 같은 단계별 공정에 의해 진행된다. On the other hand, the granule manufacturing method of the first ammonium phosphate granule manufacturing apparatus for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process according to the present invention is carried out by a step-by-step process as shown in FIG.

먼저, 폐액수거기(10)를 통해 인산암모늄 폐액을 집액하여 저장탱크(20)에 저장하고, 인산암모늄 폐액의 pH를 조정하기 위해 pH조정부(30)를 통해 일정량의 알칼리성 물질 또는 산성 물질을 포함하는 조정성분을 투하하여 pH를 6∼7로 조정하는 전처리단계(S10)가 진행된다. First, the ammonium phosphate waste liquid is collected through the waste liquid collector 10 and stored in the storage tank 20, and a predetermined amount of alkaline or acidic substance is included through the pH adjusting unit 30 to adjust the pH of the ammonium phosphate waste liquid. The pretreatment step (S10) of adjusting the pH to 6-7 is carried out by dropping the adjusting component.

이때, 상기 pH조정부(30)에서는 가성소다를 사용하여 인산암모듐 폐액의 pH를 조정하게 되는데, 알칼리성이 과도하면 다시 황산을 사용하여, 최종적으로 인산암모듐 폐액과의 혼합액 pH를 6 ∼7로 조정하게 된다. At this time, the pH adjuster 30 adjusts the pH of the ammonium phosphate waste liquid by using caustic soda. When the alkalinity is excessive, sulfuric acid is used again to finally adjust the pH of the mixed liquid with the ammonium phosphate waste liquid to 6-7. Will be adjusted.

이어서, 상기 인산암모늄 폐액에 조정성분이 투입된 혼합액을 복수의 버퍼(40)로 이송하면서 분할 저장하여 일정시간 대기하는 숙성단계(S20)가 진행된다. Subsequently, a ripening step (S20) of dividing and storing the mixed solution in which the adjustment component is added to the ammonium phosphate waste liquid and waiting for a predetermined time is performed.

또한, 숙성된 혼합액을 열풍과립기(50)를 통해 고온 건조하여 결정화된 제1인산암모늄 과립을 추출하면서 여과집진기(70)로 1차 가스를 이송하고, 필터를 통해 다시 제1인산암모늄 과립을 추출하면서 2차 가스를 배출하는 제1인산암모늄 과립 생성단계(S30)가 진행된다. In addition, the matured mixed solution is dried at a high temperature through the hot air granulator 50 to extract the first crystallized ammonium phosphate granules, and then, the primary gas is transferred to the bag filter 70, and the first ammonium phosphate granules are again passed through the filter. While extracting the first ammonium phosphate granules generating step (S30) to discharge the secondary gas is in progress.

마지막으로, 상기 여과집진기(70)에서 배출된 암모니아 가스 및 초산 가스를 촉매산화연소기(80)에서 고온으로 가열 및 촉매에 의해 산화분해하여 악취를 제거하고, 상기 악취가 제거된 고온의 가스를 열교환기(90)를 통해 폐열을 재활용하면서 깨끗한 가스(clean gas)를 배출기(100)을 통해 외부로 방출하는 가스배출단계(S40)가 진행된다. Finally, the ammonia gas and the acetic acid gas discharged from the bag filter 70 is heated to a high temperature in the catalytic combustion furnace 80 and oxidatively decomposed by a catalyst to remove odors, and the high-temperature gas from which the odors are removed is heat-exchanged. The gas discharge step (S40) of discharging clean gas to the outside through the discharger 100 while recycling waste heat through the gas 90 is performed.

이때, 상기 촉매산화연소기(80)에서 450℃ 이상의 고온 및 촉매반응이 진행되며, 열교환기(90)에서는 고온의 가스가 약 300℃ 이하로 냉각되어 배출기(100)로 이송된다.At this time, a high temperature and a catalytic reaction of 450 ° C. or higher is performed in the catalytic oxidation combustor 80, and a high temperature gas is cooled to about 300 ° C. or lower in the heat exchanger 90, and then transferred to the discharger 100.

. .

상기 열교환기(90)는 외기 흡입에 의한 공냉식으로 구성되어 가스를 냉각함과 동시에 상온의 공기를 열교환에 의해 350℃ 이상으로 승온시켜 폐열을 재활용하게 되며, 열풍과립기(50)로 전달하여 열풍과립기(50)의 열온으로 재활용하게 되는 것이다. The heat exchanger (90) is configured by air cooling by intake of outside air to cool the gas and at the same time increase the temperature of air at 350 ° C or higher by heat exchange to recycle waste heat, and transfer it to the hot air granulator (50). It will be recycled to the heat temperature of the granulator 50.

10 : 폐액수거기 20 : 저장탱크
30 : pH조정부 40 : 버퍼
50 : 열풍과립기 60 : 제1인산암노늄 과립 포집기
70 : 여과집진기 80 : 촉매산화연소기
90 : 열교환기 91 : 에코노마이저
100: 배출기
10: waste liquid collector 20: storage tank
30: pH adjuster 40: buffer
50: hot air granulator 60: monoammonium phosphate granular collector
70: bag filter 80: catalytic oxidation burner
90 heat exchanger 91 economizer
100: ejector

Claims (8)

다수의 반도체 식각공정에서 획득된 인산암모늄 폐액을 전용 운송차량에 의해 집액하는 복수의 폐액수거기(10)와;
상기 복수의 폐액수거기(10)를 통해 집액된 인산암모늄 폐액을 저장하는 저장탱크(20)와;
상기 저장탱크(20)의 pH를 조정하기 위해 일정량의 알칼리성 물질 또는 산성 물질로 이루어지는 조정성분을 투입하는 pH조정부(30)와;
상기 저장탱크(20)에서 인산암모늄 폐액에 조정성분이 투입된 혼합액을 이송하면서 분할 저장하여 일정시간 대기하는 버퍼(40)와;
상기 버퍼(40)로부터 공급된 혼합액을 분무기(atomizer) 노즐을 통해 초미립자로 분무하면서 열교환기(90)에서 공급되는 열풍에 의해 고온 건조하는 열풍과립기(50)와;
상기 열풍과립기(50)에서 배출되는 가스에서 잔존하는 미세한 제1인산암모늄 과립을 필터를 통해 취득하는 여과집진기(70)와;
상기 열풍과립기(50)에서 고온의 열풍에 의해 분해된 암모니아 가스 및 초산 가스를 직접 연소 및 촉매 분해하여 악취가 제거된 가스를 열교환기(90)로 이송하는 촉매산화연소기(80)와;
상기 촉매산화연소기(80)에서 발생된 가스의 열을 열풍과립기(50)로 전달하여 재활용하고, 냉각된 잔존 가스를 배출기(100)로 이송하는 외기 흡입에 의한 공냉식 열교환기(90);
를 포함하여 구성된 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치.
A plurality of waste liquid collectors 10 for collecting ammonium phosphate waste liquids obtained in a plurality of semiconductor etching processes by a dedicated transport vehicle;
A storage tank 20 for storing the ammonium phosphate waste liquid collected through the plurality of waste liquid collectors 10;
A pH adjusting unit 30 for inputting an adjustment component made of a predetermined amount of an alkaline substance or an acidic substance to adjust the pH of the storage tank 20;
A buffer (40) for storing a portion of the storage tank (20) by dividing and storing the mixed liquid in which the adjustment component is added to the wastewater of ammonium phosphate;
A hot air granulator (50) for drying at high temperature by hot air supplied from a heat exchanger (90) while spraying the mixed liquid supplied from the buffer (40) into an ultrafine particle through an atomizer nozzle;
A bag filter (70) for obtaining fine first ammonium phosphate granules remaining in the gas discharged from the hot air granulator (50) through a filter;
A catalytic oxidizer (80) for directly burning and catalytically decomposing ammonia gas and acetic acid gas decomposed by hot air granules in the hot air granulator (50) and transferring the gas from which odor is removed to a heat exchanger (90);
An air-cooled heat exchanger (90) by suctioning outside air to transfer heat of the gas generated by the catalytic oxidation burner (80) to the hot air granulator (50) for recycling, and to transfer the cooled residual gas to the discharger (100);
The first ammonium phosphate granules manufacturing apparatus for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process comprising a.
제 1항에 있어서,
상기 pH조정부(30)에서는 알칼리성 물질로서 가성소다를 사용하고, 산성 물질로서 황산을 사용하여,
인산암모듐 폐액과의 혼합액 pH를 6 ∼7로 조정하는 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치.
The method of claim 1,
In the pH adjusting unit 30, caustic soda is used as an alkaline substance and sulfuric acid is used as an acidic substance.
A first ammonium phosphate granule manufacturing apparatus for recycling ammonium phosphate waste liquid discharged from a semiconductor etching process, characterized in that the mixed liquid pH with the ammonium phosphate waste liquid is adjusted to 6-7.
제 1항에 있어서,
상기 열풍과립기(50)와 여과집진기(70)의 하측에는 고체 결정화된 제1인산암모늄 과립을 수거하는 제1인산암모늄 과립 포집기(60)가 설치된 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치.
The method of claim 1,
Ammonium phosphate discharged from the semiconductor etching process, characterized in that the first ammonium phosphate granular collector 60 for collecting solid crystallized first ammonium phosphate granules is installed below the hot air granulator 50 and the bag filter 70. A first ammonium phosphate granule production apparatus for recycling waste liquid.
제 1항에 있어서,
상기 열풍과립기(50)에서는 300∼350℃의 고온으로 건조하여 결정화된 제1인산암모늄 과립을 추출하면서 암모니아 가스 및 초산 가스를 생성하고,
상기 촉매산화연소기(80)에서는 여과집진기(70)를 통과한 암모니아 가스 및 초산 가스를 다시 450℃ 이상의 고온으로 직접 연소 및 촉매 분해하여 악취를 제거하는 것을 특징으로 하는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치.
The method of claim 1,
The hot air granulator 50 is dried at a high temperature of 300 ~ 350 ℃ to extract the crystallized ammonium phosphate granules to produce ammonia gas and acetic acid gas,
The catalytic oxidation burner (80) is a first to recycle the ammonium phosphate waste liquid, characterized in that the ammonia gas and the acetic acid gas passing through the bag filter 70 to directly burn and catalytic decomposition again to a high temperature of 450 ℃ or more to remove the odor Ammonium phosphate granule production apparatus.
제 1항에 있어서,
상기 열교환기(90)의 후단에는 에코너마이저(economizer)(91)가 부가되어, 폐열에 의해 온수를 생성할 수 있도록 구성된 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조장치.
The method of claim 1,
The first stage of recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process, characterized in that the economizer (91) is added to the rear end of the heat exchanger (90) to generate hot water by waste heat. Ammonium phosphate granule production apparatus.
폐액수거기(10)를 통해 인산암모늄 폐액을 집액하여 저장탱크(20)에 저장하고, 인산암모늄 폐액의 pH를 조정하기 위해 pH조정부(30)를 통해 일정량의 알칼리성 물질 또는 산성 물질을 포함하는 조정성분을 투하하여 pH를 6∼7로 조정하는 전처리단계(S10)와;
상기 인산암모늄 폐액에 조정성분이 투입된 혼합액을 복수의 버퍼(40)로 이송하면서 분할 저장하여 일정시간 대기하는 숙성단계(S20)와;
숙성된 혼합액을 열풍과립기(50)를 통해 고온 건조하여 결정화된 제1인산암모늄 과립을 추출하고, 여과집진기(70)에서 필터를 통해 열풍과립기(50)에서 미처 추출되지 못한 제1인산암모늄 과립을 재추출하면서 암모니아 가스 및 초산 가스를 배출하는 제1인산암모늄 과립 생성단계(S30)와;
상기 여과집진기(70)에서 배출된 암모니아 가스 및 초산 가스를 촉매산화연소기(80)에서 고온으로 직접 연소 및 촉매분해하여 악취성분을 제거한 깨끗한 가스(clean gas)를 배출기(100)을 통해 외부로 방출하는 가스배출단계(S40);
가 순차적으로 진행되는 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조방법.
The ammonium phosphate waste liquid is collected through the waste liquid collector 10 and stored in the storage tank 20, and an adjustment including a predetermined amount of alkaline or acidic substance through the pH adjusting unit 30 to adjust the pH of the ammonium phosphate waste liquid. A pretreatment step (S10) of dropping the components to adjust the pH to 6-7;
A ripening step (S20) of dividing and storing the mixed liquid into which the adjustment component is added to the ammonium phosphate waste liquid and waiting for a predetermined time;
The matured mixed solution was dried at high temperature through the hot air granulator 50 to extract the crystallized ammonium phosphate granules, and the first ammonium phosphate that was not extracted from the hot air granulator 50 through the filter in the bag filter 70. Generating a first ammonium phosphate granule (S30) for discharging the ammonia gas and the acetic acid gas while re-extracting the granules;
Ammonia gas and acetic acid gas discharged from the bag filter 70 are directly burned and catalytically decomposed at a high temperature in the catalytic oxidation furnace 80 to release clean gas from which the odor component is removed to the outside through the discharger 100. A gas discharge step (S40);
Method for producing a first ammonium phosphate granules for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process characterized in that proceeding sequentially.
제 6항에 있어서,
상기 촉매산화연소기(80)에서 450℃ 이상의 고온 및 촉매에 의해 분해된 암모니아 가스 및 초산 가스는 열교환기(90)를 통해 300℃이하로 냉각되어 배출기(100)로 외부 방출되는 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조방법.
The method of claim 6,
The ammonia gas and the acetic acid gas decomposed by the catalyst at a high temperature of 450 ° C. or higher and the catalyst in the catalytic oxidation furnace 80 are cooled to 300 ° C. or less through the heat exchanger 90, and are externally discharged to the discharger 100. A method for producing primary ammonium phosphate granules for recycling ammonium phosphate waste liquid discharged from an etching process.
제 7항에 있어서,
상기 열교환기(90)는 외기 흡입에 의한 공냉식으로 구성되고, 촉매산화연소기(80)의 고온 가스에서 발생되는 폐열에 의해 상온의 공기를 300℃ 이상으로 승온시켜 열풍과립기(50)의 에너지원으로 공급하는 것을 특징으로 하는 반도체 식각공정에서 배출되는 인산암모늄 폐액을 재활용하는 제1인산암모늄 과립 제조방법.
The method of claim 7, wherein
The heat exchanger 90 is configured by air cooling by intake of outside air, and heats the air at room temperature to 300 ° C. or more by using waste heat generated from the hot gas of the catalytic combustion engine 80, thereby making it an energy source of the hot air granulator 50. Method for producing a first ammonium phosphate granules for recycling the ammonium phosphate waste liquid discharged from the semiconductor etching process, characterized in that the supply to.
KR1020190066891A 2019-06-05 2019-06-05 Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method KR102031920B1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
KR1020190066891A KR102031920B1 (en) 2019-06-05 2019-06-05 Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
KR1020190066891A KR102031920B1 (en) 2019-06-05 2019-06-05 Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method

Publications (1)

Publication Number Publication Date
KR102031920B1 true KR102031920B1 (en) 2019-10-14

Family

ID=68171376

Family Applications (1)

Application Number Title Priority Date Filing Date
KR1020190066891A KR102031920B1 (en) 2019-06-05 2019-06-05 Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method

Country Status (1)

Country Link
KR (1) KR102031920B1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102131679B1 (en) * 2020-03-02 2020-07-09 (주)에코이노베이션 Waste fluid treatment apparatus containing salt and method for treating same

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20110083112A (en) * 2010-01-13 2011-07-20 로하스텍(주) High fumctional amino acid power, fertilizer mauufacturing device

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20110083112A (en) * 2010-01-13 2011-07-20 로하스텍(주) High fumctional amino acid power, fertilizer mauufacturing device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102131679B1 (en) * 2020-03-02 2020-07-09 (주)에코이노베이션 Waste fluid treatment apparatus containing salt and method for treating same

Similar Documents

Publication Publication Date Title
WO2022110803A1 (en) Flue gas treatment system for hazardous waste incineration, and flue gas treatment method for hazardous waste incineration
KR102031920B1 (en) Manufacturing apparatus for pHospHoric acid granules recycling waste ammonium pHospHate and its manufacturing method
CN108502880A (en) A kind of phosphoric acid method prepares the environment-protective process of activated carbon
CN112898999A (en) Catalytic pyrolysis-oxidation multi-stage furnace treatment integrated device and method for waste salt containing organic pollutants
JP2008272720A (en) Polluted soil treatment system using waste heat
JP2000506062A (en) Desulfurization method and apparatus by electron beam irradiation
CN110332552B (en) Resourceful treatment system and method for chlorine-sulfur-containing organic waste liquid
CN109099437B (en) Comprehensive waste treatment system and treatment method thereof
CN212025143U (en) Contain Cu industrial sludge danger useless resourceful treatment system
CN106268230A (en) A kind of waste heat of coke-oven flue gas reclaim and purify system and technique
CN112390451A (en) Waste water treatment process generated in waste acrylic regeneration and recovery process
CN209934459U (en) Be applied to flue gas purification system of desorption in soil remediation heat
KR101634649B1 (en) Process for steel treatment and steel treatment plant
CN217235616U (en) Waste gas and waste liquid incineration and recovery processing device containing chlorosilane
CN110631032A (en) High-salt organic waste liquid incineration treatment system and method
KR102131679B1 (en) Waste fluid treatment apparatus containing salt and method for treating same
CN211204070U (en) High organic waste liquid incineration disposal system that contains salt
CN110926227B (en) Smelting furnace smoke dust collecting and treating method
CN111925840A (en) Synthetic gas purification method of plasma gasification melting furnace
CN101746737A (en) Preparation method and device of sulfuric acid
CN217356908U (en) Incineration treatment system containing high-COD sodium sulfate wastewater
CN111116006A (en) Circulating regenerative sludge treatment system and method
CN214147894U (en) Tail gas purification equipment suitable for rural domestic waste low temperature pyrolysis treatment
CN214147897U (en) Tail gas purifying equipment suitable for domestic waste pyrolysis treatment
CN216513678U (en) Paint slag harmless treatment device

Legal Events

Date Code Title Description
E701 Decision to grant or registration of patent right
GRNT Written decision to grant