KR20010037075A - Sludge dry-plant - Google Patents

Sludge dry-plant Download PDF

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Publication number
KR20010037075A
KR20010037075A KR1019990044372A KR19990044372A KR20010037075A KR 20010037075 A KR20010037075 A KR 20010037075A KR 1019990044372 A KR1019990044372 A KR 1019990044372A KR 19990044372 A KR19990044372 A KR 19990044372A KR 20010037075 A KR20010037075 A KR 20010037075A
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South Korea
Prior art keywords
drying
sludge
exhaust gas
unit
dry
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KR1019990044372A
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Korean (ko)
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한상일
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한상일
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Priority to KR1019990044372A priority Critical patent/KR20010037075A/en
Publication of KR20010037075A publication Critical patent/KR20010037075A/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/13Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F26DRYING
    • F26BDRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
    • F26B1/00Preliminary treatment of solid materials or objects to facilitate drying, e.g. mixing or backmixing the materials to be dried with predominantly dry solids
    • F26B1/005Preliminary treatment of solid materials or objects to facilitate drying, e.g. mixing or backmixing the materials to be dried with predominantly dry solids by means of disintegrating, e.g. crushing, shredding, milling the materials to be dried
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F26DRYING
    • F26BDRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
    • F26B25/00Details of general application not covered by group F26B21/00 or F26B23/00
    • F26B25/005Treatment of dryer exhaust gases
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F26DRYING
    • F26BDRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
    • F26B3/00Drying solid materials or objects by processes involving the application of heat
    • F26B3/02Drying solid materials or objects by processes involving the application of heat by convection, i.e. heat being conveyed from a heat source to the materials or objects to be dried by a gas or vapour, e.g. air
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/002Construction details of the apparatus
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/02Temperature
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F26DRYING
    • F26BDRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
    • F26B2200/00Drying processes and machines for solid materials characterised by the specific requirements of the drying good
    • F26B2200/18Sludges, e.g. sewage, waste, industrial processes, cooling towers
    • 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
    • Y02W10/20Sludge processing

Abstract

PURPOSE: A sewage sludge drying plant is provided, to prevent air pollution due to dioxin, odor generation by reclamation and underground water pollution caused by heavy metals and harmful microbes and to recycle the sludge particles containing Si02, Al2O3, Fe2O3, and CaO in large quantities as a cement source. CONSTITUTION: The sewage sludge drying plant comprises: i) a drying-crushing part(100) that controls cake-form sludge to 400-650deg.C using a multiple-hearth furnace or a direct rotary kiln and repeats drying and crushing for water content to reach 70-80%; ii) a conveying part(200) that dries the sludge particles at low temperature and conveys them; iii) a drying silo(300) that crushes the sludge particles and dries them by variation in air current; iv) a centrifugal classifier(400) separating dust emitted from the drying-crushing part(100) and the drying silo(300); v) a wet scrubber(500) purifying odor and noxious exhaust gas using sodium hydroxide; vi) a condenser(600) cooling the purified gas to normal temperature; and vii) an exhaust gas measuring part(700) discharging odor and dust contained in the exhaust gas of normal temperature into the air.

Description

오폐수슬러지의 건조처리장치{Sludge dry-plant}Sludge dry-plant

본 발명은 생활하수 및 폐수처리장에서 발생되는 슬러지를 건조처리하고 SiO₂,Al₂O₃,Fe₂O₃,CaO,가 다량 함유된 슬러지분말을 시멘트원료로 공급하여 재활용할수 있는 환경친화적인 오폐수슬러지의 건조처리장치에 관한 것이다.The present invention relates to an environmentally friendly wastewater sludge drying treatment apparatus that can dry and recycle sludge generated in domestic sewage and wastewater treatment plants and supply sludge powder containing a large amount of SiO₂, Al₂O₃, Fe₂O₃, CaO as a cement raw material. will be.

경제발전 및 생활의 향상은 생활 하수나 공업폐수발생의 증가를 초래하고, 이에 따라 생활하수나 공장폐수처리에서 발생되는 슬러지(sludge;汚尼)량도 증가하게되어 이의 처리방법이 환경문제로 대두되고 있다.Economic development and improvement of life lead to an increase in domestic sewage and industrial wastewater, and the amount of sludge generated from domestic sewage and factory wastewater treatment also increases, and its treatment method becomes an environmental problem. It is becoming.

현재까지 슬러지의 처리방법으로 유동상식 소각방법, 스토커식 소각방법 등 폐기물을 소각시키는 몇가지 소각방법이 개발되어 있으나, 상기의 소각방법에 의할 경우 시설투자비가 과다하게 소요되며 처리량이 제한되고, 소각할때 건조효율이 낮아 소각온도가 낮아지게 되어 인체에 유해한 중금속의 휘산(揮散)과 다이옥신 등이 발생할 염려가 있다.Until now, several incineration methods have been developed to incinerate wastes such as sludge disposal methods and stalker incineration methods.However, the above incineration methods require excessive facility investment costs and limited throughput. When the drying efficiency is low when the incineration temperature is lowered, there is a fear that the volatilization and dioxins of heavy metals harmful to the human body may occur.

또한, 슬러지의 매립방식은 수분이 많이 함유된 슬러지에 의해 악취발생으로 매립장주변 지역주민들에 의한 집단민원이 발생하고 있고, 매립으로 발생하는 침출수에는 다량의 중금속과 유해한 미생물이 포함되어 있어서 지하수를 오염시키는 2차적 오염의 주요인이 되고 있으며, 슬러지등에는 수분함유율이 높아서 매립지의 지반을 약화시키는 원인이 된다.In addition, the landfill of sludge is caused by the sludge which contains a lot of moisture, causing mass complaints by local residents around the landfill, and the leachate generated by landfill contains a large amount of heavy metals and harmful microorganisms, contaminating groundwater. It is a major cause of secondary pollution, and the sludge, etc., has a high water content, which causes the ground of the landfill to be weakened.

또한, 슬러지의 열분해 방식은 슬러지 중에 포함된 고분자 유기물을 열분해 하여 저분자의 오일을 얻는 방식으로 아직 연구 단계이며 열분해시 필요한 추가열이 필요하게되는 경제성에 개성이 요구되고 있는 것이다.In addition, the pyrolysis method of the sludge is a method of obtaining a low molecular oil by pyrolyzing the polymer organic matter contained in the sludge and is still in the research stage, and individuality is required for economic efficiency that requires additional heat required for pyrolysis.

근래에는 주요성분인 SiO₂,Al₂O₃,Fe₂O₃,CaO를 함유하고 있는 슬러지를 시멘트원료로 제공하는 재활용 방안이 학술적인 면에서 다방면으로 연구가 진행되고는 있으나 구체적인 시스템은 가시화되지 못하고 있다.Recently, many researches have been conducted on the recycling method of providing sludge containing SiO₂, Al₂O₃, Fe₂O₃, and CaO as cement raw materials, but the specific system has not been visualized.

시멘트 제조방법을 요약하면, SiO₂,Al₂O₃,Fe₂O₃ 및 CaO,의 4가지 성분을 함유하는 원료를 배합,분쇄,혼합한후 용융되기 전까지 소성하여 만든 시멘트의 반제품인 클린커(clinker)에 적량의 응결지연제인 석고를 첨가하여 분쇄하는 것으로 알려져 있다.To summarize the cement manufacturing method, the condensation of a suitable amount in the clinker, a semi-finished product of cement made by mixing, pulverizing and mixing raw materials containing four components of SiO₂, Al₂O₃, Fe₂O₃ and CaO, before melting them It is known to grind by adding gypsum which is a retardant.

본 발명은 상기 문제점을 해결하기 위하여 이루어진 것으로써, 특히 저효율건조기방법을 슬러지건조처리에 도입하여 완전한 건조를 유도하며, 완전한 건조분말 상태의 슬러지분말을 시멘트 공장으로 운반하여 시멘트원료로 제공함으로서, 재활용시멘트로 생산하여 일체의 폐기물이 발생되지 않아 환경친화적인 오페수슬러지의 건조장치(sludge Dry-plant)를 제공함에 있다.The present invention has been made to solve the above problems, in particular, by introducing a low-efficiency dryer method to the sludge drying treatment to induce complete drying, by transporting the sludge powder in a complete dry powder state to the cement plant to provide as a cement raw material, recycling It is to provide environmentally friendly sludge dry-plant because no waste is produced by producing cement.

본 발명의 다른 목적은 완전한 건조 분말 상태로 시멘트 공장으로 운반하여 시멘트 소성시 유해가스 발생을 최대한 억제하고 소성로에서 완전 연소로 분해되는 재활용 시멘트원료로 생산하므로서 환경친화적인 페수슬러지 건조장치를 제공함에 있는 것이다.Another object of the present invention is to provide an environmentally friendly waste water sludge drying apparatus by transporting to a cement factory in a completely dry powder state to minimize the generation of harmful gases during cement firing and to produce recycled cement material that is decomposed by the complete combustion in the kiln. will be.

본 발명은 상기의 목적을 달성하기 위하여 직하열을 400~600℃정도로 제어하는 다단식건조기(multiple-hearth furnace) 또는 직하열을 450~650℃정도로 제어하는 직접가열킬른(direct rotary kiln)으로 슬러지의 수분함량 70-80%의 건조 및 분쇄공정이 이루어지는 건조분쇄부와, 상기의 건조분쇄부를 경유한 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부와, 상기의 이송부를 경유한 슬러지입자를 열풍기류의 속도차에 의해 2차분쇄가 되고 건조량 15~25%를 담당하는 건조사이로와, 상기의 건조분쇄부와 건조저장사이로에서 배출되는 분진가스를 분리하는 원심분급기와, 상기의 원심분급기를 경유한 배기가스 및 미분을 가성소다로 중화시키켜 배출하는 습식세정부와, 상기의 습식세정부에서 정화된 배기가스를 냉각시키는 열교환부와, 화성탄으로 악취와 유해가스를 재정화시켜 대기로 배출시키는 배기가스측정부,로 구성됨을 특징으로 한다.The present invention is a multiple-hearth furnace for controlling the direct heat to about 400 ~ 600 ℃ to achieve the above object or a direct rotary kiln (direct rotary kiln) to control the direct heat to about 450 ~ 650 ℃. Dry air pulverization, which is dried and pulverized with a water content of 70-80%, a transport unit for transporting the sludge particles through the dry crushing unit at low temperature to the storage, and the sludge particles passing through the transport unit. The centrifugal classifier which separates the dust gas discharged between the dry grinding unit and the dry storage, which is secondary grinding by the speed difference of 15% to 25%, and the centrifugal classifier A wet washing unit that neutralizes and discharges the exhaust gas and fines with caustic soda, a heat exchanger that cools the exhaust gas purified by the wet washing unit, and a odor with Characterized in that it consists of an exhaust gas measuring unit, to re-enact the harmful gas to the atmosphere.

도1은 본 발명을 구현한 오폐수슬러지의 건조처리장치의 일예시도1 is an exemplary view of a drying treatment apparatus for wastewater sludge implementing the present invention.

도2는 본 발명을 구현한 오폐수슬러지의 건조처리장치의 다른 예시도Figure 2 is another illustration of a drying treatment apparatus for wastewater sludge implementing the present invention

*도면중 주요부분에 대한 부호설명** Description of symbols on the main parts of the drawings *

100; 건조분쇄부 110; 다단식건조기100; Dry grinding unit 110; Multistage Dryer

120; 슬러지공급부 130; 버어너120; Sludge supply unit 130; Burner

200; 이송부 210; 냉각기200; Transfer unit 210; cooler

220; 스크류콘베어 230; 바켓콘베어220; Screw conveyor 230; Basket Conveyor

300; 건조사이로 310; 배출구300; 310 between drying; outlet

320; 집진기 400; 운심분급기320; Dust collector 400; Fortune Classer

500; 습식세정부 510; 배기가스정화탑500; Wet tax government 510; Exhaust gas purification tower

520; 가성소다탱크 530; 순환펌프520; Caustic soda tank 530; Circulation pump

540; 활성탄 600; 열교환부540; Activated carbon 600; Heat exchanger

700; 배기가스측정부 110a;직접가열킬른건조기700; Exhaust gas measuring unit 110a; direct heating kiln dryer

이하, 본 발명 페수슬러지 건조장치의 실시예를 도시한 첩부도면에 의해 상세히 설명한다.It will be described below in detail by a gluing drawing showing an embodiment of the wastewater sludge drying apparatus of the present invention.

도1은 본 발명의 일실시예을 표시한 전체도로서, 오폐수의 슬러지를 탈수 및 정련하여 공급하는 슬러지공급부에 의해 공급되는 케이크상의 슬러지를 가열온도를 400~600℃정도로 제어하여 슬러지를 건조및 분쇄작용을 반복하여 슬러지를 함수율15-20%의 슬러지입자로 처리하는 건조분쇄부(100)와, 상기 건조분쇄부(100)로 부터 건조처리되어 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부(200)와, 상기의 이송부(200)에 의해 공급되는 슬러지입자를 기류차에 의해 분쇄 및 건조되는 건조사이로(300)와, 상기의 건조분쇄부(100)와 건조사이로(300)에서 배출되는 분진가스를 분리하는 원심분급기(400)와, 상기의 원심분급기(400)에서 배기되는 악취 및 유해배기가스를 가성소다로 정화시키는 습식세정부(500)와, 상기의 습식세정부(500)로 부터 분진제거 및 악취를 중화시켜 정화된 배기가스를 상온으로 냉각시키는 열교환부(condenser)(600)와, 상기의 열교환부(600)에서 상온의 배기가스중에 함유된 악취 및 분진을 완전제거하여 대기중으로 방출시키는 배기가스측정부(700)로 구성되고 있다.1 is an overall view showing an embodiment of the present invention, drying and pulverizing the sludge by controlling the heating temperature of the cake-like sludge supplied by the sludge supply unit for dewatering and refining the sludge of the waste water to about 400 ~ 600 ℃ Drying grinding unit 100 for treating sludge with sludge particles having a water content of 15-20% by repeating the operation, and a transfer unit for drying the sludge particles by drying from the dry grinding unit 100 and transporting the sludge particles to storage between them ( 200 and the drying cycle 300 in which the sludge particles supplied by the transfer unit 200 are pulverized and dried by an airflow difference, and the dust discharged from the dry grinding unit 100 and the drying passage 300. A centrifugal classifier 400 for separating gas, a wet cleaner 500 for purifying odor and harmful exhaust gas exhausted from the centrifugal classifier 400 with caustic soda, and the wet cleaner 500 described above. Dust removal from A heat exchanger 600 that cools the exhaust gas purified by neutralizing the odor to room temperature, and an exhaust gas that completely removes the odor and dust contained in the exhaust gas at room temperature in the heat exchange unit 600 and discharges it to the atmosphere. The gas measuring part 700 is comprised.

상기와 같이 본 발명을 구성하는 건조분쇄부(100)는 건조온도 400~600℃정도로 제어하는 다단식건조기(multiple-hearth furnace)(110)와 생활하수 및 공업폐수에서 발생되는 케이크상의 슬러지를 투입하는 슬러지공급기(120)와 다단식건조기로 부터 유출되는 배기가스의 온도를 감지하여 다단식건조기의 내부가 일정온도를 유지하도록 외부공기의 유입량과 연소연료량을 제어하는 저가열용 버어너(130)가 연결설치되며, 다단식건조기(110)는 투입되는 케이크상의 슬러지를 방사형태로 안쪽에서 바깥쪽으로 또는 반대방향으로 쓸어 케이크상의 슬러지이를 건조 및 입자상태로 분쇄하여 단계적으로 하부로 낙하시키는 단들(hearths), 팔(arms), 잇날(rabble teeth)등의 구성을 구비하고 있는 것이다.As described above, the dry grinding unit 100 constituting the present invention is a cake-type sludge generated from a multiple-hearth furnace 110 and living sewage and industrial wastewater controlled at a drying temperature of about 400 to 600 ° C. Low-temperature heat burner 130 is installed to detect the temperature of the exhaust gas flowing out of the sludge feeder 120 and the multi-stage dryer to control the inflow of the outside air and the amount of combustion fuel so that the inside of the multi-stage dryer is maintained at a constant temperature. The multi-stage dryer 110 sweeps the introduced sludge on the cake in a radial direction from the inside to the outside or in the opposite direction to dry and grind the sludge on the cake in a granular state to drop down stepwise (hearths), arms ( arms, rabbit teeth, and so on.

또, 상기의 이송부(200)에는 건조분쇄부(100)에서 건조 및 분쇄된 분말상의 슬러지입자를 냉각시키는 냉각기(210를 구비하는 스크류콘베어(220)과 바켓콘베어In addition, the conveying unit 200 has a screw conveyor 220 and a bucket conveyor having a cooler 210 for cooling the powdered sludge particles dried and pulverized in the dry grinding unit 100.

(230)으로 이루어져 냉각된 슬러지입자를 건조사이로(300)에 이송시켜 저장한다.Consisting of the 230, the cooled sludge particles are transferred to the drying path 300 to be stored.

또, 상기의 건조사이로(300)내에는 이송부(200)에 의해 공급되어진 슬러지입자를 기류차에 의한 분쇄 및 건조기능를 구비하며 하부에는 스러지배출구(310) 건조사이로(300)에서 배기되는 배기가스주에 함유된 분진를 제거하는 집진기(310)를 구비하여 건조사이로에서 배기되는 배기가스중에 분진을 제거하여 배기한다.In addition, in the drying passage 300, the sludge particles supplied by the conveying unit 200 are provided with a pulverization and drying function by an airflow car, and the exhaust gas exhausted from the sludge discharge port 310 drying passage 300 is disposed at the lower portion. The dust collector 310 which removes the dust contained in the main | line is provided, and dust is removed and exhausted in the exhaust gas exhausted between the drying paths.

또한, 본 발명에서는 원심분급기(400)를 다단식건조기(110)와 건조사이로In addition, in the present invention, the centrifugal classifier 400 between the multi-stage dryer 110 and the drying.

(300)에 연결구성하여 상기의 다단식건조기(110) 및 건조사이로(300)에서 배기되는 분진 및 배기가스를 원심분리방법에 의해 슬러지미진을 수집하고 배기가스만을 배기할수있게 하며 수집된 슬러지미분를 배출하는 배출구(410)를 하부에 구성한다.It is connected to the configuration 300 to collect the sludge dust by the centrifugal method of dust and exhaust gas exhausted from the multi-stage dryer 110 and the drying path 300, and exhaust only the exhaust gas and discharge the collected sludge fine powder The outlet 410 is configured to be lower.

그리고, 상기의 원심분급기(400)와 연결되는 습식세정부(500)는 배기가스를 정화시키는 배기가스정화탑(510)과, 가성소다수가 저장된 가성소다수탱크(520)와 상기 가성소다수탱크(520)로 부터 가성소다수를 분사시키는 순환펌프(530)와 상기 배기가스정화탑(510)에서 분무된 가성소다수를 가성소다수탱크(520)로 순환시키는 순환구성과 배기가스의 악취를 제거시키는 활성탄층(540)를 구비하고 있다.In addition, the wet cleaner 500 connected to the centrifugal classifier 400 includes an exhaust gas purification tower 510 for purifying exhaust gas, a caustic soda water tank 520 in which caustic soda water is stored, and the caustic soda water tank ( 520, a circulating pump for injecting caustic soda water and an activated carbon layer for circulating caustic soda water sprayed from the exhaust gas purification tower 510 to the caustic soda water tank 520 and to remove odors of the exhaust gas. 540 is provided.

이와같이 구성되어 있는 본 발명의 일실시예에 의한 오폐수슬러지의 건조장치의 작용에 대하여 설명한다.The operation of the wastewater sludge drying apparatus according to the embodiment of the present invention configured as described above will be described.

먼저, 생활하수 및 공버용폐수처리에서 발생되는 케이상슬러지(오니)는 함수율 70-85%인 상태로 슬러지공급부(120)의해 건조분쇄부(100)의 다단식 건조기First, the multi-stage dryer of the dry crushing unit 100 by the sludge supply unit 120 in the state of the sewage sludge (sludge) generated in the domestic sewage and waste water treatment for the deburred wastewater is 70-85%

(110)로 유입되면 다단식건조기로 부터 유출되는 배기가스의 온도를 감지하여 다단식건조기의 내부가 일정온도를 유지하도록 외부공기의 유입량과 연소연료량을 제어하는 저가열용 버어너(130)에 의해 다단식거조기의 건조온도가 400~600℃정도로 자동제어되며 동시에 단들(hearths), 팔(arms), 잇날(rabble teeth)들의 작동에 의해 케이상슬러지가 방사형태로 안쪽에서 바깥쪽으로 또는 반대방향으로 쓸어내리는 케이크상의 슬러지이를 건조 및 입자상태로 분쇄하여 단계적으로 하부로 낙하된다.When entering the 110, the multi-stage by low-temperature burner 130 to sense the temperature of the exhaust gas flowing out of the multi-stage dryer to control the inflow of the outside air and the amount of combustion fuel so that the inside of the multi-stage dryer to maintain a constant temperature The drying temperature of the tank is automatically controlled to 400 ~ 600 ℃, and at the same time, the Cay sludge is swept radially from inside to outside or in the opposite direction by the operation of hearths, arms and teeth. The sludge teeth on the cake are dried and pulverized into a granular state and fall to the bottom step by step.

이때, 본 발명에서는 다단식건조기(110)의 건조온도를 400~600℃정도로 제어하므로서, 슬러지를 구성하는 SiO₂,Al₂O₃,Fe₂O₃ 및 CaO, 잔존되는 동시에 슬러지의 유기화합물은 분해되고 다이옥신(Dioxin)등의 약성 물질을 파괴함과 동시에 재생성을 예방하게된다.At this time, in the present invention by controlling the drying temperature of the multi-stage dryer 110 to about 400 ~ 600 ℃, SiO₂, Al₂O₃, Fe₂O₃ and CaO constituting the sludge, the organic compound of the sludge is decomposed and dioxins (Dioxin), etc. At the same time, it destroys weak substances and prevents their regeneration.

그리고, 상기의 다단식건조기(110)에서 건조처리되는 슬러지에서 발생하는 황산화물(SOx),질소산화물(NOx), 염화수소(HCL) 등 각종 유해가스는 다단식건조기의 배기관을 통하여 원심분급기(400)로 배기된다.In addition, various harmful gases such as sulfur oxides (SOx), nitrogen oxides (NOx), and hydrogen chloride (HCL) generated from the sludge dried in the multistage dryer 110 are centrifugal classifiers 400 through exhaust pipes of the multistage dryer. Is exhausted.

또한, 상기의 다단식건조기(110)에 의해 함수율 20~30%로 건조된 슬러지입자는 상기 이송부(200)의 냉각기(210)가 설치된 스크류콘베어(220)에 의해 냉각되면서 바켓콘베어(230)으로 이송되고 다시 바켓콘베어(230)에 의해 건조사이로(300)에 저장된다,In addition, the sludge particles dried at a water content of 20 to 30% by the multi-stage dryer 110 are transferred to the bucket conveyor 230 while being cooled by the screw conveyor 220 in which the cooler 210 of the transfer unit 200 is installed. And again stored in the drying path 300 by the bucket conveyor 230,

이때, 건조사이로(300)내에서도 전체 건조량의 15~25%가 건조되며, 슬러지 입자와 열풍기류가 병류로서 이동하면서 슬러지 입자와 열풍과의 속도차이에 의하여 2차 분쇄가 이루어져 슬러지입자는 더욱 잘개 분쇄되어 저장되며 여기에서 방생되는 악취을 함유한 배기가스와 분진은 다음의 원심분급기(400)로 이동할때 건조사이로에 설치되고 있는 집진기(320)를 경유하면서 분진이 제거되고 배기가스만 배기되는 것이다.At this time, in the drying cycle 300, 15 to 25% of the total amount of drying is dried, and the sludge particles and hot air streams are moved as co-currents, and the secondary grinding is performed by the speed difference between the sludge particles and the hot air. When the exhaust gas containing the odor generated therein and dust are moved to the next centrifugal classifier 400, the dust is removed and the exhaust gas is exhausted via the dust collector 320 installed between the drying paths.

이렇게, 건조사이로(300)에 저장되는 함수율15%정도 내외의 슬러지입자를 얻게되고 이러한 슬러지입자는 SiO₂,Al₂O₃,Fe₂O₃ 및 CaO,을 주성분으로 하고있어 시멘트원료의 주성분이 풍부한 오폐수슬러지를 시멘트원료로 재활용 할수있게 되므로서, 경제적가치의 증대와 종전의 소각방법에서 대두되던 인체에 유해한 중금속의 휘산(揮散)과 다이옥신발생 방지, 슬러지의 매립방식에서 야기되는 악취, 유해성 중금속 및 지하수오염, 매립지의 지반약화,등 환경문제등을 모두 해결하게 된다.Thus, sludge particles of about 15% of moisture content stored in the drying path 300 are obtained, and these sludge particles are mainly composed of SiO₂, Al₂O₃, Fe₂O₃ and CaO, and the wastewater sludge, which is rich in the main component of cement raw material, is used as cement raw material. As it can be recycled, it increases the economic value and prevents the volatilization and dioxin generation of heavy metals harmful to the human body, which has emerged in previous incineration methods, the odors caused by the landfilling method of sludge, harmful heavy metals and groundwater pollution, and the ground of landfills. We will solve all environmental problems such as weakening.

그리고, 상기와 같이 다단식건조기(110)의 배기구와 건조사이로(300)의 집진기(320)을 경유하여 배기되는 분진과 배기가스는 원심분급기(400)에서 분진과 가스로 분리되며, 여기에서 잔유되는 슬러지분진은 수집하여 재활용 시멘트원료로 공급하고 또한 악취와 황산화물(SOx),질소산화물(NOx), 염화수소(HCL) 등 각종 유해가스를 포함하는 배기가스는 송풍기에 의해 습식세정부(500)의 배기가스정화탑In addition, as described above, the dust and the exhaust gas exhausted through the exhaust port of the multistage dryer 110 and the dust collector 320 of the drying path 300 are separated into the dust and the gas in the centrifugal classifier 400, where the residual oil Sludge dust is collected and supplied as recycled cement raw materials, and exhaust gases containing various odorous gases such as odors, sulfur oxides (SOx), nitrogen oxides (NOx) and hydrogen chloride (HCL) are blown by a blower (500). Exhaust gas purification tower

(510)으로 공급되는데, 이때 배기가스정화탑(510)으로 공급된 배기가스는 배기가스정화탑(510)과, 가성소다수가 저장된 가성소다수탱크(520)와 상기 가성소다수탱크The exhaust gas supplied to the exhaust gas purification tower 510 is an exhaust gas purification tower 510, a caustic soda water tank 520 in which caustic soda water is stored, and the caustic soda water tank.

(520)로 부터 가성소다수를 분사시키는 순환펌프(530)와 상기 배기가스정화탑(510)에서 분무된 가성소다수를 가성소다수탱크(520)로 순환시키는 순환구성에 의해 황산화물(SOx),질소산화물(NOx), 염화수소(HCL) 등 각종 유해가스가 중화되는 동시에 활성탄층(540)을 경유하면서 악취가 완전정화되어 배기된다.Sulfur oxide (SOx), nitrogen by a circulation configuration for circulating the caustic soda water sprayed from the exhaust gas purification tower 510 to the caustic soda water tank 520 from the circulation pump 530 for injecting caustic soda water from 520 Various harmful gases such as oxides (NOx) and hydrogen chloride (HCL) are neutralized and the odor is completely purified and exhausted via the activated carbon layer 540.

상기와 같은 원심분급기(400)에 의한 분진제거 처리과정과 습식세정부(500)에 의한 악취 및 유해가스을 경유하면서 정화처리된 배기가스는 열교환부(600)에서 상온으로 냉각시키고 다시 배기가스측정부(700)의 활성탄 및 기타휠터처리과정으로 재정화처리한후 연통을 통하여 인체에 무해한 청정가스를 배출하게되는 것이다.The exhaust gas purified by the dust removal process by the centrifugal classifier 400 and the odor and harmful gas by the wet cleaning unit 500 is cooled to room temperature in the heat exchange unit 600, and the exhaust gas is measured again. After refining the activated carbon and other filter treatment of the part 700 is to discharge clean gas harmless to the human body through the communication.

도 2 는 본 발명의 다른 실시예을 표시한 전체도로서, 오폐수의 슬러지를 탈수 및 정련하여 공급하는 슬러지공급부에 의해 공급되는 케이크상의 슬러지를 가열온도를 400~600℃정도로 제어하여 슬러지를 건조및 분쇄작용을 반복하여 슬러지를 함수율15-20%의 슬러지입자로 처리하는 건조분쇄부(100)와, 상기 건조분쇄부2 is a general view showing another embodiment of the present invention, drying and pulverizing the sludge by controlling the heating temperature of the cake-like sludge supplied by the sludge supply unit for dewatering and refining the sludge of the waste water to about 400 ~ 600 ℃ A dry grinding part 100 for repeatedly treating the sludge with sludge particles having a water content of 15-20%, and the dry grinding part

(100)로 부터 건조처리되어 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부(200)와, 상기의 이송부(200)에 의해 공급되는 슬러지입자를 기류차에 의해 분쇄 및 건조되는 건조사이로(300)와, 상기의 건조분쇄부(100)와 건조사이로(300)에서 배출되는 분진가스를 분리하는 원심분급기(400)와, 상기의 원심분급기(400)에서 배기되는 악취 및 유해배기가스를 가성소다로 정화시키는 습식세정부(500)와, 상기의 습식세정부(500)로 부터 분진제거 및 악취를 중화시켜 정화된 배기가스를 상온으로 냉각시키는 열교환부(condenser)(600)와, 상기의 열교환부(600)에서 상온의 배기가스중에 함유된 악취 및 분진을 완전제거하여 대기중으로 방출시키는 배기가스측정부(700)로 구성되고 있으며, 여기에서는 케이크상의 슬러지를 건조및 분쇄작용을 반복하여 슬러지를 함수율15-20%의 슬러지입자로 처리하는 건조분쇄부Drying process from (100) and the sludge particles to be transported to the low-temperature drying between the storage unit 200, and between the sludge particles supplied by the conveying unit 200 is dried and crushed and dried by an airflow vehicle (300) ), The centrifugal classifier 400 for separating the dust gas discharged from the dry grinding unit 100 and the drying path 300, and the odor and harmful exhaust gas exhausted from the centrifugal classifier 400 A wet cleaner 500 for purifying with caustic soda, a heat exchanger 600 for neutralizing dust removal and odor from the wet cleaner 500, and cooling the purified exhaust gas to room temperature; It consists of an exhaust gas measuring unit 700 to completely remove the odor and dust contained in the exhaust gas at room temperature in the heat exchange unit 600 of the discharge to the atmosphere, where the sludge on the cake is dried and pulverized repeatedly Sludge Dry milling unit for processing the sludge particles in 15-20% yield

(100)의 건조수단을 다단식건조기를 대신하여 직접가열킬른(direct rotary kiln)Direct heating kiln (direct rotary kiln) in place of the multi-stage dryer

(110a)으로 케이상 슬러지를 건조분쇄처리 한다.Dry grinding treatment of the k-phase sludge at 110a.

이러한, 직접가열킬른은 이미 알려진것과 같이 나선익(spiral flights)Such direct heating kilns are already known as spiral flights.

,양정익(lifting flights), 회전통(shell)등의 구성으로 이루어지며, 여기에서도 직열을 450~650℃정도로 제어하여 케이크상 슬러지의 건조 및 분쇄처리과정이 횡적으로 이루어지는 것으로, 횡적구성으로 건조로의 길이변경이 용이하여 설치조건이 간편하고 건조온도를 안정적으로 체류시켜서 슬러지건조온도 및 처리량을 조정이 용이한 이점이 있다.It consists of a lifting flight, a shell, etc. Here, the direct heat is controlled at about 450 ~ 650 ℃, and the drying and grinding process of cake-like sludge is performed horizontally. Easy to change the length, the installation conditions are simple, and the drying temperature is stably maintained, so that the sludge drying temperature and throughput can be easily adjusted.

그리고, 여기에서도 직접가열킬른(110a)의 건조온도를 450~650℃정도로 제어하므로서, 슬러지를 구성하는 SiO₂,Al₂O₃,Fe₂O₃ 및 CaO, 잔존되는 동시에 슬러지의 유기화합물은 분해되고 다이옥신(Dioxin)등의 약성 물질을 파괴함과 동시에 재생성을 예방하게되는 것이고, 건조처리되는 슬러지에서 발생하는 황산화물Also, by controlling the drying temperature of the direct heating kiln (110a) to about 450 to 650 ° C., SiO2, Al₂O₃, Fe₂O₃, and CaO, which constitute sludge, remain and at the same time, organic compounds of sludge are decomposed and dioxins (Dioxin), etc. It destroys weak substances and at the same time prevents regeneration, and sulfur oxides generated from dried sludge.

(SOx),질소산화물(NOx), 염화수소(HCL) 등 각종 유해가스는 다단식건조기의 배기관을 통하여 원심분급기(400)로 배기된다.Various harmful gases such as (SOx), nitrogen oxides (NOx) and hydrogen chloride (HCL) are exhausted to the centrifugal classifier 400 through the exhaust pipe of the multistage dryer.

또한, 함수율 20~30%로 건조된 슬러지입자를 이송부(200)의 의해 건조사이로(300)에 저장하고 여기에서도 건조량의 15~25%가 건조되어 저장되며 집진기In addition, the sludge particles dried at a water content of 20 to 30% are stored in the drying path 300 by the transfer part 200, and here, 15 to 25% of the dry amount is dried and stored, and the dust collector

(320)를 경유하면서 분진이 제거되고 배기가스만 배기되는 것이다.Dust is removed while passing through 320 and only the exhaust gas is exhausted.

이렇게, 건조사이로(300)에 저장되는 함수율15%정도 내외의 슬러지입자를 얻게되고 이러한 슬러지입자는 SiO₂,Al₂O₃,Fe₂O₃ 및 CaO,을 주성분으로 하고있는 오폐수슬러지를 시멘트원료로 재활용되는 경제적가치와 다이옥신발생예방, 악취, 유해성 중금속,지하수오염,등 환경문제등을 모두 해결하게 점도 동일하다.Thus, sludge particles having a moisture content of about 15% stored in the drying path 300 are obtained, and these sludge particles have economic value and dioxins recycled from wastewater sludge mainly composed of SiO₂, Al₂O₃, Fe₂O₃ and CaO as cement raw materials. The same is true for solving environmental problems such as prevention of occurrence, odor, harmful heavy metals, groundwater pollution, etc.

또한, 원심분급기(400)에서 분진과 가스로 분리하고 악취와 황산화물(SOx),질소산화물(NOx), 염화수소(HCL) 등 각종 유해가스를 포함하는 배기가스는 송풍기에 의해 습식세정부(500)에서 가성소다수중화방법으로 황산화물(SOx),질소산화물In addition, in the centrifugal classifier 400, the exhaust gas containing various odorous gases such as odor, sulfur oxides (SOx), nitrogen oxides (NOx) and hydrogen chloride (HCL) is separated into dust and gas by a blower. Caustic Soda Neutralization Method (SOx, Nitrogen Oxide)

(NOx), 염화수소(HCL) 등 각종 유해가스가 중화되는 동시에 활성탄층(540)을 경유하면서 악취가 완전정화 시기는 처리과정과, 정화처리된 배기가스는 열교환부(600)에서 상온으로 냉각시키고 다시 배기가스측정부(700)의 활성탄 및 기타휠터처리과정으로 재정화처리한후 연통을 통하여 인체에 무해한 청정가스를 배출한다.(NOx), hydrogen chloride (HCL) and other harmful gases are neutralized and the odor is completely purified while passing through the activated carbon layer 540, and the purified exhaust gas is cooled to room temperature in the heat exchange unit 600, After refining the activated carbon and other filter treatment process of the exhaust gas measuring unit 700, the exhaust gas is discharged clean gas harmless to the human body.

이상에서와 같이 본 발명은 직하열을 400~600℃정도로 제어하는 다단식건조기 또는 직하열을 450~650℃정도로 제어하는 직접가열킬른건조기 및 분쇄공정의 건조분쇄부와, 열풍기류의 속도차에 의해 2차분쇄를 담당하는 건조사이로와, 배출되는 분진가스를 분리하는 원심분급기와, 유해한 배기가스 및 미분을 가성소다로 중화시키켜 배출하는 습식세정부의 구성에 의해 오폐수슬러지를 재활용 시멘트원료를 생산하므로서, 경제성이 높고 슬러지처리가 완전히 해결하며 종전의 슬러지처리과정에서 발생되던 공기/수질오염등의 공해요인도 해결되는 환경친화적인 효과가크다.As described above, the present invention is a multi-stage dryer for controlling direct heat at about 400 to 600 ° C. or a direct heating kiln dryer for controlling direct heat at about 450 to 650 ° C., and a dry grinding part of a pulverizing process, and by a speed difference between hot air flows. Waste cement sludge is recycled by the construction of the drying cycle in charge of secondary crushing, centrifugal classifier separating the emitted dust gas, and a wet washing machine that neutralizes and discharges harmful exhaust gases and fines with caustic soda. Therefore, it is economical, and the sludge treatment is completely solved, and the environmentally friendly effect of solving the pollution factors such as air / water pollution generated in the conventional sludge treatment process is great.

Claims (3)

직하열을 400~600℃정도로 제어하는 다단식건조기 또는 직하열을 450~650℃정도로 제어하는 직접가열킬른건조기로 슬러지의 수분함량 70-80%의 건조 및 분쇄공정이 이루어지는 건조분쇄부(110)와, 상기의 건조분쇄부를 경유한 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부(200)와, 상기의 이송부를 경유한 슬러지입자를 열풍기류의 속도차에 의해 2차분쇄가 되고 건조량 15~25%를 담당하는 건조사이로(300)와, 상기의 건조분쇄부와 건조저장사이로에서 배출되는 분진가스를 분리하는 원심분급기(400)와, 상기의 원심분급기를 경유한 배기가스 및 미분을 가성소다로 중화시키켜 배출하는 습식세정부(500)와, 상기의 습식세정부에서 정화된 배기가스를 냉각시키는 열교환부(600)와, 화성탄으로 악취와 유해가스를 재정화시켜 대기로 배출시키는 배기가스측정부(700)로 구성됨을 특징으로 하는 오폐수슬러지의 건조처리장치.Dry grinding unit 110, which is a multi-stage dryer that controls direct heat at about 400-600 ° C. or a direct heating kiln dryer that controls direct heat at about 450-650 ° C., and a drying and grinding process of water content of sludge 70-80%. The secondary part is crushed by the speed difference of the hot air stream, and the conveyance part 200 which transfers the sludge particle through the said dry grinding part to low temperature dryness, and transfers it between storage, and the dry amount 15-25 Caustic soda is a drying cycle (300) responsible for the%, a centrifugal classifier (400) for separating the dust gas discharged between the dry grinding section and the dry storage, and the exhaust gas and the fine powder via the centrifugal classifier. A wet washing unit 500 neutralized and discharged, a heat exchange unit 600 cooling the exhaust gas purified by the wet washing unit, and an exhaust gas that redefines odors and harmful gases to the atmosphere by burning coal. 'S dry processing apparatus of the sewage sludge, characterized by consisting of a measuring unit (700). 제1항에 있어서, 직하열을 400~600℃정도로 제어하는 다단식건조기(110)로 슬러지의 수분함량 70-80%의 건조 및 분쇄공정이 이루어지는 건조분쇄부(110)와, 상기의 건조분쇄부를 경유한 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부According to claim 1, Dry grinding unit 110 and the drying grinding unit is a drying and grinding process of 70-80% of the water content of the sludge with a multi-stage dryer 110 to control the direct heat to about 400 ~ 600 ℃ degree Transfer part to transfer diesel sludge particles at low temperature to the storage area (200)와, 상기의 이송부를 경유한 슬러지입자를 열풍기류의 속도차에 의해 2차분쇄가 되고 건조량 15~25%를 담당하는 건조사이로(300)와, 상기의 건조분쇄부와 건조저장사이로에서 배출되는 분진가스를 분리하는 원심분급기(400)와, 상기의 원심분급기를 경유한 배기가스 및 미분을 가성소다로 중화시키켜 배출하는 습식세정부(200), and the sludge particles passing through the conveying section is secondary grinding by the speed difference of the hot air flow, and the drying cycle (300) responsible for 15 to 25% of the drying amount, and between the dry grinding portion and the dry storage. Centrifugal classifier (400) for separating the dust gas discharged from the water, and the wet washing machine to neutralize and discharge the exhaust gas and the fine powder via the centrifugal classifier with caustic soda (500)와, 상기의 습식세정부에서 정화된 배기가스를 냉각시키는 열교환부(600)와, 화성탄으로 악취와 유해가스를 재정화시켜 대기로 배출시키는 배기가스측정부(700)로 구성됨을 특징으로 하는 오폐수슬러지의 건조처리장치.500, a heat exchanger 600 for cooling the exhaust gas purified by the wet cleaning unit, and an exhaust gas measurement unit 700 for refining the odor and harmful gas with ignited coal and exhausting it to the atmosphere. A wastewater treatment sludge drying treatment apparatus. 제1항에 있어서, 직하열을 450~650℃정도로 제어하는 직접가열킬른건조기(110a)로 슬러지의 수분함량 70-80%의 건조 및 분쇄공정이 이루어지는 건조분쇄부(110)와, 상기의 건조분쇄부를 경유한 슬러지입자를 저온건조하여 저장사이로 까지 이송하는 이송부(200)와, 상기의 이송부를 경유한 슬러지입자를 열풍기류의 속도차에 의해 2차분쇄가 되고 건조량 15~25%를 담당하는 건조사이로(300)와, 상기의 건조분쇄부와 건조저장사이로에서 배출되는 분진가스를 분리하는 원심분급기(400)와, 상기의 원심분급기를 경유한 배기가스 및 미분을 가성소다로 중화시키켜 배출하는 습식세정부(500)와, 상기의 습식세정부에서 정화된 배기가스를 냉각시키는 열교환부(600)와, 화성탄으로 악취와 유해가스를 재정화시켜 대기로 배출시키는 배기가스측정부The method of claim 1, wherein the dry grinding unit 110, the drying and grinding process of the water content of 70-80% of the sludge is performed by a direct heating kiln dryer (110a) that controls the direct heat to about 450 ~ 650 ℃ degree, and the drying The transport unit 200 for drying the sludge particles via the crushing unit at low temperature and transferring them between the storage units and the sludge particles passing through the conveying unit are secondary crushed by the speed difference of the hot air flow, and responsible for 15 to 25% of the drying amount. Neutralize the exhaust gas and the fine powder via the centrifugal classifier 400 for separating the dust gas discharged between the drying cycle 300, the dry grinding section and the dry storage, and the caustic soda. A wet cleaner 500 for discharging, a heat exchanger 600 for cooling the exhaust gas purified by the wet cleaner, and an exhaust gas measuring unit for refining the odor and harmful gas to the atmosphere by ignited coal (700)로 구성됨을 특징으로 하는 오폐수슬러지의 건조처리장치.Wastewater sludge drying treatment apparatus, characterized in that consisting of (700).
KR1019990044372A 1999-10-13 1999-10-13 Sludge dry-plant KR20010037075A (en)

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CN110408414A (en) * 2019-07-29 2019-11-05 王凯军 A kind of organic solid waste of High water cut is sprayed desiccation-pyrolysis integrating device and method

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JPH0952023A (en) * 1995-08-18 1997-02-25 Kawasaki Steel Corp Waste drying apparatus
KR0128985B1 (en) * 1994-12-13 1998-04-16 Kang Jae Won Low pollution rotary kiln
JPH11138144A (en) * 1997-11-12 1999-05-25 Toshiba Corp Garbage drying and treating apparatus
KR100268592B1 (en) * 1998-06-27 2000-10-16 김재국 Process for treatment of foul water sludge

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Publication number Priority date Publication date Assignee Title
KR0128985B1 (en) * 1994-12-13 1998-04-16 Kang Jae Won Low pollution rotary kiln
JPH0952023A (en) * 1995-08-18 1997-02-25 Kawasaki Steel Corp Waste drying apparatus
JPH11138144A (en) * 1997-11-12 1999-05-25 Toshiba Corp Garbage drying and treating apparatus
KR100268592B1 (en) * 1998-06-27 2000-10-16 김재국 Process for treatment of foul water sludge

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110408414A (en) * 2019-07-29 2019-11-05 王凯军 A kind of organic solid waste of High water cut is sprayed desiccation-pyrolysis integrating device and method

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