KR20020022483A - A sewage treatment plant used microorganism - Google Patents
A sewage treatment plant used microorganism Download PDFInfo
- Publication number
- KR20020022483A KR20020022483A KR1020000055274A KR20000055274A KR20020022483A KR 20020022483 A KR20020022483 A KR 20020022483A KR 1020000055274 A KR1020000055274 A KR 1020000055274A KR 20000055274 A KR20000055274 A KR 20000055274A KR 20020022483 A KR20020022483 A KR 20020022483A
- Authority
- KR
- South Korea
- Prior art keywords
- solid filler
- reaction tower
- reaction
- andesite
- pumice
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/10—Packings; Fillings; Grids
- C02F3/105—Characterized by the chemical composition
- C02F3/107—Inorganic materials, e.g. sand, silicates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/06—Aerobic processes using submerged filters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/1205—Particular type of activated sludge processes
- C02F3/121—Multistep treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/22—Activated sludge processes using circulation pipes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Microbiology (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Biodiversity & Conservation Biology (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Materials Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
본 발명은 부식물(腐植物)을 이용한 배수처리장치에 관한 것이며, 상세하게는 부식물의 효능을 보다 효과적으로 발휘되도록 하는 부식물을 이용한 배수처리장치에 관한 것이다.The present invention relates to a wastewater treatment apparatus using corrosives, and more particularly, to a wastewater treatment apparatus using corrosives to more effectively exhibit the efficacy of the corrosives.
종래 부식물을 이용한 배수의 처리방법에 있어서, 부식물을 충전한 반응탑(이하 "리액터"라고 하는 경우가 있다)을 이용하는 수법은 알려져 있다.In the conventional method for treating wastewater using a corrosive, a method using a reaction column (hereinafter sometimes referred to as "reactor") filled with a corrosive is known.
그러나 종래의 수법에서는 리액터가 단독이기 때문에 장시간에 걸쳐 오니의 질을 개선하려고 하여도 부식물의 효능이 한계가 있어 부식물이 유효하게 기능하지 않는 일이 많았다.However, in the conventional method, since the reactor is sole, even when trying to improve the quality of the sludge over a long time, the effectiveness of the corrosive is limited, and the corrosive does not function effectively in many cases.
그래서 본 발명자는 상기 과제를 해결하기 위하여 예의 검토한 결과 부식물 등을 충전한 2개의 반응탑을 순환식으로 구성함에 따라 오니의 활성화 및 질의 개선을 꾀하고 부식물의 효능을 한층 더 향상시키는 것에 착안하여 본 발명에 이르게 된 것이다.Therefore, the present inventors focused on activating and improving the quality of the sludge and further improving the effectiveness of the corrosive substances by circulating the two reaction towers filled with the corrosive substances as a result of earnestly examining in order to solve the above problems. This has led to the present invention.
또 본 발명자는 관련되는 순환타입의 반응탑에 의하여 배수처리도 가능하다는 것에 착안하였다.In addition, the inventors of the present invention have focused on the possibility of drainage treatment by a related-type reaction tower.
그러므로 본 발명의 첫째 목적은 복수의 리액터를 이용하여 오니의 활성화 및 질의 개선을 꾀하고 부식물의 효능을 한층 더 향상시킨 배수처리장치를 제공하는데 있다.Therefore, the first object of the present invention is to provide a wastewater treatment apparatus that improves the activation and quality of sludge by using a plurality of reactors and further improves the effectiveness of the corrosive.
또 본 발명의 둘째 목적은 복수의 리액터를 이용하여 부식물의 효능을 발휘시켜서 효율적으로 배수처리하는 배수처리장치를 제공하는데 있다.In addition, a second object of the present invention is to provide a wastewater treatment apparatus that efficiently drains by exerting the efficacy of the corrosives using a plurality of reactors.
상기 첫째의 목적은 폭기수단과 고액(固液)분리수단을 가지는 배수처리장치에 있어서, 고액분리수단에서 분리된 오니를 폭기조에 반송하는 과정에, 제 1 반응탑과 제 2 반응탑으로 이루어지는 2개의 순환형 반응탑을 개재시켜서 이루어지고, 상기 제 1 반응탑은 고형충전재를 충전하여 이루어지는 충전부를 가지며, 상기 충전부의 아래쪽에 산기부를 가지고 이루어지고, 상기 제 2 반응탑은 고형충전재를 충전하여 이루어지는 충전부를 가지고, 상기 제 1 반응탑과 제 2 반응탑은 순환라인에 의하여 순환이 가능하게 구성되어 있고, 상기 고형충전재가 특정한 부식물 등인 것을 특징으로 하는 배수처리장치에 의하여 달성된다.The first object of the present invention is a wastewater treatment apparatus having an aeration means and a solid-liquid separation means, wherein the sludge separated by the solid-liquid separation means is conveyed to an aeration tank, wherein the first reaction tower and the second reaction tower are formed of two. The first reaction tower has a charging unit formed by filling a solid filler, and has an acid group under the charging unit, and the second reaction tower is filled with a solid filler. The first reaction tower and the second reaction tower are configured to be circulated by a circulation line, and the solid filler is achieved by a wastewater treatment system, characterized in that the solid filler is a specific corrosive or the like.
상기 둘째 목적은 배수를 제 1 반응탑과 제 2 반응탑으로 이루어지는 2개의 순환형 반응탑에 도입하여 처리하는 배수처리장치에 있어서, 상기 제 1 반응탑은 고형 충전재를 충전하여 이루어지는 충전부를 가지며, 상기 충전부의 아래쪽에 산기부를 가지고 이루어지고, 상기 제 2 반응탑은 고형 충전재를 충전하여 이루어지는 충전부를 가지고, 상기 제 1 반응탑과 제 2 반응탑은 순환라인에 따라 순환이 가능하게 구성되어 있고, 상기 고형충전재가 특정한 부식물 등인 것을 특징으로 하는 배수처리장치에 의하여 달성된다.The second object of the present invention is a wastewater treatment apparatus for introducing and treating wastewater into two circulation type reaction towers comprising a first reaction tower and a second reaction tower, wherein the first reaction tower has a filling part formed by filling a solid filler, It is made of a lower portion of the filling unit having an acidic portion, the second reaction tower has a filling portion formed by filling a solid filler, the first reaction tower and the second reaction tower is configured to be circulated along the circulation line , The solid filler is achieved by a wastewater treatment apparatus, characterized in that the specific corrosive and the like.
도 1 은 본 발명의 일실시형태를 도시하는 설명도.BRIEF DESCRIPTION OF THE DRAWINGS Explanatory drawing which shows one Embodiment of this invention.
도 2는 본 발명의 다른 실시형태를 도시하는 설명도.2 is an explanatory diagram showing another embodiment of the present invention.
♣도면의 주요부분에 대한 부호의 설명 ♣♣ Explanation of symbols for main parts of drawing ♣
1 : 초침지 2 : 조정조1: Second hand immersion 2: Adjustment tank
3 : 원수펌프 4 : 폭기조3: raw water pump 4: aeration tank
5 : 최종 침전지 6 : 농축조5: final sedimentation basin 6: concentration tank
7 : 리액터 70 : 제 1 반응탑7: reactor 70: first reaction tower
71 : 제 2 반응탑 10 : 순환형리액터71: second reaction column 10: circulating reactor
13 : 침전지 100 : 조정조13: sedimentation basin 100: adjustment tank
101 : 제 1 반응탑 102 : 제 2 반응탑101: first reaction tower 102: second reaction tower
701 : 충전부 710 : 충전부701: charging unit 710: charging unit
다음은 본 발명의 실시형태를 도면에 따라 설명한다.Next, embodiments of the present invention will be described with reference to the drawings.
도 1은 본 발명의 바람직한 실시형태를 도시하는 설명도이고, 이 도면에서 (1)은 예를 들면 하수, 배설물, 생활배수 등의 각종 배수를 받아 고형분을 침강(沈降)분리하는 초침지이다. 이 초침지(1)의 전공정에는 스크린 등의 분리수단을 개재시킬 수도 있다.BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is an explanatory diagram showing a preferred embodiment of the present invention, in which (1) is a super-immersion for sedimentation and separation of solids by receiving various wastewater such as sewage, feces, and domestic wastewater. In the previous step of the second immersion 1, separation means such as a screen may be interposed.
(2)는 조정조이며 배수의 량의 변동이 있는 경우에 처리량을 균등하게 하여 후공정으로 보내기 위하여 마련되는 버퍼(buffer)탱크로서의 기능을 한다.(2) is an adjustment tank and functions as a buffer tank provided for equalizing the throughput and sending it to the post-process in the case of fluctuations in the amount of drainage.
조정조(2)에서 원수펌프(3)에 의하여 일정량씩 폭기조(4)로 배수가 보내진다.The drainage is sent from the adjustment tank 2 to the aeration tank 4 by a fixed amount by the raw water pump 3.
폭기조(4)에서는 조내의 미생물에 의하여 생물적인 처리에 따라 유기물을 분해처리한다.In the aeration tank 4, the organic matter is decomposed by the microorganisms in the tank according to the biological treatment.
(40)은 폭기조(4)에 폭기공기를 공급하기 위한 부로워(blower)이다.40 is a blower for supplying aeration air to the aeration tank 4.
폭기조(4)에서 보내오는 현탁액은 최종침전지(5)에서 오니와 처리수로 분리된다.The suspension from the aeration tank 4 is separated into sludge and treated water in the final settler 5.
침전된 오니는 농축조(6)로 보내져 농축되고 혹은 농축되지 않고 직접 순환형 리액터(7)로 보내진다.The precipitated sludge is sent to the concentration tank 6 and concentrated or not to be sent directly to the circulating reactor 7.
순환형 리액터(7)는 제 1 반응탑(70)과 제 2 반응탑(71)에 의하여 구성되고, 상기 제 1 반응탑(70)은 고형충전재를 충전하여 이루어지는 충전부(701)를 가지며 이 충전부(701)의 아래쪽에 산기부(702)를 가지고 있다. (74)는 순환펌프이다.The circulating reactor 7 is constituted by a first reaction tower 70 and a second reaction tower 71, and the first reaction tower 70 has a charging unit 701 formed by charging a solid filler, and this charging unit The diffuser 702 is provided below the 701. 74 is a circulation pump.
또 상기 제 2 반응탑(71)은 고형충전재를 충전하여 이루어지는 충전부(71)를 가지고 있다.In addition, the second reaction tower 71 has a filling part 71 formed by filling a solid filler.
상기 제 1 반응탑(70)과 제 2 반응탑(71)은 순환라인(72, 73) 및 순환펌프(74)에 의하여 순환이 가능하도록 구성되어 있다.The first reaction tower 70 and the second reaction tower 71 are configured to be circulated by circulation lines 72 and 73 and a circulation pump 74.
상기 제 1 반응탑(70)과 제 2 반응탑(71)에 충전되는 고형충전재의 예로서는 다음 ①∼④의 형태를 들 수 있다.Examples of the solid filler to be filled in the first reaction tower 70 and the second reaction tower 71 may include the following ① to ④.
① 제 1 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트① Solid filler in the first reaction column: Ferrets mainly containing corrosive substances
제 2 반응탑의 고형충전재 : 안산암질 혹은 유문암질 등의 활성도가 높은 불안정시리카를 포함하는 경석Solid filler in the second reaction tower: Pumice containing unstable silica with high activity such as andesite or rhyolite
② 제 1 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트② Solid filler in the first reaction column: Ferrets mainly containing corrosive substances
제 2 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트 및 안산암질 혹은 유문암질 등의 활성도가 높은 불안정시리카를 포함하는 경석Solid filler of the second reaction tower: Pumice containing ferrite containing corrosive as a main component and unstable silica with high activity such as andesite or rhyolite
③ 제 1 반응탑의 고형충전재 : 안산암질 혹은 유문암질 등의 활성도가 높은 불안정시리카를 포함하는 경석③ Solid filler of the first reaction tower: Pumice containing unstable silica with high activity such as andesite or pyloric
제 2 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트Solid filler in the second reaction tower: Ferrets mainly containing corrosive substances
④ 제 1 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트 및 안산암질 혹은 유문암질 등의 활성도가 높은 불안정시리카를 포함하는 경석④ Solid filler of the first reaction column: Pumice containing ferrite containing corrosive as the main component and unstable silica with high activity such as andesite or rhyolite
제 2 반응탑의 고형충전재 : 부식물을 주성분으로 하는 페렛트Solid filler in the second reaction tower: Ferrets mainly containing corrosive substances
상술한 고형충전재로서 이용하는 부식물을 주성분으로 하는 페렛트는 시판되는 것으로서 입수가 가능하며, 예를 들면 동양바이오리액터사 제품「TOYO-ROZAI(A)-PL」를 들 수 있다.Ferrets containing, as a main component, the corrosives used as the solid filler as described above are commercially available and available, for example, "TOYO-ROZAI (A) -PL" manufactured by Dongyang Bioreactor.
또, 안산암질 혹은 유문암질 등의 활성도가 높은 불안정시리카를 포함하는 경석도 시판되는 것으로 입수가 가능하고, 동양바이오리액터사 제품「TOYO-ROZAI(B)-SO」를 들 수 있다.In addition, pumice containing unstable silica having high activity such as andesite or pyloric is also commercially available, and "TOYO-ROZAI (B) -SO" manufactured by Dongyang Bioreactor Co., Ltd. may be mentioned.
상기한 형태에 있어서 제 1 및 제 2 반응탑의 형상은 사각형 또는 원형모양으로 세워진 용기본체인 것이 좋다.In the above-described form, the first and second reaction towers may have a shape of a container body standing in a square or circular shape.
고형충전재를 충전한 충전부와 제 1 반응탑 및 제 2 반응탑의 중앙에 용기를 고정(달아매어도 좋음)하고 이 용기의 내부에 고형충전재를 충전하는 것이 좋다.It is preferable to fix the container in the center of the charging section filled with the solid filler, the first reaction column and the second reaction column, and to fill the inside of the container with the solid filler.
충전부의 아래쪽에 마련된 산기부는 산소를 공급할 뿐만 아니라 상승류를 형성하는 역할을 한다.The diffuser provided below the charging section not only supplies oxygen but also forms an upward flow.
상기한 순환형 리액터를 이용한 결과 고형충전재의 성분인 부식물의 용출성분이 오니중에 용출하고 또 경석의 용출성분도 오니중에 용출한다. 부식물의 용출성분은 페놀노출기를 가지는 성분을 포함하고 항균성을 가지며 부패균을 살균하므로 악취의 발생을 억제하는 효과가 있다. 또 경석의 성분은 시리카이고 이것들이 생물의 활성화에 기여한다.As a result of using the above-described circulating reactor, the eluting component of the corrosive substance which is a component of the solid filler is eluted in the sludge, and the eluting component of the pumice is also eluted in the sludge. The elution component of the corrosives includes an ingredient having a phenolic exposure group, has antimicrobial properties, and sterilizes decaying bacteria, thereby suppressing the occurrence of odor. The component of pumice is Sirica and these contribute to the activation of living things.
하나의 리액터만으로는 부식물이나 혹은 경석의 일방적인 성분에 편중하여 버려 양성분이 균등하게 증가하지 않는 결점이 있으나 둘의 리액터의 사이를 오니를 순환시키면 페놀노출기를 가지는 성분과 시리카의 양쪽 성분이 오니중에 용출하여 양쪽이 모두 균등하게 증가하는 효과가 있다.Although one reactor alone is concentrated on corrosive or pumice constituents, the amount of nutrients does not increase evenly, but when circulating sludge between two reactors, both components having phenolic exposure groups and silica are eluted. Both sides have the effect of increasing evenly.
상기한 순환형 리액터에서 활성화 된 오니는 조정조(2)와 폭기조(4)의 어느쪽에나 반송되어도 좋고 또 그 일부는 잉여오니로서 뽑아내거나 탈수 등의 처리를 실시 할 수 있다.The sludge activated in the above-mentioned circulating reactor may be conveyed to either the adjusting tank 2 or the aeration tank 4, and a part of the sludge may be taken out as a surplus sludge, or dehydration may be performed.
다음은 본 발명의 다른 실시형태를 도 2에 의거하여 설명한다.Next, another embodiment of the present invention will be described with reference to FIG. 2.
도 2에서 (10)은 순환형 리액터이고, 제 1 반응탑(101)과 제 2 반응탑(102)에 의하여 구성된다.In FIG. 2, reference numeral 10 denotes a circulating reactor, and is constituted by the first reaction tower 101 and the second reaction tower 102.
이 형태는 배수를 직접 리액터에 도입하여 처리하는 것으로, 이 형태로는 리액터내에 미생물을 미리 생식시켜 둘 필요가 있으나 이러한 미생물의 농도, 균수(菌數) 등을 일정하게 유지하므로서 고형충전재가 효과를 발휘한다. 특히 부식물을 주성분으로 하는 페렛트에 바칠루수(Bazillus)균의 포자를 다수포함하고 있어 이것들이 배수와 접촉하면 바칠루스균의 포자가 발아하여 균수가 증가(증식)한다.In this form, the wastewater is introduced directly into the reactor and processed. In this form, microorganisms need to be reproduced in advance in the reactor, but the solid filler is effective by maintaining a constant concentration of the microorganisms and the number of bacteria. Exert. In particular, the ferret containing the corrosive substance contains a large number of spores of bacillus bacillus, and when they come into contact with the drainage, the bacillus spores germinate and increase the number of bacteria.
배수는 조정조(100)에 도입되어 유량 및 농도 등이 조정되며 펌프(100a)를 이용하여 제 1 반응탑(101)에 정량만큼 도입된다.The drainage water is introduced into the adjustment tank 100 to adjust the flow rate and the concentration, and is introduced into the first reaction tower 101 by the quantitative amount using the pump 100a.
이어서 제 1 반응탑(101)과 제 2 반응탑(102)의 2개의 리액터사이에서 배수와 오니가 순환하면 배수와 오니의 접촉시간이 늘어나고 또 오니중의 용출성분이 도 1의 경우와 마찬가지로 증량하고 살규효과, 악취방치효과를 발휘한다.Subsequently, when the drainage and sludge circulate between the two reactors of the first reaction tower 101 and the second reaction tower 102, the contact time between the drainage and the sludge increases, and the elution component of the sludge increases as in the case of FIG. It has a killing effect and odor control effect.
(11)은 순환펌프이다.(11) is a circulation pump.
2개의 리액터에 의하여 처리된 배수는 침전지(13)에서 고액분리처리되고 처리수가 얻어진다. 침강한 오니를 도시하니 않았으나 리액터(10)의 어느 한쪽으로 반송되는 것이 바람직하다.The drainage treated by the two reactors is subjected to solid-liquid separation in the settling basin 13 to obtain treated water. Although the settled sludge is not shown, it is preferable to be conveyed to either side of the reactor 10.
도2에서 도1과 동일한 부호의 부위는 동일한 구성이므로 그 설명을 생략한다. 고형충전재에 대하여도 도 1의 형태와 같으면 좋다.In FIG. 2, since portions having the same reference numerals as in FIG. 1 have the same configuration, description thereof will be omitted. The solid filler may be the same as that of FIG. 1.
본 발명에 의하면 복수의 리액터를 이용하여 오니의 활성화 및 질의 개선을 꾀하고 부식물의 효능을 한층더 향상시킨 배수의 처리장치를 제공할 수 있다.According to the present invention, it is possible to provide a wastewater treatment apparatus which utilizes a plurality of reactors to improve the activation and quality of sludge and further improve the efficacy of the corrosive.
Claims (2)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020000055274A KR20020022483A (en) | 2000-09-20 | 2000-09-20 | A sewage treatment plant used microorganism |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020000055274A KR20020022483A (en) | 2000-09-20 | 2000-09-20 | A sewage treatment plant used microorganism |
Publications (1)
Publication Number | Publication Date |
---|---|
KR20020022483A true KR20020022483A (en) | 2002-03-27 |
Family
ID=19689590
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1020000055274A KR20020022483A (en) | 2000-09-20 | 2000-09-20 | A sewage treatment plant used microorganism |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR20020022483A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100393921B1 (en) * | 2001-01-26 | 2003-08-06 | 이성일 | Process for Sewage treatment by humix reaction |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0531490A (en) * | 1991-08-02 | 1993-02-09 | Ebara Jitsugyo Kk | Biological treatment of organic sewage |
KR960002236U (en) * | 1994-06-30 | 1996-01-19 | 대우자동차 주식회사 | Grommet for supporting round bar material used for attaching to flat materials |
JPH10296288A (en) * | 1997-04-22 | 1998-11-10 | Toyo Bio Reactor Kk | Sludge reforming method in batch type and oxidation ditch type waste water treatment method |
-
2000
- 2000-09-20 KR KR1020000055274A patent/KR20020022483A/en not_active Application Discontinuation
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0531490A (en) * | 1991-08-02 | 1993-02-09 | Ebara Jitsugyo Kk | Biological treatment of organic sewage |
KR960002236U (en) * | 1994-06-30 | 1996-01-19 | 대우자동차 주식회사 | Grommet for supporting round bar material used for attaching to flat materials |
JPH10296288A (en) * | 1997-04-22 | 1998-11-10 | Toyo Bio Reactor Kk | Sludge reforming method in batch type and oxidation ditch type waste water treatment method |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100393921B1 (en) * | 2001-01-26 | 2003-08-06 | 이성일 | Process for Sewage treatment by humix reaction |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
AU682984B2 (en) | Wastewater treatment method and plant | |
US7935251B2 (en) | Waste treatment apparatus | |
ES8406390A1 (en) | Activated sludge wastewater treating process. | |
CN106477829A (en) | The innoxious Waste Water Treatment of spoil and method of wastewater treatment | |
CN101200338A (en) | Method for removing organics and ammonia nitrogen from aquaculture water | |
CN101734826B (en) | Process method for treating coking wastewater | |
CN110217949A (en) | A kind of process for treating high ammonia nitrogen waste water | |
de Souza et al. | Optimization of ozone application in post-treatment of cattle wastewater from organic farms | |
KR102171918B1 (en) | Recycling and water quality purification treatment system of livestock manure | |
US6395173B1 (en) | Method and device for biologically treating a fluid charged with organic materials whilst producing biogas | |
KR100260979B1 (en) | A process of the treatment for waste smell by using microbe fixed cillium ball, and the bio-reactor therefor | |
US6764600B2 (en) | Lagoon for hog waste and the method of treatment thereof | |
KR20020022483A (en) | A sewage treatment plant used microorganism | |
Collivignarelli et al. | Synergy between anaerobic digestion and a post‐treatment based on Thermophilic Aerobic Membrane Reactor (TAMR) | |
CN206298494U (en) | The innoxious Waste Water Treatment of spoil | |
CN105693007A (en) | Chemical industrial sewage deep treatment system capable of deodorization | |
CA2126156A1 (en) | Biological treatment of wastewater and facilities for its application | |
JP6792303B2 (en) | Sewage treatment system | |
KR101634296B1 (en) | Sbr wastewater treatment system using soil microorganism | |
CN101200691B (en) | White rot fungi reactor capable of controlling mixed fungi pollution and controlling method therefor | |
JP2006231228A (en) | Treatment method of sweet potato shochu lees waste water | |
JP6393491B2 (en) | Water treatment equipment and biological treatment method of organic waste water | |
CN107043195B (en) | Treatment method of areca nut wastewater | |
CN1880242A (en) | Waste water treatment process of almond processing factory | |
ES2155990T3 (en) | INSTALLATION OF BIOLOGICAL CLARIFICATION OF SMALL SIZE. |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
N231 | Notification of change of applicant | ||
E902 | Notification of reason for refusal | ||
E801 | Decision on dismissal of amendment | ||
E601 | Decision to refuse application |