KR100364984B1 - Manufacturing method and apparatus for powdered active carbon - Google Patents
Manufacturing method and apparatus for powdered active carbon Download PDFInfo
- Publication number
- KR100364984B1 KR100364984B1 KR1019990063125A KR19990063125A KR100364984B1 KR 100364984 B1 KR100364984 B1 KR 100364984B1 KR 1019990063125 A KR1019990063125 A KR 1019990063125A KR 19990063125 A KR19990063125 A KR 19990063125A KR 100364984 B1 KR100364984 B1 KR 100364984B1
- Authority
- KR
- South Korea
- Prior art keywords
- activated carbon
- carbon
- unreacted
- basic activated
- basic
- Prior art date
- Legal status (The legal status 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 status listed.)
- Expired - Lifetime
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/30—Active carbon
- C01B32/312—Preparation
- C01B32/318—Preparation characterised by the starting materials
- C01B32/324—Preparation characterised by the starting materials from waste materials, e.g. tyres or spent sulfite pulp liquor
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/30—Active carbon
- C01B32/39—Apparatus for the preparation thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/90—Other properties not specified above
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Carbon And Carbon Compounds (AREA)
- Water Treatment By Sorption (AREA)
Abstract
본 발명은 분말활성탄의 제조방법 및 제조장치에 관한 것으로, 더욱 상세하게는 폐기물로 취급하던 기존의 기초활성탄이나 미반응 카본을 사용하여 흡착력이 우수한 분말활성탄을 제조함으로써 기초활성탄이나 미반응 카본에 의한 환경오염을 방지하고, 이러한 폐기물을 처리시 발생되는 비용을 절감할 수 있는 분말활성탄의 제조장치 및 제조방법을 제공함에 그 목적이 있다.The present invention relates to a method for producing powdered activated carbon and a manufacturing apparatus, and more particularly, by using a basic activated carbon or unreacted carbon, which is treated as waste, to prepare powdered activated carbon having excellent adsorption power, It is an object of the present invention to provide an apparatus and a method for manufacturing powdered activated carbon which can prevent environmental pollution and reduce the cost of treating such waste.
그리고, 상기한 목적을 달성하기 위하여 본 발명은 기초활성탄이나 미반응 카본을 30~80메시로 1차 분쇄하는 단계와; 분쇄된 기초활성탄은 180~250℃에서 20분간 소성하거나, 분쇄된 미반응 카본은 400℃에서 20분간 소성하는 단계와; 소성된 기초활성탄이나 미반응 카본을 195~205메시로 2차 분쇄하는 단계와; 2차 분쇄된 기초활성탄이나 미반응 카본을 집진하여 분말활성탄으로 포집하는 단계; 및 상기 포집된 분말활성탄에 물을 분사하여 수분율을 조절하는 단계;로 구성되는 것을 특징으로 하는 분말활성탄의 제조방법을 제공하게 된다.In order to achieve the above object, the present invention comprises the steps of first crushing the basic activated carbon or unreacted carbon to 30 to 80 mesh; Pulverizing basic activated carbon for 20 minutes at 180 to 250 ° C., or pulverizing unreacted carbon for 20 minutes at 400 ° C .; Secondly pulverizing the calcined basic activated carbon or unreacted carbon with 195 to 205 mesh; Collecting the secondary ground basic activated carbon or unreacted carbon and collecting the powdered activated carbon; And controlling the moisture content by spraying water on the collected powdered activated carbon.
또한 본 발명은 기초활성탄이나 미반응 카본을 정량 투입하는 정령투입기(2-1)와; 상기 정량투입기(2-1)에서 정량 투입되는 기초활성탄이나 미반응 카본을 분쇄하는 제1분쇄기(2-2)와; 상기 제1분쇄기(2-2)에서 분쇄된 기초활성탄이나 미반응 카본을 저장하는 원료저장호퍼(2-4)와; 상기 원료저장호퍼(2-4)에서 투입되는 기초활성탄이나 미반응 카본을 소성하는 소성로(208)와; 상기 소성로(208)에서 배출되는 기초활성탄이나 미반응 카본을 분쇄하는 제2분쇄기(2-9)와; 상기 제2분쇄기(2-9)의 기초활성탄이나 미반응 카본을 집진하는 제2집진기(2-10)와; 상기 소성로(208)에서 배출되는 기초활성탄이나 미반응 카본의 미분을 미량으로 집진하여 상기 제2분쇄기(2-9) 또는 제2집진기(2-10)에 공급하는 제1집진기(2-13); 및 상기 제2집진기(2-10)에서 배출되는 분말활성탄에 물을 분사하여 수분율을 조절하는 수분조절기(2-11);로 구성되는 것을 특징으로 하는 분말활성탄의 제조장치를 제공하게 된다.In addition, the present invention is an element injector (2-1) for quantitatively adding basic activated carbon or unreacted carbon; A first mill (2-2) for milling basic activated carbon or unreacted carbon, which is metered in the metering unit (2-1); A raw material storage hopper (2-4) for storing the basic activated carbon or unreacted carbon pulverized in the first mill (2-2); A firing furnace 208 for firing basic activated carbon or unreacted carbon introduced from the raw material storage hopper 2-4; A second mill (2-9) for milling basic activated carbon or unreacted carbon discharged from the kiln (208); A second dust collector (2-10) for collecting the basic activated carbon or unreacted carbon of the second mill (2-9); A first dust collector (2-13) which collects a fine amount of basic activated carbon or unreacted carbon discharged from the kiln 208 and supplies it to the second mill (2-9) or the second dust collector (2-10); ; And a water regulator (2-11) for controlling water content by spraying water on the powdered activated carbon discharged from the second dust collector (2-10) to provide the apparatus for producing powdered activated carbon.
Description
본 발명은 분말활성탄의 제조방법 및 제조장치에 관한 것으로, 더욱 상세하게는 폐기물로 취급하던 기존의 기초활성탄이나 미반응 카본을 사용하여 흡착력이 우수한 분말활성탄을 제조하게 되는 분말활성탄의 제조방법 및 제조장치에 관한 것이다.일반적으로, 석유화학공정에서는 석유화학제품의 기초원료를 생산하기 위하여 합성가스를 제조하게 되는데, 이 합성가스의 제조공정은 벙커시오일과 크루드오일(Crude-Oil)등을 산소와 스팀하에서 산화시켜 탄소, 일산화탄소, 수소, 일산화 탄소+수소 등의 제조과정을 거쳐 합성가스를 제조하게 된다.다시 말하면, 도 1a에 도시한 바와 같이 가스화반응기(1-3)에서 벙커시오일과 기타오일을 보일러(1-1)와 산소예열기(1-2)를 이용하여 부분산화시켜 합성가스(CO+H2)를 제조하게 되고, 1~2%의 기초활성탄(반활성 및 미반응상태)을 생성하게 된다.이때, 가스화반응기(1-3)에서 부분산화시 발생되는 열은 폐열교환기(1-4)에 서 40kg/㎤G의 고압스팀으로 회수하게 된다.또한, 가스화반응기에서 생성된 가스중의 검댕과 매연, 재는 억제탑(Quench Tower)(1-5)및 분리탑(1-6)을 거치면서 제거되고, 이처럼 억제탑과 분리탑을 거치면서 생성되는 기초활성탄은 압축여과기(1-7)에서 탈수되어 회수된다.그리고, 벙커시오일 및 기타오일이 연료로 사용되어 연소실(1-9)에서 연소될 경우 미반응 카본이 사이클론(1-10)과 집진기(1-11)를 거쳐 포집된다.한편, 상기와 같은 공정을 통해 발생되는 기초활성탄 및 미반응 카본은 지금까지 산업폐기물로 분류되어 소각 및 폐기물로 처분되면서 그 과다한 처리비용과 환경오염을 초래하는 등의 문제가 있었다.The present invention relates to a method for producing powdered activated carbon and a manufacturing apparatus, and more particularly, to a method for producing powdered activated carbon which produces powdered activated carbon having excellent adsorptive power by using existing basic activated carbon or unreacted carbon treated as waste. In general, in petrochemical processes, syngas is produced to produce basic raw materials for petrochemical products. The process for syngas production includes bunker oil and crude oil. Oxidized under oxygen and steam to produce a synthesis gas through the manufacturing process of carbon, carbon monoxide, hydrogen, carbon monoxide + hydrogen, etc. In other words, as shown in Figure 1a, bunker sea oil in the gasification reactor (1-3) And other oils are partially oxidized using a boiler (1-1) and an oxygen preheater (1-2) to produce syngas (CO + H 2 ), and 1 to 2% of basic activated carbon (semi-active and In this case, heat generated during partial oxidation in the gasification reactor (1-3) is recovered by the high pressure steam of 40kg / cm3G in the waste heat exchanger (1-4). Soot, soot and ash in the gas produced in the reactor are removed through the quench tower (1-5) and the separation tower (1-6), and thus the basic activated carbon produced through the suppression tower and the separation tower. Is dehydrated and recovered in a compressed filter (1-7). When bunker sea oil and other oils are used as fuels and burned in the combustion chamber (1-9), unreacted carbon is stored in a cyclone (1-10) and a dust collector ( On the other hand, basic activated carbon and unreacted carbon generated through the above process are classified as industrial wastes so far and disposed of as incineration and wastes, resulting in excessive processing cost and environmental pollution. There was a problem.
본 발명은 이러한 종래의 문제를 개선하기 위하여 안출된 것으로, 폐기물로 취급하던 기존의 기초활성탄이나 미반응 카본을 사용하여 흡착력이 우수한 분말활성탄을 제조함으로써 기초활성탄이나 미반응 카본에 의한 환경오염을 방지하고, 이러한 폐기물을 처리시 발생되는 비용을 절감할 수 있는 분말활성탄의 제조장치 및 제조방법을 제공함에 그 목적이 있다.The present invention has been made in order to improve such a conventional problem, and by using the existing basic activated carbon or unreacted carbon treated as waste to produce powdered activated carbon having excellent adsorptive power to prevent environmental pollution by the basic activated carbon or unreacted carbon And, it is an object of the present invention to provide an apparatus and a method for producing powder activated carbon that can reduce the cost generated when treating such waste.
도 1a 및 도 1b는 석유화학공정의 합성가스제조설비에서 기초활성탄을 회수하는 공정을 예시한 예시도,1A and 1B are exemplary views illustrating a process of recovering basic activated carbon in a syngas manufacturing facility of a petrochemical process;
도 1c는 연료연소에 의해 미반응 카본을 회수한 공정을 예시하는 예시도,1C is an exemplary diagram illustrating a process of recovering unreacted carbon by fuel combustion;
도 2는 본 발명의 실시예를 나타내는 구성도,2 is a block diagram showing an embodiment of the present invention,
도 3및 도4는 본 발명의 사용방법을 예시한 예시도이다.3 and 4 are exemplary views illustrating the use method of the present invention.
<도면의 주요 부분에 대한 부호의 설명><Explanation of symbols for the main parts of the drawings>
1-1: 보일러 1-2 : 산소예열기 1-3: 가스화반응기 1-4: 폐열교환기1-1: boiler 1-2: oxygen preheater 1-3: gasification reactor 1-4: waste heat exchanger
1-5 : 억제탑 1-6: 분리탑 1-7 : 압축여과기 1-8: 다단소각로 1-9: 연소실1-5: suppression tower 1-6: separation tower 1-7: compression filter 1-8: multi-stage incinerator 1-9: combustion chamber
1-10: 사이클론 1-11: 집진기1-10: Cyclone 1-11: Dust Collector
2-1 : 정량 투입기 2-2 : 제1분쇄기 2-3: 콘베어벨트2-4: 원료저장호퍼 2-8: 소각로2-1: Dosing machine 2-2: First grinder 2-3: Conveyor belt 2-4: Raw material storage hopper 2-8: Incinerator
2-9 : 제2분쇄기 2-10: 제2집진기 2-11 : 수분조절기2-9: second grinder 2-10: second dust collector 2-11: moisture controller
2-12 : 부원료저장호퍼 2-13 : 제1집진기2-12: secondary raw material storage hopper 2-13: first dust collector
상기한 목적을 달성하기 위하여 본 발명은 기초활성탄이나 미반응 카본을 30~80메시로 1차 분쇄하는 단계와; 분쇄된 기초활성탄은 180~250℃에서 20분간 소성하거나, 분쇄된 미반응 카본은 400℃에서 20분간 소성하는 단계와; 소성된 기초활성탄이나 미반응 카본을 195~205메시로 2차 분쇄하는 단계와; 2차 분쇄된 기초활성탄이나 미반응 카본을 집진하여 분말활성탄으로 포집하는 단계; 및 상기 포집된 분말활성탄에 물을 분사하여 수분율을 조절하는 단계;로 구성되는 것을 특징으로 하는 분말활성탄의 제조방법을 제공하게 된다.또한 본 발명은 기초활성탄이나 미반응 카본을 정량 투입하는 정량투입기와; 상기 정량투입기에서 정량 투입되는 기초활성탄이나 미반응 카본을 분쇄하는 제1분쇄기와; 상기 제1분쇄기에서 분쇄된 기초활성탄이나 미반응 카본을 저장하는 원료저장호퍼와; 상기 원료저장호퍼에서 투입되는 기초활성탄이나 미반응 카본을 소성하는 소성로와; 상기 소성로에서 배출되는 기초활성탄이나 미반응 카본을 분쇄하는 제2분쇄기와; 상기 제2분쇄기의 기초활성탄이나 미반응 카본을 집진하는 제2집진기와; 상기 소성로에서 배출되는 기초활성탄이나 미반응 카본의 미분을 미량으로 집진하여 상기 제2분쇄기 또는 제2집진기에 공급하는 제1집진기; 및 상기 제2집진기에서 배출되는 분말활성탄에 물을 분사하여 수분율을 조절하는 수분조절기;로 구성되는 것을 특징으로 하는 분말활성탄의 제조장치를 제공하게 된다.이하, 첨부된 도면을 참조하여 본 발명의 바람직한 실시예를 설명하기로 한다.도2는 본 발명의 실시예를 나타내는 구성도이고, 도3및 도4는 본 발명의 사용방법을 예시한 예시도이다.석유화학공정에 있어서 석유화학제품의 기초원료를 생산하기 위한 합성가스의 제조공정에서 발생되는 기초활성탄이나, 연소시 발생되는 미반응 카본을 정량투입기(2-1)를 통해 제1분쇄기(2-2)에 투입하게 된다.그리고, 제1분쇄기(2-2)에서는 정량투입기(2-1)에서 공급된 미반응 카본을 30~80메시(mesh)로 분쇄하게 되고, 이처럼 분쇄된 미반응 카본을 콘베어벨트(2-3)를 이용하여 원료저장호퍼(2-4)에 저장하게 되며, 다시 원료저장호퍼(2-4)에서 일정량씩 소성로(2-8)로 투입하게 된다.이때, 상기 소성로(2-8)는 로터리킬른(Rotary kiln)방식으로 그 투입구가 높고 토출구가 낮게 설치되어 흡입팬에 의한 열원의 이동과 로내의 열체류시간을 용이하게 조절하도록 구성되어 있다.여기서 소성로(2-8)는 600~800℃로 운전되는데, 합성가스의 제조공정에서 발생되는 기초활성탄을 원료로 사용하는 경우 180~250℃의 온도로 20분간 소성하게 되지만, 연료연소공정에서의 미반응 카본을 원료로 사용하는 경우 350~450℃의 온도로 20분간 소성하게 된다.또한, 소성로(2-8)에서 소성처리된 원료는 제2분쇄기(2-9)로 이송되어 195~205메시의 미분으로 분쇄되지만, 제1집진기(2-13)에서는 흡입팬을 이용하여 소성로에서 제2분쇄기로 투입되는 소성원료중 미량의 미분을 흡입하여 저장하게 된다.그리고, 제1집진기(2-13)에 집진된 미량의 미분은 제2분쇄기(2-9)에 재투입되어 부원료(규조토, 백토, 벤토나이트, 제오라이트, 석유화학 소각재, 무연탄 소각재 등)와 혼합되거나 제2집진기(2-10)에 재투입된다.이때, 부원료저장호퍼(2-12)에 저장되는 규조토, 백토, 벤토나이트, 제오라이트, 석유화학 소각재, 무연탄 소각재 등과 같은 각종 부원료는 사용용도에 따라 선택되어 분말활성탄의 충전재(Filler)로서 혼합되어 사용되는데, 상기와 같이 부원료저장호퍼(2-12)에 저장되어 있다가 제2분쇄기(2-9)에 투입되거나 소성로(2-8)의 입구를 통해 소성로내에 투입되기도 한다.여기서, 제2집진기(2-10)에 집진된 원료는 수분조절기(2-11)에서 슈요가가 원하는 수분율로 조절되어 분말활성탄으로 출하되는데, 수분조절기에서는 분사노즐을 통해 물을 스프레이하여 미분상태의 원료에 수분을 혼합시켜 분말활성탄의 수분율을 조절하게 된다.한편, 상기와 같은 제조장치 및 방법을 통해 제조되는 분말활성탄은 폐수처리용으로 사용될 경우, 폐수의 성상과 조건에 따라 사용방법이 달라질 수 있으나 일반적으로 물에 녹여 사용하는 것이 바람직하다.특히, 도3에 예시한 바와 같이 집수장(3-1)에 분말활성탄을 투입하여 유기물 및 색도를 제거하는 (가)의 사용방법은 화학적 산소요구량(COD), 생물학적 산소요구량(BOD) 등과 색도가 일반적으로 약한 경우 사용하게 되고, 공기 및 교반기로 3시간이상 교반하여 침전 처리한 후, 방류 및 미생물처리 등의 기타 공정으로 진행된다,또한, (나)의 위치에서 분말활성탄을 투입하는 사용방법은 집수장(3-1)의 폐수를 화학처리조(3-2)에서 화학처리하고, 침전조(3-3)에서 침전처리하여 화학적 산소요구량과 색도를 제거한 다음 분말활성탄을 투입하게 되며, 미생물폭기조(3-4)에서 3시간이상 교반체류 후에 침전조(3-5)로 방류하게 된다.그리고, (다)의 위치에서 분말활성탄을 투입하는 사용방법은 미생물폭기조(3-4)의 입구에 분말활성탄을 투입하는 방법으로써, 미생물증식, 화학적 산소요구량, 생물학적 산소요구량 및 색도제거가 동시에 진행되며, 일정량의 미생물과 폐활성탄소를 미생물폭기조의 말단으로부터 침전조(3-5)를 이용하여 제거하면서 폐기처리된다.더욱이, (라)의 위치에서 분말활성탄을 투입하는 사용방법은 전처리공정인 물리, 화학적 처리를 기본으로 화학적 산소요구량, 생물화학적 산소요구량, 색도를 제거하였으나 제거되지 않은 난분해성 등의 물질로 인한 화학적 산소요구량, 생물화학적 산소요구량, 색도가 잔존된 경우 사용하는 방법으로써 가장 바람직한 사용방법이라 할수 있으며, 2차처리조 및 침전조(3-6)의 입구에서 분말활성탄을 투입한후, 3시간 이상 교반처리 후 침전 방류하여야 한다.도4에 예시한 바와 같이 본 발명에 따른 분말활성탄을 비료(유기비료나 화학비료)와 흙(4-1)과 함께 로터리(4-2) 등에서 혼합하여 식물의 파종 및 생장에 사용하거나, 먼저 분말활성탄과 흙(4-1)을 로터리에서 혼합한 혼합흙(4-3)을 이용하여 식물의 파종 및 생장에 사용하고 생장관리시 비료를 투입하는 방법이 있다.이때, 분말활성탄은 다공성에 의한 보습, 보온의 효과와 원활한 영양의 흡수 및 방출에 따라 식물이 잘 성장하도록 작용하게 된다.부언하면, 본 발명의 분말활성탄은 그 흡착능력이 매우 우수하여 쓰레기소각시 연소가스중에 연속 주입시키게 되면 연소가스중 다이옥신과 함께 중금속 등을 완벽하게 흡착하여 제거하게 된다.In order to achieve the above object, the present invention comprises the steps of first crushing the basic activated carbon or unreacted carbon to 30 to 80 mesh; Pulverizing basic activated carbon for 20 minutes at 180 to 250 ° C., or pulverizing unreacted carbon for 20 minutes at 400 ° C .; Secondly pulverizing the calcined basic activated carbon or unreacted carbon with 195 to 205 mesh; Collecting the secondary ground basic activated carbon or unreacted carbon and collecting the powdered activated carbon; And controlling the moisture content by spraying water on the collected powdered activated carbon. The present invention also provides a method for preparing powdered activated carbon. Wow; A first crusher for pulverizing basic activated carbon or unreacted carbon quantitatively inputted in the quantitative input machine; A raw material storage hopper storing basic activated carbon or unreacted carbon pulverized in the first mill; A kiln for firing basic activated carbon or unreacted carbon introduced from the raw material storage hopper; A second mill for milling basic activated carbon or unreacted carbon discharged from the kiln; A second dust collector for collecting the basic activated carbon or unreacted carbon of the second mill; A first precipitator which collects fine powder of basic activated carbon or unreacted carbon discharged from the kiln in a small amount and supplies it to the second mill or the second dust collector; And a water regulator for controlling water content by spraying water on the powdered activated carbon discharged from the second dust collector. Hereinafter, the present invention will be described with reference to the accompanying drawings. 2 is a block diagram showing an embodiment of the present invention, Figure 3 and Figure 4 is an exemplary view illustrating the method of use of the present invention. Basic activated carbon generated in the synthesis gas production process for producing the basic raw material or unreacted carbon generated during combustion is introduced into the first grinder 2-2 through the quantitative feeder 2-1. In the first mill (2-2), the unreacted carbon supplied from the metering unit (2-1) is crushed into 30 to 80 mesh, and the unreacted carbon is crushed to the conveyor belt (2-3). By using the raw material storage hopper (2-4) Then, the raw material storage hopper (2-4) is put into the kiln (2-8) by a predetermined amount. At this time, the kiln (2-8) is a rotary kiln (Rotary kiln) method, the inlet is high and the discharge port is low It is configured to easily control the movement of heat source by the suction fan and the heat residence time in the furnace. Here, the kiln 2-8 is operated at 600 to 800 ° C, and the basic activated carbon generated in the manufacturing process of syngas Is fired for 20 minutes at a temperature of 180 to 250 ° C, but when unreacted carbon in the fuel combustion process is used as a raw material, it is fired for 20 minutes at a temperature of 350 to 450 ° C. The raw material calcined in 2-8) is transferred to the second mill (2-9) and pulverized into fine powders of 195 to 205 mesh. However, in the first dust collector (2-13), the second mill in the kiln using a suction fan. A small amount of fine powder is sucked and stored in the fired raw material. The fine powder collected in the first dust collector (2-13) is re-injected into the second mill (2-9) and mixed with secondary raw materials (diatomaceous earth, clay, bentonite, zeolite, petrochemical incinerator, anthracite incinerator, etc.) or It is re-injected into the dust collector (2-10). At this time, various secondary raw materials such as diatomaceous earth, clay, bentonite, zeolite, petrochemical incineration ash, anthracite incineration ash, etc. stored in the secondary raw material storage hopper (2-12) are selected according to the intended use. It is mixed and used as a filler of powdered activated carbon, which is stored in the secondary raw material storage hopper 2-12 as described above, and then put into the second mill 2-9 or through the inlet of the kiln 2-8. Here, the raw material collected in the second dust collector (2-10) is controlled by the moisture content of the moisture regulator (2-11) to the desired moisture content and shipped as powder activated carbon. By spraying water The moisture content of the powdered activated carbon is controlled by mixing water with the raw material. Meanwhile, when the powdered activated carbon produced by the above-described manufacturing apparatus and method is used for wastewater treatment, the method of use may vary depending on the characteristics and conditions of the wastewater. However, in general, it is preferable to dissolve it in water and use it. Particularly, as shown in FIG. 3, the method of using (a) to remove organic matter and chromaticity by adding powdered activated carbon to the water collecting plant 3-1 includes chemical oxygen demand. (COD), Biological Oxygen Demand (BOD), etc., are generally used when the chromaticity is weak, followed by precipitation for 3 hours or more with air and agitator, followed by other processes such as discharge and microbial treatment. The method of injecting powdered activated carbon at the position of b) requires chemical oxygen treatment by chemical treatment of wastewater in the sump (3-1) in a chemical treatment tank (3-2) and precipitation treatment in a precipitation tank (3-3). After removing the amount and chromaticity, the powder activated carbon is added, and after stirring for 3 hours or more in the microbial aeration tank (3-4), it is discharged to the settling tank (3-5). The method of use is the method of injecting powder activated carbon into the inlet of the microbial aeration tank (3-4), and the microbial growth, chemical oxygen demand, biological oxygen demand and color removal are carried out simultaneously. In addition, the method of adding powdered activated carbon at the position of (D) is based on the chemical oxygen demand and biochemical process based on the physical and chemical treatment, which is a pretreatment process. It is used when chemical oxygen demand, biochemical oxygen demand, and chromaticity remain due to substances such as oxygen demand and chromaticity that have been removed but not removed. As a method, it is the most preferable method of use, and powder activated carbon is introduced at the inlet of the secondary treatment tank and the settling tank (3-6), and then precipitated and discharged after stirring for 3 hours or more. Powdered activated carbon according to the invention is mixed with fertilizers (organic fertilizers or chemical fertilizers) and soil (4-1) in a rotary (4-2) and the like and used for planting and growth of plants, or first, powdered activated carbon and soil (4-1). ) Is used for planting and growing plants using mixed soil (4-3) mixed at the rotary, and fertilizer is added during the growth management. Plants grow well according to the absorption and release of nutrients. In addition, the powdered activated carbon of the present invention has an excellent adsorption capacity, and when it is continuously injected into the combustion gas during incineration of garbage, It is removed completely absorbed in the like.
본 발명에서는 기존에 폐기물로 취급하던 기초활성탄이나 미반응 카본을 재활용하여 우수한 품질의 분말활성탄을 만들어 사용함으로써 환경오염을 방지하고, 폐기물처리시 발생되는 비용을 절감할 수 있는 등의 효과를 제공하게 된다.In the present invention, it is possible to recycle the basic activated carbon or unreacted carbon, which was previously treated as waste, to make powdered activated carbon of good quality, to prevent environmental pollution, and to reduce the cost of waste disposal. do.
Claims (3)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR1019990063125A KR100364984B1 (en) | 1999-12-27 | 1999-12-27 | Manufacturing method and apparatus for powdered active carbon |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR1019990063125A KR100364984B1 (en) | 1999-12-27 | 1999-12-27 | Manufacturing method and apparatus for powdered active carbon |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| KR20010060716A KR20010060716A (en) | 2001-07-07 |
| KR100364984B1 true KR100364984B1 (en) | 2002-12-26 |
Family
ID=19630509
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| KR1019990063125A Expired - Lifetime KR100364984B1 (en) | 1999-12-27 | 1999-12-27 | Manufacturing method and apparatus for powdered active carbon |
Country Status (1)
| Country | Link |
|---|---|
| KR (1) | KR100364984B1 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR102362474B1 (en) | 2021-09-08 | 2022-02-14 | 박윤기 | Apparatus and method for manufacturing activated carbon |
| KR20220141023A (en) | 2021-04-12 | 2022-10-19 | 무림케미칼 주식회사 | Manufacturing method of powdered active carbon by use of unreacted carbon |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110090620A (en) * | 2019-05-10 | 2019-08-06 | 广州尊卓环保科技有限公司 | A kind of spherical filtrate and its preparation method and application except organophosphorus pesticide |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3994829A (en) * | 1970-11-23 | 1976-11-30 | Standard Oil Company | Process for production of activated carbon |
| JPH08143306A (en) * | 1994-11-15 | 1996-06-04 | Hokkaido Rehabili | Granular carbon |
| JPH08231212A (en) * | 1995-02-28 | 1996-09-10 | Kansai Electric Power Co Inc:The | Activated carbon manufacturing method |
| KR19990045875A (en) * | 1999-02-03 | 1999-06-25 | 이선균 | Composition for treating waste-water and method for producing thereof |
| KR100210363B1 (en) * | 1997-06-19 | 1999-07-15 | 송민헌 | Preparation of absorbent using waste dust and process for abosrptive filtration |
-
1999
- 1999-12-27 KR KR1019990063125A patent/KR100364984B1/en not_active Expired - Lifetime
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3994829A (en) * | 1970-11-23 | 1976-11-30 | Standard Oil Company | Process for production of activated carbon |
| JPH08143306A (en) * | 1994-11-15 | 1996-06-04 | Hokkaido Rehabili | Granular carbon |
| JPH08231212A (en) * | 1995-02-28 | 1996-09-10 | Kansai Electric Power Co Inc:The | Activated carbon manufacturing method |
| KR100210363B1 (en) * | 1997-06-19 | 1999-07-15 | 송민헌 | Preparation of absorbent using waste dust and process for abosrptive filtration |
| KR19990045875A (en) * | 1999-02-03 | 1999-06-25 | 이선균 | Composition for treating waste-water and method for producing thereof |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20220141023A (en) | 2021-04-12 | 2022-10-19 | 무림케미칼 주식회사 | Manufacturing method of powdered active carbon by use of unreacted carbon |
| KR102362474B1 (en) | 2021-09-08 | 2022-02-14 | 박윤기 | Apparatus and method for manufacturing activated carbon |
Also Published As
| Publication number | Publication date |
|---|---|
| KR20010060716A (en) | 2001-07-07 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Wang et al. | Technological options for the management of biosolids | |
| CN101839488B (en) | Method for gasifying and incinerating combustible solid wastes by utilizing rotary kiln | |
| CN100534649C (en) | Domestic garbage cleaning treatment method | |
| CN106734084A (en) | A kind of solid waste substance treating method | |
| DE10021383A1 (en) | Processing of organic waste materials to produce fuels, electricity and fertilizer includes fermentation, carbonization and steam reforming | |
| KR101348132B1 (en) | Combined production process for solid fuel and rreducing agent of nox using organic waste sludge | |
| CN112044395A (en) | Phosphate adsorbent preparation system and method using excess sludge and biological shell wastes as raw materials | |
| US20020148780A1 (en) | Method of enhancing biological activated sludge treatment of waste water, and a fuel product resulting therefrom | |
| CN115634907A (en) | A method of co-processing construction waste and domestic waste to make garden planting soil | |
| Spinosa | From sludge to resources through biosolids | |
| CN207845456U (en) | A kind of system using garden waste harmless treatment domestic sludge | |
| KR20150019062A (en) | Food wastes dry product fertilizer using food waste and manufacturing the same | |
| CN112047597A (en) | Comprehensive treatment process and system for preparing gas fertilizer by combining biological drying and gasification of sludge | |
| CN107900069A (en) | A kind of method and system of domestic garbage resource | |
| KR100741696B1 (en) | Organic Fertilizer Manufacturing Method Using Food Waste | |
| CN202543012U (en) | Fluid sludge treatment device for generating clean combustible gas | |
| Rusanescu et al. | Recovery of treated sludge | |
| CN110777057B (en) | A coordinated treatment system for urban organic solid waste | |
| JP7268647B2 (en) | Sludge-to-fuel device, sludge-to-fuel system, sludge-to-fuel factory, and sludge-to-fuel method | |
| CN101812313A (en) | Sludge fuel oil | |
| CN210915973U (en) | Sludge biomass fuel particle production device | |
| CN107601795A (en) | A kind of method and system using garden waste harmless treatment domestic sludge | |
| EP0970933A2 (en) | Slow release matrix bound fertilisers | |
| CN117716969A (en) | A method for preparing improved soil by calcining sludge coupled with carbide residue | |
| CN114525146B (en) | Double-internal-circulation activated sludge resource utilization type disposal method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A201 | Request for examination | ||
| PA0109 | Patent application |
Patent event code: PA01091R01D Comment text: Patent Application Patent event date: 19991227 |
|
| PA0201 | Request for examination | ||
| PG1501 | Laying open of application | ||
| E902 | Notification of reason for refusal | ||
| PE0902 | Notice of grounds for rejection |
Comment text: Notification of reason for refusal Patent event date: 20020130 Patent event code: PE09021S01D |
|
| E701 | Decision to grant or registration of patent right | ||
| PE0701 | Decision of registration |
Patent event code: PE07011S01D Comment text: Decision to Grant Registration Patent event date: 20021128 |
|
| GRNT | Written decision to grant | ||
| PR0701 | Registration of establishment |
Comment text: Registration of Establishment Patent event date: 20021203 Patent event code: PR07011E01D |
|
| PR1002 | Payment of registration fee |
Payment date: 20021204 End annual number: 3 Start annual number: 1 |
|
| PG1601 | Publication of registration | ||
| J204 | Request for invalidation trial [patent] | ||
| PJ0204 | Invalidation trial for patent |
Patent event date: 20050614 Comment text: Request for Trial Patent event code: PJ02042R01D Patent event date: 20021203 Comment text: Registration of Establishment Patent event code: PJ02041E01I Appeal kind category: Invalidation Request date: 20050614 Decision date: 20060529 Appeal identifier: 2005100001366 |
|
| PR1001 | Payment of annual fee |
Payment date: 20051201 Start annual number: 4 End annual number: 4 |
|
| J301 | Trial decision |
Free format text: TRIAL DECISION FOR INVALIDATION REQUESTED 20050614 Effective date: 20060529 |
|
| PJ1301 | Trial decision |
Patent event code: PJ13011S05D Patent event date: 20060601 Comment text: Trial Decision on Invalidation (Patent, Utility Model, Industrial Design) Appeal kind category: Invalidation Request date: 20050614 Decision date: 20060529 Appeal identifier: 2005100001366 |
|
| PR1001 | Payment of annual fee |
Payment date: 20061204 Start annual number: 5 End annual number: 5 |
|
| PR1001 | Payment of annual fee |
Payment date: 20071130 Start annual number: 6 End annual number: 6 |
|
| PR1001 | Payment of annual fee |
Payment date: 20081203 Start annual number: 7 End annual number: 7 |
|
| PR1001 | Payment of annual fee |
Payment date: 20090925 Start annual number: 8 End annual number: 8 |
|
| PR1001 | Payment of annual fee |
Payment date: 20101124 Start annual number: 9 End annual number: 9 |
|
| PR1001 | Payment of annual fee |
Payment date: 20111130 Start annual number: 10 End annual number: 10 |
|
| FPAY | Annual fee payment |
Payment date: 20121129 Year of fee payment: 11 |
|
| PR1001 | Payment of annual fee |
Payment date: 20121129 Start annual number: 11 End annual number: 11 |
|
| FPAY | Annual fee payment |
Payment date: 20131121 Year of fee payment: 12 |
|
| PR1001 | Payment of annual fee |
Payment date: 20131121 Start annual number: 12 End annual number: 12 |
|
| FPAY | Annual fee payment |
Payment date: 20140929 Year of fee payment: 13 |
|
| PR1001 | Payment of annual fee |
Payment date: 20140929 Start annual number: 13 End annual number: 13 |
|
| FPAY | Annual fee payment |
Payment date: 20151102 Year of fee payment: 14 |
|
| PR1001 | Payment of annual fee |
Payment date: 20151102 Start annual number: 14 End annual number: 14 |
|
| FPAY | Annual fee payment |
Payment date: 20161202 Year of fee payment: 15 |
|
| PR1001 | Payment of annual fee |
Payment date: 20161202 Start annual number: 15 End annual number: 15 |
|
| FPAY | Annual fee payment |
Payment date: 20171116 Year of fee payment: 16 |
|
| PR1001 | Payment of annual fee |
Payment date: 20171116 Start annual number: 16 End annual number: 16 |
|
| FPAY | Annual fee payment |
Payment date: 20181119 Year of fee payment: 17 |
|
| PR1001 | Payment of annual fee |
Payment date: 20181119 Start annual number: 17 End annual number: 17 |
|
| FPAY | Annual fee payment |
Payment date: 20191202 Year of fee payment: 18 |
|
| PR1001 | Payment of annual fee |
Payment date: 20191202 Start annual number: 18 End annual number: 18 |
|
| PC1801 | Expiration of term |
Termination date: 20200627 Termination category: Expiration of duration |