KR19990073118A - Microbial media unit for biological wastewater treatment - Google Patents
Microbial media unit for biological wastewater treatment Download PDFInfo
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- KR19990073118A KR19990073118A KR1019990018220A KR19990018220A KR19990073118A KR 19990073118 A KR19990073118 A KR 19990073118A KR 1019990018220 A KR1019990018220 A KR 1019990018220A KR 19990018220 A KR19990018220 A KR 19990018220A KR 19990073118 A KR19990073118 A KR 19990073118A
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- 230000000813 microbial effect Effects 0.000 title claims abstract description 28
- 238000004065 wastewater treatment Methods 0.000 title abstract description 9
- 238000005273 aeration Methods 0.000 claims abstract description 23
- 239000002351 wastewater Substances 0.000 claims abstract description 22
- 230000005484 gravity Effects 0.000 claims abstract description 20
- 244000005700 microbiome Species 0.000 claims abstract description 13
- 238000011049 filling Methods 0.000 claims abstract description 10
- 239000002245 particle Substances 0.000 claims abstract description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 30
- 239000011248 coating agent Substances 0.000 claims description 16
- 238000000576 coating method Methods 0.000 claims description 16
- 238000000034 method Methods 0.000 claims description 15
- 239000000853 adhesive Substances 0.000 claims description 14
- 230000001070 adhesive effect Effects 0.000 claims description 14
- 239000004927 clay Substances 0.000 claims description 12
- 239000000463 material Substances 0.000 claims description 9
- 239000000203 mixture Substances 0.000 claims description 9
- 239000004033 plastic Substances 0.000 claims description 9
- 229920003023 plastic Polymers 0.000 claims description 9
- 239000004480 active ingredient Substances 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 5
- 229910052742 iron Inorganic materials 0.000 claims description 3
- 239000010935 stainless steel Substances 0.000 claims description 3
- 229910001220 stainless steel Inorganic materials 0.000 claims description 3
- 239000004925 Acrylic resin Substances 0.000 claims description 2
- 229920000178 Acrylic resin Polymers 0.000 claims description 2
- 239000004593 Epoxy Substances 0.000 claims description 2
- 239000004372 Polyvinyl alcohol Substances 0.000 claims description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 2
- 239000004568 cement Substances 0.000 claims description 2
- 238000000465 moulding Methods 0.000 claims description 2
- 229920002635 polyurethane Polymers 0.000 claims description 2
- 239000004814 polyurethane Substances 0.000 claims description 2
- 229920002451 polyvinyl alcohol Polymers 0.000 claims description 2
- 235000019353 potassium silicate Nutrition 0.000 claims description 2
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 claims description 2
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 claims description 2
- 239000010802 sludge Substances 0.000 abstract description 11
- 239000012530 fluid Substances 0.000 abstract description 6
- 239000000969 carrier Substances 0.000 description 11
- 238000004519 manufacturing process Methods 0.000 description 8
- PPBRXRYQALVLMV-UHFFFAOYSA-N Styrene Chemical compound C=CC1=CC=CC=C1 PPBRXRYQALVLMV-UHFFFAOYSA-N 0.000 description 6
- 238000010304 firing Methods 0.000 description 4
- 239000007788 liquid Substances 0.000 description 4
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 2
- 229920006328 Styrofoam Polymers 0.000 description 2
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 239000002734 clay mineral Substances 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 238000003795 desorption Methods 0.000 description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 239000005373 porous glass Substances 0.000 description 2
- 239000008261 styrofoam Substances 0.000 description 2
- 239000010457 zeolite Substances 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 230000005526 G1 to G0 transition Effects 0.000 description 1
- 239000005909 Kieselgur Substances 0.000 description 1
- 239000004793 Polystyrene Substances 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 230000005587 bubbling Effects 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000010485 coping Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 238000010348 incorporation Methods 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000004745 nonwoven fabric Substances 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920005594 polymer fiber Polymers 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 229920005749 polyurethane resin Polymers 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000002062 proliferating effect Effects 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000008961 swelling Effects 0.000 description 1
- 239000000454 talc Substances 0.000 description 1
- 229910052623 talc Inorganic materials 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 239000010455 vermiculite Substances 0.000 description 1
- 229910052902 vermiculite Inorganic materials 0.000 description 1
- 235000019354 vermiculite Nutrition 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
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- 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
- C02F3/105—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
- C02F3/10—Packings; Fillings; Grids
- C02F3/105—Characterized by the chemical composition
- C02F3/108—Immobilising gels, polymers or the like
-
- 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
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- Chemical & Material Sciences (AREA)
- Life Sciences & Earth 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)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
본 발명은 오/폐수 처리용 미생물 담체 유니트에 관한 것으로,The present invention relates to a microorganism carrier unit for wastewater / wastewater treatment.
오/폐수가 내부로 관통하도록 망상 구조로된 형틀 상자 내부에Inside the frame box with mesh structure to allow the waste water to pass through
비중을 조절한 미생물 담체를 고정상용으로는 5∼70체적%를, 그리고 유동상용으로는 30∼90체적%를 충진시킨 뒤 망상 구조로된 뚜껑을 덮고,After filling the microorganism carrier with the specific gravity adjusted to 5 to 70% by volume for the fixed bed and 30 to 90% by volume for the fluidized bed, cover the lid of the network structure,
이와 같이 제조된 고정상용 담체 유니트를 혐기조 내지는 폭기조에 50∼100체적%로 설치하거나 혹은 상기 유동상용 담체 유니트를 폭기조에 30∼70체적%로 설치한 미생물 담체 유니트가 제공된다.Provided is a microbial carrier unit provided with a fixed bed carrier unit prepared in this way in an anaerobic or aeration tank at 50 to 100% by volume, or in a fluid tank at 30 to 70% by volume.
본 발명에 의하면, 손쉽게 담체 입자를 담을 수 있고 오/폐수가 내부로 관통하도록 제조한 형틀에 적절한 담체 유니트를 적당량 충진시킴으로써 활성 담체의 분산성을 개선시키고, 폐수의 흐름 채널을 형성가능하게 되어 슬러지 막힘 현상을 개선시킬 수 있다.According to the present invention, by filling an appropriate amount of a suitable carrier unit in a mold which can easily contain carrier particles and penetrate the wastewater / wastewater therein, the dispersibility of the active carrier can be improved, and the flow channel of the wastewater can be formed so that sludge can be formed. The clogging phenomenon can be improved.
Description
본 발명은 오/폐수 처리용 미생물 담체 유니트에 관한 것이다. 보다 상세하게는 본 발명은 형틀에 미생물 담체를 적당량 충진시켜 혐기조 및 폭기조 모두에서 오/폐수를 효과적으로 처리하는 미생물 담체 유니트에 관한 것이다.The present invention relates to a microbial carrier unit for wastewater / wastewater treatment. More specifically, the present invention relates to a microbial carrier unit for effectively treating wastewater / waste water in both anaerobic and aeration tanks by filling an appropriate amount of microbial carriers in a mold.
생물학적 오/폐수 처리 공법은 크게 활성 슬러지 공법과 생물막 공법으로 나눌 수 있다. 활성슬러지법에 의한 오/폐수 처리의 경우 부하변동에 대한 대처능력이 낮고 잉여 오니가 많이 발생하는 등의 문제점이 있다.Biological wastewater treatment methods can be largely divided into activated sludge process and biofilm process. In the case of wastewater treatment by activated sludge method, there are problems such as low coping capacity against load fluctuations and a lot of surplus sludge.
이에 반하여, 미생물을 부착, 증식시킨 미생물 접촉제를 오/폐수 처리 시설에 설치하여 부착증식된 미생물에 의해 오염물을 분해시켜 처리하는 생물막 공법의 경우에는 담체에 미생물이 고농도로 부착되어 슬러지의 팽화 현상을 방지할 수 있고, 고농도/저농도의 부하에도 제거 효율이 좋으며, 슬러지 발생량이 적고 슬러지 반송이 불필요하여 시설비와 동력비면에서 경제적이고 반응기 크기도 작으며, 처리 물량에 탄력적인 대응이 가능한 점등 많은 장점이 있다.On the other hand, in the biofilm process in which microbial contactants that attach and multiply microorganisms are installed in wastewater / wastewater treatment facilities to decompose and treat contaminants by proliferating microorganisms, microorganisms are adhered to the carrier at high concentrations to cause swelling of sludge. It can be prevented, and the removal efficiency is good even at high / low concentration load, the amount of sludge generated and sludge transportation is unnecessary, so it is economical in terms of facility cost and power, and the reactor size is small. There is this.
일반적으로 생물막을 이용한 오/폐수 처리 공정에서는 미생물을 부착시키기 위해서 여러 가지 담체가 사용되고 있다. 그 재질로는 고분자계, 세라믹계 또는 활성탄계로 나뉘며, 그 형태로는 구형이나 튜브형태로 성형한 것과 섬유상 또는 부직포 형태로 제조한 것등 다양한 형태가 있다.In general, various carriers are used to attach microorganisms in wastewater / wastewater treatment processes using biofilms. The material is divided into polymer, ceramic, or activated carbon, and the shape may be in various forms such as spherical or tube-shaped and fibrous or non-woven fabrics.
고분자계 담체는 원하는 모양으로 제작하기 쉽고 가격이 싸지만 비표면적이 작고 물리/화학적으로 불안정하여 미생물의 탈리가 빈번하며 슬러지 발생량이 많다.Polymeric carriers are easy to manufacture in a desired shape and are inexpensive, but have a small specific surface area and are physically / chemically unstable, causing frequent desorption of microorganisms and a large amount of sludge generation.
이에 반해 활성탄이나 세라믹계 담체는 비표면적이 크고 물리/화학적으로 안정하며 미생물 막이 얇게 형성되고 슬러지 발생량이 적은 장점이 있으나, 통상 2∼10mm정도의 미립자로 성형되어 직접 반응조에 투입하기 곤란하고 비중이 커서 유동상으로는 사용하기 불가능하다는 단점이 있다.On the other hand, activated carbon or ceramic carriers have the advantages of large specific surface area, physical / chemical stability, thin microbial film formation, and low sludge generation rate, but are usually formed into fine particles of about 2 to 10 mm and difficult to directly enter into the reactor. The disadvantage is that it cannot be used with a cursor fluidized bed.
생물막 공법에 사용되는 미생물 고정화 담체를 혐기조나 폭기조에 투입하여 사용하기 위해서는 반응기에 따라 서로 다른 방법이 요구된다. 혐기조는 일반적으로 공기의 혼입을 막기 위해 내외부 혼합 장치에 의해 액체를 혼합하기 어렵고 액체 흐름 또한 난류 형성이 전혀 없는 층흐름이기 때문에 물질 전달력을 향상시키기 위해서는 담체가 반응조 전체에 골고루 위치하고 담체간 거리가 일정하게 유지되는 것이 좋다.In order to use the microorganism immobilization carrier used in the biofilm process in an anaerobic tank or aeration tank, a different method is required depending on the reactor. The anaerobic tank is generally a layer flow that is difficult to mix liquids by internal and external mixing devices to prevent the incorporation of air, and liquid flow and turbulence formation are not formed. It is good to stay constant.
이 때문에 섬유상 또는 부직포 담체 등을 판형으로 제작하여 반응기 내부에 일정한 간격으로 설치하는 형태의 PPR(parallel passage 반응기)로 설치 운용하는 예가 많으나, 재질로 인한 담체로서의 성능의 한계때문에 크게 보편화되지 못하고 있다.For this reason, there are many examples in which a fiber-like or non-woven carrier is manufactured in a plate shape and installed and installed in a reactor (parallel passage reactor), which is installed at regular intervals inside the reactor.
이에 반하여 활성탄이나 점토 광물등으로 제조된 입자형 담체는 그 모양의 한계성으로 인해 대형 얇은 판상 형태의 직육면체 철망 상자에 충진한 뒤 이 철망 상자를 평행으로 배치하여 PPR 형태로 설치하게 되나, 개개 담체의 반응기내 분산 효율이 떨어지고 담체를 채우는 철망 상자의 폭을 얇게 할 수가 없으므로 담체의 반응기내 체적 점유율을 낮추기 위해서는 철망 상자간의 거리가 멀어지고 따라서 유체와 담체간 물질 전달 속도가 늦어져 전체적인 효율이 떨어지는 단점이 있다.On the contrary, the granular carrier made of activated carbon or clay mineral is filled in a large thin plate-shaped rectangular parallelepiped wire mesh box due to its limitation in shape, and then placed in parallel in the form of PPR by placing the wire mesh box in parallel. Dispersion efficiency in the reactor is inferior and the width of the wire mesh box filling the carrier cannot be reduced, so that the distance between the wire mesh boxes is shortened in order to lower the volume share of the carrier in the reactor, and thus the overall efficiency decreases due to the slow speed of mass transfer between the fluid and the carrier. There is this.
또한 폭기조에서는 원활한 폭기를 위해서 담체가 한쪽으로 쏠리거나 폭기 저항이 나타나지 않도록 조심해야 하며, 담체의 반응기내 차지하는 체적은 줄이면서 분산성과 표면적은 높아야 처리 효율이 개선된다. 이러한 이유로 폭기조에서는 고정상 담체보다 유동상 담체가 선호되나, 아직까지 성능좋고 값싸게 제작할 수 있는 유동상 담체가 없었다.In addition, in the aeration tank, care must be taken not to lean the carrier to one side or to exhibit aeration resistance for smooth aeration, and the dispersibility and surface area of the carrier should be reduced while improving the treatment efficiency. For this reason, the fluidized bed carrier is preferred to the fixed bed carrier in the aeration tank, but there has been no fluidized bed carrier which can be manufactured in good performance and cheaply.
따라서 이와 같은 단점을 극복하기 위하여, 대한민국 특허 공고 96-9384호에서는 플라스틱으로 제조된 새장 모양의 유동상 유니트내에 비중 조절 물체를 삽입 고정하고 수세미상으로된 섬유상 담체를 삽입하여 비중 조절이 가능한 유동상 미생물 접촉제 유니트를 제시하고 있으나, 이 경우에는 합성 수지로된 수세미상 미생물 접촉제로서 활성탄이나 점토류 계통의 담체에 비하여 미생물이 친화적이지 못하고, 물리/화학적으로 불안정하며 구조상 제조하기가 어려운 단점이 있다.Therefore, in order to overcome this disadvantage, Korean Patent Publication No. 96-9384 is a fluidized bed capable of adjusting the specific gravity by inserting and fixing a specific gravity control object in a cage-shaped fluidized bed unit made of plastic and inserting a scrubber-like fibrous carrier. The microbial contact unit has been proposed, but in this case, it is a synthetic scrubber-like microbial contactant, which is disadvantageous in that microorganisms are not friendly, physical / chemically unstable, and difficult to manufacture structurally compared to activated carbon or clay-based carriers. have.
이뿐만 아니라 대한민국 특허공개 98-33594호에는 고분자계 섬유사를 이용한 유동상 미생물 접촉제를 제시하고 있으나, 고분자계이기 때문에 미생물의 탈리가 발생하는 등의 문제점이 남아 있으며, 비중이 물에 근접하는 작은 섬유를 주성분으로 하므로 유동이 약하거나 폭기가 없을 때에는 물위로 부유하는 단점이 있다.In addition, the Republic of Korea Patent Publication No. 98-33594 proposes a fluidized bed microbial contact agent using a polymer fiber yarn, but because the polymer is a problem such as desorption of microorganisms, and the specific gravity is close to water Since small fibers are the main component, there is a disadvantage in that they float on water when the flow is weak or there is no aeration.
이와는 별도로 대한민국 특허 공개 97-26944호에는 고분자대신 구형의 다공성 유리 담체를 사용한 유동화 담체를 제시하고 있는데, 내부 중심에 발포 스티렌 막대를 사용하고 그위에 동결 건조된 균주가 부착된 다공성 유리 담체를 얹고 다시 그물망으로 감싸야 하므로 제작하기가 용이하지 않을 뿐만 아니라 유니트 내부가 막힌 발포스티렌 막대로 되어 있어서 유체의 흐름이 내부를 관통하여 원활하게 흐르지 않는 단점이 있다.Separately, Korean Patent Publication No. 97-26944 discloses a fluidizing carrier using a spherical porous glass carrier instead of a polymer, and using a foamed styrene rod at the inner center and a porous glass carrier having a freeze-dried strain attached thereto. It is not easy to manufacture because it must be wrapped in a net, it is made of a foamed styrene rod is blocked inside the unit has a disadvantage that the flow of fluid does not flow smoothly through the inside.
또한 대한민국 특허 97-42320호에는 구형의 활성탄 및 발포 스티렌을 철망으로 감싼 유동상 담체 유니트를 제안하고 있으나, 특수 균주를 접목하여 사용하는 범위가 한정되고 구형의 담체들이 철망에 감싸여 서로 붙어 고정되어 있기 때문에 담체 유니트내로의 유량 흐름이 좋지 않고 또한 철망을 감싸는 제작 과정이 불편하여 대량 생산시 문제가 발생한다.In addition, Korean Patent No. 97-42320 proposes a fluidized bed carrier unit wrapped with a spherical activated carbon and expanded styrene in a wire mesh, but the scope of use by grafting a special strain is limited and the spherical carriers are wrapped in a wire mesh and fixed to each other. As a result, the flow rate into the carrier unit is not good and the manufacturing process of wrapping the wire mesh is inconvenient, causing problems in mass production.
이에 본 발명의 목적은 상기 문제점을 극복하기 위하여, 망상 구조를 응용하여 오/폐수가 내부로 관통하는 형틀을 제조하고, 여기에 비중이 조절된 담체 입자를 충진시켜 담체 유니트를 제조한 다음, 이를 혐기조와 폭기조에 각각 효과적인 양으로 적용함으로써 생물학적 오/폐수를 효과적으로 처리하게 되는 미생물 담체 유니트를 제공하려는데 있다.Accordingly, an object of the present invention, in order to overcome the above problems, by applying a network structure to prepare a mold penetrating the waste water / wastewater inside, and filling the carrier particles with a specific gravity controlled therein to prepare a carrier unit, then The present invention is to provide a microbial carrier unit that effectively treats biological wastewater by applying an effective amount to an anaerobic tank and an aeration tank, respectively.
도 1(a)는 망상 구조의 철, 스테인레스(SUS), 플라스틱 등의 재질로 제작된 원기둥형 형틀의 상자와 뚜껑을 도시한 입체도이며,Figure 1 (a) is a three-dimensional view showing the box and lid of the cylindrical frame made of a material such as iron, stainless steel (SUS), plastic of the network structure,
도 1(b)는 1(a)에서 사용된 재질로 제작된 육면체 형태의 형틀을 도시한 입체도이며,Figure 1 (b) is a three-dimensional view showing a mold in the form of a cube made of the material used in 1 (a),
도 1(c)는 형틀 상자 내부에 공간 분할 요소(space divider)를 넣어서 여러개의 방으로 나눈 것을 나타내는 입체도이며,Figure 1 (c) is a three-dimensional view showing a space divider (space divider) inside the form box divided into several rooms,
도 1(d)는 점토류나 점토류-활성탄 복합 재료를 튜브 형태로 성형하고 망상 구조의 뚜껑을 덮어 씌운 형태의 형틀을 도시한 입체도이며,Figure 1 (d) is a three-dimensional view showing the mold in the form of a clay or clay-activated carbon composite material in the form of a tube and covered with a lid of the network structure,
도 2(a)는 활성탄이나 점토류 또는 그 혼합물을 접착제를 이용하여 성형하고 소성시켜 제조한 입자상의 미생물 담체를 나타내는 단면도이며,Figure 2 (a) is a cross-sectional view showing a particulate microbial carrier prepared by molding and firing activated carbon, clay or a mixture thereof using an adhesive,
도 2(b)는 활성탄이나 점토류 또는 그 혼합물을 발포 플라스틱에 피복하여 비중을 조절하는 입자상 미생물 담체를 나타내는 단면도이며,Figure 2 (b) is a cross-sectional view showing a particulate microbial carrier for controlling specific gravity by coating activated carbon, clay or a mixture thereof on the foamed plastic,
도 2(c)는 발포 플라스틱 입자를 나타내는 단면도이며,2 (c) is a cross-sectional view showing the foamed plastic particles,
도 3은 도 1(a)의 망상 구조로된 형틀 상자에 도 2(a)내지 2(c)의 담체/입자들을 충진한 최종 담체 유니트를 나타내는 입체도이다.FIG. 3 is a stereoscopic view showing a final carrier unit in which the carrier / particles of FIGS. 2 (a) to 2 (c) are filled in the frame box of the network structure of FIG. 1 (a).
*도면의 간단한 부호에 대한 설명** Description of the simple signs in the drawings *
A... 미생물 담체를 충진시킬 형틀 상자A ... mold box for filling microbial carriers
B... 뚜껑 C... 공간 분할 요소(space divider)B ... Lid C ... Space divider
본 발명에 의하면,According to the invention,
오/폐수가 내부로 관통하도록 망상 구조로된 형틀 상자 내부에Inside the frame box with mesh structure to allow the waste water to pass through
비중을 조절한 미생물 담체를 고정상용으로는 5∼70체적%를, 그리고 유동상용으로는 30∼90체적%를 충진시킨 뒤 망상 구조로된 뚜껑을 덮고,After filling the microorganism carrier with the specific gravity adjusted to 5 to 70% by volume for the fixed bed and 30 to 90% by volume for the fluidized bed, cover the lid of the network structure,
이와 같이 제조된 고정상용 담체 유니트를 혐기조 내지는 폭기조에 50∼100체적%로 설치하거나 혹은 상기 유동상용 담체 유니트를 폭기조에 30∼70체적%로 설치한 미생물 담체 유니트가 제공된다.Provided is a microbial carrier unit provided with a fixed bed carrier unit prepared in this way in an anaerobic or aeration tank at 50 to 100% by volume, or in a fluid tank at 30 to 70% by volume.
이하, 본 발명에 대하여 도면을 참조하여 상세히 설명한다.Hereinafter, the present invention will be described in detail with reference to the drawings.
본 발명의 망상 구조로된 형틀은 활성 담체를 담을 형틀 상자(A)과 뚜껑(B)으로 이루어진다.The mold having a network structure of the present invention comprises a mold box (A) and a lid (B) to contain an active carrier.
이때 형틀은 단단한 재질의 철, 스테인레스, 플라스틱 등을 가공하여 상단이 개방된 원통형 또는 다각형 튜브 형태(도 1(a) 및 1(b)참조), 혹은 활성 성분이나 기타 단단한 것을 튜브 형태로 성형하여 형틀 상자를 제조한 다음 그 상단에 망을 씌우고 망상 구조로된 뚜껑을 씌운 형태(도 1(d)참조)로 만든다.At this time, the mold is formed by processing a hard material such as iron, stainless steel, plastic, or a cylindrical or polygonal tube shape with an open top (see FIGS. 1 (a) and 1 (b)), or by forming an active ingredient or other hard material into a tube shape. After the form box is manufactured, it is made into a meshed top and a capped form (see Fig. 1 (d)).
그런 다음, 상기 형틀에 비중이 조절된 미생물 담체를 일부 충진한다.Then, the mold is partially filled with a microbial carrier having a specific gravity.
형틀 상자안에 충진할 미생물 담체로는 부력체에 (ⅰ)부력체 표면에 적절한 접착제를 사용하여 점토류 또는 점토류-활성탄 복합물(이하, '활성 성분'이라 한다)을 피복함으로써 그 비중을 물보다 가볍게 한 담체(이하, '활성피복담체'라 한다) 및/또는 (ⅱ) 상기 활성 성분을 입자 형태로 성형한 담체(이하, '활성 담체'라 한다)가 혼합 사용가능하다.As the microbial carrier to be filled in the mold box, the specific gravity is higher than that of water by coating a clay or clay-activated carbon composite material (hereinafter referred to as 'active ingredient') with a buoyant body using an appropriate adhesive on the surface of the buoyant body. Lightened carriers (hereinafter referred to as 'active coating carriers') and / or (ii) carriers in which the active ingredient is molded in the form of particles (hereinafter referred to as 'active carriers') can be mixedly used.
여기서 부력체로는 발포 플라스틱, 스티로폼, 비중이 물보다 낮은 목재 및 속이 빈 플라스틱 볼등을 사용할 수 있다.The buoyant body may be foamed plastic, styrofoam, wood with a specific gravity lower than water, and hollow plastic balls.
상기 활성 피복 담체는 비중이 물보다 낮은 2∼10mm 크기의 부력체에 활성 성분과 접착제 및 임의의 기공 조절제로된 수용액 또는 유기 용액 슬러리를 분무 피복한 뒤 300℃이하에서 소성하여 비중이 1보다 적은 피복 활성 담체 형태를 제조한다(도 2(b) 참조).The active coating carrier is sprayed with an aqueous solution or an organic solution slurry of the active ingredient, an adhesive and an optional pore control agent on a buoyant body having a specific gravity of 2 to 10 mm lower than that of water, and then fired at 300 ° C. or less to have a specific gravity less than 1. Prepare a coating active carrier form (see Figure 2 (b)).
300℃이상에서 소성하게 되면, 고온소성시 부력체 일부가 분해될 수 있으므로 바람직하지 않다.When firing at 300 ° C. or higher, a part of the buoyancy body may be decomposed at high temperature firing, which is not preferable.
상기 활성 피복 담체의 직경은 2∼20mm, 보다 바람직하게는 3∼10mm인 것이 좋다. 상기 범위를 벗어나게 되면 사용하는 양에 비해서 얻어지는 비표면적이 적절치 않아 바람직하지 않다.The active coating carrier has a diameter of 2 to 20 mm, more preferably 3 to 10 mm. If it is out of the above range, the specific surface area obtained is not suitable compared to the amount used, which is not preferable.
또한 이와 같은 직경의 활성 담체와 유니트의 크기비는 1:4∼1:40, 보다 바람직하게는 1:10∼1:25의 범위인 것이 바람직한 바, 상기 범위내에서 제조하는 활성 피복 담체의 직경을 조절하는 것이 좋다. 상기 범위를 벗어나게 되면, 비경제적일 뿐만 아니라 제조시 유니트 제조 및 그후에 적용처에서 설치시 개선된 반응 효율을 얻을 수 없다.In addition, it is preferable that the size ratio of the active carrier and the unit having such a diameter is in the range of 1: 4 to 1:40, more preferably in the range of 1:10 to 1:25. It is good to adjust. Beyond this range, not only is it uneconomical, but improved reaction efficiency cannot be obtained when manufacturing the unit during manufacture and subsequent installation in the application.
이때 사용되는 활성 성분은 제올라이트, 점토류(옹기토, 차지토, 고령토, 규조토, 질석, 활석, 황토등), 제철소 폐슬래그, 화산재, 연소재 등을 단독 혹은 2이상 혼합하여 사용하거나 여기에 활성탄을 추가로 첨가하여 사용할 수 있다. 이때 활성탄이 사용될 경우 그 첨가량은 10∼30중량%가 바람직하다.At this time, the active ingredients used are zeolite, clays (ongyo clay, clay clay, kaolin, diatomaceous earth, vermiculite, talc, loess, etc.), steel mill waste slag, volcanic ash, combustion materials, etc. alone or in combination of two or more activated carbon It can be added and used further. At this time, when activated carbon is used, the addition amount is preferably 10 to 30% by weight.
접착제로는 유기 또는 무기 접착제를 사용할 수 있는데, 이중 유기 접착제로는 폴리비닐알코올, 폴리우레탄, 에폭시, 아크릴 수지 등을 그리고 무기 접착제로는 알루미나졸, 실리카졸, 물유리, 시멘트 등을 사용할 수 있다.As the adhesive, an organic or inorganic adhesive may be used, among which an organic adhesive may be polyvinyl alcohol, polyurethane, epoxy, acrylic resin, and the like, and an inorganic adhesive may be alumina sol, silica sol, water glass, cement, or the like.
상기 활성 성분들은 유기 혹은 무기 접착제와 60∼90:40∼10의 중량비로 혼합하는 것이 바람직하다. 접착제 첨가량이 10% 미만이 되면 물에서 일부 재료들이 풀어지게 되며, 40%를 초과하게 되면 결과 담체의 흡착력이나 미생물 부착 능력에 악영향을 미치게 되어 적절하지 않다.The active ingredients are preferably mixed with an organic or inorganic adhesive in a weight ratio of 60 to 90:40 to 10. If the amount of adhesive added is less than 10%, some materials will be released from the water, and if it exceeds 40%, it will not be suitable because it adversely affects the adsorption capacity of the carrier or the ability of microbial adhesion.
이와 같이 제조된 혼합물에 임의로 기공 조절제를 혼합하는 것이 바람직하다. 사용가능한 기공조절제는 암모늄 카보네이트, 암모늄 나이트레이트 등의 무기 염료 혹은 에틸렌 글리콜, 셀룰로오스, 녹말 등의 유기 고분자 물질이며, 이들을 활성 성분과 접착제의 전체 중량을 기준으로 10중량%이하로 사용하는 것이 바람직하다. 상기 범위를 벗어나게 되면, 강도면에 있어 불량하게 되고 또한 경제적인 면에서도 부적절하다.It is preferable to optionally mix the pore regulator with the mixture thus prepared. The pore control agents that can be used are inorganic dyes such as ammonium carbonate and ammonium nitrate or organic high molecular materials such as ethylene glycol, cellulose and starch, and it is preferable to use them in an amount of 10% by weight or less based on the total weight of the active ingredient and the adhesive. . If it is out of the above range, it is poor in terms of strength and inadequate in terms of economy.
이와 같이 제조된 활성 피복 담체의 피복 두께는 원하는 비중에 따라 조절되게 되는 것으로, 사용할 혐기조 내지는 폭기조의 수위에 따라 달라지지만 일반적으로 5mm이하이면 충분하다.The coating thickness of the active coating carrier prepared as described above is to be adjusted according to the desired specific gravity, and depends on the level of the anaerobic tank or aeration tank to be used, but generally 5 mm or less is sufficient.
이뿐만 아니라 미생물 담체로서 상기 활성 피복 담체대신 활성 담체를 부력체와 혼합하여 사용할 수 있는데, 이는 상기 활성 성분을 입자 형태로 성형하고 500℃이하에서 저온 소성시켜 지름이 2∼20mm인 구형 또는 기타 형태의 입자로 제조된다(도 2(a) 참조).In addition to this, an active carrier may be used as a microbial carrier, instead of the active coating carrier, mixed with a buoyant body, which may be molded into particles and baked at 500 ° C. or lower at low temperature to form a spherical or other shape having a diameter of 2 to 20 mm. It is made of particles of (see Fig. 2 (a)).
제조된 활성 담체의 직경은 상기 활성 피복 담체와 마찬가지로 2∼20mm, 보다 바람직하게는 3∼10mm인 것이 좋다.The diameter of the prepared active carrier is preferably 2 to 20 mm, more preferably 3 to 10 mm, similarly to the active coating carrier.
또한 소성 온도가 500℃이상이 되면 접착력을 상실하게 되므로 바람직하지 않다.In addition, when the firing temperature is 500 ° C or higher, the adhesive force is lost, which is not preferable.
이와 같이 제조된 미생물 담체를 도 3에서 보듯이, 고정상용으로는 5∼70체적%를, 그리고 유동상용으로는 30∼90체적%를 충진시킨 뒤 망상 구조로된 뚜껑을 덮어 담체 유니트를 완성한다.As shown in FIG. 3, the microbial carrier thus prepared is filled with 5 to 70% by volume for the fixed bed and 30 to 90% by volume for the fluidized bed, and then the lid is made of a network structure to complete the carrier unit. .
고정상용으로는 제조된 미생물 담체를 담체 유니트 체적의 5∼70%, 보다 바람직하게는 10∼40%로 충진하는 것이 바람직하다. 상기 범위를 벗어나게 되면 확산, 비중 및 성능면에서 바람직하지 않다.For the stationary phase, it is preferable to fill the prepared microbial carrier with 5 to 70%, more preferably 10 to 40% of the volume of the carrier unit. Deviation from the above range is undesirable in terms of diffusion, specific gravity and performance.
또한 유동상용으로는 제조된 미생물 담체를 담체 유니트 체적의 30∼90%, 보다 바람직하게는 50∼70%로 충진하는 것이 바람직하다. 상기 범위를 벗어나게 되면 효율 및 성능면에 있어 바람직하지 않다.In addition, for the fluidized bed, it is preferable to fill the prepared microbial carrier with 30 to 90%, more preferably 50 to 70% of the volume of the carrier unit. Outside the above range is not preferable in terms of efficiency and performance.
이와 같이 제조된 담체 유니트를 설치용 보조 시설없이 사용하고자 하는 혐기조 혹은 폭기조에 적정 체적 범위내로 설치하여 오/폐수 처리 공정에 사용한다.The carrier unit thus manufactured is installed in an anaerobic tank or aeration tank to be used without an auxiliary facility for installation within an appropriate volume range and used for a wastewater treatment process.
구체적으로는 고정상용 담체 유니트를 혐기조 내지는 폭기조에 오/폐수가 잠기는 부분의 액체 체적의 50∼100체적%를 투여하게 되는데, 상기 범위를 벗어나면 효율 및 성능면에 있어 바람직하지 않다.Specifically, the fixed phase carrier unit is administered in an anaerobic or aeration tank with 50 to 100% by volume of the liquid volume of the part where the waste water is immersed. Outside of the above range, it is not preferable in terms of efficiency and performance.
또한 상기 유동상용 담체 유니트를 폭기조에 사용시에는 폭기조의 체적을 기준으로 30∼70체적%로 투여한다. 폭기조의 경우에는 발포(bubbling)로 인한 흐름(flow)이 강하므로 유동상용 담체 유니트를 사용하는 경우에는 고정상용 담체 유니트를 사용하는 경우에 비하여 보다 작은 양을 투여할 수 있다.In addition, when the fluidized bed carrier unit is used in the aeration tank, it is administered at 30 to 70% by volume based on the volume of the aeration tank. In the case of the aeration tank, the flow due to bubbling is strong, and thus, when using the fluidized bed carrier unit, a smaller amount may be administered than when the fixed bed carrier unit is used.
또한 형틀 내부에 공간 분할 요소를 부가하여 각 방의 크기가 30∼1000cm3가 되도록 여러개의 방으로 나눈 뒤 여기에 담체를 조금씩 나누어 충진시킴으로써 반응조내에 고루 퍼지게 할 수 있다(도 1(c) 참조).In addition, by adding a space dividing element inside the mold, each room is divided into several rooms such that the size of the room is 30 to 1000 cm 3 , and the carrier is divided into small portions and filled so as to spread evenly in the reaction tank (see FIG. 1 (c)).
실시예Example
이하, 실시예를 본 발명에 대하여 보다 상세히 설명한다.Hereinafter, the present invention will be described in more detail with respect to the present invention.
<실시예 1><Example 1>
크기가 5cm×5cm×5cm인 사각 플라스틱 유니트에 제올라이트 60중량%, 활성탄 20중량% 및 폴리우레탄 수지 20중량%를 혼합하여 150℃에서 소성시킨 충진용 활성담체(φ5mm×ℓ5mm)와 폴리스티렌에 동일한 조성으로 코팅한 활성 피복 담체를 3:1 체적비, 유니트 체적을 기준으로 50체적% 정도가 되도록 충진시킨 후 5ℓ 폭기조에 담체 유니트를 70체적%로 투입하여 COD 제거 효율 및 NH4 +-N의 제거 효율을 측정하였다.The same composition is used for the active carrier for filling (φ5mm × ℓ5mm) and polystyrene, which are fired at 150 ° C by mixing 60 wt% zeolite, 20 wt% activated carbon and 20 wt% polyurethane resin in a square plastic unit having a size of 5 cm × 5 cm × 5 cm. Filled coated carrier to 3: 1 volume ratio, 50 volume% based on unit volume, and then 70% by volume of carrier unit in 5 liter aeration tank to remove COD and NH 4 + -N. Was measured.
상기 폭기조에 폐수(Cin200ppm)을 유입하고 처리한 결과, COD 제거효율은 98%였으며, 폐수(Cin=30ppm)에 대한 NH4 +-N 제거 효율은 93%이었다.Wastewater (C in 200ppm) was introduced into the aeration tank and treated, and the COD removal efficiency was 98%, and the NH 4 + -N removal efficiency was 93% for the wastewater (C in = 30ppm).
<실시예 2><Example 2>
암모늄 나이트레이트 10중량%를 첨가한 것을 제외하고는 실시예 1과 동일한 조건으로 활성 담체를 제조하였다. 실시예 1과 동일한 조건에서 실험한 결과 COD 제거효율은 98%이고 NH4 +-N 제거 효율은 95%였다.An active carrier was prepared under the same conditions as in Example 1 except that 10% by weight of ammonium nitrate was added. Experiments under the same conditions as in Example 1 showed that the COD removal efficiency was 98% and the NH 4 + -N removal efficiency was 95%.
<실시예 3><Example 3>
5cm×5cm×5cm 크기의 사각 SUS 유니트를 사용하고, 활성 피복 담체를 저온 소성 담체보다 2배 가량 더 첨가한 것을 제외하고는 실시예 1에서와 동일한 방법으로 담체 유니트를 제조한 다음, 실시예 1에서와 동일한 실험을 거쳤다. COD 제거율은 97%였으며, NH4 +-N 제거 효율은 93%였다.A carrier unit was prepared in the same manner as in Example 1, except that a rectangular SUS unit having a size of 5 cm × 5 cm × 5 cm was used, and an active coating carrier was added about twice as much as the low temperature calcined carrier, and then Example 1 We went through the same experiment as in COD removal was 97% and NH 4 + -N removal efficiency was 93%.
<실시예 4><Example 4>
직경 2mm인 구형의 스티로폼(금호케미컬(주))에 실시예 3과 동일한 조성비로 코팅 두께 1.5mm가 되도록 4회 코팅하여 비중이 1-1.3인 담체 유니트를 제조하였다. 제조된 유니트를 2ℓ폭기조에서 실시예 3과 동일한 조건하에 폐수 처리를 수행한 결과, COD 제거율은 96% 그리고 NH4 +-N 제거 효율은 87%였다.A carrier unit having a specific gravity of 1-1.3 was prepared by coating a styrofoam (Kumho Chemical Co., Ltd.) having a diameter of 2 mm four times so as to have a coating thickness of 1.5 mm at the same composition ratio as in Example 3. The waste water treatment was carried out in the 2 L aeration tank under the same conditions as in Example 3, and the COD removal rate was 96% and the NH 4 + -N removal efficiency was 87%.
<실시예 5>Example 5
실시예 2에서 제조한 담체 유니트를 5ℓ혐기조에 담체 유니트를 70% 체적으로 투여한 결과, 탈질 효율은 84%(Cin, NO3 -=30ppm)이었다.Example 2 was administered the carrier unit by 70% by volume of the carrier unit to the anaerobic tank 5ℓ prepared in result, the denitration efficiency of 84% (C in, NO 3 - = 30ppm) was.
<비교예 1>Comparative Example 1
종래에 고정용 담체로 사용되는 SARAN ROCK(일본, 구레하 화학 공업(주))을 폭기조와 혐기조에서 상기 실시예와 동일한 실험을 수행한 결과, COD 제거율은 91%였으며, NH4 +-N 제거 효율은 76%였고 탈질 효율(혐기조내)은 72%였다.As a result of performing the same experiment as in the above example with SARAN ROCK (Kureha Chemical Co., Ltd.), which is conventionally used as a fixing carrier in an aeration tank and an anaerobic tank, the COD removal rate was 91% and NH 4 + -N removal. The efficiency was 76% and the denitrification efficiency (in the anaerobic tank) was 72%.
본 발명의 제조 방법에 의해 제조된 미생물 담체 유니트의 잇점은 다음과 같다.Advantages of the microbial carrier unit produced by the production method of the present invention are as follows.
(1)본 발명의 방법에 의해 제조된 담체 유니트는 활성탄과 점토계 광물질 또는 그 혼합물로 이루어지므로 고분자로 만들어진 기타 유동상 담체에 비하여 미생물막의 두께가 얇고 탈리의 문제가 없으며 비표면적이 넓고 물리/화학적으로 안정하여 오염물질 제거 능력이 우수하며 반영구적이다.(1) Since the carrier unit produced by the method of the present invention is composed of activated carbon and clay mineral or mixture thereof, the thickness of the microbial membrane is thinner, there is no problem of detachment, the specific surface area is wide, and the physical / Chemically stable, excellent in removing pollutants and semi-permanent.
(2)또한 형틀에 충진할 활성 담체는 그 크기가 작아 외표면적이 많아지고 비중을 원하는 값으로 조절할 수 있으므로, 특히 유동상 담체 유니트를 제작하는데 유리하다. 따라서 폭기조내에서 담체 유니트가 비중이 너무 낮아 수면으로 뜨기만 하거나 비중이 너무 높아 바닥으로 몰리는 일없이 내부 순환이 원활하게 이루어지면서도 담체 유니트 내부가 완전히 충진되지 않아서 담체의 유니트내 동작뿐만 아니라 액체의 유니트 내부로의 흐름이 활발하여 담체와 오/폐수간의 섞임이 활발하게 되어 처리 효율이 높아진다.(2) In addition, the active carrier to be filled in the mold has a small size, so that the outer surface area and the specific gravity can be adjusted to a desired value, which is particularly advantageous for producing a fluidized bed carrier unit. Therefore, the specific gravity of the carrier unit in the aeration tank is so low that it floats to the water surface or the gravity is too high so that the internal circulation is smooth and the inside of the carrier unit is not completely filled. As the flow into the unit is active, the mixing between the carrier and the waste water is increased, thereby increasing the treatment efficiency.
(3)혐기조에서는 투하시켜 쌓인 담체 유니트들 내부에 존재하는 빈 내부공간과 담체 유니트간의 외부 공간이 유체의 흐름을 원활하게 하기 위한 일정 크기의 채널을 형성시켜 발생 슬러지의 침적에 의한 유로 형성의 방해를 방지한다.(3) In the anaerobic tank, the empty inner space and the outer space between the carrier units formed by dropping the carrier units form a channel of a certain size to facilitate the flow of fluid, thereby preventing the formation of a flow path due to the deposition of sludge generated. To prevent.
(4)유니트내 담체 투입량 정도에 따라 내부 공간 채널의 크기를 조절할 수 있으며 또한 담체 유니트의 혐기조내 자유 투하로 인해 내외부 공간에서 생기는 채널이 곡선 형태로 형성되어 자연스럽게 유체의 난류 효과를 더해 준다.(4) The size of the inner space channel can be adjusted according to the amount of carrier in the unit, and the channel generated in the inner and outer space is formed in a curved form due to the free drop in the anaerobic tank of the carrier unit, which naturally adds the turbulence effect of the fluid.
(5)또한 혐기조내에서 담체가 차지하는 체적비를 보다 적게 유지시켜 액체의 반응기내 체류 시간을 크게 하면서도 담체를 혐기조 전체에 골고루 분산시킬 수 있는 장점이 있다.(5) In addition, there is an advantage that the carrier can be evenly dispersed throughout the anaerobic tank while maintaining the volume ratio occupied by the carrier in the anaerobic tank to increase the residence time of the liquid in the reactor.
상기한 바에 따르면, 손쉽게 담체 입자를 담을 수 있고 오/폐수가 내부로 관통하도록 제조한 형틀에 적절한 담체 유니트를 적당량 충진시킴으로써 활성 담체의 분산성을 개선시키고, 폐수의 흐름 채널을 형성가능하게 되어 슬러지 막힘 현상을 개선시킬 수 있다.According to the above, by filling an appropriate amount of a suitable carrier unit in the mold prepared to easily contain the carrier particles and penetrate the waste water / waste water therein, it is possible to improve the dispersibility of the active carrier and to form a flow channel of the waste water, thereby allowing sludge The clogging phenomenon can be improved.
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KR19990073454A (en) * | 1999-07-09 | 1999-10-05 | 성기달 | 5) For the treatment of waste water, functional carriers and combined purification tanks using them |
KR100336820B1 (en) * | 2000-01-13 | 2002-05-16 | 양금모 | A method for manufacturing fixed tubular type biocarrier and a fixed biocarrier for biological wastewater treatment and offensive odor gas removal manufactured using the method |
KR100351062B1 (en) * | 2001-04-17 | 2002-09-05 | 엄동식 | Microorganism contact materials case for disposing waste water |
KR100453233B1 (en) * | 2002-03-20 | 2004-10-15 | 한상배 | Novel Bio-Media with improved specific surface area, bio-affinity and water-fluidization |
-
1999
- 1999-05-20 KR KR1019990018220A patent/KR100282212B1/en not_active IP Right Cessation
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20010054140A (en) * | 1999-12-03 | 2001-07-02 | 박경주 | Supporting apparatus of media for contacting the biomembrane |
KR100512251B1 (en) * | 2003-03-04 | 2005-09-23 | 조현준 | Method for manufacture of Media plate for sewage detail disposal |
KR100948556B1 (en) * | 2009-11-04 | 2010-03-18 | 석성기업주식회사 | Manufacturing method for concrete blocks for water purification and manufactured concrete blocks using the method thereof |
CN108147554A (en) * | 2018-02-12 | 2018-06-12 | 苏州首创嘉净环保科技股份有限公司 | Integrated domestic sewage treatment device |
Also Published As
Publication number | Publication date |
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KR100282212B1 (en) | 2001-02-15 |
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