KR20030003159A - The Apparatus of Manufacturing Refuse Derived Fuel (R.D.F) Using Sewage Sludge & Refuse Synthetic Resin, and the Manufacturing Process - Google Patents
The Apparatus of Manufacturing Refuse Derived Fuel (R.D.F) Using Sewage Sludge & Refuse Synthetic Resin, and the Manufacturing Process Download PDFInfo
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- KR20030003159A KR20030003159A KR1020020072116A KR20020072116A KR20030003159A KR 20030003159 A KR20030003159 A KR 20030003159A KR 1020020072116 A KR1020020072116 A KR 1020020072116A KR 20020072116 A KR20020072116 A KR 20020072116A KR 20030003159 A KR20030003159 A KR 20030003159A
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/46—Solid fuels essentially based on materials of non-mineral origin on sewage, house, or town refuse
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/406—Solid fuels essentially based on materials of non-mineral origin on plastic
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Treatment Of Sludge (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
Abstract
Description
본 발명은 종말처리장의 유기성 하수 슬러지(열량가 2,000Kcal∼2,200Kcal/Kg)와 폐합성수지류(8,000Kcal∼9,000Kcal)를 건조, 혼합, 첨가제 투입 등의 공정을 거쳐 이를 원료로 이용하여 압출 ·성형으로 수분함량 10%이하의 건조고형물(열량가5,000Kal∼5,500Kcal)을 제조하여 농촌 비닐하우스의 온수 Boiler 및 산업체의 Steem용 Boiler에 대체에너지로 재활용하기 위한 폐기물 고형연료 제조방법에 관한 것이다.The present invention uses an organic sewage sludge (caloric value 2,000Kcal ~ 2,200Kcal / Kg) and waste synthetic resins (8,000Kcal ~ 9,000Kcal) of the terminal treatment plant by drying, mixing, adding additives, etc. The present invention relates to a waste solid fuel manufacturing method for producing dry solids having a moisture content of 10% or less (caloric value of 5,000 Kal to 5,500 Kcal) and recycling them as alternative energy in hot water boilers in rural vinyl houses and industrial steem boilers.
종래의 하수 Sludge처리는 공해상 해상투기(51.4%), 육상 매립장 매립(40.2%) 및 기타 소각, 재활용 등으로 처리하였으나, 매립장의 한계성과 중금속 오염및 침출수 발생 등으로 환경오염문제가 발생하여 2003년 7월부터 해상투기 및 육상매립을 전면 금지시킴으로써, 향후 발생되는 Sludge(현 4,500Ton/日 생산)의 적정 처리가 사회적 환경문제로 크게 부각됨에 따라, 농촌의 폐비닐과 산업체의 폐합성수지류 등의 처리 대책이 절실히 요구되는 시점에서 이들을 적절히 이용 ·처리하는 방법이 강구되어야 한다.Conventional sewage sludge treatment was carried out by offshore dumping (51.4%), landfill site (40.2%) and other incineration and recycling, but due to the limitations of landfill, heavy metal contamination and leachate generation, By prohibiting offshore dumping and land reclamation from July, proper disposal of sludge (currently 4,500 tons / day production), which occurs in the future, has been highlighted as a social environmental problem. When treatment measures are urgently needed, a method of using and treating them properly should be devised.
특히 현재 폐비닐, 페합성수지류 등의 처리는 원료상태가 깨끗하고 오염이 없는 것들은 재생용으로 원료화하고 있으나, 전체 발생량의 10∼15%에 불과하고,탄화장치에 의한 건류소각이 일부 행해지고 있으나 건조 등의 전처리공정이 불비하여 불완전연소로 인한 다이옥신 발생 등 제2의 공기오염으로 발전하였다.Particularly, waste vinyl and synthetic resins are processed into clean materials without pollution and are recycled, but only 10-15% of the total amount is generated. Due to lack of pretreatment such as drying, it has developed into a second air pollution such as dioxin generation due to incomplete combustion.
또한 고형화 방법으로 대체에너지화 하려는 노력을 기울였으나 분리수거, 선별, 원료배합, 조정 및 안정화 등의 미숙으로 고형화의 생산성저하와 고형물의 보관시 유기물의 부패로 인한 악취발생 및 고형물 연소시 숯덩이 상태(Char)로 표면이 굳어져 완전 연소가 불가능하여 많은 양의 Ash 발생과, R.D.F 원료의 전처리과정에서 금속류의 선별이 불량하고 불완전연소로 인하여 다이옥신류의 대기오염물질이 발생함은 물론 그 배출 Gas로 인하여 2차환경오염의 새로운 원인으로 주목받게 되었다.In addition, although efforts have been made to solidify alternative energy through solidification methods, the productivity of solidification is reduced due to immaturity of separation collection, sorting, raw material mixing, adjustment, and stabilization. As the surface is hardened by Char), it is impossible to completely burn it, so a large amount of ash is generated, and the selection of metals is poor during the pretreatment of RDF raw materials, and incomplete combustion generates air pollutants of dioxins as well as the exhaust gas. This has attracted attention as a new cause of secondary environmental pollution.
본 발명은 종말처리장의 하수 슬러지와 폐합성수지류를 이용하여 제자원화하고 이를 재활용하여 대체에너지로서의 경제적 부가가치를 창출하고자 하는 목적에 따라, 상기의 폐기물을 건조, 혼합, 중화제 첨가, 성형 등의 공정을 거쳐 고형화하고 이를 연료로 재활용하기 위한 방법으로서,The present invention is a process for drying, mixing, adding neutralizing agents, molding, and the like, according to the purpose of recycling the wastewater by using sewage sludge and waste synthetic resins and recycling them to create economic added value as alternative energy. As a way to solidify and recycle it as fuel,
상기의 목적을 달성하기 위하여 첫째 하수 Sludge의 함수율을 75%에서 25%로 건조하되 이때 유기성 슬러지가 탄화되거나 소각되지 않도록 직열이 아닌 열교환 폐열로써 건조하고, 한편 폐합성수지류는 1차파쇄공정에서 100m/m∼200m/m 크기로 절단 ·파쇄한 후 혼재하고 있는 금속류는 자석선별하고, 돌 등의 불연물과 오물은 진동장치에 의하여 제거한 후 30m/m∼50m/m의 크기로 2차파쇄하여 상기의 두 원료를 중량비 4:6의 비율로 혼합하고, 여기에 유해가스발생을 억제하기 위하여 중화제인 소석회(Ca(OH)2)를 투입하며, 건조 ·혼합공정에서 수분함량 15%정도로 건조 ·조정한 후, 압출 ·성형공정을 거쳐 고형화하고 또한 제조된 R.D.F의 일부를 상기 공정의 건조 열원으로 공급하기 위하여 열분해 연소장치에서 이것의 연소열을 건조장치의 열원으로 재이용하는 고형연료화 대체에너지 제조공정이다.In order to achieve the above object, first, the water content of the sewage sludge is dried from 75% to 25%. At this time, the organic sludge is dried by heat exchange waste heat instead of direct heat so as not to be carbonized or incinerated. Metals mixed after cutting and crushing in the size of / m to 200m / m are selected by magnet, and non-combustible materials such as stones and dirt are removed by vibrating device, and then secondly crushed into the size of 30m / m to 50m / m. Mix the two raw materials in a ratio of 4: 6 by weight, and add calcium hydroxide (Ca (OH) 2 ), a neutralizing agent, to suppress harmful gas generation, and dry and adjust the water content to about 15% in the drying and mixing process. After the solidification through the extrusion and molding process, and in order to supply a part of the prepared RDF to the drying heat source of the process, the heat of combustion of the combustion heat in the pyrolysis combustion apparatus as the heat source of the drying apparatus. Ryohwa replace the energy producing process.
상기 공정에서 하수 Sludge와 폐합성수지류의 혼합원료제조의 전처리 원료화공정에서 특히 유의해야할 사항은 ①혼합비율, ②수분함량, ③중화제투입량, ④건조온도 등 원료의 적정한 전처리공정을 관리함으로써 의하여 균질 ·균일한 제품생산은 물론 환경오염을 최소화할 수 있는 폐기물의 재활용 제조방법이다.In the above process, particular attention should be paid to pretreatment of raw materials for the production of mixed raw materials of sewage sludge and waste synthetic resins by controlling the appropriate pretreatment process of raw materials such as ① mixing ratio, ② water content, ③ neutralizing agent input, and ④ drying temperature. · It is a recycling method of waste that can minimize environmental pollution as well as produce uniform products.
도1은 본 발명에 따른 고형화연료 제조 공정도1 is a solid fuel production process according to the present invention
도2는 열분해 연소열을 이용한 제조 시스템2 is a manufacturing system using pyrolysis combustion heat
도3은 폐열이용 건조 및 혼합 시스템Figure 3 is a waste heat drying and mixing system
도4는 열분해 연소열 이용 시스템의 상세도4 is a detailed view of a pyrolysis combustion heat utilization system;
도5는 스크루식 정량공급장치와 쌍스크루에 의한 압출 ·성형 시스템5 is an extrusion and molding system using a screw type metering device and a double screw.
***도면중 주요 부분에 대한 부호의 설명****** Description of the symbols for the main parts of the drawings ***
11 : 폐합성수지류 하치·선별 12 : 1차파쇄공정11: Waste synthetic resin basin, screening 12: 1st shredding process
13 : 금속류 자석선별공정 14 : 2차파쇄공정13 metal sorting process 14: secondary crushing process
15 : 파쇄합성수지류 중간저장 16 : 하수 Sludge 하치·저장15: Intermediate storage of crushed synthetic resin paper 16: Sludge sewage storage and storage
17 : 정량공급 Screw Feeder 18 : 연소폐열이용 건조공정17: Fixed feed screw feeder 18: Drying process using combustion waste heat
19 : 연료 용R.D.F 하치·저장 20 : 정량공급 Feeder19: Fuel R.D.F lower storage and storage 20: Fixed quantity feeder
21 : 열분해 연소장치 22 : 열분해 Gas 연소장치21: pyrolysis combustion apparatus 22: pyrolysis gas combustion apparatus
24 : 건식 열교환 공정 25 : 혼합원료 Feeder24: dry heat exchange process 25: mixed raw material feeder
26 : 열풍이용 원료혼합 ·건조공정 27 : 중화용 첨가제 투입장치26: mixing and drying raw materials for hot air 27: adding additive for neutralization
28 : 원료혼합 중간저장 Silo 29 : 압출·성형공정28: Intermixed storage of raw materials Silo 29: Extrusion and molding process
30 : 파쇄공정 (20m/m∼30m/m) 31 : 제품저장 및 이송공정30: Crushing process (20m / m ~ 30m / m) 31: Product storage and transfer process
이하 첨부된 도면에 의하여 본 발명을 상세히 설명하면 다음과 같다.Hereinafter, the present invention will be described in detail with reference to the accompanying drawings.
도1의 공정에 따른 본 발명은 종말처리장에서 발생하는 하수 슬러지와 산업체에서 발생하는 일반폐기물과 생활폐기물 중의 폐P.P, P.E 등을 원료로 이용하여 재활용 대체에너지화의 폐기물 고형연료 제조방법을 나타낸 것으로서,The present invention according to the process of Figure 1 shows a method for producing waste solid fuel for recycling alternative energy by using waste PP, PE, etc. in wastewater and sewage sludge generated in the terminal treatment plant and industrial waste generated from industrial wastes as raw materials. ,
산업폐기물과 생활폐기물 중에서 P.V.C와 유황화합물 등 유해가스발생이 많은 폐기물과 불연물을 분리하며 적치 ·선별하는 공정(11)과 100m/m∼200m/m의 크기로 절단 ·파쇄하는 1차파쇄공정(12)과 폐비닐 등에 혼재한 금속류를 분리 ·제거하는 자석선별공정(13)을 거쳐 중간저장 Silo(15)에 이송하고,Process of separating and sorting wastes and non-combustibles, such as PVC and sulfur compounds, which have a lot of harmful gases, among industrial wastes and household wastes (11) and primary shredding process to cut and shred to 100m / m ~ 200m / m. 12) and transferred to the intermediate storage silo (15) through the magnet sorting process (13) for separating and removing the mixed metals such as waste vinyl,
한편 종말처리장의 하수 슬러지는 R.D.F 열분해 연소장치(21)의 열분해 Gas 연소열을 이용하는 Drum형 건조공정(18)에서 수분함량 75∼80%의 슬러지를 간접폐열을 이용하여 수분함량 25% 정도로 건조함으로써, 상기의 폐합성수지와 하수 Sludge의 1단계 원료화 처리공정이 끝난다.On the other hand, the sewage sludge in the terminal treatment plant is dried in the drum type drying process 18 using the pyrolysis gas combustion heat of the RDF pyrolysis combustion apparatus 21 by drying the sludge with water content of about 75% to about 80% by using indirect waste heat. The one-step raw material treatment process of the waste synthetic resin and sewage sludge is completed.
상기의 1단계 원료화 처리공정이 끝난 건조 하수 슬러지와 폐합성수지류를 각각 중량비 4:6의 비율(Sludge 4, 폐합성수지 6)로 혼합하며 원료 Feeder공정(25)에 의하여 열풍이용 건조 ·혼합장치(26)에 공급하고, 여기에서 혼합원료는 수분함량 15%정도로 건조 ·혼합되며, 이때에 중화제인 첨가제(소석회)를 분사, 투입, 혼합함으로써 건조 및 성형시에 SOx, HCl, CO 등의 유해가스발생으로 인한 다이옥신류의 배기를 억제하고 성형시 제품을 안정화하는데 효과가 있다.Drying sewage sludge and waste synthetic resins after the first stage raw material treatment process are mixed in a ratio of 4: 6 by weight ratio (Sludge 4, waste synthetic resin 6), respectively. (26), where the mixed raw materials are dried and mixed with a water content of about 15%. At this time, by spraying, injecting and mixing the additive (calcite lime), which is a neutralizing agent, harmful substances such as SOx, HCl, CO, etc. during drying and molding are supplied. It is effective in suppressing the exhaust of dioxins due to gas generation and stabilizing the product during molding.
상기의 전처리공정을 끝낸 원료는 혼합원료 Silo(28)를 거쳐 압출 · 성형공정(29)에서 고형화 성형하고, 이때 제조된 불규칙적인 크기의 성형물을 파쇄공정(30)에서 20m/m∼30m/m의 크기로 절단 ·파쇄하여 제품화하는 폐기물의 재활용 제조방법이다.The raw material which has completed the above pretreatment process is solidified in the extrusion and molding process 29 through the mixed raw material silo 28, and at this time, the molded product of irregular size is 20m / m to 30m / m in the crushing process 30. It is a recycling method for recycling wastes that are cut and crushed into a product of size.
상기의 재활용 제조 방법을 공정별로 상세히 설명하면 첫째, 폐합성수지류 하치 및 선별부(11)에서는 인력에 의한 불연물 기타 부적절한 재료를 분리 ·선별하고 종류별로 2∼3부분으로 분류 ·적치하여 균일 ·균질의 원료투입을 가능하도록 하는 공정이고, 1차파쇄공정(12)에서는 혼합 투입되는 원료를 길이 또는 직경이 100m/m∼200m/m의 사이즈로 절단·파쇄하는 공정이고, 전자석에 의한 금속류 선별공정(13)에서는 금속 또는 비철금속 및 흙, 돌맹이 등을 선별하고 고형화에 기계적영향을 주는 물질을 제거한 후 1단계 전처리공정을 완료하여 중간저장 Silo(15)에 이송한다.The recycling method described above is described in detail by process. First, the waste synthetic resin feed basin and sorting unit 11 separates and selects incombustibles and other inappropriate materials by manpower, and classifies and classifies them into two to three parts by uniformity and homogeneity. In the primary shredding step (12), the raw material to be mixed and introduced is cut and shredded to a size of 100 m / m to 200 m / m in length or diameter. In (13), the metal or non-ferrous metal, soil, boulder and the like are removed, and the material that has a mechanical effect on the solidification is removed, and the first step of pretreatment is completed to transfer to the intermediate storage silo (15).
둘째 하수 슬러지 하치장(16)에서는 종말처리장에서 탈수하여 폐기하는 슬러지(수분함량 75%∼80%)를 운송카고로 이송하여 하치하는 곳으로서 이미 종말처리장에서 활성탄(Active Carbon)처리로 악취가 제거된 상태이므로 별도의 방지시설이 필요 없는 하치장이며, 정량공급 Screw Feeder(17)에 의하여 일정량이 Drum형 건조공정(18)에 투입되고, 이 건조공정은 간접 폐열에 의한 건조방식이므로 건조 슬러지 중 유기물의 탄화를 방지하여 슬러지 본래의 연소발열량(2,000∼2,200Kcal/Kg)을 유지하며 수분함량 25% 정도로 건조하는 하수 Sludge의 1단계 원료화 전처리공정이다.Second, the sewage sludge dump (16) transfers sludge (water content 75% ~ 80%) which is dehydrated and disposed of at the end treatment plant to the transportation cargo, and has already been removed by odor treatment by active carbon treatment at the end treatment plant. Since it is a state, it is a dump which does not need a separate prevention facility, and a certain amount is put into the drum type drying process (18) by a fixed-quantity supply screw feeder (17), and this drying process is a drying method by indirect waste heat. It is a one-step raw material pretreatment process for sewage sludge that prevents carbonization and maintains the original combustion calorific value (2,000 ~ 2,200Kcal / Kg) and dries to 25% moisture content.
상기의 전처리공정이 끝난 하수 Sludge와 폐합성수지류는 중량비 4:6의 비율로 혼합하며 원료 Feeder(25)의 Hopper에 이송하여 혼합하면서 열풍이용 건조 ·혼합공정(26)에 투입하고 이때에 중화제인 소석회(Ca(OH)2)가 혼합원료 중량대비 0.5%∼0.8% 정도로 함께 투입되어 원료의 혼합 ·건조(수분함량 15%정도)조정공정이 이루어져 고형화 원료의 전처리공정이 끝나게 된다.The sewage sludge and waste synthetic resin finished after the pretreatment process are mixed in a ratio of 4: 6 by weight, and transferred to the hopper of the raw material feeder 25, and mixed into the drying and mixing process 26 using hot air. Slaked lime (Ca (OH) 2 ) is added together at about 0.5% to 0.8% of the weight of the mixed raw material, and the mixing and drying (about 15% moisture content) adjustment process of the raw material is completed, thus completing the pretreatment of the solidified raw material.
특히 첨가제인 소석회(Ca(OH)2)는 압출 ·성형공정(29)에서 250℃∼300℃의 높은 열에 의하여 합성수지류의 분해 현상이 있을시에 유황화물(SOx), 염화수소가스(HCl)등과 반응하여 중화함으로써 유해 Gas 발생을 억제하고, 또한 고형화의 압출 ·성형 제조시에 제품을 안정화하는 역할을 한다.In particular, slaked lime (Ca (OH) 2 ), an additive, is sulphide (SOx), hydrogen chloride gas (HCl), etc. when decomposition of synthetic resins occurs due to high heat of 250 ° C to 300 ° C in the extrusion and molding process (29). By reacting and neutralizing, it suppresses the generation of harmful gas and stabilizes the product during the extrusion and molding of solidification.
상기의 공정에서 건조공정(18)에 필요한 열원은 도1, 도2의 고형연료 제조공정에 의하여 제조된 고형연료(R.D.F)중 일부(120kg/hr∼150kg/hr)를 R.D.F 열분해연소장치(21)에서 최소한의 공기(이론 공기량의 60%∼70%)와 폐합성수지류의 열분해온도(400℃∼500℃)를 유지하며 열분해반응으로 얻어지는 미연소 가연성가스를 2차연소실(Combustor)(22)에 보내고, 여기에 F.D Fan에 의한 과잉의 공기를 공급하여 연소시킴으로써, 배출온도를 800℃이상 1000℃까지 높여 완전 연소는 물론 유해가스의 분해로 인하여 다이옥신의 발생을 최소화시킬 수 있으며, 이와 같이 높은 열을 건식 열교환기(24)를 통한 폐열(300℃∼500℃)은 슬러지 건조장치에 공급하여 수분함량 75%∼80%인 폐슬러지를 25%정도로 건조하고, 아울러 열교환기에 의하여 가열 열교환된 열풍(120℃∼150℃)은 건조 ·혼합공정(26)에 공급하여 수분함량(15%)을 조절하며 원료를 건조 ·혼합하고 조정한다.The heat source required for the drying process 18 in the above process is a part of the solid fuel (RDF) manufactured by the solid fuel manufacturing process of FIGS. 1 and 2 (120 kg / hr to 150 kg / hr). The secondary combustion chamber (22) maintains the minimum amount of air (60% to 70% of the theoretical air) and the pyrolysis temperature (400 ° C to 500 ° C) of the waste synthetic resin, and obtains the unburned combustible gas obtained by the pyrolysis reaction. By supplying and burning the excess air by FD Fan here, the discharge temperature can be increased to 800 ℃ or more and 1000 ℃ to minimize the generation of dioxins due to the complete combustion and decomposition of harmful gases. Waste heat (300 ° C. to 500 ° C.) through the dry heat exchanger 24 is supplied to the sludge drying apparatus to dry waste sludge having a water content of 75% to 80% to about 25%, and hot air heat-exchanged by a heat exchanger. (120 ℃ ~ 150 ℃) is dry and mixed hole Fed to 26 by controlling the water content (15%), and drying the raw material mixture, and adjusting.
혼합원료 Silo(28)공정에서는 압출 ·성형 공정(29)에 투입되기에 앞서 원료의 배합 및 혼합조건, 수분함량, 첨가제 투입의 적정 등 최적의 원료 상태를 조정하는 공정으로서 분사, 분무, 교반 등의 장치가 부착되어 있으며, <도5>의 압출 ·성형공정(29)은 쌍스크루type(Double Screw)의 용융 ·압출식 성형 장치로서, 전기코일에 의한 250℃∼300℃의 열을 가하여 폐합성수지류의 열분해를 최소화하고 폐합성수지류의 접착력을 이용하여 하수 슬러지와 함께 고형화 압출 ·성형하는 제조공정이다.In the mixed raw material silo (28) process, prior to being introduced into the extrusion and molding process (29), the process of adjusting the optimal raw material state such as mixing and mixing conditions of the raw materials, moisture content, and addition of additives is carried out by spraying, spraying, stirring, etc. The extrusion and molding process (29) of FIG. 5 is a double screw type (double screw) melting / extrusion molding apparatus, which is closed by applying heat of 250 ° C to 300 ° C by an electric coil. Minimizes thermal decomposition of synthetic resins and solidifies extrusion and molding together with sewage sludge by using adhesive strength of waste synthetic resins.
압출 ·성형공정(29)에서 불규칙한 사이즈로 성형된 고형물은 Steel망 진동이송장치로 파쇄공정(30)으로 이송되며 이때 냉풍을 이용하여 건조하고, 굳어진 건조 성형물은 20m/m∼30m/m의 크기로 절단·파쇄하여 제품화하는 폐기물의 재활용 자원화의 고형연료 제조방법이다.Solids molded into irregular sizes in the extrusion and molding process (29) are transferred to the crushing process (30) by a steel mesh vibration feeder. At this time, they are dried using cold air, and the hardened dry moldings have a size of 20 m / m to 30 m / m. It is a method for producing solid fuel by recycling waste material that is cut and crushed into a commercial product.
상기 공정에 의하여 제조된 고형화 연료는 제품 Silo(31)로 이송 ·보관되며, 포장 ·출하되고 이 중 일부(120kg/hr∼150kg/hr)는 하수 슬러지 건조공정(18)의 열원으로 이용하기 위하여 연료용 R.D.F저장조(19)에 이송하고 이것들은 R.D.F 열분해 연소장치(21)에 이송되어 연료로 재이용하는 고형연료화 제조방법이다.The solidified fuel produced by the above process is transported and stored in the product silo 31, packed and shipped, and some of them (120 kg / hr to 150 kg / hr) are used as heat sources of the sewage sludge drying process 18. The fuel is transferred to the RDF storage tank 19 for fuel, and these are solid fuel production methods that are transported to the RDF pyrolysis combustion apparatus 21 for reuse as fuel.
이상에서 설명한 바와 같이 폐하수 슬러지와 산업체의 폐합성수지류 및 생활폐기물 중의 P.E, P.P 등을 이용하여 자연친화적 처리공법에 의한 재활용 고형연료 제조방법으로서As described above, P.E, P.P, etc. in wastewater sewage sludge, industrial waste synthetic resins, and household wastes are used as a method for producing recycled solid fuel by a natural treatment method.
지금까지의 소각, 매립, 방치 등으로 인한 환경훼손 폐기물들을 대체에너지로 재이용할 수 있는 고형연료로 제조하여, 농촌 비닐하우스의 난방용으로 또한 산업체의 Boiler용으로 보급, 사용할 수 있게 하기 위한 대체에너지화 공법으로서,Alternative energy to make it possible to disseminate environmentally damaging wastes caused by incineration, landfilling, and disposal until now as alternative energy, and to disseminate and use it for heating of rural vinyl houses and industrial boilers. As a method,
특히 생산된 고형연료(R.D.F) 중 일부(건조용 열원, 120kg/hr∼150kg/hr)를 본 제조공정의 열원으로 사용함으로써 1일 5D/M~6D/M의 화석연료를 절감할 수 있는 대체 효과가 있으며, 1차 R.D.F 열분해 장치(21)와 2차 열분해 Gas 연소장치(22)에 의하여 고열로 폐기물을 완전 연소함으로써 다이옥신류의 발생을 최소화함은 물론 열교환, 집진, 활성탄여과 등의 대기오염 방지시설을 통하여 배기가스를 정화하여 배출하는 System으로, 폐기물을 재활용 고형연료로 제조하여 재활용하는 데 그 효과가 있다.In particular, by using some of the produced solid fuel (RDF) (drying heat source, 120kg / hr ~ 150kg / hr) as the heat source of the manufacturing process, it is possible to save 5D / M ~ 6D / M fossil fuel per day. It is effective and completely burns waste by high temperature by primary RDF pyrolysis unit 21 and secondary pyrolysis gas combustion unit 22 to minimize the generation of dioxins, as well as air pollution such as heat exchange, dust collection and activated carbon filtration. It is a system that purifies and discharges exhaust gas through prevention facilities, and it is effective to manufacture and recycle waste as recycled solid fuel.
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CN116177843B (en) * | 2023-04-27 | 2023-07-18 | 沧州信昌化工股份有限公司 | Treatment system and treatment method for water-containing coal slime |
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