JP2007160295A - Three phase aerator and sewage purifying apparatus equipped therewith - Google Patents

Three phase aerator and sewage purifying apparatus equipped therewith Download PDF

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JP2007160295A
JP2007160295A JP2005381035A JP2005381035A JP2007160295A JP 2007160295 A JP2007160295 A JP 2007160295A JP 2005381035 A JP2005381035 A JP 2005381035A JP 2005381035 A JP2005381035 A JP 2005381035A JP 2007160295 A JP2007160295 A JP 2007160295A
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tank
sewage
aeration
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Konichi Komatsu
艮一 小松
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Physical Water Treatments (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Sludge (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Biological Treatment Of Waste Water (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a sewage purifying apparatus of preventing drug-induced sufferings caused by a detergent, pesticide passing through the inside of the body, chemical fertilizer or food additive, particularly a coagulant or chlorine sterilizer used for improving an effect of purification in conventional purification tanks, and reducing air pollution due to the consumption of oxygen and an increase in carbon dioxide by use of a fossil fuel, and the like, in addition to purifying sewage, a cause of environmental pollution in the river water. <P>SOLUTION: Provided is a sewage purifying apparatus in which a purification tank is an underground installation, but has a structure unharmful for the maintenance of a life environment and for health and hygiene. The purification tanks are improved depending on their usage. Conventional sewage aerators for the apparatus are replaced with three phase aerators. The purification tanks for multiple applications are divided into general and specific facilities. The treatment procedure is classified into the redox and reduction techniques. The effluent is not treated with a chlorine sterilizer, but by magnetic sterilization. The effluent is made to be regenerated water to be capable of reuse for pond water in which fish can live, or for cleaning of water closets, or watering for plants, thereby making fresh oxygen directly through plants. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は浄化槽により、直接的、又、間接的に発生する大気汚染、河川水域の環境汚染防止に係るものであり、特に生活環境の保全と健康衛生上支障のない浄化槽として、化石燃料による酸素の消耗防止と二酸化炭素の増加防止問題を解決し、水域の汚水を還元水として魚の住める水に再生し、又、植物の灌水や水洗トイレの洗滌水として再利用を可能にする汚水浄化装置に係るものである。  The present invention relates to the prevention of air pollution and environmental pollution of river water areas directly or indirectly generated by a septic tank, and in particular, as a septic tank that does not hinder the maintenance of the living environment and health and hygiene, A wastewater purification device that solves the problem of preventing exhaustion of carbon dioxide and preventing the increase in carbon dioxide, reclaims sewage in the water area as water that can be used as fish, and can be reused as water for plant irrigation and flushing in flush toilets. It is concerned.

従来の建築基準法に基づく、その構造基準による技術に準じた現場造り製の鉄筋コンクリ−ト製浄化槽は、現状に於いて、工場生産物で商品化されたFRP製浄化槽と比較して価格の安さ工事の速さ等で、商業上対抗できず、その工事業者は廃業が目立ち壊滅状態にある。全国の市場をFRP製浄化槽が独占している現状であるが、然し乍ら、FRP製浄化槽は化学製品である上に、更に、装置も構造も本発明とは全く異なるものであるから、現場造り製の鉄筋コンクリ−ト製浄化槽業者の再生復興が望まれる実状である。  Reinforced concrete septic tanks built on-site in accordance with the technology based on the structural standards based on the existing Building Standards Law are currently priced lower than FRP septic tanks commercialized as factory products. Due to the speed of cheap construction, etc., it is impossible to compete commercially, and the contractor is noticeably out of business. Although the FRP septic tank is monopolized in the national market, however, the FRP septic tank is a chemical product, and the equipment and structure are completely different from the present invention. Rehabilitation and reconstruction of a steel septic tank supplier is desired.

従来、工場生産のFRP製浄化槽の製造工程で発生する環境汚染として、シンナ−製の凝固剤を使用していることの弊害に加え、材料の研磨、切断の際に発生するプラスチック等の粉塵公害、及び、残骸物の償却の際に有害なダイオキシンを放出して大気を汚染している。又、浄化力に於いても、洗剤を含んだ汚水や体内から排出される農薬や食品添加物の除去の対策がなく、放流BOD低下のために多量の凝集剤や塩素滅菌剤を使用しておりそのために河川水域の生態は狂い、魚介類や藻類は死滅状態にある。これらを解決しなければならない課題がある。  Conventionally, as environmental pollution that occurs in the manufacturing process of factory-produced FRP septic tanks, in addition to the harmful effects of using thinner coagulant, dust pollution such as plastics generated during polishing and cutting of materials In addition, harmful deoxins are released during the depreciation of debris and pollute the atmosphere. Also, in terms of purifying power, there is no measure for removing sewage containing detergent, agricultural chemicals and food additives discharged from the body, and a large amount of flocculant and chlorine sterilant are used to reduce released BOD. For this reason, the ecology of river water is crazy, and seafood and algae are dead. There are issues that must be resolved.

従来のFRP製浄化槽に於いては、生物膜方式の接触曝気型が主流であり、化学製品のハニカム等の多様な接触材を用い、生物膜である糸状菌を付着させる手段にあるが、化学製品には生物膜は付着した例はなく、又、従来の曝気装置は流動性微生物によって分解浄化する活性汚泥方式に用いるもので、これを生物膜方式の接触材に使用しても、これが旋回流を妨げ嫌気性となり、悪臭が発生し、又、酸素の消耗により生活環境の保全に支障をきたすもので問題である。  In conventional FRP septic tanks, the biofilm contact aeration type is the mainstream, and there are various contact materials such as honeycombs of chemical products, and it is a means to attach filamentous fungi that are biofilms. There are no examples of biofilm adhering to products, and the conventional aeration apparatus is used for activated sludge system that decomposes and purifies with fluid microorganisms. This is a problem because it obstructs the flow, becomes anaerobic, generates a foul odor, and impairs the maintenance of the living environment due to the consumption of oxygen.

従来のFRP性浄化槽の販売施工に於いて、生物膜方式分離接触型として、同機種をもって一般施設やレストラン、ホテル、食品工場と所かまわず販売施工しているが、これを一般施設用と特定施設用に分別し、清掃時の汚泥の搬出や汚泥量の減量を計らなければならない課題がある。  In the conventional FRP-type septic tank sales and construction, as a biofilm separation contact type, the same model is sold and constructed regardless of whether it is a general facility, restaurant, hotel, or food factory. There is a problem that it must be sorted for facilities, and sludge carried out during cleaning and the amount of sludge reduced.

問題を解決するための手段Means to solve the problem

課題[03、04]でFRP製浄化槽の弊害として掲げた、大気汚染についてはコンクリ−ト製浄化槽にすることにより解決できるとし、既設のFRP製浄化槽の生態の不良や凝集剤や塩素滅菌剤により起こる河川水域の魚介類や藻類への被害は、請求項3の散水▲ろ▼床型浄化槽を装備した三次処理浄化装置、及び、磁力滅菌装置により解決するものである  Air pollution, which was listed as an adverse effect of FRP septic tanks in Problem [03, 04], can be solved by using concrete septic tanks. Due to poor ecology of existing FRP septic tanks, flocculants and chlorine sterilants The damage to the seafood and algae in the river water area that occurs is solved by the tertiary treatment purification device equipped with the watering septic tank of claim 3 and the magnetic sterilization device.

課題[04]について、従来の生物膜方式のFRP製浄化槽に於ける曝気装置や化学製品のハニカム等の接触材、及び、生物膜の生物処理等の欠点は、三相曝気装置によって解決し、併せて、汚水を嫌気性から好気性に変え、酸性を中性にして汚濁物をミネラル化にし、微細菌から後生動物に到る植物連鎖を生じさせ汚水を処理する。  Regarding the problem [04], the disadvantages such as the aeration apparatus in the conventional biofilm type FRP septic tank, the contact material such as the honeycomb of the chemical product, and the biological treatment of the biofilm are solved by the three-phase aeration apparatus, At the same time, the sewage is treated by changing the sewage from anaerobic to aerobic, neutralizing the acidity to mineralize the pollutant, producing a plant chain from microbacteria to metazoans.

課題[05]について、生物膜方式の接触曝気型の使用途別に方式型式を1日の流入BOD濃度200PPM以下、1日流入汚水量40リッポ−メ−トル以下のものを請求項4の酸化還元方式の汚水浄化装置としこれを一般施設用とする。又、1日流入BOD濃度200PPM以上、1日流入汚水量40リッポ−メ−トル以上のものを請求項5の還元方式汚水浄化装置としこれを特定施設用浄化装置とする。  Regarding subject [05], the oxidation type reduction according to claim 4 having a daily inflow BOD concentration of 200 PPM or less and a daily inflow sewage amount of 40 Lippo meter or less depending on the use of the biofilm contact aeration type This system will be used for general facilities. Further, the daily inflow BOD concentration of 200 PPM or more and the daily inflow sewage amount of 40 Lippo meter or more are defined as the reduction-type sewage purification apparatus according to claim 5, and this is the purification apparatus for specific facilities.

発明の効果The invention's effect

請求項1、2について、従来の活性汚泥方式や生物膜方式で浄化槽内に酸素を溶解させ好気性微生物によって汚水を浄化する曝気装置とは異なり、本願では、床材に空気と汚水を激突接触させ、床材のもつ遠赤外線の効果を高め、そして、それにより新しい酸素を造り、汚水を還元水とすることで汚水の浄化力を高める効果を奏する。  About Claims 1 and 2, unlike an aeration apparatus that dissolves oxygen in a septic tank and purifies sewage by aerobic microorganisms using a conventional activated sludge method or a biofilm method, in this application, the floor material collides with air and sewage. This increases the far-infrared effect of the flooring material, thereby creating new oxygen and increasing the purification capacity of sewage by using sewage as reducing water.

請求項3の三次処理では、従来の既設浄化槽の浄化不良や凝集剤、塩素滅菌剤が起している公害を起さない効果を奏する。  In the tertiary treatment of claim 3, there is an effect of not causing the poor purification of the existing septic tank and the pollution caused by the flocculant and the chlorine sterilant.

請求項4については、嫌気性酸化槽に於いて、汚水中の汚濁物や体内から排出される農薬や食品添加物を沈殿させ、嫌気性細菌によって酸化させ、同時に、曝気還元槽に於いて請求項2の三相曝気装置をもって汚水を還元汚水として、微生物間の植物連鎖を利用し、汚泥の減量を計り、更に、請求項3の三次処理をもって魚の住める水として河川に放流し又、水の再利用も可能とする効果を奏する。  Regarding claim 4, in the anaerobic oxidation tank, pollutants in the sewage and agricultural chemicals and food additives discharged from the body are precipitated, oxidized by anaerobic bacteria, and simultaneously charged in the aeration reduction tank. Using the three-phase aeration device according to Item 2, wastewater is reduced to wastewater, using a plant chain between microorganisms to reduce sludge, and further to the river as water where fish can live by the tertiary treatment according to Claim 3, There is an effect that can be reused.

請求項5については、汚水中の固形物を自動掻上機をもって汚泥貯留槽に除去し、曝気還元槽に於いては、請求項1、2の三相曝気装置の効果によって汚水を還元汚水とし、微生物間の植物連鎖による汚泥の減量を計り、沈殿槽に沈殿した汚泥を汚泥貯留槽に返送して汚泥の搬出を容易にし、更に、請求項3の三次処理をもって魚の住める還元水として放流する効果を得、又、その一部を再利用可能とする効果を奏する。  Regarding claim 5, solid matter in sewage is removed to a sludge storage tank with an automatic rake, and in the aeration reduction tank, the sewage is reduced to sewage by the effect of the three-phase aeration apparatus of claims 1 and 2. Measure the amount of sludge reduced by the plant chain between microorganisms, return the sludge settled in the sedimentation tank to the sludge storage tank to facilitate the removal of the sludge, and discharge it as reduced water where fish can live with the tertiary treatment of claim 3 The effect is obtained, and a part of the effect can be reused.

請求項1の三相曝気装置1について、図1で示すように丸型容器2の下部に、通気通水口7を形成した床材受6で底版を構成し、容器2内に硅藻土と黒ボク土、及び、火山灰を加えて焼成し、所定の寸法に割石した(特許第3040097号)を床材9として充填しその上部で網目蓋8を固着して床材9の流出を防止し、ブロワ−11より散気管5を通じて空気を散気装置4に送り、散気口5より矢印のように散気し、通気通水口7から通気して床材9に空気と汚水を激突接触させながら床材間を上昇させ、その間、汚水と空気は床材のもつ遠赤外線の作用により、その効果を得て新鮮な酸素を造り出し、酸性の汚水は中性にし溶存酸素を増大させて還元汚水にして、曝気還元槽内の好気性の流動微生物の活動を活発にし汚水の分解浄化を行なう。  In the three-phase aeration apparatus 1 according to claim 1, as shown in FIG. 1, a bottom plate is constituted by a floor material receptacle 6 in which a vent hole 7 is formed in a lower part of a round container 2, and diatomaceous earth is contained in the container 2. Black clay and volcanic ash are added and baked and crushed to a predetermined size (Patent No. 3040097) is filled as a flooring 9, and a mesh lid 8 is fixed on the top to prevent the flooring 9 from flowing out. Then, air is sent from the blower 11 to the air diffuser 4 through the air diffuser 5, diffused as indicated by an arrow from the air diffuser 5, and vented from the air vent 7, causing air and sewage to collide with the flooring 9. While raising the space between flooring materials, the wastewater and air produce the effect of the far infrared rays of the flooring material to produce fresh oxygen, the acidic wastewater becomes neutral and the dissolved oxygen is increased to reduce wastewater. In this way, the activity of aerobic fluid microorganisms in the aeration reduction tank is activated, and the sewage is decomposed and purified. Cormorant.

請求項2の備付三槽曝気装置21について、図2で示すように曝気還元槽内に単独、又は、槽の周壁を利用し備付るもので、角型容器22の下部に、通気通水口を形成する角型用床材受27を構成し、その上の角型容器22内に硅藻土と黒ボク土に火山礫、又は、ゼオライトを加え凝固剤で固め所定の割石とした角型用床材29を充填し、角型用床材受27の下方で、ブロワ−11よりの圧縮空気を散気する散気管23を配し、散気口24より圧縮空気を散気させ、圧縮空気と汚水を床材に激突接触させ床材間を上昇させながら、その間で、圧縮空気と水を床材のもつ遠赤外線の作用により、新鮮な酸素が造られ汚水を還元水とする。  About the equipped three tank aeration apparatus 21 of Claim 2, as shown in FIG. 2, it installs in the aeration reduction tank independently or using the peripheral wall of a tank, and a ventilation water inlet is provided in the lower part of the square container 22. The square floor material receiver 27 to be formed is configured, and in the square container 22 thereabove, volcanic gravel or zeolite is added to diatomaceous earth and black urine, and solidified with a coagulant to form a predetermined crushed stone. A floor tube 29 is filled, and an air diffuser pipe 23 that diffuses compressed air from the blower 11 is disposed below the square floor material receiver 27, and the compressed air is diffused from the air diffuser port 24. The sewage and the sewage collide with the flooring material to raise the space between the flooring materials, and in the meantime, fresh oxygen is produced by the action of the far infrared rays with the compressed air and the water of the flooring material, and the sewage is used as reduced water.

請求項3の三次処理装置について、図3、図4で示すように散水▲ろ▼床槽本体31と放流ポンプ槽39を組合せて構成し、散水▲ろ▼床槽本体31に流入する汚水は、配水枡32によって、▲ろ▼材受33の上の内部に硅藻土と黒ボク土、及び、火山灰礫、又は、ゼオライトを凝固剤で固めて割石とした床材36を充填した▲ろ▼床35の上から、上部に配列した散水管37の散水口43により滴下散水し、▲ろ▼床35よって▲ろ▼過する工程で床材36のもつ遠赤外線の作用により還元水として貯留槽38に貯留させる。  As for the tertiary treatment apparatus of claim 3, as shown in FIG. 3 and FIG. 4, it is configured by combining the sprinkling floor body 31 and the discharge pump tank 39, and the sewage flowing into the sprinkling floor body 31 is The distribution pad 32 is filled with a flooring 36 made of diatomaceous earth and black-boiled earth, and volcanic ash gravel or zeolite solidified with a coagulant inside the material tray 33. ▼ Dropping water is sprinkled from the top of the floor 35 through the sprinkling ports 43 of the sprinkling pipes 37 arranged in the upper part, and is stored as reduced water by the action of far infrared rays of the flooring 36 in the process of passing through the floor 35. It is stored in the tank 38.

貯留した還元水は、貯留槽38と連なるポンプ槽39に設置した循環ポンプ47とその配水管46に設けた散水ノズルによって、▲ろ▼床の上から霧状に散水して循環させる。  The stored reduced water is circulated in a mist form from above the floor by a circulation pump 47 installed in a pump tank 39 connected to the storage tank 38 and a water spray nozzle provided in the water distribution pipe 46.

散水▲ろ▼床槽31の床版に設置した散気管45でブロワ−11よりの圧縮空気を▲ろ▼床35内に送り、嫌気性を防止し、好気性生物の活動を活発にして還元水の再浄化をする仕組みである。  Sprinkling ▲ The compressed air from the blower-11 is sent to the floor 35 by the diffusing pipe 45 installed on the floor slab of the floor tank 31 to prevent anaerobic activity and reduce the activity of aerobic organisms. It is a mechanism for repurifying water.

放流ポンプ槽39に設置した二相放流ポンプと磁力滅菌装置を用い、放流水を高度に処理した還元水として、再利用、及び、魚の住める水として河川へ放流する仕組みである。  Using a two-phase discharge pump and a magnetic sterilization device installed in the discharge pump tank 39, the discharged water is reused as a highly treated reduced water and discharged into the river as water where fish can live.

請求項4の施設用酸化還元方式浄化装置について、図5、図6で示すように、流入する汚水は第一嫌気酸化槽51に設置した導入管58により、対角線上に設けたバッフル59間を上昇し、第二嫌気酸化槽53に流入し、予備▲ろ▼過槽52で請求項2の床材36によって▲ろ▼過され、この過程で汚水中の洗剤や食品添加物は汚濁物と共に沈殿して嫌気酸化され汚泥は減量されて除去する仕組みである。  About the oxidation reduction type | system | group purification apparatus for facilities of Claim 4, as shown in FIG. 5, FIG. 6, the inflow sewage is between the baffles 59 provided on the diagonal by the introduction pipe | tube 58 installed in the 1st anaerobic oxidation tank 51. Ascending and flowing into the second anaerobic oxidation tank 53 and passing through the preliminary filtration tank 52 by the flooring 36 of claim 2, in this process the detergent and food additives in the sewage together with the contaminants It is settled, anaerobically oxidized, and the sludge is reduced and removed.

予備▲ろ▼過槽52で▲ろ▼過された嫌気性汚水は第一曝気還元槽54、第二曝気還元槽55に装備した請求項2の三相曝気還元装置の作用により、好気性汚水、還元汚水となって新しい酸素を造り、還元汚水中の嫌気性細菌や汚濁物は微生物に到る植物連鎖を利用し、汚物の減量と高度な還元汚水を造り出す仕組みである。  The anaerobic sewage filtered in the preliminary tank 52 is aerobic sewage by the action of the three-phase aeration / reduction apparatus of claim 2 installed in the first aeration reduction tank 54 and the second aeration reduction tank 55. It is a mechanism that creates new oxygen as reduced sewage, anaerobic bacteria and pollutants in the reduced sewage use a plant chain that leads to microorganisms, and reduces the amount of sewage and creates highly reduced sewage.

このように処理された還元汚水は沈殿槽56に取り付けたバッフル59の間を通過し、還元汚水中の汚泥は沈殿し、エアリフトポンプによって第一嫌気酸化槽に返送し、又、上澄還元汚水は越流堰75を経て、請求項3の三次処理装置の散水▲ろ▼床へ流入して、高度な還元水として池水は植物の灌水、水洗トイレの洗滌水として再利用を可能とし、又、魚の住める水として河川に放流する仕組みである。  The reduced sewage thus treated passes between the baffles 59 attached to the settling tank 56, the sludge in the reduced sewage settles, and is returned to the first anaerobic oxidation tank by the air lift pump. After passing through the overflow weir 75, it flows into the watering floor of the tertiary treatment device according to claim 3 and the pond water can be reused as irrigation for plants and washing water for flush toilets as advanced reducing water. It is a mechanism that releases it to the river as water for fish.

請求項5の特定施設用酸化還元方式浄化装置について、図7、図8で示すように、流入する汚水は導入管66により前処理装置61に流入し、設置したブロワ−11で攪拌散気管67により攪拌して、汚水中の固形物を自動掻上機により汚泥貯留槽65へと除去する  As shown in FIGS. 7 and 8, the inflowing sewage flows into the pretreatment device 61 through the introduction pipe 66 and the stirring diffuser pipe 67 is installed in the installed blower-11. The solid matter in the sewage is removed to the sludge storage tank 65 by an automatic rake.

前処理装置61で処理した汚水は、流量調整槽62にて汲上ポンプにより汲上て、計量器71で計量して第一曝気還元槽54に流入し、請求項1の複数の三相曝気還元装置1によって還元汚水となり、バッフル59を通じ、第二曝気還元槽55に流入して、装備した請求項2の備付三相曝気装置21と、旋回流を正常化する曝気攪拌装置72によって高度な還元水となり、微生物の植物連鎖により汚泥の減量を計り、新しい酸素を造り出す仕組みである。  The sewage treated by the pretreatment device 61 is pumped up by a pumping pump in the flow rate adjusting tank 62, measured by the measuring device 71 and flows into the first aeration reduction tank 54, and a plurality of three-phase aeration reduction apparatuses according to claim 1. 1 becomes reduced sewage, flows into the second aeration reduction tank 55 through the baffle 59, and is equipped with the reduced three-phase aeration device 21 according to claim 2 and the aeration stirrer 72 for normalizing the swirl flow to provide highly reduced water. It is a mechanism that measures sludge reduction by microbial plant chain and creates new oxygen.

サイドウエル73を通じ、二相式沈殿槽63に流入した還元汚水中の沈殿汚泥はエアリフトポンプによって汚泥濃縮槽64に返送し沈殿した汚泥はエアリフトポンプで汚泥貯留槽へ移送して搬出し、浮上スカムはスカムスキ−マにより、汚泥濃縮槽64へ移送する。  Through the side well 73, the precipitated sludge in the reduced sewage flowing into the two-phase sedimentation tank 63 is returned to the sludge concentration tank 64 by the air lift pump, and the precipitated sludge is transferred to the sludge storage tank by the air lift pump and carried out for floating scum. Is transferred to the sludge concentration tank 64 by a scum skimmer.

処理された上澄み還元汚水は越流堰75を経て、請求項3の三次処理装置31によって高度な還元水として再利用を可能とし、又、魚の住める水として河川に放流する。  The treated supernatant reduced sewage passes through the overflow weir 75, and can be reused as highly reduced water by the tertiary treatment device 31 according to claim 3, and is discharged into the river as water where fish can live.

三槽曝気装置の正面断面図である。It is front sectional drawing of a three-tank aeration apparatus. 備付三槽曝気装置の正面断面図である。It is front sectional drawing of an equipped 3 tank aeration apparatus. 三次処理浄化装置の正面断面図である。It is front sectional drawing of a tertiary treatment purification apparatus. 図3の平面図である。FIG. 4 is a plan view of FIG. 3. 施設用酸化還元方式浄化装置のフロ−シ−トである。It is a flow sheet of a redox purification device for facilities. 図5の平面図である内部を一部断面図で示してある。The inside which is the top view of FIG. 5 is shown with a partial cross section figure. 特定施設用酸化還元方式浄化装置のフロ−シ−トである。It is a flow sheet of a redox purification device for a specific facility. 図7の平面図である。FIG. 8 is a plan view of FIG. 7.

符号の説明Explanation of symbols

1 三槽曝気装置
2 丸形容器
3 散気管
4 散気装置
5 散気口
6 床材受
7 通気通水口
8 網目蓋
9 床材(マグマライト)
10 架台脚
11 ブロワ−
21 曝気還元槽
22 角型容器
23 散気管
24 散気口
27 角型用床材受
29 角型用床材
31 散水▲ろ▼床槽本体
32 配水枡
33 ▲ろ▼材受
34 汚水流入管
35 ▲ろ▼床
36 床材
37 散水管
38 貯留槽
39 放流ポンプ槽
40 放流ポンプ
41 放流管
42 磁力滅菌装置
43 散水口
44 散水ノズル
45 散気管
51 第一嫌気酸化槽
52 予備▲ろ▼過槽
53 第二嫌酸化槽
54 第一曝気還元槽
55 第二曝気還元槽
56 沈殿槽
57 エアリフトポンプ
58 導入管
59 バッフル
61 前処理装置
62 流量調整槽
63 二相式沈殿槽
64 汚泥濃縮槽
65 汚泥貯留槽
66 導入管
67 攪拌散気管
68 自動掻上機
69 流量調整槽
70 汲上ポンプ
71 計量器
72 曝気攪拌装置
73 サイドウエル
74 スカムスキ−マ
75 越流堰
DESCRIPTION OF SYMBOLS 1 Three tank aeration apparatus 2 Round container 3 Air diffuser tube 4 Air diffuser apparatus 5 Air diffuser opening 6 Floor material receiver 7 Ventilation water outlet 8 Mesh cover 9 Floor material (magma light)
10 Base legs 11 Blower
21 Aeration / reduction tank 22 Square container 23 Aeration pipe 24 Aeration port 27 Square floor material receiver 29 Square floor material 31 Sprinkling ▲ Filter ▼ Floor tank body 32 Distribution tank 33 ▲ Filter ▼ Material receiver 34 Sewage inflow pipe 35 ▲ Filter ▼ Floor 36 Floor material 37 Sprinkling pipe 38 Reservoir 39 Discharge pump tank 40 Discharge pump 41 Discharge pipe 42 Magnetic sterilizer 43 Sprinkling port 44 Sprinkling nozzle 45 Aeration pipe 51 First anaerobic oxidation tank 52 Preliminary ▲ Filter ▼ Over tank 53 Second anaerobic tank 54 First aeration reduction tank 55 Second aeration reduction tank 56 Precipitation tank 57 Air lift pump 58 Introduction pipe 59 Baffle 61 Pretreatment device 62 Flow rate adjustment tank 63 Two-phase precipitation tank 64 Sludge concentration tank 65 Sludge storage tank 66 Introduction pipe 67 Stirring diffuser pipe 68 Automatic scraping machine 69 Flow rate adjusting tank 70 Pumping pump 71 Metering device 72 Aeration stirrer 73 Side well 74 Scum skimmer 75 Overflow weir

Claims (5)

下部の通気孔と通水孔を床材受けで形成した底板と、上部の網目蓋と円筒形胴体で容器を形成し、全体を架台脚で設置可能としたその容器の中程で、網目蓋と底板を貫通させ支持させた円形パイプで成る散気管の下端の、直径2〜3ミリメ−トルの散気孔を有させた散気装置で、散気管へブロワ−から送風され散気装置の散気孔から吹き出す空気を底板の通気孔を通過させ、容器内に充填した硅藻土と黒ボク土に火山灰を加え焼成し、所定の割石として成る床材に激突接触させる構造で構成した三相曝気装置を、汚水浄化槽内の曝気還元槽に設置し、汚水を曝気することで床材に激突接触させる空気で同時に汚水を激突接触させ、床材の持つ遠赤外線の効果により、新しい酸素を造り、汚水を還元水とすることを特徴とする三相曝気装置とその汚水浄化装置。  A container is formed by a bottom plate with a lower vent and a water vent formed by a floor material holder, an upper mesh lid and a cylindrical body, and the mesh lid is the middle of the container that can be installed by a pedestal. The air diffuser has an air diffuser with a diameter of 2 to 3 millimeters at the lower end of a diffuser pipe made of a circular pipe that is passed through and supported by the bottom plate. The air diffuser is blown from the blower to the air diffuser. A three-phase aeration system constructed by passing the air blown out from the pores through the vents in the bottom plate, adding volcanic ash to the diatomaceous earth and black soil filled in the container, firing the ash, and colliding with the floor material as a predetermined crushed stone The equipment is installed in the aeration and reduction tank in the sewage septic tank, and the sewage is abutted against the flooring by aeration of the sewage. A three-phase aeration apparatus characterized by using sewage as reduced water and its Sewage purification equipment. 下部に角形用床材受けを有させ、その下に散気口を有させブロワ−に連結した散気管を装備し、単独で角形容器に形成したものと、又は、曝気還元槽の周壁を利用し同様な角型容器を形成したその容器の内部に、硅藻土と黒ボク土に火山礫、又は、ゼオライトを加え凝固剤で固め所定の割石としたものを床材として充填し、ブロワ−からの圧縮空気を散気孔から噴出させ、曝気還元槽内の汚水を、噴出させる圧縮空気で床材に激突接触させ、床材間を上昇させる間で、床材の持つ遠赤外線の効果により汚水中に新鮮な酸素を発生させ還元水とする請求項1の備付三相曝気装置とその汚水浄化装置。  A rectangular flooring receptacle is provided at the bottom, an aeration pipe connected to the blower with an air diffuser below it, and a single rectangular container or a peripheral wall of the aeration reduction tank is used. Then, the same square container was formed, and the inside of the container was filled with flocculate gravel or zeolite added to diatomaceous earth and Kuroboku soil, and solidified with a coagulant to form a predetermined crushed stone as a flooring material. Compressed air from the air diffuser holes, and the sewage in the aeration reduction tank is struck by the compressed air to be blown against the flooring and raised between the flooring. The equipped three-phase aeration apparatus according to claim 1 and its sewage purification apparatus according to claim 1, wherein fresh oxygen is generated to produce reduced water. 三次処理をする散水▲ろ▼床槽の下部に床材受けを有させ、その上内部に硅藻土と黒ボク土及び、火山灰礫、又は、ゼオライトを凝固剤で固めて所定の割石とした床材を充填した▲ろ▼床の上部で、排水枡に配列した散水管の散水口より汚水を滴下散水し、▲ろ▼床で▲ろ▼過しながら床材の持つ遠赤外線の効果によって還元水とし、床版でブロワ−からの圧縮空気を▲ろ▼床内に送る散気管を設置した貯留槽に貯留させ、併設して貯留させた放流ポンプ槽の循環ポンプで配水管の散水ノズルから霧状散水して循環させ、下方、散気管からの空気で▲ろ▼床内の嫌気性を防止し好気性生物を活発にして還元水の再浄化をする仕組みで、併せて、放流ポンプ槽に装備した二相放流ポンプに配管した放流パイプに有させた磁力滅菌装置で、高度に処理した還元水を、再利用、又は、魚の住める水として河川へ放流することを可能とした三次処理浄化装置を有した三相曝気装置とその汚水浄化装置。  Sprinkling water for the tertiary treatment. The floor tank is provided with a floor material receptacle, and diatomaceous earth, black urn earth, volcanic ash gravel, or zeolite is solidified with a coagulant inside to form a predetermined calcite. At the top of the floor filled with flooring material, sewage is dripped from the sprinkling port of the water pipe arranged in the drainage basin, and the far infrared effect of the flooring material passes through the floor while passing through the floor. Sprinkling nozzles for water distribution pipes using recirculation pumps in the discharge pump tanks, which are stored in a storage tank with a diffuser pipe installed in the floor to send compressed air from the blower to the floor with reduced slab. A mist-like water spray is circulated, and the air from the bottom and the air diffuser is used to prevent anaerobic reaction in the floor and activate aerobic organisms to repurify the reduced water. This is a magnetic sterilizer equipped with a discharge pipe connected to a two-phase discharge pump installed in the tank. The reduced water obtained by physical, reused, or it possible to discharge into the river as habitable fish water were tertiary treatment purifier three-phase aeration device having its sewage purifier. 施設用の酸化還元方式浄化の施設を第一嫌気酸化槽、第二嫌気酸化槽、第一曝気還元槽第二曝気還元槽、沈殿槽、三次処理装置で構成し、第一曝気還元槽、第二曝気還元槽内に備付三相曝気装置を設置し、第一嫌気酸化槽内へ導入管から流入する汚水が対角線上に有させたバッフル間を上昇し、第二嫌気酸化槽に流入し設置した予備▲ろ▼過槽に充填した請求項2の床材により▲ろ▼過され、汚水中の洗剤や食品添加物は汚濁物と共に沈殿して嫌気酸化され、汚泥は減量されて除去する仕組みで、予備▲ろ▼過槽で▲ろ▼過した嫌気性汚水は第一曝気還元槽、第二曝気還元槽に設置した請求項2の備付三相曝気装置の作用により、好気性の還元汚水となり沈殿槽内のバッフル間を通過し、還元汚水中の汚泥は沈殿しエアリフトポンプで第一嫌気酸化槽に返送する。そして、上澄還元汚水は越流堰を経て、請求項3の三次処理浄化装置に流入して高度な還元水となり、池水は植物の灌水や水洗トイレの洗滌にと再利用可能とし、又、魚の住める水として河川に放流も可能とした三相曝気装置とその汚水浄化装置。  The facility for redox purification for facilities consists of a first anaerobic oxidation tank, a second anaerobic oxidation tank, a first aeration reduction tank, a second aeration reduction tank, a precipitation tank, and a tertiary treatment device. Installed three-phase aeration equipment in the two aeration reduction tanks, the sewage flowing from the introduction pipe into the first anaerobic oxidation tank rises between the baffles on the diagonal, and flows into the second anaerobic oxidation tank A system that removes the sludge by reducing the amount of sludge after it is filtered by the flooring of claim 2 filled in the excess tank, and the detergent and food additives in the sewage are precipitated together with the pollutant and anaerobically oxidized. Then, the anaerobic sewage that has passed through the preliminary aeration tank is aerobic reduced sewage by the action of the three-phase aeration apparatus provided in the first aeration reduction tank and the second aeration reduction tank. Passing between the baffles in the settling tank, the sludge in the reduced sewage settles and is primarily dissipated by the air lift pump. It is returned to the oxidation tank. The supernatant reduced sewage flows through the overflow weir and flows into the tertiary treatment purification device of claim 3 to become highly reduced water, and the pond water can be reused for irrigation of plants and washing of flush toilets, A three-phase aeration device and its sewage purification device that can be discharged into rivers as fish-living water. 特定施設用の還元方式浄化の施設を前処理装置、流量調整槽、第一曝気還元槽、第二曝気還元槽、二相式沈殿槽、汚泥濃縮槽、汚泥貯留槽、三次処理装置から構成し、導入管からの汚水の固形物を前処理装置で除去した後、ブロワ−を有した散気管を設置した流量調整槽で攪拌し、残る固形物は自動掻上機で汚泥貯留槽に除去し、汚水は調整ポンプにより汲上、計量器で計量して第一曝気還元槽に流入させ、その槽内に複数設置した請求項1の三相曝気装置で還元汚水にし、更に、バッフルを通じ第二曝気還元槽に流入し、槽内に装備した請求項2の備付三相曝気装置で旋回流を正常化し、又、曝気攪拌装置により、微生物の食物連鎖で汚泥の減量を計り、新しい酸素を作り出し、高度な還元汚水にして二相式沈殿槽に流入させ、沈殿した汚泥はエアリフトポンプで汚泥濃縮槽に返送し濃縮され、エアリフトポンプにより汚泥貯留槽へ移送して搬出する。二槽式水沈殿槽の上澄還元汚水が請求項3の三次処理装置によって処理され、還元水として再利用、又は、魚の住める水として河川に放流する構成とした三相曝気装置とその汚水浄化装置。  The reduction system purification facility for specific facilities consists of pretreatment equipment, flow rate adjustment tank, first aeration reduction tank, second aeration reduction tank, two-phase precipitation tank, sludge concentration tank, sludge storage tank, and tertiary treatment equipment. After removing the solid matter of sewage from the introduction pipe with a pretreatment device, it is stirred in a flow rate adjustment tank equipped with a diffuser pipe with a blower, and the remaining solid matter is removed to a sludge storage tank with an automatic scraper. The sewage is pumped up by a regulating pump, measured by a measuring instrument and introduced into the first aeration / reduction tank. A plurality of the sewage is installed in the tank to form reduced sewage, and further through the baffle through the second aeration. The swirl flow is normalized with the equipped three-phase aeration apparatus according to claim 2 that flows into the reduction tank and is installed in the tank, and the sludge is reduced in the microbial food chain by the aeration stirrer to produce new oxygen, Highly reduced sewage is made to flow into the two-phase settling tank and settled. It is returned to the sludge concentration tank with an airlift pump concentrated unloaded and transferred to the sludge storage tank by the air lift pump. A three-phase aeration apparatus and a sewage purification system in which the supernatant reduced sewage of the two-tank water settling tank is treated by the tertiary treatment apparatus of claim 3 and reused as reduced water or discharged into the river as water for fish. apparatus.
JP2005381035A 2005-12-15 2005-12-15 Three phase aerator and sewage purifying apparatus equipped therewith Pending JP2007160295A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100912603B1 (en) 2007-08-13 2009-08-19 월드테크 주식회사 Movable zero discharge system
CN102190367A (en) * 2010-03-04 2011-09-21 中持盈佰利(北京)环境工程有限公司 Filter material cutting device and biological aerated filter provided with same
JP2012055801A (en) * 2010-09-06 2012-03-22 Fuji Clean Co Ltd Air diffuser for water treatment and water treatment apparatus
CN103613191A (en) * 2013-12-05 2014-03-05 乐山世峰环保科技有限责任公司 Aeration sewage treatment pond
CN107215953A (en) * 2017-08-01 2017-09-29 广州华浩能源环保集团股份有限公司 A kind of sewage of low concentration processing system
CN114573167A (en) * 2022-03-29 2022-06-03 苏州敬天爱人环境科技有限公司 Water treatment facilities with peculiar smell processing function

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100912603B1 (en) 2007-08-13 2009-08-19 월드테크 주식회사 Movable zero discharge system
CN102190367A (en) * 2010-03-04 2011-09-21 中持盈佰利(北京)环境工程有限公司 Filter material cutting device and biological aerated filter provided with same
CN102190367B (en) * 2010-03-04 2013-02-06 中持盈佰利(北京)环境工程有限公司 Filter material cutting device and biological aerated filter provided with same
JP2012055801A (en) * 2010-09-06 2012-03-22 Fuji Clean Co Ltd Air diffuser for water treatment and water treatment apparatus
CN103613191A (en) * 2013-12-05 2014-03-05 乐山世峰环保科技有限责任公司 Aeration sewage treatment pond
CN107215953A (en) * 2017-08-01 2017-09-29 广州华浩能源环保集团股份有限公司 A kind of sewage of low concentration processing system
CN114573167A (en) * 2022-03-29 2022-06-03 苏州敬天爱人环境科技有限公司 Water treatment facilities with peculiar smell processing function
CN114573167B (en) * 2022-03-29 2023-04-28 苏州敬天爱人环境科技有限公司 Water treatment device with peculiar smell treatment function

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