KR100241496B1 - Sewage purifying facility of suspended pattern making use of a microorganism - Google Patents
Sewage purifying facility of suspended pattern making use of a microorganism Download PDFInfo
- Publication number
- KR100241496B1 KR100241496B1 KR1019980004254A KR19980004254A KR100241496B1 KR 100241496 B1 KR100241496 B1 KR 100241496B1 KR 1019980004254 A KR1019980004254 A KR 1019980004254A KR 19980004254 A KR19980004254 A KR 19980004254A KR 100241496 B1 KR100241496 B1 KR 100241496B1
- Authority
- KR
- South Korea
- Prior art keywords
- suspension
- tank
- contact
- sewage
- pipe
- 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 - Fee Related
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
-
- 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)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
본 발명은 현수미생물 현탁식 오수정화장치에 관한 것이다.The present invention relates to a suspension microorganism suspended sewage purification apparatus.
즉, 혐기성 및 임의성, 호기성 미생물이 복합적으로 서식할 수 있는 현수관접촉재의 특성과 침전실 하단에 무폭기의 임의성분해실을 형성함으로서 하천이나 강의 녹조, 적조현상의 근원인 T-N, T-P의 제거율이 가일층 향상되어 있는 반면에, 미생물의 신진대사 전화기의 사멸회복, 성장리듬을 감지할 수 없는 자율형미생물상이 구현되어 지속적으로 정화율을 높일 수 있는 특징이 있는 것이다.In other words, the characteristics of the suspension tube contact material which can inhabit the anaerobic, random and aerobic microorganisms in combination with the formation of a non-aerobic random decomposition chamber at the bottom of the sedimentation chamber to remove TN and TP, which are the source of green algae and red tide, On the other hand, the microbial metabolism recovery of the microorganisms, the autonomous microorganisms that can not detect the growth rhythm is implemented, which is characterized by the ability to continuously increase the purification rate.
Description
제1도는 본 발명의 측면도.1 is a side view of the present invention.
제2도는 제1도의 A-A선 단면도.2 is a cross-sectional view taken along the line A-A of FIG.
제3도는 제1도의 B-B선 단면도.3 is a cross-sectional view taken along the line B-B in FIG.
제4도는 본 발명의 횡단면도.4 is a cross-sectional view of the present invention.
제5도는 본 발명의 유량조정조의 측단면도.5 is a side cross-sectional view of the flow adjustment tank of the present invention.
제6도는 본 발명의 현탁접촉1조의 측단면도.6 is a side cross-sectional view of a set of suspension contact of the present invention.
제7도는 본 발명의 현탁접촉2조의 측단면도.7 is a side cross-sectional view of a set of two suspension contact of the present invention.
제8도는 본 발명의 현탁접촉3, 4조의 측단면도.8 is a cross-sectional side view of the suspension contact 3, 4 of the present invention.
제9도는 본 발명의 임의성분해조의 측단면도.9 is a side cross-sectional view of the optional cracking tank of the present invention.
제10도는 본 발명에 적용된 현수관접촉재의 일부절결 확대단면도.10 is a partially cut-away enlarged cross-sectional view of a suspension pipe contact member applied to the present invention.
제11도는 본 발명의 적용된 현수형접촉재의 일부절결 확대단면도.11 is a partially cut-away enlarged cross-sectional view of a suspended contact member applied to the present invention.
제12도는 본 발명에 적용된 순환폭기구의 확대도.12 is an enlarged view of the circulation width mechanism applied to the present invention.
제13도는 본 발명에 적용된 가압팽창식호스의 확대도.Figure 13 is an enlarged view of the pressure expansion hose applied to the present invention.
[발명의 목적][Purpose of invention]
본 발명은 현수미생물 현탁식 오수정화장치에 관한 것으로서, 특히 정화장치 내부에 유기물은 물론 부유물 질소 인까지 높은 효율로 처리하는 기능과 아울러 사후관리가 간편한 것을 제공하는 것이다.The present invention relates to a suspension microorganism suspended sewage purification apparatus, and in particular, to provide a high efficiency treatment of organic matter as well as suspended nitrogen phosphorus in the purifier, as well as easy post-management.
[발명이 속하는 기술분야 및 그 분야의 종래기술][Technical field to which the invention belongs and the prior art in that field]
본 발명은 각종 생활오수를 정화하여 유출시키는 정화조에 관한 것이다. 이와 같은 종래의 정화조는 많은 방식의 모델과 각기에 특성을 갖는 정화시스템이 많이 보급되어있다.The present invention relates to a septic tank to purify and discharge various kinds of household sewage. In the conventional septic tank, many types of models and purification systems having respective characteristics are widely used.
그러나 사람의 문화생활과 관련하여 부수적으로 파생되는 생활오수는 많은 유기물과 협잡물을 내포하고 있어 다변화 되어 가는 배출수의 특성을 심도 있게 파악하지 못한 기존의 정화시설로는 정화율이 낮은 상태로 하천에 흘러가 수질을 더욱 어렵게 만드는 요인이었다. 특히 종래의 정화방식은 오수중의 혐기성 협잡물을 수시로 제거해야하는 불편함이 있는데, 이를 제거할 인력과 여건이 충족치못하여 시설물만 그대로 방치하여 무용지물이 되는 현상이 주류를 이루고 있어, 오수처리시설후의 사후관리가 매우 어려움이 많은 것이다. 또한 오수처리 범위가 유기물에 국한되어 하천이나 호수의 녹조현상의 주원인인 N, P의 제거에 매우 미흡한 문제점이 있었다.However, the sewage derived from incidentality related to human cultural life contains many organic substances and contaminants, so that existing purification facilities that do not understand the characteristics of the diversified effluent deeply flow into rivers with low purification rate. It was a factor that made water quality more difficult. In particular, the conventional purification method is inconvenient to remove the anaerobic contaminants in the sewage from time to time, the manpower and conditions to remove them are not satisfied, leaving only the facilities as it is the mainstream phenomena, the post-management after sewage treatment facilities There is a lot of very difficult. In addition, the sewage treatment range was limited to organic matters, so there was a problem in that the removal of N, P, which is the main cause of green algae in rivers and lakes, was insufficient.
[발명이 이루고자 하는 기술적 과제][Technical problem to be achieved]
본 발명은 상기와 같은 문제점을 해결하기 위하여 안출한 것으로서, 그 목적으로는 혐기성 및 임의성, 호기성 미생물이 복합적으로 서식할 수 있는 현수관접촉재의 특성과 침전실 하단에 무폭기의 임의성분해실을 형성함으로서, 하천이나 강의 녹조, 적조현상의 근원인 T-N, T-P의 제거율이 가일층 향상되어 있는 반면에, 미생물의 신진대사 전화기의 사멸회복, 성장리듬을 감지할 수 없는 자율형미생물상이 구현되어 지속적으로 정화율을 높일 수 있는 것을 제공함에 그 목적이 있는 것이다.The present invention has been made to solve the above problems, for the purpose of forming a non-aerobic random decomposition chamber of the suspension tube contact material and anaerobic, random, aerobic microorganisms can inhabit the complex and the bottom of the precipitation chamber The removal rate of TN and TP, which is the source of green algae and red tide in rivers and rivers, is further improved, while autonomous microorganisms that cannot detect the death of microbial metabolism and growth rhythms are realized and continuously purified. The purpose is to provide what can increase the rate.
[발명의 구성 및 작용][Configuration and Function of Invention]
상기 목적을 달성하기 위한 본 발명은 생활오수에 포함된 협잡물을 중력차에 의해 분리시키고 분리저장된 협잡물을 일정시간 저장 분해할 수 있는 협잡물분리조와, 상기 협잡물분리조로부터 유입된 처리수를 저장 및 혼합하기 위한 산기교반장치, 유출부하를 제어하는 리프트형 이송관을 갖는 유량조정조와, 1~4조로 구분된 현탁접촉조에 수직으로 입설된 현수형접촉제와 상기 현수형접촉제의 주변에 혐기성 및 임의성, 호기성 미생물이 복합적으로 서식할 수 있는 현수관접촉재와, 현탁접촉1~2조 저부 중앙에 형성된 산기관 상부에 산기수의 흐름을 유도시키면서 폭기시키는 산기수유도관과 현탁접촉1조의 일측벽에 황토가 폭기수와 혼합하여 현탁액으로 정화조 내부에 공급되는 토양공급실과, 상기 현탁접촉1~2조에서 정화된 오수가 현탁접촉3~4조로 유도하기 위한 이류관과 상기 현탁접촉3~4조의 저부에 공기압에 의해 산기공이 수축과 팽창이 되는 가압팽창식호스와 상기 현탁접촉3~4조와 임의 성분해조를 통과한 오수가 최종 마무리 정화가 되는 최종침전실과, 상기 최종침전실과 현탁접촉1조의 저부에는 침전실에 쌓인 잔여 침전물을 재처리과정을 거치게 하는 순환관과 상기 순환관 끝단에는 공기의 상승기류에 의해 침전물이 함께 이송되는 이젝트형의 순환폭기장치와 상기 현탁접촉3~4조와 침전실 사이에 형성된 임의성분해조와, 상기 임의성분해조의 일측에는 최종처리수가 현탁접촉4조로부터 이동하도록 하는 복수개의 순환공이 형성되고, 자립자를 형성 용존산소를 소비하면서 잔류된 유기물 및 T-N, T-P의 제거를 하게되는 복수개의 고정형여재층이 배치되며, 상기 현탁접촉4조와 3조 사이에 현탁접촉4조로 유도하도록 되어 있는 이류관과 현탁접촉4조로 이동된 처리수가 임의성분해조를 경유 상기 최종침전실로 유도되도록 하는 상승유출공과, 상기 최종침전실의 상부에는 상기 상승유출공에 의해 유도된 처리수가 최종 배수되는 월류웨어로 배치된 특징이 있는 것이다.The present invention for achieving the above object is to separate the contaminants contained in the domestic sewage by gravity difference and to store and decompose the stored and stored debris stored for a certain time, and storing and mixing the treated water introduced from the contaminant separation tank Anaerobic stirrer, flow control tank having lift-type transfer pipe to control outflow load, suspended contact agent vertically installed in suspension contact tank divided into 1 ~ 4 tanks, and anaerobic and randomness around the suspension contact agent On the one side wall of the suspension pipe contacting material, which can inhabit aerobic microorganisms, and the aerobic water induction pipe and suspension contacting which aeration while inducing the flow of acidic water in the upper part of the diffuser formed in the center of the suspension contact 1 to 2 tank bottoms. The soil supply chamber is mixed with the aerated water and supplied into the septic tank as a suspension, and the filthy water purified in the suspension contact 1 to 2 tank is suspended to 3 to 4 tank. The pressurized expansion hose which contracts and expands the acid pores by air pressure at the bottom of the air flow pipe and the suspension contact 3 to 4 tanks, and the filthy water passing through the suspension contacts 3 to 4 tanks and the optional component sea bath are finally cleaned. At the bottom of the final settling chamber, the bottom of the settled contacting chamber and one set of suspension contact, a circulation pipe for reprocessing the remaining deposits accumulated in the settling chamber and an ejection type circulation in which sediment is transferred together by an upward airflow at the end of the circulation pipe. An optional cracking tank formed between the aeration device, the suspension contact 3 to 4 tank and the settling chamber, and a plurality of circulation holes are formed at one side of the random cracking tank to move the final treated water from the suspension contact 4 tank, forming a self-supporting dissolved oxygen A plurality of fixed media layers are disposed to remove the organic matter and TN and TP while consuming, and between the four and three tanks in suspension contact. An upflow hole for directing the treated water moved to the four-contact tank and the suspension contact tank to the final settling chamber via an arbitrary decomposition tank; and an upper portion of the final settling chamber induced by the rising outlet. It is characterized by being arranged as overflowware where the treated water is finally drained.
이하, 본 발명을 첨부된 도면을 참고로 하여 상세히 설명하면 다음과 같다.Hereinafter, the present invention will be described in detail with reference to the accompanying drawings.
즉, 제1도는 본 발명의 측면도이고 제2도는 제1도의 A-A선 단면도이며, 제3도는 제1도의 B-B선 단면도이고 제4도는 본 발명의 횡단면도이다.1 is a side view of the present invention, FIG. 2 is a cross-sectional view taken along the line A-A of FIG. 1, FIG. 3 is a cross-sectional view taken along the line B-B of FIG. 1, and FIG. 4 is a cross-sectional view of the present invention.
상기 도시된 바와 같이 정화조본체(10)를 협잡물분리조(20), 유량조정조(30), 현탁접촉1조(40), 현탁접촉2조(50), 현탁접촉3조(60), 현탁접촉4조(70), 임의성분해조(80), 최종침전실(90)로 구분하여 설명하면 다음과 같다.As shown in the figure, the septic tank main body 10 has a contaminant separation tank 20, a flow adjusting tank 30, a suspension contact 1 tank 40, a suspension contact 2 tank 50, a suspension contact 3 tank 60, and a suspension contact. The four tanks (70), random decomposition tank (80), the final settling chamber 90 is described as follows.
협잡물분리조(20)일측의 유입구(21)로는 최초 유입수가 유입되고 벽면(22)의 수직으로 봉스크린(23)을 형성하고 상기 봉스크린의 일측에는 복수개의 구멍(23′)을 상기 유입구와 반대방향으로 천공한 것이다.The first inflow water flows into the inlet 21 of one side of the contaminant separation tank 20 and forms a rod screen 23 perpendicular to the wall surface 22, and a plurality of holes 23 'are formed at one side of the rod screen. Perforated in the opposite direction.
유량조정조(30) 저부 중앙에는 유입된 혐기분해된 오수를 호기성으로 전환되는 것과 공기를 혼합하기 위한 산기교반장치(31)를 형성하고 제5도에 도시된 바와 같이 측벽(32)에 형성된 리프트형 이송관은 다음 과정으로 오수를 소량씩 이송케하며, 외부로부터 오수유입량 단절시 수위가 낮아져 공기만 유출됨에 따라 이송량이 자연 감소되고, 외부로부터 오수유입량이 많을 경우 수위가 상승하면 소량씩 증가되는 특성을 지니는 에어리프트형 이송관이라 한다.In the center of the bottom of the flow control tank 30, an anaerobic stirrer 31 is formed for converting the introduced anaerobic sewage into aerobic and air mixing, and a lift type formed on the side wall 32 as shown in FIG. The transfer pipe allows small amount of sewage to be transferred by the following process, and when the sewage inflow is cut off from the outside, the water level decreases as only the air flows out, and when there is a large amount of sewage inflow from the outside, it increases by a small amount. It is called an air lift type conveying tube having a.
현탁접촉1~2조(40)(50)의 중앙에 통상의 현수형접촉제(41)(51)형성하고 제6도 내지 제7도에 도시된 바와 같이 상기 현수형접촉제의 주변에는 내부에 섬유사(42′)(52′)가 불규칙적으로 내장된 복수개의 현수관접촉재(42)(52)를 횡으로 설치하여 접촉제 미층진공간에 효율적인 접촉기능을 부여함과 아울러, 상기 현수형접촉제의 충진율 저하와 기존의 미생물의 낮은 접촉율을 크게 향상시키며, 현탁접촉1~2조 저부 중앙에 형성된 산기관(43)(53) 상부에 산기수의 흐름을 유도시키면서 폭기시키는 산기수유도관(44)(54)이 형성되며, 현탁접촉1조의 상부에는 황토흙이 내장된 토양공급실(45)을 형성한 것으로, 황토흙이 폭기수와 접촉되면 현탁액 상태로 서서히 유출공(45′)으로 유출되어 오수와 혼합됨으로서, 토양 속의 이산화규소 50~70%, 산화마그네슘 20~30%, 산화알미늄 10%, 산화칼슘 5% 내외의 조성비를 갖는 무기질과 수많은 미생물 및 미립자의 현탁액이 혼합되어 처리공정을 순화함으로서, 흙 속의 무기물 및 오수의 유기물이 혼재되어 우점균의 과대배양이나 일시적인 폐사현상 등의 편곡이 없는 미생물의 균형이 연계되고, 미립자의 부유오니의 비중이 현탁액과 혼제되어 중력증가로 부유물의 침전능력증대 등의 탁월한 효과와 더불어 상기 최종침전실(90) 하단에 침전된 혼합물은 순환조절밸브(46′)를 갖는 침전물 순환폭기장치(46)에 의해 다시 현탁접촉1조로 재 순환되어 연속공정을 이루며, 상기 토양공급실의 현탁토(황토)는 6개월에 1회 정도로 투입하되 유입량의 250PPM 범위로 투입하면 지속적인 순환 공정이 연계되어 높은 정화율을 얻는 것이다.A suspension type contact agent 41, 51 is formed in the center of the suspension contact 1 to 2 tanks 40 and 50, and as shown in FIGS. A plurality of suspension pipe contact members 42 and 52 having irregularly embedded fiber yarns 42 'and 52' are provided laterally to impart an efficient contact function to the contact layer space, and the suspension type An acid water induction pipe that greatly improves the filling rate of the contact agent and the low contact rate of existing microorganisms and induces the flow of acidic water in the upper part of the acid pipes 43 and 53 formed at the bottom of the suspension contact 1 to 2 tanks. (44) (54) are formed, and the upper part of the suspension contacting tank is formed with a soil supplying chamber (45) in which ocher soil is embedded. By spilling and mixing with sewage, 50 ~ 70% of silicon dioxide in soil, 20 ~ 30% of magnesium oxide, alumi A mixture of minerals with a composition ratio of about 10% and calcium oxide of about 5% and a suspension of numerous microorganisms and microparticles is used to purify the treatment process, resulting in the mixing of inorganic and sewage organic matter in the soil, resulting in overcultivation of dominant bacteria and temporary death. The balance of microorganisms without arrangement is linked, and the specific gravity of the suspended sludge of the fine particles is mixed with the suspension, and the mixture precipitated at the bottom of the final settling chamber 90 with the excellent effect of increasing the sedimentation capacity of the suspended solids due to the increase of gravity. The sediment circulation aeration device 46 having the valve 46 'is recirculated back into the suspension contacting tank to form a continuous process, and the suspended soil (ocher) of the soil supply chamber is introduced about once every six months, but has 250PPM of inflow. In the range, high clarification rates are achieved by linking the continuous circulation process.
현탁접촉3~4조(60)(70) 중앙에 형성된 격벽(B)을 중심으로 현수형접촉제(61)(71)가 형성되며, 제8도와 제10도에 도시된 바와 같이 상기 현수형접촉제의 하부와 일측면에 섬유사(62′)(72′)가 불규칙적으로 내장된 복수개의 현수관접촉재(62)(72)를 횡으로 설치하며, 현탁접촉3~4조의 저부 양측으로는 가요성인 가압팽창식호스(63)(73)를 설치한 것으로, 상기 가압팽창식호스는 일정압의 공기가 가해지면 그 압에 의해 팽창산기공(63′)(73′)이 개방되어 공기 방울이 미세하게 유출되어 수중에 용존산소를 높여주고, 반면 공기압이 낮아지면 팽창산기공이 수축되어 구멍이 폐쇄됨으로서, 오수속에 이 물질 유입이 차단되어 이 물질 유입에 따른 산기공의 막힘이 없는게 특징이 있다.Suspension type contact agent 61, 71 is formed centering on partition B formed in the center of suspension contact 3-4 tank 60, 70. As shown in FIG. 8 and FIG. On the lower side and one side of the contact agent, a plurality of suspension pipe contact members 62 and 72 having irregularly embedded fiber yarns 62 'and 72' are horizontally installed. Is a flexible pressure expansion hose (63) (73) is installed, the pressure expansion hose when the air of a constant pressure is applied, the expansion acid pores (63 ') (73') is opened by the pressure to air The droplets are finely discharged to increase dissolved oxygen in the water, while when the air pressure decreases, the expansion acid pores contract and the pores are closed, which prevents the entry of this substance into the sewage, so there is no blockage of acid pores due to the inflow of the substance. have.
임의성분해조(80)는 상기 현탁접촉1~4조 공정을 통과하고 현탁접촉3~4의 충분한 산소공급으로 정화된 처리수가 제9도에 도시된 바와 같이 복수개의 순환공(81)으로 유입되면, 자립자를 형성 용존산소를 소비하면서 잔류된 유기물 및 T-N, T-P의 제거를 원활하게 하는 복수개의 고정형여재층(82)이 저장되어 있고, 상기 고정형여재층에 의해 일정시간 체류되어 정화된 최종처리수는 상승유출공(83)으로 배수되어 제2도에 도시된 바와 같이 최종침전실(90)의 월류웨어(91)로 배수가 되고 최종처리수 중에 일부가 침전되는 잔여 침전물은 침전실 저부에 형성된 순환관(92)으로 유입되어, 상기 현탁접촉1조의 순환폭기장치(46)로 재순환되거나 협잡물분리조(20)로 연결된 잉여침전물이송장치(24)로 재 이송되도록 구성된 것이다.When the random decomposition tank 80 passes through the suspension contact 1 to 4 tank process and the treated water purified by sufficient oxygen supply of the suspension contact 3 to 4 flows into the plurality of circulation holes 81 as shown in FIG. And a plurality of stationary filter layers 82 for smoothly removing residual organic substances and TN and TP while consuming dissolved oxygen to form self-supporting particles. Is drained to the rise-out hole 83 and drained to the overflowware 91 of the final settling chamber 90 as shown in FIG. 2, and the remaining precipitate which is partially precipitated in the final treated water is formed at the bottom of the settling chamber. Is introduced into the circulation pipe 92, it is configured to be recycled to the circulation contact aeration device 46 of the suspension contact or re-transmitted to the surplus sediment transfer device 24 connected to the contaminant separation tank 20.
상기와 같이 구성된 본 발명에 의해 실시예를 설명하면 다음과 같다.Referring to the embodiment according to the present invention configured as described above are as follows.
[실시예]EXAMPLE
50여개소의 정화시설을 5년간 실태파악 끝에 생활오수의 물리적 리듬을 찾아 가장 합리적인 정화방식으로 그 실시예를 살펴보면 다음의 표와 같다.After looking at 50 purification facilities for 5 years, the physical rhythm of sewage is found in the most rational purification method.
[표][table]
상기 표에서와 같이 정화율의 평균은 BOD 97%, SS96.9%, T-N 94.2%, T-P 77.4%의 처리율을 얻을 수 있으며, 기존의 정화방식에서 많이 발생된 오니의 생성성장의 사멸의 순환 신진대사 리듬에 방류수의 처리율 변화는 감지할 수 없었다.As shown in the table above, the average of the purification rate can be obtained BOD 97%, SS96.9%, TN 94.2%, TP 77.4%, and the circulating budding of the production growth of sludge generated a lot in the conventional purification method Changes in effluent throughput in metabolic rhythms could not be detected.
또한 혐기성 및 임의성, 호기성 미생물의 복합적으로 서식할 수 있는 현수관 접촉제의 특성과 침전실 저부에 무폭기의 임의성분해조를 형성함으로서, 하천이나 강의 녹조, 적조 현상의 근원인 T-N, T-P의 제거율이 기존의 방식보다 탁월한 결과를 얻을 수 있으며, 반면에 미생물의 진신대사 전환기의 사멸회복, 성장리듬을 감지할 수 없는 자율조절형 미생물상의 구현되어 지속적으로 정화율을 높일 수 있는 특징으로 대두되었다.In addition, the characteristics of suspension contactants that can inhabit a mixture of anaerobic, random, and aerobic microorganisms, and the formation of a non-aerobic random decomposition tank at the bottom of the sedimentation chamber to remove TN and TP, which are the source of green algae and red tide, can be found. This result is superior to the conventional method, while the recovery of microbial metabolic transition phase, embodied in a self-regulating microorganism that can not detect the growth rhythm has emerged as a feature that can continuously increase the purification rate.
[발명의 효과][Effects of the Invention]
이상에서 설명한 바와 같이 본 발명은 혐기성 및 임의성, 호기성 미생물이 복합적으로 서식할 수 있는 현수관접촉재의 특성과 침전실 하단에 무폭기의 임의성 분해실을 형성함으로서, 하천이나 강의 녹조, 적조현상의 근원인 T-N, T-P의 제거율이 가일층 향상되어 있는 반면에, 미생물의 신진대사 전화기의 사멸회복, 성장리듬을 감지할 수 없는자율형미생물상이 구현되어 지속적으로 정화율을 높일 수 있고, 황토흙이 폭기수와 접촉되어 처리공정을 순화함으로서, 흙 속의 무기물 및 오수의 유기물이 혼재되어 우점균의 과대배양이나 일시적인 폐사현상 등의 편곡이 없는 미생물의 균형이 연계되고, 미립자의 부유오니의 비중이 현탁액과 혼제되어 중력증가로 부유물의 침전능력증대 등의 탁월한 효과와 더불어 황토를 일정한 기간으로 투입하면 지속적인 순환공정이 연계되어 높은 정화율을 얻는 것이다.As described above, the present invention is characterized by the nature of the suspension pipe contact material which can inhabit a mixture of anaerobic, random, and aerobic microorganisms and the formation of a non-aerated random decomposition chamber at the bottom of the sedimentation chamber, the source of green algae, red tide While the removal rate of phosphorus TN and TP is further improved, autonomous microorganisms that cannot detect the death and growth rhythm of microbial metabolic phones can be realized, and the purification rate can be continuously increased. By contacting with and purifying the treatment process, inorganic and sewage organic matters in the soil are mixed to balance microorganisms without overdiffusion of dominant bacteria or temporary death, and the specific gravity of suspended sludge of the fine particles is mixed with suspension. As a result of the gravity increase, it has an excellent effect of increasing the sedimentation capacity of suspended solids. This cyclic process are linked to obtain a high purification rate.
Claims (6)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR1019980004254A KR100241496B1 (en) | 1998-02-13 | 1998-02-13 | Sewage purifying facility of suspended pattern making use of a microorganism |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR1019980004254A KR100241496B1 (en) | 1998-02-13 | 1998-02-13 | Sewage purifying facility of suspended pattern making use of a microorganism |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| KR19990069792A KR19990069792A (en) | 1999-09-06 |
| KR100241496B1 true KR100241496B1 (en) | 2000-02-01 |
Family
ID=19532973
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| KR1019980004254A Expired - Fee Related KR100241496B1 (en) | 1998-02-13 | 1998-02-13 | Sewage purifying facility of suspended pattern making use of a microorganism |
Country Status (1)
| Country | Link |
|---|---|
| KR (1) | KR100241496B1 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100418429B1 (en) * | 1999-08-26 | 2004-02-11 | 이병수 | A wastewater disposal plant using contact treatment method of variability facultative anaerobic |
| KR100432298B1 (en) * | 2001-11-19 | 2004-05-22 | 주식회사 앤바이오 | Recovery Treatment Equipment of wastewater and concentrated metabolic materials thereof |
| KR100798349B1 (en) * | 2007-06-14 | 2008-01-28 | 구제진 | Organic Waste Disposal Equipment |
-
1998
- 1998-02-13 KR KR1019980004254A patent/KR100241496B1/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| KR19990069792A (en) | 1999-09-06 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| AU2010327174B2 (en) | Waste water treatment equipment | |
| US3563888A (en) | Method and apparatus for treating waste-containing liquor | |
| US3968034A (en) | Process and apparatus for treating wastes by a combined activated sludge and biological filter bed | |
| KR20160077233A (en) | Method and device for the treatment of waste water | |
| CA2176260A1 (en) | System and method for treatment of polluted water | |
| KR20160029272A (en) | a simple structured wastewater treatment system using multi step aerating floation method and the wastewater treatment method | |
| CN104556562A (en) | Advanced treatment method for industrial park wastewater | |
| KR20160032067A (en) | a simple structured wastewater treatment system using multi step aerating floation method and the wastewater treatment method | |
| KR101541070B1 (en) | method and device for controlling using turbulence stimulation and filter member | |
| US5344563A (en) | Wastewater treatment system | |
| KR100241496B1 (en) | Sewage purifying facility of suspended pattern making use of a microorganism | |
| CN109678301A (en) | Each door type sewage disposal device | |
| RU1836301C (en) | Installation for waste-water-cleaning | |
| US3075645A (en) | Water treatment in municipal and industrial water systems | |
| KR100880535B1 (en) | Filtration tank using wetland tank | |
| JP3177432B2 (en) | Polluted water purification method and polluted water purification device | |
| KR101898183B1 (en) | Wastewater treatment apparatus equipped with a complex carrier and a spray water flow apparatus, and a method for removing phosphorus and nitrogen using the same | |
| KR100992829B1 (en) | System phosphorus treatment | |
| CN111204868A (en) | Sequencing batch type continuous discharge sewage processor and application method thereof | |
| KR200257303Y1 (en) | Device for treating stream and lake polluted | |
| KR100381901B1 (en) | The treatment system of discharging water in the treatment equipment of sewage and serious contaminated rivers water utilizing the contact oxidation method | |
| KR100279943B1 (en) | Wastewater Purifier | |
| RU38755U1 (en) | BIOLOGICAL WASTE WATER TREATMENT PLANT | |
| JPS6274489A (en) | Recirculation aeration type sewage treatment apparatus | |
| KR20190067338A (en) | Device for air blower at settling tank of sewage treatment machine |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A201 | Request for examination | ||
| PA0109 | Patent application |
St.27 status event code: A-0-1-A10-A12-nap-PA0109 |
|
| PA0201 | Request for examination |
St.27 status event code: A-1-2-D10-D11-exm-PA0201 |
|
| R17-X000 | Change to representative recorded |
St.27 status event code: A-3-3-R10-R17-oth-X000 |
|
| PG1501 | Laying open of application |
St.27 status event code: A-1-1-Q10-Q12-nap-PG1501 |
|
| D14-X000 | Search report completed |
St.27 status event code: A-1-2-D10-D14-srh-X000 |
|
| E701 | Decision to grant or registration of patent right | ||
| PE0701 | Decision of registration |
St.27 status event code: A-1-2-D10-D22-exm-PE0701 |
|
| GRNT | Written decision to grant | ||
| PR0701 | Registration of establishment |
St.27 status event code: A-2-4-F10-F11-exm-PR0701 |
|
| PR1002 | Payment of registration fee |
St.27 status event code: A-2-2-U10-U11-oth-PR1002 Fee payment year number: 1 |
|
| PG1601 | Publication of registration |
St.27 status event code: A-4-4-Q10-Q13-nap-PG1601 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 4 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 5 |
|
| R18-X000 | Changes to party contact information recorded |
St.27 status event code: A-5-5-R10-R18-oth-X000 |
|
| S14-X000 | Exclusive voluntary license recorded |
St.27 status event code: A-4-4-S10-S14-lic-X000 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R11-asn-PN2301 |
|
| S16-X000 | Recordation of exclusive voluntary license cancelled |
St.27 status event code: A-4-4-S10-S16-lic-X000 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R14-asn-PN2301 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 6 |
|
| S14-X000 | Exclusive voluntary license recorded |
St.27 status event code: A-4-4-S10-S14-lic-X000 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 7 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 8 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R11-asn-PN2301 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 9 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 10 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 11 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 12 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 13 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R11-asn-PN2301 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R14-asn-PN2301 |
|
| FPAY | Annual fee payment |
Payment date: 20121101 Year of fee payment: 14 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 14 |
|
| R18-X000 | Changes to party contact information recorded |
St.27 status event code: A-5-5-R10-R18-oth-X000 |
|
| R18-X000 | Changes to party contact information recorded |
St.27 status event code: A-5-5-R10-R18-oth-X000 |
|
| FPAY | Annual fee payment |
Payment date: 20131101 Year of fee payment: 15 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 15 |
|
| R18-X000 | Changes to party contact information recorded |
St.27 status event code: A-5-5-R10-R18-oth-X000 |
|
| FPAY | Annual fee payment |
Payment date: 20141103 Year of fee payment: 16 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 16 |
|
| PN2301 | Change of applicant |
St.27 status event code: A-5-5-R10-R13-asn-PN2301 St.27 status event code: A-5-5-R10-R11-asn-PN2301 |
|
| FPAY | Annual fee payment |
Payment date: 20151102 Year of fee payment: 17 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 17 |
|
| FPAY | Annual fee payment |
Payment date: 20161103 Year of fee payment: 18 |
|
| PR1001 | Payment of annual fee |
St.27 status event code: A-4-4-U10-U11-oth-PR1001 Fee payment year number: 18 |
|
| LAPS | Lapse due to unpaid annual fee | ||
| PC1903 | Unpaid annual fee |
St.27 status event code: A-4-4-U10-U13-oth-PC1903 Not in force date: 20171104 Payment event data comment text: Termination Category : DEFAULT_OF_REGISTRATION_FEE |
|
| R18-X000 | Changes to party contact information recorded |
St.27 status event code: A-5-5-R10-R18-oth-X000 |
|
| PC1903 | Unpaid annual fee |
St.27 status event code: N-4-6-H10-H13-oth-PC1903 Ip right cessation event data comment text: Termination Category : DEFAULT_OF_REGISTRATION_FEE Not in force date: 20171104 |