KR0116808Y1 - Nitrification reactor of waste water containing ammonia - Google Patents
Nitrification reactor of waste water containing ammonia Download PDFInfo
- Publication number
- KR0116808Y1 KR0116808Y1 KR2019940038968U KR19940038968U KR0116808Y1 KR 0116808 Y1 KR0116808 Y1 KR 0116808Y1 KR 2019940038968 U KR2019940038968 U KR 2019940038968U KR 19940038968 U KR19940038968 U KR 19940038968U KR 0116808 Y1 KR0116808 Y1 KR 0116808Y1
- Authority
- KR
- South Korea
- Prior art keywords
- wastewater
- ammonia
- reactor
- nitrification
- synthetic resin
- 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
- C02F3/101—Arranged-type packing, e.g. stacks, arrays
-
- 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
- C02F3/106—Carbonaceous materials
-
- 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
- C02F3/109—Characterized by the shape
-
- 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
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
- C02F3/303—Nitrification and denitrification treatment characterised by the nitrification
-
- 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
- C02F2003/001—Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
-
- 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)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Microbiology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
본 고안은 생물막공법을 이용한 암모니아 함유 폐수처리시 생물화학적 산소요구량(BOD), 화학적 산소용구량(COD)을 안정시켜 효율적으로 처리한후 질산화시키는 암모니아 함유폐수 질산화 반응 장치에 관한 것이다The present invention relates to an ammonia-containing wastewater nitridation apparatus which stabilizes biochemical oxygen demand (BOD) and chemical oxygen demand (COD) and efficiently nitrates the treated ammonia-containing wastewater using biofilm method.
본 고안은 폐수를 저장하는 원수 탱크와 폐수공급펌프를 갖는 폐수 공급장치: 상기 폐수공급장치에서 제공된 폐수를 내부에 담고, 오니의 퇴적을 방지하는 교반바(stirrer Bar)와 교반기를 갖추며, 내부에 산소를 공급하는 압축기와 유량계 및 복수개의 산기관을 갖는 한편, 다수개의 합성수지 매질을 일렬로 엮어서 내장한 반응조: 상기 반응조내의 폐수온도를 일정하게 하는 온수기와 순환펌프를 갖는 가온장치: 및 상기 반을조에서 유출된 처리수를 침전시켜서 방류하는 침전장치:를 포함함을 특징으로 하는 암모니아 함유 폐수질산화반응장치를 제공한다.The present invention is a wastewater supply device having a raw water tank and a wastewater supply pump for storing wastewater: containing a wastewater provided by the wastewater supply device therein, and having a stir bar and agitator to prevent deposition of sludge, A reactor having a compressor for supplying oxygen, a flow meter, and a plurality of diffusers, and a plurality of synthetic resin media interwoven with each other: a warmer having a water heater and a circulation pump for maintaining a constant wastewater temperature in the reactor; and It provides an ammonia-containing wastewater oxidization reaction apparatus comprising: a precipitation device for precipitating and discharging the treated water flowing out of the tank.
Description
제1도는 본 고안에 따른 암모니아 함유 폐수질산화 반응장치를 도시한 구성도1 is a block diagram showing an ammonia-containing waste water oxidation reaction apparatus according to the present invention
제2도는 본 고안에 따른 암모니아 함유 폐수 질산화 반응장치에 사용되는 다공성 매질의 구성도이다.2 is a block diagram of a porous medium used in the ammonia-containing wastewater nitrification apparatus according to the present invention.
*도면의 주요 부분에 대한 부호의 설명* Explanation of symbols for main parts of drawing
10 : 반응조 12 : 합성수지 매질10 Reactor 12 Synthetic Resin Medium
15 : 폐수공급장치 20 : 교반바(stirrer Bar)15: waste water supply device 20: stirring bar (stirrer bar)
25 : 압축기 31 : 가온장치25 Compressor 31 Heating Device
40 : 침전장치40: precipitation device
본 고안은 생물막공법을 이용한 암모니아 함유 폐수처리시 생물화학적 산소요구량(BOD), 화학적 산소요구량(COD)을 안정시켜 효율적으로 처리한 후 질산화시키는 암모니아 함유폐수 질산화 반응장치에 관한 것이다.The present invention relates to an ammonia-containing wastewater nitrification apparatus which stabilizes biochemical oxygen demand (BOD) and chemical oxygen demand (COD) and efficiently nitrates the treated ammonia-containing wastewater using a biofilm method.
종래, 오염물질(BOD, COD)과 암모니아 화합물을 동시 처리하는 생물학적인 방법으로는 반응조를 2단으로하여 제 1 반응조에는 유동상(流動床)을 유지시켜 유기물을 산화분해하고, 제 2 반응조에는 고정상(固定床)을 설치하여 질산화하는 방법이 알려지고 있다. 그러나 이경우는 2개의 반응조를 별도 관리해야하고, 제 1 반응조에서의 효율이 떨어질 경우 제 2 반응조에서는 질산화를 거의 기대할 수 없는 문제점을 내포하고 있으며, 이러한 방법들은 비교적 농도가 낮은 폐수나 도시하수의 처리에 많이 이용되어 졌다. 그러나 산업폐수가 다량 함유되어 있는 도시하수 및 오니처리수등에는 오염물질과 암모니아 화합물의 함량이 높기 때문에 종래의 방법을 그Conventionally, biological processes for simultaneously treating contaminants (BOD, COD) and ammonia compounds are carried out in two stages of reaction tanks, oxidative decomposition of organic substances by maintaining a fluidized bed in the first reactor, and in the second reactor. It is known to install a stationary phase and to nitrify. In this case, however, two reactors must be managed separately, and if the efficiency of the first reactor is poor, the second reactor has a problem that nitrification can hardly be expected. These methods treat wastewater or municipal sewage with relatively low concentrations. It's used a lot. However, municipal sewage and sludge treatment water containing a large amount of industrial wastewater has a high content of pollutants and ammonia compounds.
대로 적용하기란 상당히 곤란하다. 질산화가 일어나기 위해서는 먼저 탄소화합물의 분해가 이루어져야 하며, BOD로 환산 20mg/ℓl이하가 되어야만 질산화가 시작되기 때문에 유기물의 층분한 분해는 질산화에 있어서 중요한 관건이다. 유기물과 암모니아 화합물의 농도가 높을 경우 반응조내에서 아질산화가 진행되어 아질산이It is quite difficult to apply it as it is. In order for nitrification to occur, carbon compounds must be decomposed first, and nitrification is only possible when BOD conversion is less than 20 mg / ll. Therefore, the decomposition of organic matters is an important factor for nitrification. When the concentrations of organic and ammonia compounds are high, nitrite oxidation proceeds in the reactor,
측적된다. 아질산성 질소 1mg은 COD 1.14mg으로 환산되기 때문에 처리수의 COD를 높일 염려가 있고, 고정상의 담체가 폐쇄 및 탈리(脫離)현상이 자주 발생하여 용존산소의 분산이 원활하지 못하고 오니가 퇴적될 경우 암모니아의 농도를 높일 가능성이크며, 처리시간이 길어질 가능성이 높다.It is measured. Nitrite nitrite 1mg is converted to COD 1.14mg, which raises the COD of the treated water, and the fixed phase carrier frequently closes and desorptions, so that dissolved oxygen is not dispersed and sludge is deposited. It is very likely to increase the concentration of ammonia, and the processing time is likely to be long.
본 고안은 상기와 같은 문제점을 해소하기 위한 것으로, 생물막공법을 이용하여 반응 조내의 미생물의 농도을 높여 하나의 반응조 내에서 유기물의 제거와 암모니아의 질산화가 동시에 일어나게 하고 고정상에서의 생물막의 막힘과 탈리 현상을 방지하며 미생물농도의 적정 유지가 가능하게 하는 암모니아 함유 폐수 질산화 반응장치을 제공함데 그 목적이 있다.The present invention is to solve the above problems, by using the biofilm method to increase the concentration of microorganisms in the reaction tank to remove the organic matter and nitrification of ammonia in one reaction tank at the same time, clogging and desorption phenomenon of the biofilm on the fixed bed The purpose of the present invention is to provide ammonia-containing wastewater nitrification apparatus that prevents the microorganisms and maintains the microbial concentration.
상기 목적을 달성하기 위항여 본 고안은, 암모니아 함유 폐수 질산화 반응장치에 있어서, 폐수를 저장하는 원수 탱크와 폐수공급펌프를 갖는 폐수 공급장치 상기 폐수공급부에서 제공된 폐수를 내부에 담고, 오니의 퇴적을 방지하는 교반바(stirrer Bar)와 교반기를 갖추며, 내부에 산소를 공급하는 압축기와 유량계 및 복수개의 상기관을 갖는 한편, 다수개의 합성수지 매질을 일렬로 엮어서 내장한 반응조 : 상기 반응조내의 폐수온도를 일정하게 하는 온수기와 순환펌프를 갖는 가온장치 : 및 상기 반응조에서 유출된 처리수를 침전시켜서 방류하는 침전장치:를포함함을 특징으로 하는 암모니아 함유 폐수질산화반응장치를 마련함에 의한다. 이하, 본 고안을 도면에 따라서 보다 상세히 설명한다.In order to achieve the above object, the present invention is an ammonia-containing wastewater nitrification apparatus, a wastewater supply apparatus having a raw water tank for storing wastewater and a wastewater supply pump containing wastewater provided by the wastewater supply unit therein, and depositing sludge Reactor having a stirring bar (stirrer bar) and a stirrer to prevent, supplying oxygen therein and a flow meter and a plurality of said pipes, and a plurality of synthetic resin mediums in a row, built-in: a waste water temperature in the reactor According to the present invention, there is provided a heating apparatus having a water heater and a circulation pump, and a precipitation apparatus for precipitating and discharging the treated water flowing out of the reaction tank. Hereinafter, the present invention will be described in more detail with reference to the drawings.
제1도에는 본 고안에 따른 폐수 질산화 반응장치(1)가 도시되어 있다. 상기 폐수질산화 반응장치(1)는 일정크기의 1개의 반응조(10)를 갖추고, 상기 반응조(10)내에는 다수개의 합성수지 매질(Plastic Media)(12)이 일렬로 엮여서 다수개의 즐을 이루어 고정배치된다. 상기 합성수지 매질(12)은 제 2도에 도시된 바와 같은 수세미 형태의 다수개의 구멍(12a)을 갖추고, 합성수지 플라스틱으로 이루어지며, 반응조(10)내용적의 대략 50%까지 층진된다.1 shows a wastewater nitrification apparatus 1 according to the present invention. The wastewater nitrification reaction apparatus 1 includes one reactor 10 having a predetermined size, and in the reactor 10, a plurality of synthetic media 12 are woven in a row to form a plurality of blas to fix the batch. do. The resin medium 12 has a plurality of pores 12a in the form of a loofah as shown in FIG. 2, made of synthetic resin plastic, and stratified to approximately 50% of the contents of the reactor 10.
따라서, 상기 반응조(10)내에는 50%의 고정상과, 그외의 50%의 유동상이 형성되는 것이다. 그리고, 상기 반응조(10)내로 폐수를 공급하는 폐수공급장치(15)는 폐수 저장용 원수 탱크(16)와 폐수 공급펌프(17)를 갖추고 있다.Accordingly, 50% of the fixed bed and 50% of the fluidized bed are formed in the reactor 10. The wastewater supply device 15 for supplying wastewater into the reactor 10 includes a raw water tank 16 for storing wastewater and a wastewater supply pump 17.
그리고, 상기 반응조(10)하부에는 오니의 퇴적을 방지하는 교반바(20)와 교반기(22)가 장착되고, 반응조(10)내부로 산소(oxy Gen)를 공급하는 압축기(25)와 유량계(27) 및 복수개의 산기관(29)이 갖춰진다. 또한, 산기 반응조(10)내부의 폐수를 순환시켜서 일정온도로 유지시키는 가온장치(31)는 온수기(32)와 순환펌프(35)를 갖추며, 상기 반응조(10)에서 유출된 처리수를 침전시켜서 방류하는 침전장치(40)를 갖는다. 미설명부호(42)는 배플(Baffle),(16a)는 교반기(Agitator)이다.In addition, a stirring bar 20 and an agitator 22 are installed below the reaction tank 10 to prevent deposition of sludge, and a compressor 25 and a flow meter for supplying oxygen (oxygen) to the inside of the reaction tank 10 ( 27) and a plurality of diffusers 29 are provided. In addition, the heating device 31 for circulating the waste water in the acidic reaction tank 10 to maintain a constant temperature is equipped with a water heater 32 and the circulation pump 35, by precipitating the treated water flowing out of the reaction tank 10 It has a precipitation apparatus 40 which discharges. Reference numeral 42 is a baffle, 16a is an agitator.
상기와 같이 구성된 본 고안은, 반응조(10)내부로 폐수가 유입되는 경우, 반응조(10)내부에는 합성수지 매질(12)이 50% 정도 충진되어 있기 때문에 하나의 반응조내에 고정상과 유동상을 유지시킬수 있고, 고정상에 고농도 미생물 유지가 가능하여 반송오니가 필요없으며, 유동상을 통하여 반응조내의 오염물질의 균일한 분산을 통하여 미생물과의 효율적인 접촉을 기할수 있으며 pH온도, 교반속도의 조절을 통하여 유기물 제거 및 질산화의 효율을 높일 수 있다. 또한, 반응조(10)내에 50% 정도 차지하고 있는 수세미형태의 합성수지 매질(12)은 미생물의 침강성을 개선시키고 미생물의 농도를 높이 유지할 수 있어 반송오니를 생략할 수 있고, 특히, 고착성이 강한 질산화 박테리아인Nitrosomonas. Nitrobactor 의 부착 성장에 아주 좋은 특징을 갖고 있으므로 고정 담체를 사용하지 않는 경우와 비교하여 처리시간을 ½이상 단축할 수 있고, 처리 효을 역시 미생물의 고농도 유지로 인하여 F/M비(kg Bod/kg MLSS비)가 낮아져 처리율을 높일 수 있고, 충격부하에도 강한 현상을 나타내고 있다. 그리고, 반응조(10)내의 유동상에서는 바닥에 설치된 2개의 산기관(29)에 의하여 유입원수와 용존산소의 균일한 혼합작용을 통하여 박테리아나 보티셀라(Voticella) 등의 활성을 촉진시켜 탄소화합물의 분해를 가속시킬 수 있다.When the wastewater is introduced into the reactor 10, the present invention configured as described above can maintain the fixed and fluidized beds in one reactor because the reaction medium 10 is filled with about 50% of the synthetic resin 12. It is possible to maintain high concentration of microorganisms in the fixed phase and does not require return sludge.Effective contact with microorganisms can be achieved through uniform dispersion of contaminants in the reaction tank through the fluidized bed, and organic matter is removed by adjusting pH temperature and stirring speed. And the efficiency of nitrification can be improved. In addition, the scouring pad-type synthetic resin medium 12 occupies about 50% in the reaction tank 10 can improve the settling properties of microorganisms and keep the concentration of microorganisms high, so that the return sludge can be omitted, and in particular, strong nitrifying bacteria Nitrosomonas. As it has very good characteristics for nitrobactor adhesion growth, the treatment time can be shortened by ½ or more compared with the case where no fixed carrier is used, and the treatment effect is also due to the high concentration of microorganisms (kg Bod / kg MLSS B) is lowered, the treatment rate can be increased, and the phenomenon is also strong against the impact load. In the fluidized bed in the reaction tank 10, two acid pipes 29 installed at the bottom promote the activity of bacteria or Voticella through the uniform mixing of inflow water and dissolved oxygen to decompose carbon compounds. Can be accelerated.
뿐만 아니라, 반응조(10)의 바닥에 설치된 교반바(Stirrer Bar)(20)는 오니의 퇴적으로 인한 험기성을 방지할 수 있고 유동상내의 흐름을 조절하여 고정상면에 부착된 생물막이 두께와 성장을 조정하여 반응조내의 처리부하에 적당한 미생물의 농도 유지가 가능하다.In addition, the stirring bar 20 installed at the bottom of the reactor 10 can prevent the roughness due to the deposition of sludge and control the flow in the fluidized bed to increase the thickness and growth of the biofilm attached to the fixed bed surface. It is possible to maintain a suitable concentration of microorganisms in the treatment load in the reaction tank by adjusting the.
또한, 페수를 일정온도로 순환시키는 가온장치(31)는 온수기(32)와 순환펌프(35)를 통하여 대략25 C로 페수 온도를 유지시켜 반응 효율을 향상시킨다.In addition, the heating device 31 for circulating the waste water at a constant temperature maintains the waste water temperature at approximately 25 C through the water heater 32 and the circulation pump 35 to improve the reaction efficiency.
이와 같이 본 고안은, 고정상과 유동상의 비율을 하나의 반응조내에50 : 50 비율로배치하므로서 상호작용을 통하여 암모니아가 함유된 유기성 산업페수, 오니처리수 등의 고효율 처리가 가능하고 Nitrosomonas 보다 Nittobactor의 활성이 상대적으로 강해져 아질산성 질소의 축적을 방지하고 질산화를 가속시켜 처리수질을 향상시킨다. 이하, 본 고안의 작용효과를 실시예를 통하여 보다 상세히 설명한다.As such, the present invention enables the high-efficiency treatment of organic industrial wastewater and sludge treated water containing ammonia through the interaction by arranging the ratio of the fixed and fluidized phases in one reactor at a ratio of 50:50, and the activity of Nittobactor is more effective than Nitrosomonas. This relatively strong prevents the accumulation of nitrite nitrogen and accelerates nitrification to improve the treated water quality. Hereinafter, the effects of the present invention will be described in more detail with reference to Examples.
(실시예)(Example)
본 실험에 사용한 페수는 함모니아가 함유한 유기성 산업페수로서 본고안의 효과를 확인하기 위하여 실시하였으며 실험페수의 성상은 표1에서 보는 바와 같이 BOD 260mg/1, COD 330mg/1, 암모니아성 질소가 50mg/1 이었다.The wastewater used in this experiment was an organic industrial wastewater containing hammonia, and was used to confirm the effect of this paper. The characteristics of the wastewater were as follows: BOD 260mg / 1, COD 330mg / 1, ammonia nitrogen 50mg. / 1.
반응조(10)에는 가로 2.5cm, 세로 2.0cm, 두께 1.0cm인 수세미 형태의 합성수지 매질(12)을 제1도와 같이 일렬로 엮어서 미생물 고정용으로 50%을 넣고 DO의 농도는 4-6 ppm을 유지하도록 공기를 공급하고 반응조 온도를 25도로 유지시켰으며, 질산화의 진행에 따른 pH저하를 반지하기 위해 알카리를 투입 pH를 8.0-8.3으로 조정하였고, 교반바(20)의 속도는 80-100 rpm으로 교반하면서 14일 동안 활성오니를 순응시킨후 반응시간을 8-10시간(BOD용적부하 0.2-0.4BOD. Kg/m )되도록 폐수공급 펌프(17)를 사용하여 실험원수를 반응조에 유입시켰다. 이때 유입수의 완전한 혼합을 위하여 폐수가 바닥으로 떨어진 다음 유입될 수 있도록 유입구에 배플(baffle 42)을 설치하였다. 이렇게 반응조(10)에 유입된 폐순는 반응후 침전조(40)에서 전치후방류된다. 4개월 동안 연속적으로 처리 하였으며, 최종 처리수의 결과는 하기표1에 나타냈다. 표1.에서 보는 바와 같이 BOD가 13.0mg/1이하, COD가 43mg/1이하, 암모니아성 질소가 5.8mg/1이하로 양호하였다.In the reactor 10, a synthetic scrubber medium 12 having a width of 2.5 cm, a length of 2.0 cm, and a thickness of 1.0 cm was woven in a line as shown in FIG. 1, and 50% was added for fixing microorganisms, and the concentration of DO was 4-6 ppm. Air was maintained to maintain the temperature and the reactor temperature was maintained at 25 degrees, alkali was added to adjust the pH to 8.0-8.3 to ring the pH decrease with the progress of nitrification, the speed of the stirring bar 20 is 80-100 rpm After acclimatizing the activated sludge for 14 days with stirring, the raw water was introduced into the reactor using a wastewater supply pump (17) so that the reaction time was 8-10 hours (BOD volume load 0.2-0.4BOD. Kg / m). At this time, a baffle 42 was installed at the inlet so that the wastewater fell into the bottom for inflow of the inlet completely. As such, the wastewater introduced into the reaction tank 10 is pre-back discharged from the settling tank 40 after the reaction. The treatment was performed continuously for 4 months, and the results of the final treated water are shown in Table 1 below. As shown in Table 1, BOD was 13.0 mg / 1 or less, COD 43 mg / 1 or less, and ammonia nitrogen was 5.8 mg / 1 or less.
이 실험결과을 보아 유기물의 효율적인 제거가 가능하고, 특히, 암모니아의 질산화가 잘일어너고 있음을 확인할 수 있었다.The experimental results showed that organic matters can be efficiently removed, and in particular, nitrification of ammonia is well performed.
표1. 실험원수와, 본고안과 총래방식에 따른 처리수의 평균농도Table 1. Average concentration of treated water and treated water according to this paper and conventional method
(단위 : mg/1)(Unit: mg / 1)
상기에서와 같이 본 고안에 의하면, 유기성 산업폐수, 오니처리수 등의 암모니아 함유폐수중의 유기물 처리 및 질산화에 있어서 다음과 같은 효과가 있다.According to the present invention as described above, there is the following effects in the treatment and nitrification of organic matter in ammonia-containing wastewater, such as organic industrial wastewater, sludge treated water.
즉, 하나의 반응조내에 고정상과 유동상을 50:50의 비율로 설치함으로서 종래의 활성 오니공법에서의 반송오니를 생략시켰고, 고정상 생물학의 막힘과 탈리 현상의 방지를 통하여 치리시간을 ½이상 단축할 수 있었다.In other words, by installing the fixed bed and the fluidized bed in a ratio of 50:50 in one reactor, the return sludge in the conventional activated sludge process was omitted, and the control time was reduced by ½ or more by preventing the blockage and detachment phenomenon of the fixed bed biology. Could.
생물화학적산소요구량(BOD) 95% 화학적산소요구량(COD) 87%의 높은 처리효율을 나타냈으며 암모니아 화합물 역시 72.8%까지 질산화 시킬 수 있는 것이다.Biochemical Oxygen Demand (BOD) 95% Chemical Oxygen Demand (COD) 87%. The ammonia compound can also nitrify up to 72.8%.
Claims (2)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR2019940038968U KR0116808Y1 (en) | 1994-12-30 | 1994-12-30 | Nitrification reactor of waste water containing ammonia |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR2019940038968U KR0116808Y1 (en) | 1994-12-30 | 1994-12-30 | Nitrification reactor of waste water containing ammonia |
Publications (2)
Publication Number | Publication Date |
---|---|
KR960022571U KR960022571U (en) | 1996-07-20 |
KR0116808Y1 true KR0116808Y1 (en) | 1998-04-23 |
Family
ID=19405162
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR2019940038968U KR0116808Y1 (en) | 1994-12-30 | 1994-12-30 | Nitrification reactor of waste water containing ammonia |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR0116808Y1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100852208B1 (en) * | 2008-03-20 | 2008-08-13 | 글로벌 후소 주식회사 | Multistage waste water treatment apparatus |
-
1994
- 1994-12-30 KR KR2019940038968U patent/KR0116808Y1/en not_active IP Right Cessation
Also Published As
Publication number | Publication date |
---|---|
KR960022571U (en) | 1996-07-20 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101473050B1 (en) | Method and device for removing biological nitrogen and support therefor | |
CA2542894C (en) | Multi-environment wastewater treatment method | |
CN205893017U (en) | Coking wastewater biological processing device | |
KR20180043689A (en) | Eco-friendly Sewage System By Contact Oxidation Method Using Plastic Material As Bio-film Filtration | |
KR100527172B1 (en) | A method and apparatus for nitrogenous waste water of nitrogen and sewage | |
JPH11333496A (en) | Microorganism carrier for denitrification | |
KR100497810B1 (en) | System of circulated sequencing batch Reactor with media containing zeolite for organic matters, nitrogen and phosphorus removal in sewage and waste waters | |
KR100293568B1 (en) | Biological treatment device for leather wastewater and sludge reduction | |
JP2006314991A (en) | Apparatus and method for treating high-concentration nitrogen-containing dirty waste water such as waste water from livestock farmer and excreta | |
KR100365314B1 (en) | Waste-Water Disposal System And Method For Removing Nitrogen, Phosphorus and Sludge by Using Aerobic and Anaerobic logarithmic/Endogenous Microorganism growth | |
KR0116808Y1 (en) | Nitrification reactor of waste water containing ammonia | |
KR100435107B1 (en) | Advance Treatment Equipment and Process for Nitrogen and Phosphate Removal in Sewage and Wastewater | |
KR100321680B1 (en) | Advance wastewater treatment method by wastewater passage alternation | |
JPH09253687A (en) | Anaerobic and aerobic treatment apparatus for waste water | |
KR100321679B1 (en) | Advanced wastewater treatment method | |
KR100346303B1 (en) | Nutrient removal process for fixed biofilm | |
KR960011888B1 (en) | Method and apparatus for biological treatment of waste water including nitrogen and phosphorus | |
KR101032068B1 (en) | Sewage-wastewater treating system and method the same, using high-effciency sequencing batch reactor process | |
JP3807945B2 (en) | Method and apparatus for treating organic wastewater | |
KR970069904A (en) | Method and apparatus for simultaneous removal of biological nitrogen, phosphorus from sewage and waste water | |
JPH03232590A (en) | Treatment of sewage | |
KR100202066B1 (en) | Wastewater treatment method using biological 3 step digestion process in one reactor | |
KR19990075815A (en) | Wastewater Treatment System and Method Using Fixed Biofilm Process | |
KR100318367B1 (en) | Waste water treatment apparatus | |
JP2673488B2 (en) | Method and apparatus for treating organic wastewater |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E701 | Decision to grant or registration of patent right | ||
REGI | Registration of establishment | ||
FPAY | Annual fee payment |
Payment date: 20001228 Year of fee payment: 4 |
|
LAPS | Lapse due to unpaid annual fee |