WO2020101119A1 - Activated carbon pretreatment apparatus, and method for manufacturing anaerobic biological activated carbon by using same - Google Patents

Activated carbon pretreatment apparatus, and method for manufacturing anaerobic biological activated carbon by using same Download PDF

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WO2020101119A1
WO2020101119A1 PCT/KR2019/003398 KR2019003398W WO2020101119A1 WO 2020101119 A1 WO2020101119 A1 WO 2020101119A1 KR 2019003398 W KR2019003398 W KR 2019003398W WO 2020101119 A1 WO2020101119 A1 WO 2020101119A1
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Abstract

The objective of the present invention is to provide an activated carbon pretreatment apparatus for forming an optimal environment for the growth of anaerobes in order to promote the production of biogas including methane, and a method for manufacturing anaerobic biological activated carbon by using same. The activated carbon pretreatment apparatus according to the present invention comprises: a heating chamber (10) storing water therein, and having a heating part (12) for heating the water; a pretreatment compartment (20) which is immersed in the water inside the heating chamber (10) and which stores activated carbon (1) therein; a heating compartment (30) which is formed in the inner lower area of the heating chamber (10) around the pretreatment compartment (20), and which is provided so that hot water is generated by means of the heating part (12), and thus gas solubility of the pretreatment compartment (20) is reduced; a hot water collecting compartment (40) formed in the inner upper area of the heating chamber (10) with respect to the pretreatment compartment (20); and a gas collecting compartment (50) which is formed as an empty space in the upper area of the hot water collecting compartment (40) so as to collect steam vaporized inside the heating chamber (10) and gas (1a) containing oxygen removed from the activated carbon (1), and which has an exhaust pipe (52) that discharges the collected steam and gas (1a) to the outside of the heating chamber (10).

Description

활성탄 전처리장치 및 이를 이용한 혐기성 생물활성탄 제조방법Activated carbon pretreatment device and anaerobic bioactive carbon manufacturing method using same
본 발명은 활성탄 전처리장치 및 이를 이용한 혐기성 생물활성탄 제조방법으로서, 이를 보다 상세히 설명하면 메탄을 포함한 바이오 가스를 생산을 촉진하기 위해 혐기성 미생물의 증식에 최적의 환경을 조성하는 활성탄 전처리장치 및 이를 이용한 혐기성 생물활성탄 제조방법에 관한 것이다.The present invention is an activated carbon pretreatment device and an anaerobic bioactive carbon production method using the same, and in more detail, an activated carbon pretreatment device and an anaerobic system using the activated carbon pretreatment device that creates an optimal environment for the growth of anaerobic microorganisms to promote the production of biogas containing methane It relates to a method for producing bioactive carbon.
일반적으로 최근 인구증가, 산업발달, 생활수준의 향상에 따라 생활오수, 산업폐수, 가축폐수를 비롯한 각종 유기성폐수 등의 배출량이 급속히 증가하여 이로 인한 강, 하천, 호수, 바다 등의 수질오염이 심각한 지경에 이르고 있다. 특히 수질오염의 주원인인 유기물을 정화하기 위한 방법으로 화학적 처리 방법 및 생물학적 처리방법 등이 사용되고 있으나, 화학적 처리방법은 장비와 약품비가 고가이므로 비교적 운영비용이 저렴한 미생물을 이용한 생물학적 처리방법을 선호하는 추세이다.In general, due to the recent increase in population, industrial development, and improvement in living standards, discharges of various types of organic wastewater such as domestic wastewater, industrial wastewater, livestock wastewater have increased rapidly, resulting in serious water pollution in rivers, rivers, lakes, and seas. It is reaching the point. In particular, chemical treatment methods and biological treatment methods are used as methods for purifying organic substances that are the main cause of water pollution, but chemical treatment methods tend to prefer biological treatment methods using microorganisms, which are relatively inexpensive to operate, because equipment and chemicals are expensive. to be.
하지만, 생물학적 처리방법은 미생물이 유기물을 분해하는 방법으로서 미생물이 유기물을 분해하기까지 상당한 시간이 소요되고 고액분리를 하는 침전조에서의 슬러지 부상 등으로 인한 침전효율 저하 및 운전의 어려움으로 인한 안정적인 처리 수질 확보가 어려움으로 근자에는 활성탄을 이용하여 오염물질을 흡착 제거하고자 하는 기술이 개발되고 있다.However, the biological treatment method is a method in which microorganisms decompose organic substances, and it takes considerable time for microorganisms to decompose organic substances, and stable treatment water quality due to deterioration in precipitation efficiency and difficulty in operation due to sludge injury in a sedimentation tank that separates solids and liquids As it is difficult to secure, recently, a technique for adsorbing and removing contaminants using activated carbon has been developed.
여기서 활성탄은 흡착제로 주로 많이 사용 되는 물질로써 각종 유기물이나 무기물로 이루어진 오염원뿐만 아니라 세균 및 미생물 등이 활성탄 칼럼을 통과할 때 오염물질들이 각 활성탄의 표면에 흡착한다. 이처럼 활성탄은 넓은 비표면적으로 흡착용량이 크고, 뛰어난 흡착 능력으로 오염물질 제거효율에 높은 특징을 나타내며 다른 처리방법에 비해 매우 저렴하다는 장점이 있다. 하지만 표면이 비극성이기 때문에 암모니아 등 비점이 낮고 극성성분에 대해서는 흡착 효율이 낮은 것으로 알려져 있다.Here, activated carbon is a material mainly used as an adsorbent, and contaminants adsorb on the surface of each activated carbon when bacteria, microorganisms, etc., pass through the activated carbon column as well as pollutants made of various organic or inorganic materials. As such, activated carbon has a large specific surface area, a large adsorption capacity, and has excellent characteristics for removing pollutants with excellent adsorption ability, and is very cheap compared to other treatment methods. However, since the surface is non-polar, it is known that a boiling point such as ammonia is low and adsorption efficiency is low for polar components.
이에 종래에 개시된 한국등록특허 10-1407506호의 “활성탄 제조를 위한 탄소원료의 전처리 방법”에는 흡착성능을 높이기 위하여 기공 표면에 산이나 알칼리를 첨착 시킨 후, 그 흡착성능을 높여 특정 성분에 대하여 선택적으로 흡착 시킬 수 있는 활성탄의 제조방법을 개시되어 있지만, 화학 물질을 세정하기 위해서 다량의 물을 소모시키고 세척된 물을 다시 처리해야만 하여 비용 및 시간이 많이 소요되고, 또 강력한 화학 반응에 의해서 활성탄이 가지고 있는 고유한 흡착 능력이 파괴되어 오염물질의 제거 효율이 떨어지는 문제점이 따랐다.Accordingly, in the prior art disclosed in Korean Patent Registration No. 10-1407506, “Pretreatment method of carbon raw material for the production of activated carbon,” impregnated with an acid or alkali on the surface of the pores in order to increase the adsorption performance, and then selectively increase the adsorption performance to select specific components. Although a method of producing activated carbon capable of adsorbing is disclosed, it is costly and time consuming because a large amount of water is consumed in order to clean chemicals and the washed water must be treated again, and activated carbon is possessed by a strong chemical reaction. The inherent adsorption ability was destroyed, and the removal efficiency of pollutants fell.
또, 다른 종래기술인 특허등록 10-1564368호의 “복합미생물 부착형 활성탄 제조방법”는 복합미생물 부착형 활성탄 제조방법에 관한 것으로, 보다 상세하게는 활성탄 제조 시 활성화 단계에서 죽초액을 이용하여 수소이온지수를 조절하고 미생물을 복합, 접종하여 수질 정화능력을 극대화한 구성이 선 등록된바 있지만, 활성탄 기공에 잔류하는 기체(산소)로 인해 혐기성 미생물을 접종 시 증식율이 크게 저하되고, 특히 활성탄을 이용하여 수질 정화능력을 향상시키기 위한 전용용도이므로, 유기물 분해와 더불어 바이오 가스를 생산하는 범용의 혐기성 생물활성탄으로 적용이 불가능한 폐단이 따랐다.In addition, another prior art patent registration No. 10-1564368 "Compound Microorganism Attached Activated Carbon Manufacturing Method" relates to a composite microbial attached activated carbon manufacturing method. Although the composition has been pre-registered to maximize the water purification ability by controlling and inoculating and inoculating microorganisms, the proliferation rate is greatly reduced when inoculating anaerobic microorganisms due to the gas (oxygen) remaining in the activated carbon pores. Since it is a dedicated purpose for improving the purification ability, it is a general purpose anaerobic bioactive carbon that produces biogas along with decomposition of organic matter, which is impossible to apply.
본 발명에서는 상기한 종래 기술의 제반 문제점들을 해결코자 새로운 기술을 창안한 것으로서, 전처리장치의 히팅챔버 내에서 온수 순환구조로 인해 활성탄 기공에 잔류하는 기체(산소) 제거율이 우수하여 혐기성 미생물의 증식에 최적의 환경을 조성하기 위한 활성탄 전처리장치를 제공함을 발명에서 해결하고자 하는 과제로 한다.In the present invention, in order to solve the above-mentioned problems in the prior art, a new technique was devised, and the removal rate of gas (oxygen) remaining in the pores of activated carbon is excellent due to the circulation structure of the hot water in the heating chamber of the pre-treatment device, thereby proliferating anaerobic microorganisms. The problem to be solved in the present invention is to provide an activated carbon pretreatment device for creating an optimal environment.
또한, 기체가 제거된 활성탄을 냉각하여 기공에 물이 채워진 상태로 혐기성 미생물이 부착되는 커버링단계를 수행하므로, 산소가 존재하지 않은 조건하에서 혐기성 미생물의 증식시켜 유기물에 대해 분해 효율이 향상되는 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법을 제공하는 것에 그 목적이 있다.In addition, by performing a covering step in which the anaerobic microorganisms are attached in a state where water is filled in the pores by cooling the activated carbon from which the gas has been removed, the activated carbon pretreatment in which the anaerobic microorganisms multiply under the absence of oxygen to improve the decomposition efficiency for organic matter is improved. It is an object to provide a method for producing anaerobic bioactive carbon using a device.
이러한 목적을 달성하기 위해 본 발명의 특징은, 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비되는 히팅챔버(10); 상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장되는 전처리실(20); 상기 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키도록 구비되는 히팅실(30); 상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)와 함께 저장되도록 구비되는 온수포집실(40); 및 상기 온수포집실(40) 상부 영역에 빈 공간으로 형성되어 히팅챔버(10) 내부에서 기화된 스팀 및 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 포집되고, 포집된 스팀 및 기체(1a)를 히팅챔버(10) 외부로 배출하는 배기관(52)이 구비되는 기체포집실(50);을 포함하여 이루어지는 것을 특징으로 한다.In order to achieve this object, the features of the present invention, the water is stored therein, the heating chamber 10 is provided with a heating unit 12 for heating the water; The heating chamber 10 is installed to be immersed in the water inside, and a perforation is formed so that water passes through the pretreatment chamber 20 in which activated carbon 1 is stored; The heating chamber 30 is formed in the lower region inside the heating chamber 10 around the pretreatment chamber 20 and is provided to reduce the gas solubility of the pretreatment chamber 20 by generating hot water by the heating unit 12. ); The hot water formed in the upper region inside the heating chamber 10 based on the pretreatment chamber 20 and circulated by convection flows from the heating chamber 30 to the top through the pretreatment chamber 20 to activate carbon 1 A hot water collecting chamber 40 provided to be stored together with the gas 1a containing oxygen desorbed from the air; And the gas (1a) is formed as an empty space in the upper region of the hot water collecting chamber 40, the gas vaporized in the heating chamber 10 and oxygen desorbed from the activated carbon (1) is collected, the collected steam and It characterized in that it comprises a; gas collection chamber 50 is provided with an exhaust pipe 52 for discharging the gas (1a) to the outside of the heating chamber (10).
이때, 상기 히팅실(30)과 온수포집실(40)은 히팅챔버(10) 외측으로 연결되는 순환관(60)에 의해 연통되고, 히팅실(30)에서 발생되는 온수는 밀도가 작아지면서 대류현상에 의해 상부 전처리실(20)을 통과하여 온수포집실(40)로 이동되고, 온수포집실(40)에서 밀도가 증가된 온수는 순환관(60)을 통하여 히팅실(30)로 이동되는 순환구조를 가지는 것을 특징으로 한다.At this time, the heating chamber 30 and the hot water collecting chamber 40 are communicated by a circulation pipe 60 connected to the outside of the heating chamber 10, and the hot water generated in the heating chamber 30 becomes condensed while decreasing in density. Due to the phenomenon, it passes through the upper pretreatment chamber 20 and is moved to the hot water collecting chamber 40, and hot water having an increased density in the hot water collecting chamber 40 is moved to the heating chamber 30 through the circulation pipe 60. It is characterized by having a circulating structure.
또한, 상기 순환관(60)은 일단이 온수포집실(40)과 대응하는 히팅챔버(10) 외벽에 연결되고, 다른 일단은 복수의 분배관(62)이 구비되고, 분배관(62)은 히팅실(30)과 대응하는 히팅챔버(10) 바닥면에 분산 배치되어, 온수포집실(40)에서 순환 이송되는 온수가 복수의 분배관(62)을 통하여 히팅실(30) 바닥면으로 분산 공급되도록 구비되는 것을 특징으로 한다.In addition, one end of the circulation pipe 60 is connected to the outer wall of the heating chamber 10 corresponding to the hot water collecting chamber 40, the other end is provided with a plurality of distribution pipes 62, the distribution pipe 62 is The hot water that is circulated and distributed in the hot water collecting chamber 40 and distributed to the floor of the heating chamber 10 corresponding to the heating chamber 30 is distributed to the floor of the heating chamber 30 through a plurality of distribution pipes 62. It is characterized by being provided to be supplied.
그리고, 본 발명에 따른 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법은, 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비되는 히팅챔버(10)와, 상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장되는 전처리실(20)와, 상기 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키도록 구비되는 히팅실(30)과, 상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)와 함께 저장되도록 구비되는 온수포집실(40)과, 상기 온수포집실(40) 상부 영역에 빈 공간으로 형성되어 히팅챔버(10) 내부에서 기화된 스팀 및 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 포집되고, 포집된 스팀 및 기체(1a)를 히팅챔버(10) 외부로 배출하는 배기관(52)이 구비되는 기체포집실(50)을 포함하여 이루어지는 활성탄 전처리장치를 이용하여 활성탄 기공 내 존재하는 산소를 포함하는 기체(1a)를 제거하는 전처리단계(S1); 상기 전처리단계(S1)를 거친 활성탄을 냉각하여 기공에 물이 채워지도록 하는 냉각단계(S2); 및 상기 냉각단계(S2)를 거친 활성탄(1)에 혐기성 미생물을 부착하여 혐기성 생물활성탄을 형성하는 커버링단계(S3);를 포함하여 이루어지는 것을 특징으로 한다.In addition, the method for manufacturing anaerobic bioactive carbon using the activated carbon pretreatment device according to the present invention includes a heating chamber 10 in which water is stored and provided with a heating unit 12 for heating water, and the heating chamber 10 ) It is installed to be immersed in the inner water, and a perforation is formed so that water passes therethrough, and a pretreatment chamber 20 in which activated carbon 1 is stored, and an inner lower region inside the heating chamber 10 around the pretreatment chamber 20. It is formed on, the heating chamber 30 is provided to reduce the gas solubility of the pre-treatment chamber 20 by generating hot water by the heating unit 12, and the heating chamber 10 based on the pre-treatment chamber 20 The hot water formed in the inner upper region and circulated by the convection phenomenon moves from the heating chamber 30 to the upper side through the pretreatment chamber 20 and is stored together with the gas 1a containing oxygen desorbed from the activated carbon 1. The hot water collecting chamber 40 provided as much as possible, and a gas formed of an empty space in the upper region of the hot water collecting chamber 40 and vaporized inside the heating chamber 10 and gas containing oxygen desorbed from the activated carbon 1 ( In the activated carbon pores using an activated carbon pretreatment device comprising a gas collecting chamber 50 in which 1a) is collected, and the exhaust pipe 52 for discharging the collected steam and gas 1a to the outside of the heating chamber 10 is provided. A pre-treatment step (S1) for removing the gas 1a containing the present oxygen; A cooling step (S2) of cooling the activated carbon that has been subjected to the pretreatment step (S1) so that the pores are filled with water; And a covering step (S3) of forming anaerobic bioactive carbon by attaching anaerobic microorganisms to the activated carbon 1 subjected to the cooling step (S2).
상술한 과제 해결을 위한 구체적인 수단에 의하면, 본 발명에 의한 활성탄 전처리장치는 히팅챔버 내에서 온수로 인한 기체 용해도 감소 및 온수 순환구조로 인해 활성탄 기공에 잔류하는 기체(산소) 제거율이 우수한 장점이 있다. According to a specific means for solving the above-described problem, the activated carbon pretreatment apparatus according to the present invention has an advantage of excellent gas removal rate (removal) remaining in the pores of the activated carbon due to reduced gas solubility due to hot water in the heating chamber and circulating hot water. .
또한, 기체가 제거된 활성탄을 냉각하여 기공에 물이 채워진 상태로 혐기성 미생물이 부착되는 커버링단계를 수행하므로, 산소가 존재하지 않은 조건하에서 혐기성 미생물의 증식에 최적의 환경을 조성하여 유기물에 대해 분해 효율이 향상됨과 더불어 메탄을 포함하는 바이오 가스 생산량 증대를 도모하는 효과가 있다.In addition, since the activated carbon from which the gas has been removed is cooled, a covering step in which the anaerobic microorganisms are attached while the pores are filled with water is carried out, so that an optimal environment for the growth of the anaerobic microorganisms under oxygen-free conditions is created to decompose organic substances. In addition to improving the efficiency, there is an effect of promoting the production of biogas containing methane.
도 1은 본 발명의 일실시예에 따른 활성탄 전처리장치를 전체적으로 나타내는 구성도.1 is a block diagram showing an activated carbon pretreatment apparatus according to an embodiment of the present invention as a whole.
도 2 내지 도 3은 본 발명의 일실시예에 따른 활성탄 전처리장치의 순환관을 나타내는 구성도.2 to 3 is a block diagram showing a circulation pipe of the activated carbon pretreatment apparatus according to an embodiment of the present invention.
도 4는 본 발명의 일 실시 예에 따른 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법을 개략적으로 나타내는 구성도.Figure 4 is a schematic view showing a method for producing anaerobic bioactive carbon using an activated carbon pretreatment device according to an embodiment of the present invention.
이하에서 첨부된 도면을 참조하여 본 발명의 실시를 위한 구체적인 내용을 설명한다. Hereinafter, specific contents for carrying out the present invention will be described with reference to the accompanying drawings.
도 1은 본 발명의 일실시예에 따른 활성탄 전처리장치를 전체적으로 나타내는 구성도이고, 도 2 내지 도 3은 본 발명의 일실시예에 따른 활성탄 전처리장치의 순환관을 나타내는 구성도이다.1 is a configuration diagram showing an activated carbon pretreatment apparatus according to an embodiment of the present invention as a whole, and FIGS. 2 to 3 are configuration diagrams showing a circulation pipe of an activated carbon pretreatment apparatus according to an embodiment of the present invention.
본 발명은 활성탄 전처리장치에 관련되며, 이때 활성탄 전처리장치는 전처리장치의 히팅챔버 내에서 온수로 인한 기체 용해도 감소 및 온수 순환구조로 인해 활성탄 기공에 잔류하는 기체(산소) 제거율이 우수하고, 기체가 제거된 활성탄을 냉각하여 기공에 물이 채워진 상태로 혐기성 미생물이 부착되는 커버링단계를 수행하므로, 산소가 존재하지 않는 조건하에서 혐기성 미생물의 증식에 최적의 환경을 조성하여 유기물에 대해 분해 효율이 향상됨과 더불어 메탄을 포함하는 바이오 가스 생산량 증대를 도모하기 위해 히팅챔버(10), 전처리실(20), 히팅실(30), 온수포집실(40), 기체포집실(50)을 포함하여 주요구성으로 이루어진다.The present invention relates to an activated carbon pretreatment device, wherein the activated carbon pretreatment device has excellent gas (oxygen) removal rate remaining in the pores of activated carbon due to reduced gas solubility due to hot water in the heating chamber of the pretreatment device and a circulation structure of hot water, and gas Cooling the removed activated carbon to perform a covering step in which the anaerobic microorganisms are attached while the pores are filled with water, thereby creating an optimal environment for the growth of anaerobic microorganisms under the absence of oxygen, thereby improving the decomposition efficiency for organic substances. In addition, in order to increase the production of biogas containing methane, the main configuration includes a heating chamber 10, a pretreatment chamber 20, a heating chamber 30, a hot water collecting chamber 40, and a gas collecting chamber 50. Is done.
본 발명에 따른 히팅챔버(10)는 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비된다. 히팅챔버(10)는 내부가 빈 중공의 탱크로서, 상부에 개방부가 형성되어 상부덮개에 의해 개폐되도록 구비되고, 개방부를 통하여 후술하는 전처리실(20)이 수용된다.In the heating chamber 10 according to the present invention, water is stored therein, and a heating unit 12 for heating water is provided. The heating chamber 10 is an empty hollow tank inside, and is provided to be opened and closed by an upper cover with an opening formed on the upper portion, and a pretreatment chamber 20 to be described later is accommodated through the opening portion.
그리고, 상기 히팅챔버(10) 하부 바닥면에는 히팅부(12)가 구비되며, 히팅부(12)는 전기히터 또는 스팀히터 중 어느 하나 이상이 선택적으로 적용되어, 히팅챔버(10) 내부에 저장된 물이 가열되고, 히팅부(12)는 제어부에 의해 온도, 가동시간이 설정되며, 제어부는 온도센서를 이용하여 히팅챔버(10) 내에 온수 온도를 검출하여 그 값을 기준으로 히팅부(12) 작동을 제어하게 된다.In addition, a heating unit 12 is provided on the bottom surface of the heating chamber 10, and at least one of an electric heater or a steam heater is selectively applied to the heating unit 12 and stored in the heating chamber 10. The water is heated, and the heating unit 12 is set with the temperature and operating time by the control unit, and the control unit detects the temperature of the hot water in the heating chamber 10 using a temperature sensor, and the heating unit 12 is based on the value. It controls the operation.
또한, 본 발명에 따른 전처리실(20)은 상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장된다. 전처리실(20)은 어느 일측에 도어에 의해 개폐되도록 구성하여, 도어를 개방한 상태로 활성탄(1)을 투입한 다음 도어를 폐쇄한 상태로 히팅챔버(10) 내부로 투입된다.In addition, the pre-treatment chamber 20 according to the present invention is installed to be submerged inside the heating chamber 10, and a perforation is formed so that water passes therethrough, and the activated carbon 1 is stored therein. The pre-treatment chamber 20 is configured to be opened and closed by a door on one side, and then the activated carbon 1 is introduced with the door open, and then into the heating chamber 10 with the door closed.
이때 전처리실(20) 저면은 히팅챔버(10) 바닥면과 이격되는 위치에 안착되어, 전처리실(20)을 기준으로 하부영역에 히팅실(30)이 구비되고, 상부영역에 온수포집실(40), 기체포집실(50)이 형성된다. 그리고 도 1과 같이 히팅실(30), 전처리실(20), 온수포집실(40) 및 기체포집실(50)은 히팅챔버(10)의 내부공간에 연통되도록 형성되어 온수, 스팀 및 기체(1a)의 이동이 공유된다.At this time, the bottom surface of the pretreatment chamber 20 is seated at a position spaced from the bottom surface of the heating chamber 10, and the heating chamber 30 is provided in the lower region based on the pretreatment chamber 20, and the hot water collection chamber ( 40), the gas collecting chamber 50 is formed. And, as shown in Figure 1, the heating chamber 30, the pretreatment chamber 20, the hot water collecting chamber 40 and the gas collecting chamber 50 are formed so as to communicate with the internal space of the heating chamber 10, hot water, steam and gas ( The movement of 1a) is shared.
한편, 상기 전처리실(20)은 내부에 활성탄이 저장된 상태로 봉합되어, 후술하는 BAC 필터(220)의 외곽케이스로 사용되는 구성도 가능하다.On the other hand, the pre-treatment chamber 20 is sealed in a state in which activated carbon is stored therein, and may be used as an outer case of the BAC filter 220 described later.
본 발명에 따른 히팅실(30)은 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키게 된다. 히팅실(30)은 히팅챔버(10)의 바닥면과 전처리실(20) 저면 사이에 형성되는 공간으로서, 히팅챔버(10) 바닥에 설치되는 히팅부(12)에 의해 물이 가열되어 온수가 발생되는 영역이고, 히팅실(30)에서 발생되는 온수는 대류현상(밀도차이)에 의해 상측 전처리실(20)에 저장된 활성탄(1)을 거쳐 온수포집실(40)로 이동되고, 온수포집실(40)에 위치된 온수는 밀도차이(온도저하)로 인해 하방향으로 이동되는 순환구조를 가진다.The heating chamber 30 according to the present invention is formed in the lower region inside the heating chamber 10 around the pretreatment chamber 20, and hot water is generated by the heating unit 12 to increase the gas solubility of the pretreatment chamber 20. Is reduced. The heating chamber 30 is a space formed between the bottom surface of the heating chamber 10 and the bottom surface of the pretreatment chamber 20, and water is heated by the heating unit 12 installed on the bottom of the heating chamber 10 to produce hot water. It is an area that is generated, and the hot water generated in the heating chamber 30 is moved to the hot water collecting chamber 40 through the activated carbon 1 stored in the upper pretreatment chamber 20 by convection phenomenon (density difference), and the hot water collecting chamber The hot water located at (40) has a circulation structure that moves downward due to a density difference (temperature drop).
그리고, 상기 히팅실(30)에서 물이 가열됨에 따라 기체 용해도가 감소되고, 이로 인해 전처리실(20)에 저장된 활성탄 공극에 존재하는 기체(산소) 제거율이 향상되고, 특히 미세 공극에 잔류하는 기체까지 쉽게 탈리 제거된다.In addition, as the water is heated in the heating chamber 30, gas solubility decreases, thereby improving the removal rate of gas (oxygen) present in the activated carbon pores stored in the pretreatment chamber 20, particularly the gas remaining in the fine pores. Until it is easily tally removed.
또한, 본 발명에 따른 온수포집실(40)은 상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 온수포집실(40) 안에 잔존하게 된다. 온수포집실(40)은 전처리실(20)과 히팅챔버(10) 상부덮개 사이에 형성되는 공간으로서, 히팅챔버(10) 내에서 대류현상에 의해 전처리실(20)을 통과한 온수가 저장되고, 이때 활성탄(1)에서 탈리된 기체(산소)는 온수 내에 기포형태로 포함되어 온수와 함께 상측 온수포집실(40)로 신속하게 이동 후, 온수와 분리되어 후술하는 기체포집실(50)에 저장된다. In addition, the hot water collecting chamber 40 according to the present invention is formed in the upper region inside the heating chamber 10 based on the pretreatment chamber 20, and hot water circulated by convection phenomenon is pretreated in the heating chamber 30. Gas (1a) containing oxygen desorbed from the activated carbon (1) by moving to the upper portion through (20) remains in the hot water collecting chamber (40). The hot water collecting chamber 40 is a space formed between the pretreatment chamber 20 and the upper cover of the heating chamber 10, and hot water that has passed through the pretreatment chamber 20 by convection phenomenon in the heating chamber 10 is stored. At this time, the gas (oxygen) desorbed from the activated carbon 1 is included in the form of air bubbles in the hot water and quickly moves to the upper hot water collecting chamber 40 together with the hot water, and then separated from the hot water to the gas collecting chamber 50 to be described later. Is saved.
상기 온수포집실(40) 상부 영역에는 빈 공간으로 이루어진 기체포집실(50) 형성된다. 기체(1a)는 유체보다 가벼워 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 온수와 분리되어 기체포집실(50)로 포집되며, 기화된 스팀과 함께 외부로 배출하기 위한 배기관(52)이 구비된다. 기체포집실(50)은 온수포집실(40)에 저장된 온수 수면과 히팅챔버(10) 상부덮개 사이에 형성되는 공간으로서, 온수가 전처리실(20)을 통과하는 중에 활성탄(1)에서 탈리된 기체 및 온수에서 발생되는 스팀(증기)이 온수와 분리되어 저장되고, 기체포집실(50)에 포집된 기체 및 스팀은 히팅챔버(10) 상부덮개 또는 측벽에 형성되는 배기관(52)을 통하여 외부로 배출처리된다.In the upper region of the hot water collecting chamber 40, a gas collecting chamber 50 formed of an empty space is formed. The gas 1a is lighter than the fluid, and the gas 1a containing oxygen desorbed from the activated carbon 1 is separated from the hot water and collected in the gas collecting chamber 50, and exhaust pipes for discharging to the outside together with vaporized steam ( 52) is provided. The gas collecting chamber 50 is a space formed between the hot water surface stored in the hot water collecting chamber 40 and the upper cover of the heating chamber 10, and is detached from the activated carbon 1 while the hot water passes through the pretreatment chamber 20. Steam (steam) generated from gas and hot water is stored separately from hot water, and the gas and steam collected in the gas collecting chamber 50 are external to the heating chamber 10 through an exhaust pipe 52 formed on an upper cover or side wall. Is discharged.
도 2는 활성탄 전처리장치에 있어서 순환관이 더 형성된 것을 도시한 것으로, 상기 히팅실(30)과 온수포집실(40)은 히팅챔버(10) 외측으로 연결되는 순환관(60)에 의해 연통된다. 순환관(60)은 일단이 온수포집실(40)과 대응하는 온수포집실(40) 외주면에 연결되고, 다른 일단은 히팅챔버(10) 바닥면에 연통되도록 연결된다.Figure 2 shows that the circulation pipe is further formed in the activated carbon pretreatment device, the heating chamber 30 and the hot water collecting chamber 40 are communicated by the circulation pipe 60 connected to the outside of the heating chamber 10 . The circulation pipe 60 has one end connected to the outer circumferential surface of the hot water collection room 40 and the corresponding hot water collection room 40, and the other end to be connected to the bottom surface of the heating chamber 10.
이에 히팅실(30)에서 가열되는 온수는 밀도가 작아지면서 대류현상에 의해 상부 전처리실(20)을 통과하여 온수포집실(40)로 이동되고, 온수포집실(40)에서 밀도가 증가(온도저하)된 온수는 순환관(60)을 통하여 히팅실(30)로 이동되는 순환구조를 가지므로, 히팅챔버(10) 내에서 온수가 단방향으로 순환 즉, 전처리실(20) 하부에서 상측방향으로 이동이 활성화되어 활성탄(1)에서 탈리된 기체의 상방향 배출이 신속하고 원활하게 이루어지는 이점이 있다.Accordingly, the hot water heated in the heating chamber 30 decreases in density, passes through the upper pretreatment chamber 20 by convection phenomenon, moves to the hot water collecting chamber 40, and increases in density in the hot water collecting chamber 40 (temperature Since the deteriorated) hot water has a circulation structure that is moved to the heating chamber 30 through the circulation pipe 60, the hot water in the heating chamber 10 circulates in one direction, that is, from the lower portion of the pretreatment chamber 20 upwards. The movement is activated, and there is an advantage in that the upward discharge of the gas desorbed from the activated carbon 1 is quickly and smoothly performed.
한편, 상기 순환관(60)을 통한 온수 순환구조는 대류현상에 의해 자연순환방식을 이용하거나, 순환관(60)에 펌프를 설치하여 제어부에서 온도센서에 의해 온수 온도를 측정하여 설정된 온도에 도달하면 강제순환방식으로 온수를 순환시키는 구성도 가능하다. On the other hand, the hot water circulation structure through the circulation pipe 60 uses a natural circulation method by convection or a pump is installed in the circulation pipe 60 to measure the temperature of the hot water by a temperature sensor at the control unit to reach a set temperature. It is also possible to circulate hot water in a forced circulation method.
도 3에서, 상기 순환관(60)은 일단이 온수포집실(40)과 대응하는 히팅챔버(10) 외벽에 연결되고, 다른 일단은 복수의 분배관(62)이 구비되고, 분배관(62)은 히팅실(30)과 대응하는 히팅챔버(10) 바닥면에 분산 배치된다. In FIG. 3, the circulation pipe 60 has one end connected to the outer wall of the heating chamber 10 corresponding to the hot water collecting chamber 40, and the other end is provided with a plurality of distribution pipes 62 and a distribution pipe 62 ) Is distributed on the bottom surface of the heating chamber 10 corresponding to the heating chamber 30.
이에 온수포집실(40)에서 순환 이송되는 온수가 복수의 분배관(62)을 통하여 히팅실(30) 바닥면으로 고르게 분산 공급되므로, 분배관(62)을 통하여 히팅실(30)로 순환 공급된 온수가 히팅실(30) 전체영역에서 균일하게 가열되고, 이로 인해 전처리실(20)로 공급되는 온수 온도가 전체적으로 평준화되어 기체 용해도를 감소를 이용한 공극 내 기체 탈리효율이 전처리실(20) 전체영역에서 균일하게 향상되는 이점이 있다.Accordingly, since the hot water circulated and transferred from the hot water collecting chamber 40 is evenly distributed and distributed to the bottom surface of the heating chamber 30 through a plurality of distribution pipes 62, it is circulatedly supplied to the heating chamber 30 through the distribution pipes 62. The heated hot water is uniformly heated in the entire area of the heating chamber 30, whereby the temperature of the hot water supplied to the pre-treatment chamber 20 is leveled as a whole, thereby reducing the gas solubility, thereby improving the efficiency of gas desorption in the pores. It has the advantage of being uniformly improved in the region.
도 4는 본 발명의 일실시예에 따른 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법을 나타내는 흐름도로, 본 발명에 따른 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법은, 전처리단계(S1), 냉각단계(S2), 커버링단계(S3)를 포함하여 주요구성으로 이루어진다.4 is a flow chart showing an anaerobic bioactive carbon manufacturing method using an activated carbon pretreatment device according to an embodiment of the present invention, an anaerobic bioactive carbon manufacturing method using an activated carbon pretreatment device according to the present invention, a pretreatment step (S1), a cooling step (S2), including the main step (S3).
1. 전처리단계(S1)1. Pre-treatment step (S1)
본 발명에 따른 전처리단계(S1)는, 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비되는 히팅챔버(10)와, 상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장되는 전처리실(20)와, 상기 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키도록 구비되는 히팅실(30)과, 상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)와 함께 저장되도록 구비되는 온수포집실(40)과, 상기 온수포집실(40) 상부 영역에 빈 공간으로 형성되어 히팅챔버(10) 내부에서 기화된 스팀 및 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 포집되고, 포집된 스팀 및 기체(1a)를 히팅챔버(10) 외부로 배출하는 배기관(52)이 구비되는 기체포집실(50)을 포함하여 이루어지는 활성탄 전처리장치를 이용하여 활성탄 기공 내 존재하는 산소를 포함하는 기체(1a)를 제거하는 단계이다. 한편, 상기 전처리단계(S1)에서 활성탄 전처리장치는 상기 도 1 내지 도 3의 구성과 동일하므로 중복된 설명을 생략한다.Pre-treatment step (S1) according to the present invention, the water is stored therein, the heating chamber 10 is provided with a heating unit 12 for heating the water, and the heating chamber 10 is installed to be submerged in the water It is formed in the lower region inside the heating chamber 10 around the pretreatment chamber 20 and the pretreatment chamber 20 in which the activated carbon 1 is stored while the perforation is formed so that water passes therethrough, and the heating unit ( 12) is formed in the upper region inside the heating chamber 10 based on the heating chamber 30 and the heating chamber 30 provided to reduce the gas solubility of the pretreatment chamber 20 by generating hot water by The hot water collecting chamber is provided so that the hot water circulated by the convection phenomenon moves from the heating chamber 30 to the upper part through the pretreatment chamber 20 and is stored together with the gas 1a containing oxygen desorbed from the activated carbon 1 ( 40), and the gas (1a) containing oxygen desorbed from the steam and activated carbon (1) vaporized in the heating chamber (10) is formed as an empty space in the upper region of the hot water collecting chamber (40) is collected and collected Gas containing oxygen present in the activated carbon pores using an activated carbon pretreatment device comprising a gas collecting chamber 50 equipped with an exhaust pipe 52 for discharging the steam and gas 1a to the outside of the heating chamber 10 This is the step of removing (1a). On the other hand, the activated carbon pre-treatment device in the pre-treatment step (S1) is the same as the configuration of FIGS. 1 to 3, so a duplicate description is omitted.
2. 냉각단계(S2)2. Cooling stage (S2)
본 발명에 따른 냉각단계(S2)는, 상기 전처리단계(S1)를 거친 활성탄을 냉각하여 기공에 물이 채워지도록 하는 단계이다. 상기 전처리단계(S1)를 거친 활성탄의 공극은 기체가 탈리된 후 모세관현상에 의해 물이 채워지고, 이를 냉각하므로 물이 일부 채워지지 아니한 공극에도 결로현상에 의해 물이 채워지면서 공극으로 공기 중의 기체(산소)가 재유입되는 현상이 차단된다. The cooling step (S2) according to the present invention is a step of cooling the activated carbon that has passed through the pre-treatment step (S1) to fill the pores with water. The pores of the activated carbon that have undergone the pretreatment step (S1) are filled with water by capillary phenomenon after the gas is desorbed, and thus the water is filled with water by condensation even in the pores where water is not partially filled, thereby cooling the air. The phenomenon of (oxygen) re-inflow is blocked.
3. 커버링단계(S3)3. Covering step (S3)
본 발명에 따른 커버링단계(S3)는, 상기 냉각단계(S2)를 거친 활성탄(1)에 혐기성 미생물을 부착하여 혐기성 생물활성탄을 형성하는 단계이다. 혐기성 미생물은 유기물 분해와 더불어 메탄을 포함하는 바이오 가스를 생산하는 미생물로서, 산소가 전혀 존재하지 않는 조건에서만 생활하며 산소가 조금이라도 존재하면 사멸하게 되므로, 상기 전처리단계(S1), 냉각단계(S2)를 거쳐 활성탄 공극에 기체가 제거된 상태로 냉각하여 기공에 물을 채운 상태로 혐기성 미생물이 부착되고, 이로 인해 산소가 존재하지 않는 조건하에서 혐기성 미생물의 증식에 최적의 환경이 조성되어 유기물에 대해 분해 효율이 향상됨과 더불어 메탄을 포함하는 바이오 가스 생산량 증대를 도모하는 이점이 있다.The covering step (S3) according to the present invention is a step of forming anaerobic bioactive carbon by attaching anaerobic microorganisms to the activated carbon (1) that has undergone the cooling step (S2). Anaerobic microorganisms are microorganisms that produce biogas containing methane in addition to decomposition of organic matter. They live only in conditions where there is no oxygen at all, and if any oxygen is present, they are killed, so the pretreatment step (S1) and the cooling step (S2) ) To cool the activated carbon pores with the gas removed, and the anaerobic microorganisms are attached while filling the pores with water, thereby creating an optimal environment for the growth of anaerobic microorganisms under the absence of oxygen. It has the advantage of improving the decomposition efficiency and increasing the amount of biogas production including methane.
여기서, 상기 혐기성 미생물 부착은 스프레이방식, 함침방식 중 선택적으로 적용하며, 혐기성 미생물을 부착 후에는 설정 온도, 습도를 포함하는 증식조건에서 일정시간 증식과정을 거쳐는 것이 바람직하다.Here, the anaerobic microbial attachment is selectively applied by a spray method or an impregnation method, and after attaching the anaerobic microorganisms, it is preferable to undergo a proliferation process for a certain period of time under a proliferation condition including a set temperature and humidity.
이상과 같이 본 발명의 상세한 설명에는 본 발명의 가장 바람직한 실시 예에 관하여 설명하였으나, 본 발명의 기술범위에 벗어나지 않는 범위 내에서는 다양한 변형실시도 가능하다 할 것이다. 따라서 본 발명의 보호범위는 상기 실시 예에 한정하여 정하여 질 것이 아니라 후술하는 특허청구범위의 기술들과 이들 기술로부터 균등한 기술수단들에까지 보호범위가 인정되어야 할 것이다.As described above, in the detailed description of the present invention, the most preferred embodiments of the present invention have been described, but various modifications may be made without departing from the scope of the present invention. Therefore, the protection scope of the present invention should not be limited to the above-described embodiments, but the protection scope should be recognized from the technologies of the claims to be described later and the technical means equivalent to these technologies.
본 발명에 의한 활성탄 전처리장치는 히팅챔버 내에서 온수로 인한 기체 용해도 감소 및 온수 순환구조로 인해 활성탄 기공에 잔류하는 기체(산소) 제거율이 우수하고, 따라서 혐기성 미생물의 증식에 최적의 환경을 조성할 수 있어 바이오 가스의 생산을 촉진하게 되므로 산업상 이용가능성이 우수하다. The activated carbon pretreatment apparatus according to the present invention has excellent gas (oxygen) removal rate remaining in the pores of activated carbon due to reduced gas solubility due to hot water in the heating chamber and circulating structure of hot water, thus creating an optimal environment for the growth of anaerobic microorganisms. Since it can promote the production of biogas, it has excellent industrial applicability.

Claims (6)

  1. 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비되는 히팅챔버(10);Water is stored in the interior, the heating chamber 10 is provided with a heating unit 12 for heating the water;
    상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장되는 전처리실(20);The heating chamber 10 is installed to be immersed in the water inside, and a perforation is formed so that water passes through the pretreatment chamber 20 in which activated carbon 1 is stored;
    상기 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키도록 구비되는 히팅실(30);The heating chamber 30 is formed in the lower region inside the heating chamber 10 around the pretreatment chamber 20 and is provided to reduce the gas solubility of the pretreatment chamber 20 by generating hot water by the heating unit 12. );
    상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)와 함께 저장되도록 구비되는 온수포집실(40); 및 The hot water formed in the upper region inside the heating chamber 10 based on the pretreatment chamber 20 and circulated by convection flows from the heating chamber 30 to the top through the pretreatment chamber 20 to activate carbon 1 A hot water collecting chamber 40 provided to be stored together with the gas 1a containing oxygen desorbed from the air; And
    상기 온수포집실(40) 상부 영역에 빈 공간으로 형성되어 히팅챔버(10) 내부에서 기화된 스팀 및 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 포집되고, 포집된 스팀 및 기체(1a)를 히팅챔버(10) 외부로 배출하는 배기관(52)이 구비되는 기체포집실(50);을 포함하여 이루어지는 것을 특징으로 하는 활성탄 전처리장치.The gas (1a) containing the oxygen vaporized from the steam and activated carbon (1) vaporized in the heating chamber (10) is formed as an empty space in the upper region of the hot water collecting chamber (40) is collected, and the collected steam and gas Activated carbon pre-treatment device comprising a; gas collecting chamber (50) is provided with an exhaust pipe (52) for discharging (1a) to the outside of the heating chamber (10).
  2. 제 1항에 있어서,According to claim 1,
    상기 히팅실(30)과 온수포집실(40)은 히팅챔버(10) 외측으로 연결되는 순환관(60)에 의해 연통되고, 히팅실(30)에서 발생되는 온수는 밀도가 작아지면서 대류현상에 의해 상부 전처리실(20)을 통과하여 온수포집실(40)로 이동되고, 온수포집실(40)에서 밀도가 증가된 온수는 순환관(60)을 통하여 히팅실(30)로 이동되는 순환구조를 가지는 것을 특징으로 하는 활성탄 전처리장치.The heating chamber 30 and the hot water collecting chamber 40 are communicated by a circulation pipe 60 connected to the outside of the heating chamber 10, and the hot water generated in the heating chamber 30 becomes condensed while decreasing in density. By passing through the upper pre-treatment room 20 is moved to the hot water collection room 40, the hot water is increased density in the hot water collection room 40 is a circulation structure that is moved to the heating chamber 30 through the circulation pipe 60 Activated carbon pre-treatment device characterized in that it has a.
  3. 제 2항에 있어서,According to claim 2,
    상기 순환관(60)은 일단이 온수포집실(40)과 대응하는 히팅챔버(10) 외벽에 연결되고, 다른 일단은 복수의 분배관(62)이 구비되고, 분배관(62)은 히팅실(30)과 대응하는 히팅챔버(10) 바닥면에 분산 배치되어, 온수포집실(40)에서 순환 이송되는 온수가 복수의 분배관(62)을 통하여 히팅실(30) 바닥면으로 분산 공급되도록 구비되는 것을 특징으로 하는 활성탄 전처리장치.One end of the circulation pipe 60 is connected to the outer wall of the heating chamber 10 corresponding to the hot water collection chamber 40, the other end is provided with a plurality of distribution pipes 62, the distribution pipe 62 is a heating chamber Distributingly arranged on the bottom surface of the heating chamber 10 corresponding to 30, the hot water circulated and transferred from the hot water collection chamber 40 is distributed to the bottom surface of the heating chamber 30 through a plurality of distribution pipes 62 Activated carbon pre-treatment device, characterized in that provided.
  4. 내부에 물이 저장되고, 물을 가열하기 위한 히팅부(12)가 구비되는 히팅챔버(10)와, 상기 히팅챔버(10) 내측 물속에 잠기도록 설치되고, 물이 통과되도록 타공이 형성되면서 내부에 활성탄(1)이 저장되는 전처리실(20)와, 상기 전처리실(20)을 중심으로 히팅챔버(10) 내측 하부영역에 형성되고, 히팅부(12)에 의해 온수가 발생되어 전처리실(20)의 기체 용해도를 감소시키도록 구비되는 히팅실(30)과, 상기 전처리실(20)을 기준으로 히팅챔버(10) 내측 상부영역에 형성되고, 대류현상에 의해 순환되는 온수가 히팅실(30)에서 전처리실(20)을 거쳐 상부로 이동하여 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)와 함께 저장되도록 구비되는 온수포집실(40)과, 상기 온수포집실(40) 상부 영역에 빈 공간으로 형성되어 히팅챔버(10) 내부에서 기화된 스팀 및 활성탄(1)에서 탈리된 산소를 포함하는 기체(1a)가 포집되고, 포집된 스팀 및 기체(1a)를 히팅챔버(10) 외부로 배출하는 배기관(52)이 구비되는 기체포집실(50);을 포함하여 이루어지는 활성탄 전처리장치를 이용하여 활성탄 기공 내 존재하는 산소를 포함하는 기체(1a)를 제거하는 전처리단계(S1);Water is stored therein, the heating chamber 10 is provided with a heating unit 12 for heating the water, and the heating chamber 10 is installed to be immersed in the water inside, while a perforation is formed so that water passes therein In the pre-treatment chamber 20 in which the activated carbon 1 is stored, and in the lower region inside the heating chamber 10 around the pre-treatment chamber 20, hot water is generated by the heating unit 12 to generate a pre-treatment chamber ( 20) a heating chamber 30 provided to reduce gas solubility, and hot water formed in an upper region inside the heating chamber 10 based on the pretreatment chamber 20 and circulated by convection phenomenon ( 30) from the pre-treatment chamber (20) to move to the upper portion of the hot water collection chamber (40) and the hot water collection chamber (40) provided to be stored together with the gas (1a) containing oxygen desorbed from the activated carbon (1) A gas 1a formed of an empty space in the upper region and containing oxygen vaporized from the steam and activated carbon 1 vaporized inside the heating chamber 10 is collected, and the collected steam and gas 1a are collected in the heating chamber ( 10) a pre-treatment step (S1) of removing the gas (1a) containing oxygen existing in the pores of the activated carbon by using an activated carbon pre-treatment device comprising a gas collection chamber (50) provided with an exhaust pipe (52) to discharge to the outside );
    상기 전처리단계(S1)를 거친 활성탄을 냉각하여 기공에 물이 채워지도록 하는 냉각단계(S2); 및A cooling step (S2) of cooling the activated carbon that has been subjected to the pretreatment step (S1) so that the pores are filled with water; And
    상기 냉각단계(S2)를 거친 활성탄(1)에 혐기성 미생물을 부착하여 혐기성 생물활성탄을 형성하는 커버링단계(S3);를 포함하여 이루어지는 것을 특징으로 하는 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법.A method of manufacturing an anaerobic bioactive carbon using an activated carbon pretreatment device comprising: a covering step (S3) of forming an anaerobic bioactive carbon by attaching an anaerobic microorganism to the activated carbon (1) subjected to the cooling step (S2).
  5. 제 4항에 있어서,The method of claim 4,
    상기 전처리단계(S1)에서, 히팅실(30)과 온수포집실(40)은 히팅챔버(10) 외측으로 연결되는 순환관(60)에 의해 연통되고, 히팅실(30)에서 발생되는 온수는 밀도가 작아지면서 대류현상에 의해 상부 전처리실(20)을 통과하여 온수포집실(40)로 이동되고, 온수포집실(40)에서 밀도가 증가된 온수는 순환관(60)을 통하여 히팅실(30)로 이동되는 순환구조를 가지는 것을 특징으로 하는 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법.In the pre-treatment step (S1), the heating chamber 30 and the hot water collecting chamber 40 are communicated by a circulation pipe 60 connected to the outside of the heating chamber 10, and the hot water generated in the heating chamber 30 is As the density decreases, the convection phenomenon passes through the upper pretreatment chamber 20 to move to the hot water collecting chamber 40, and the hot water having increased density in the hot water collecting chamber 40 is heated through the circulation pipe 60 ( 30) Anaerobic bioactive carbon production method using an activated carbon pre-treatment device characterized in that it has a circulating structure.
  6. 제 5항에 있어서,The method of claim 5,
    상기 전처리단계(S1)에서, 순환관(60)은 일단이 온수포집실(40)과 대응하는 히팅챔버(10) 외벽에 연결되고, 다른 일단은 복수의 분배관(62)이 구비되고, 분배관(62)은 히팅실(30)과 대응하는 히팅챔버(10) 바닥면에 분산 배치되어, 온수포집실(40)에서 순환 이송되는 온수가 복수의 분배관(62)을 통하여 히팅실(30) 바닥면으로 분산 공급되도록 구비되는 것을 특징으로 하는 활성탄 전처리장치를 이용한 혐기성 생물활성탄 제조방법.In the pre-treatment step (S1), the circulation pipe 60 has one end connected to the outer wall of the heating chamber 10 corresponding to the hot water collection chamber 40, and the other end is provided with a plurality of distribution pipes 62, minutes The pipe 62 is disposed on the bottom surface of the heating chamber 10 corresponding to the heating chamber 30, and the hot water circulated and transferred from the hot water collection chamber 40 through the plurality of distribution pipes 62 is heated. ) Anaerobic bioactive carbon production method using an activated carbon pre-treatment device characterized in that it is provided to be distributed to the bottom surface.
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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0648718A (en) * 1992-07-28 1994-02-22 Nanba Kk Apparatus for producing active carbon
KR20010104899A (en) * 2000-05-16 2001-11-28 이장수 Biological activated carbon for advanced water purification treatment and method for preparing the same
KR200350129Y1 (en) * 2004-02-12 2004-05-10 김장현 A reactor of activated carbon
KR101110658B1 (en) * 2009-09-04 2012-02-16 한국전력공사 Recycle system of activated carbon and its method
KR101327809B1 (en) * 2013-01-08 2013-11-11 아름다운 환경건설(주) Heating treatment system of underground water contaminated by volatile organic contaminants
KR20140118046A (en) * 2013-03-28 2014-10-08 현대제철 주식회사 Recycle apparatus for activated carbon

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2800668B2 (en) * 1993-12-21 1998-09-21 松下電器産業株式会社 Water purifier with water heater
JPH0914763A (en) * 1995-06-28 1997-01-17 Mitsubishi Electric Corp Water circulation purifier for bathing
JP4409226B2 (en) * 2003-07-02 2010-02-03 日宝化学株式会社 Alkyl iodide recovery method and alkyl iodide recovery device
KR101407506B1 (en) 2007-12-21 2014-06-17 재단법인 포항산업과학연구원 Method for heat treatment of carbon raw materials for activated carbons
KR101564368B1 (en) 2014-08-20 2015-10-30 박서현 Manufacturing Process of Activating Carbon attached Mixed microorganism

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0648718A (en) * 1992-07-28 1994-02-22 Nanba Kk Apparatus for producing active carbon
KR20010104899A (en) * 2000-05-16 2001-11-28 이장수 Biological activated carbon for advanced water purification treatment and method for preparing the same
KR200350129Y1 (en) * 2004-02-12 2004-05-10 김장현 A reactor of activated carbon
KR101110658B1 (en) * 2009-09-04 2012-02-16 한국전력공사 Recycle system of activated carbon and its method
KR101327809B1 (en) * 2013-01-08 2013-11-11 아름다운 환경건설(주) Heating treatment system of underground water contaminated by volatile organic contaminants
KR20140118046A (en) * 2013-03-28 2014-10-08 현대제철 주식회사 Recycle apparatus for activated carbon

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