JP2006326387A - Aeration tank structure - Google Patents

Aeration tank structure Download PDF

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JP2006326387A
JP2006326387A JP2005149354A JP2005149354A JP2006326387A JP 2006326387 A JP2006326387 A JP 2006326387A JP 2005149354 A JP2005149354 A JP 2005149354A JP 2005149354 A JP2005149354 A JP 2005149354A JP 2006326387 A JP2006326387 A JP 2006326387A
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aeration tank
pipe
tank
aeration
water
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JP4848139B2 (en
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Kazuyoshi Udagawa
和義 宇田川
Takayoshi Toga
隆喜 栂
Morio Ogawa
守雄 小川
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WAKI SANGYO KK
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WAKI SANGYO KK
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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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage
    • 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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing

Abstract

<P>PROBLEM TO BE SOLVED: To provide an aeration tank structure which can carry out water purification without installing a special separator and the like for discharging suspended matter, and can be made to be simple and low-priced. <P>SOLUTION: In an aeration tank 2 comprising a first aeration tank 10 for aerating stored raw water and discharging it from a delivery port 16, and a second aeration tank 11 for aerating intermediate treated water flowing in from the first aeration tank 10 and discharging it from a delivery port 25 to outside, a return pipe 27 of which the suction port 30 opens adjacent to the tank bottom wall on the delivery port 25 side of the second aeration tank 11 is installed. The intermediate treated water of the second aeration tank 11 is returned to the first aeration tank 10 from the suction port 30 through the return pipe 27 to be purified. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、一般家庭や産業排水等の下水道汚泥及びオカラや焼酎カス或いは糞尿,食品加工時の油分を含むグリストラップ水等を浄水処理する曝気タンク構造に関する。   The present invention relates to an aeration tank structure for purifying sewage sludge such as general household and industrial wastewater, and okara, shochu waste or manure, grease trap water containing oil during food processing, and the like.

従来、生活排水や食品加工排水,産業排水等の有機汚泥からなる被処理原水(以下単に原水と言う)を曝気槽(曝気タンク)で曝気処理する際に、曝気タンク内に処理媒質となる木質細片(木材チップ)を混入し原水と共に攪拌し、有機汚泥を細菌の分解作用によってBOD値等を低減させるように処理する排水処理装置は既に公知である(例えば特許文献1。)。
特公平4−10398号公報
Conventionally, when raw water to be treated (hereinafter simply referred to as raw water) made of organic sludge, such as domestic wastewater, food processing wastewater, and industrial wastewater, is aerated in an aeration tank (aeration tank), the wood used as the processing medium in the aeration tank A wastewater treatment apparatus that mixes fine pieces (wood chips) and stirs with raw water to treat organic sludge so as to reduce the BOD value or the like by the decomposition of bacteria is already known (for example, Patent Document 1).
Japanese Examined Patent Publication No. 4-10398

上記特許文献1で示される原水の排水処理装置は、曝気タンク内で媒質中の微細な流路に目詰まりを生じ難い木材チップを攪拌し、有機汚泥を細菌の分解作用によってBOD値等を低減できる特徴がある。然し、この曝気タンクは曝気処理を行う消化室(第1曝気槽)の上方にタンク中央部を逆扇状の仕切板で区画した沈降室を設けて原水を処理するので、曝気タンクが特殊な形状になり上下方向に長大となる。また曝気タンクを多段に接続した処理施設を構成する場合に、隣接する曝気タンクの接続構造が複雑化しコスト高になる等の欠点がある。   The raw water wastewater treatment apparatus disclosed in Patent Document 1 stirs wood chips that are unlikely to clog fine channels in the medium in the aeration tank, and reduces organic sludge by reducing the BOD value, etc., by bacterial decomposition. There are features that can be done. However, this aeration tank has a special shape because the aeration tank is provided with a sedimentation chamber in which the central part of the tank is partitioned by a reverse fan-shaped partition plate above the digestion chamber (first aeration tank) for aeration treatment. It becomes long in the vertical direction. Further, when configuring a treatment facility in which aeration tanks are connected in multiple stages, there is a drawback that the connection structure of adjacent aeration tanks is complicated and the cost is increased.

さらに沈降室下方の消化室内で縦向きの散気管からエアを噴出して行う曝気時に、中間処理水の泡立ちや振動を沈降室の下部に開口される連通口から伝え沈降室を静置型にすることができず、上昇流と液面(水面)の波立ちを伴い速やかな沈降作用が行い難かったり、水面に浮遊する木材チップの細粒を含む浮遊物がいつまでも残存し易い等の構造上の問題がある。このため水面が下降変動する場合に、上澄み液を送り出すパイプ(送出管)内に浮遊物を多量に混入して送水したり詰まりを生じさせ易い等の問題もある。   Furthermore, when aeration is performed by blowing air from a vertical air diffuser in the digestion chamber below the sedimentation chamber, the bubbling and vibration of the intermediate treatment water is transmitted from the communication port opened at the bottom of the sedimentation chamber, and the sedimentation chamber is made stationary. Structural problems such as inability to perform rapid sedimentation due to the updraft and rippling of the liquid surface (water surface), and suspended solids containing fine particles of wood chips floating on the water surface. There is. For this reason, when the water surface fluctuates downwardly, there is a problem that a large amount of suspended solids are mixed in a pipe (sending pipe) for sending the supernatant liquid and water is easily fed or clogged.

上記課題を解決するための曝気タンク構造は、第1に、貯留する原水を曝気処理して送出口16から流出させる第1曝気槽10と、第1曝気槽10から流入する中間処理水を曝気処理し送出口25から外部に流出させる第2曝気槽11からなる曝気タンク2において、前記第2曝気槽11の送出口25側のタンク底壁に吸込口30を近接させて開口する返送装置26の返送管27を設け、第2曝気槽11の中間処理水を吸込口30から返送管27を介し第1曝気槽10に返送する構成としたことを特徴としている。   The aeration tank structure for solving the above-mentioned problem is firstly aerated with the first aeration tank 10 for aeration of the stored raw water and flowing out from the outlet 16 and the intermediate treated water flowing in from the first aeration tank 10. In the aeration tank 2 composed of the second aeration tank 11 to be processed and discharged to the outside from the delivery outlet 25, a return device 26 that opens with the suction port 30 close to the tank bottom wall on the delivery outlet 25 side of the second aeration tank 11. The return pipe 27 is provided, and the intermediate treated water in the second aeration tank 11 is returned from the suction port 30 to the first aeration tank 10 through the return pipe 27.

第2に、第2曝気槽11内の上流側と下流側にエア管15と返送管27を設け、該エア管15と返送管27の間に隔壁20を設けて、上流側の曝気室17と下流側の排出室19を区画して形成すると共に、隔壁20の下辺を上流側に屈曲して形成した誘導壁21とタンク底壁との間に、曝気室17と排出室19を連通させる流入間隔22を形成したことを特徴としている。   Secondly, an air pipe 15 and a return pipe 27 are provided on the upstream side and the downstream side in the second aeration tank 11, a partition wall 20 is provided between the air pipe 15 and the return pipe 27, and the upstream aeration chamber 17. The aeration chamber 17 and the discharge chamber 19 are connected between a guide wall 21 formed by bending the lower side of the partition wall 20 toward the upstream side and the tank bottom wall. An inflow interval 22 is formed.

第3に、返送管27の吸込口30内にエアを噴出するエア管29を設け、該エアによって返送管27内に上昇流を発生させ、排出室19底壁側の中間処理水を導き第1曝気槽10に返送することを特徴としている。   Thirdly, an air pipe 29 for blowing air into the suction port 30 of the return pipe 27 is provided, and an upward flow is generated in the return pipe 27 by the air, leading to intermediate treated water on the bottom wall side of the discharge chamber 19. It is characterized by being returned to one aeration tank 10.

第4に、曝気タンク2内で送出口16を備える仕切壁12によって、第1曝気槽10と第2曝気槽11を区画形成し、第1曝気槽10と第2曝気槽11の上部にメンテナンス作業用の作業口33を設けたことを特徴としている。   Fourth, a partition wall 12 having a delivery port 16 in the aeration tank 2 forms a first aeration tank 10 and a second aeration tank 11, and maintenance is performed above the first aeration tank 10 and the second aeration tank 11. A feature is that a work port 33 for work is provided.

第5に、送出口16又は送出口25を横向きのパイプからなる送出管で形成し、送出管の送り込み側に下部縦管部31と上部縦管部32を形成する縦向きパイプの中途部を連結し、下部縦管部31と上部縦管部32の開口部を、それぞれ液面から所定の深さ及び高さに位置させることを特徴としている。   Fifth, the delivery port 16 or the delivery port 25 is formed by a delivery pipe made of a horizontal pipe, and a middle part of the longitudinal pipe forming the lower vertical pipe part 31 and the upper vertical pipe part 32 is formed on the feed side of the delivery pipe. It connects, The opening part of the lower vertical pipe part 31 and the upper vertical pipe part 32 is each located in the predetermined | prescribed depth and height from a liquid level, It is characterized by the above-mentioned.

上記のように構成される本発明によれば、第1曝気槽10で曝気処理されて送り込まれた第2曝気槽11内の中間処理水の一部を吸込口30から導き、タンク底壁側の夾雑物等を返送管27によって第1曝気槽10に返送し再処理するので、第2曝気槽11内の中間処理水の浄水処理をより確実に行うことができる。また第2曝気槽11内の浮遊物を外部に廃棄する分離装置等を特別に設けることなく浄水処理を行うと共に、曝気タンク2を簡潔で廉価な構成にすることができる。   According to the present invention configured as described above, a part of the intermediate treated water in the second aeration tank 11 that has been aerated in the first aeration tank 10 and sent in is introduced from the suction port 30, and the tank bottom wall side Since the contaminants and the like are returned to the first aeration tank 10 by the return pipe 27 and reprocessed, the intermediate treatment water in the second aeration tank 11 can be purified more reliably. In addition, water purification can be performed without specially providing a separation device or the like for discarding suspended matters in the second aeration tank 11 to the outside, and the aeration tank 2 can be configured to be simple and inexpensive.

第2曝気槽11内で曝気室17と排出室19とを区画形成する隔壁20の下辺を上流側に屈曲させた誘導壁21と、タンク底壁との間に曝気室17と排出室19を連通させる流入間隔22を形成したことにより、隔壁20に沿って対流し下降する中間処理水を上流側に案内することができる。また案内によって流入間隔22近傍のタンク底壁に対する夾雑物の堆積を防止することができ、また未処理の夾雑物の排出室19内への排出移動を流入間隔22によって抑制することができる。   In the second aeration tank 11, the aeration chamber 17 and the discharge chamber 19 are provided between the guide wall 21 in which the lower side of the partition wall 20 that partitions the aeration chamber 17 and the discharge chamber 19 is bent upstream, and the tank bottom wall. By forming the inflow interval 22 for communication, the intermediate treated water that convects and descends along the partition wall 20 can be guided upstream. In addition, it is possible to prevent the accumulation of contaminants on the tank bottom wall in the vicinity of the inflow interval 22 by the guidance, and it is possible to suppress the discharge movement of untreated contaminants into the discharge chamber 19 by the inflow interval 22.

排出室19内に流入する中間処理水を夾雑物と共に流入間隔22の下流側で吸込口30から吸い込み、返送管27内で曝気処理を行いながら第1曝気槽10に返送することにより、排出室19内の浮遊物や夾雑物を第1曝気槽10に返送することができる。また排出室19内での上昇流の発生を抑制し中間処理水の沈降作用を促進することにより、きれいな処理浄水を取り出すことができる。   The intermediate treated water flowing into the discharge chamber 19 is sucked together with foreign substances from the suction port 30 on the downstream side of the inflow interval 22 and returned to the first aeration tank 10 while performing the aeration process in the return pipe 27, thereby Floating matters and impurities in 19 can be returned to the first aeration tank 10. Further, clean treated water can be taken out by suppressing the generation of the upward flow in the discharge chamber 19 and promoting the sedimentation action of the intermediate treated water.

曝気タンク2内を仕切壁12によって区画し第1曝気槽10と第2曝気槽11とを簡単に形成することができる。また第1曝気槽10と第2曝気槽11は横向きに構成され、それぞれに設けた作業口33から内部のメンテナンス作業を簡単に行うことができる。   The inside of the aeration tank 2 can be partitioned by the partition wall 12, and the first aeration tank 10 and the second aeration tank 11 can be easily formed. Moreover, the 1st aeration tank 10 and the 2nd aeration tank 11 are comprised sideways, and an internal maintenance operation | work can be easily performed from the work port 33 provided in each.

送出口を形成する横向きパイプの送出管の送り込み側に、下部縦管部31と上部縦管部32を形成する縦向きパイプの中途部を連結したことにより、下部縦管部31の開口部を液面から所定の深さに位置させ浮遊物の混入を防止し送水することができる。また上部縦管部32の開口部を液面の変動高さ以上に位置させ浮遊物の混入を防止すると共に、上部縦管部32内で液面の変動を自由にして管路内の詰まり防止や清掃等を行い易くすることができる。   By connecting the middle part of the vertical pipe forming the lower vertical pipe part 31 and the upper vertical pipe part 32 to the feed side of the delivery pipe of the horizontal pipe forming the delivery port, the opening of the lower vertical pipe part 31 is formed. It can be located at a predetermined depth from the liquid surface to prevent the floating substances from being mixed and to feed water. In addition, the opening of the upper vertical pipe part 32 is positioned above the fluctuation level of the liquid level to prevent the entry of suspended matter, and the liquid level in the upper vertical pipe part 32 is freely changed to prevent clogging in the pipeline. And cleaning can be facilitated.

以下図示する本発明の実施形態について説明する。図1は豆腐製造時に排出されるおからを含む有機汚泥等(以下単に原水と言う)を浄水処理する処理施設(処理装置)1の構成を模式的に示す平面図である。この処理施設1は原水を曝気処理する本発明に係わる曝気タンク2を直列的に多段に接続した1次処理装置3と、該1次処理装置3の最終段の曝気タンク2から送り出される処理浄水を、後述する微生物媒体剤(処理媒質)として充填された木材チップ(木質細片)Aを通して、炭酸ガスと水に分解処理する反応槽4等から構成している。   Embodiments of the present invention shown in the drawings will be described below. FIG. 1 is a plan view schematically showing the configuration of a treatment facility (treatment device) 1 for purifying organic sludge containing okara discharged during tofu production (hereinafter simply referred to as raw water). This treatment facility 1 includes a primary treatment device 3 in which aeration tanks 2 according to the present invention for aeration treatment of raw water are connected in series, and treated purified water sent from the final aeration tank 2 of the primary treatment device 3. Is made up of a reaction tank 4 that decomposes into carbon dioxide gas and water through a wood chip (wood piece) A filled as a microbial medium agent (treatment medium) described later.

上記処理施設1は、1次処理装置3の第1段目の曝気タンク2に供給する原水を貯留する投入槽5と、前記反応槽4から送り出される処理水(浄水)並びに外部から必要により供給される水道水を貯留する貯水槽6を備えている。この貯水槽6は貯留した水を外部に取り出し可能にすると共に、所定量の水を投入槽5に原水用の希釈水として供給することができる。尚、曝気タンク2の長さを例えば810cm程度にする場合、投入槽5は450cm程度とし、貯水槽6は370cm程度として、両者を合わせた長さを曝気タンク2の長さと略等しくすることが処理施設を構成する上で望ましい。   The treatment facility 1 supplies an input tank 5 for storing raw water to be supplied to the first-stage aeration tank 2 of the primary treatment apparatus 3, treated water (purified water) sent out from the reaction tank 4, and is supplied as needed from the outside. A water storage tank 6 for storing the tap water to be used is provided. The water storage tank 6 can take out the stored water to the outside, and can supply a predetermined amount of water to the input tank 5 as dilution water for raw water. For example, when the length of the aeration tank 2 is set to about 810 cm, the charging tank 5 is set to about 450 cm, the water storage tank 6 is set to about 370 cm, and the combined length of both is made substantially equal to the length of the aeration tank 2. Desirable for configuring a treatment facility.

曝気タンク2と反応槽4内には、それぞれの処理に適応する機能を備えた木質細片即ち木材チップ(微生物生息有機質濾過材)が投入され、原水を1次処理装置3によって後述する湿式の1次処理をし、且つこの1次処理水(処理浄水)を反応槽4に供給し乾式の2次処理を行い、2次処理水としてきれいな浄水を得る処理方法としている。この処理施設1で処理した浄水は、下水への放流基準値及び河川放流基準値を後述するようにクリヤーすることができ、また放流廃棄することなく貯水槽6に回収し原水用の希釈水として循環利用することを可能にしている。   In the aeration tank 2 and the reaction tank 4, wood chips having a function adapted to each treatment, that is, wood chips (microorganism habitat organic filter material) are introduced, and the raw water is wet treated by the primary treatment device 3 to be described later. A primary treatment is performed, and the primary treated water (treated purified water) is supplied to the reaction tank 4 to perform a dry secondary treatment to obtain clean purified water as the secondary treated water. The purified water treated at this treatment facility 1 can be cleared as described below for the discharge standard value to the sewage and the river discharge standard value, and can be recovered in the water storage tank 6 without being discarded and used as dilution water for raw water. It enables recycling.

そして、処理施設1に使用する木材チップAと木材チップBは、いずれも杉や檜等の針葉樹の間伐材をチップ状に粉砕した木質細片を用いることにより、木質細片の製造及び処理コストを低減し、また取り扱いを行い易くしている。
この木材チップA及び木材チップBは通常のオガ屑や木質細片をそのまま使用しないで、例えば特許文献2で示されるような攪拌洗浄処理を木質細片に施すことによって製造されたものを使用することが望ましい。
The wood chip A and the wood chip B used in the processing facility 1 both use wood chips obtained by pulverizing thinned wood of conifers such as cedars and straws into chips, thereby producing and treating the wood chips. This makes it easier to handle.
For this wood chip A and wood chip B, ordinary sawdust and wood chips are not used as they are, but for example, those produced by applying a stirring cleaning process as shown in Patent Document 2 to the wood chips are used. It is desirable.

即ち、実施形態で使用する木質細片は、杉等の針葉樹が粉砕された細片を水中で攪拌し微粒径の粒子(微粉末)並びに雑菌類を洗浄除去して得られる、2〜5mm程度の攪拌洗浄処理されたものとしている。これにより木質細片は細片構造を複雑化させて表面積を極めて大きくするように製造され、炭素質有機材としてセルロース65%,リグニン25%,ペントサン10%程度になっている。   That is, the wood pieces used in the embodiment are obtained by stirring and removing fine particles (fine powder) and various fungi, which are obtained by stirring fine pieces of crushed coniferous trees such as cedar in water. It is assumed that it has been subjected to a degree of stirring and washing treatment. As a result, the wood chips are manufactured to have a very large surface area by complicating the structure of the fragments, and the carbonaceous organic material is about 65% cellulose, 25% lignin, and about 10% pentosan.

また木質細片の雑菌処理や多孔質化を図ることが簡単で、広い表面積を有して汚泥水と接触し、内部に多数の菌体(桿菌や球菌等)のコロニーを発生させることができる。
そして、攪拌洗浄処理された木質細片の特性により微生物類(細菌)が好適に増殖する環境を提供し、長期間の浄水処理に際し微粉末による目詰まり等を抑制し木質本来の有機的な生体組織を維持するので、浄水処理を安定的に廉価に行うことができる等の特徴がある。
In addition, it is easy to treat wood chips with microbes and make them porous, and it has a large surface area and can come into contact with sludge water to generate colonies of many bacterial bodies (gonococci, cocci, etc.) inside. .
In addition, it provides an environment in which microorganisms (bacteria) can suitably grow due to the characteristics of the wood chips that have been agitated and washed, and suppresses clogging caused by fine powders during long-term water purification treatment, and the natural organic nature of wood. Since the organization is maintained, water purification can be performed stably and inexpensively.

従って、この実施形態では反応槽4に大量に充填使用される木材チップAは、上記攪拌洗浄処理された木質細片を植菌加工することなくそのまま用いることにより、保水性,吸着性,水切り性等にも優れ、水分調整の急速化と空隙率の維持並びに酸素の発生等を好適に行う。また汚泥水と接触するとき土壌菌を含む消化菌の棲家となり、そこに発生する好気性と嫌気性との両性菌を同体で保持し汚泥消滅を促進させる。そして、有機汚泥水に含まれる固形物質や浮遊物(SS)及び動植物のタンパク質,脂肪質,炭水化物等を含む汚泥水を作る物質を、微生物媒体材の発酵分解による消化作用によって水と炭酸ガスにすることができる。   Therefore, in this embodiment, the wood chip A that is used in a large amount in the reaction tank 4 is used as it is without inoculating the above-described stirred and washed wood chips, so that water retention, adsorptivity and drainage can be obtained. The water content is rapidly adjusted, the porosity is maintained, and the generation of oxygen is suitably performed. In addition, when it comes into contact with sludge water, it becomes a family of digestive bacteria including soil bacteria, and keeps the aerobic and anaerobic bacteria generated there in the same body and promotes sludge extinction. Then, solid substances contained in organic sludge water and suspended solids (SS) and substances that make sludge water containing animal and plant proteins, fats, carbohydrates, etc. are converted into water and carbon dioxide by the digestive action by fermentation decomposition of microbial media material. can do.

木材チップBは上記木材チップAと同じ木質細片に、例えばクロレラ菌,よもぎ菌,土壌菌等の菌体を予め公知の植菌手段によって植菌したものを用いる。これにより木材チップBは原水中で攪拌され様々に変形しながら汚泥と接触するとき、各菌体の特有な働きも加えながら浄水処理を促進する。   The wood chip B uses the same wood chip as the wood chip A, in which cells such as chlorella, sorghum, and soil bacteria are inoculated in advance by a known inoculation means. As a result, when the wood chip B is stirred in the raw water and comes into contact with the sludge while being deformed in various ways, the water purification treatment is promoted while adding the specific functions of each cell.

尚、木材チップBと共に原水の分解を助成するバーク材や、攪拌時に原水中の大きな固形物や夾雑物に接触して、物理的に細粒化させるプラスチック材等からなるチップ又はボール状の処理補助材を、必要により所定の割合で混入することもできる。また木材チップB等を曝気タンク2に混入する割合は、各曝気室に貯留される原水の容量及び浄水処理の程度や処理の方式等を勘案して定められる。   A chip or ball-shaped treatment made of a bark material that assists in the decomposition of raw water together with the wood chip B, or a plastic material that comes into physical contact with large solids or contaminants in the raw water during stirring. The auxiliary material can be mixed at a predetermined ratio as necessary. The ratio of mixing wood chips B and the like into the aeration tank 2 is determined in consideration of the volume of raw water stored in each aeration chamber, the degree of water purification treatment, the treatment method, and the like.

次に処理施設1の各部の構成について説明する。先ず図2〜図3を参照し曝気タンク2について説明する。この曝気タンク2は密閉可能な方形状のタンク内で、第1曝気槽(調整曝気槽)10と第2曝気槽(曝気槽)11とを左右に区画して形成する仕切壁12を設けている。また実施形態において曝気タンク2は全長を810cm程度にするとき、仕切壁12の位置は第1曝気槽10の長さを540cm程度とし、且つ第2曝気槽11の長さを270cm程度となる位置に設けることにより、横長の第1曝気槽10によって原水を十分な時間をかけて木材チップB等と攪拌し1次処理を行う。   Next, the structure of each part of the processing facility 1 will be described. First, the aeration tank 2 will be described with reference to FIGS. This aeration tank 2 is a sealable rectangular tank, and is provided with a partition wall 12 formed by dividing a first aeration tank (adjusted aeration tank) 10 and a second aeration tank (aeration tank) 11 into left and right sides. Yes. In the embodiment, when the aeration tank 2 has a total length of about 810 cm, the partition wall 12 is positioned such that the length of the first aeration tank 10 is about 540 cm and the length of the second aeration tank 11 is about 270 cm. Thus, the raw water is agitated with the wood chip B and the like in a horizontally long first aeration tank 10 for a sufficient time to perform the primary treatment.

第1曝気槽10はタンク左壁の上部側に投入槽5から原水を供給する供給口となる接続管13を備え、図示しない管理施設側に設置されるエア圧送装置と接続されるエア管15を、接続管13とタンク底部に近接した位置からエアを吹き出し供給するように設けている。これにより処理方向上手側(上流側)からエアを噴出し、原水を木材チップBを攪拌させながら処理方向下手側(下流側)に向けて対流を生じさせ曝気処理を行う。   The first aeration tank 10 includes a connection pipe 13 serving as a supply port for supplying raw water from the charging tank 5 on an upper side of the left wall of the tank, and an air pipe 15 connected to an air pressure feeding device installed on the management facility side (not shown). Is provided so that air is blown out from a position close to the connecting pipe 13 and the bottom of the tank. As a result, air is ejected from the upper side (upstream side) in the processing direction, and aeration is performed by generating convection toward the lower side (downstream side) in the processing direction while agitating the wood chip B with the raw water.

また仕切壁12には接続管13よりやや下方となる位置に送出口となる送出管16を設け、第1曝気槽10と下流側の第2曝気槽11とを連通させている。
第2曝気槽11は内部に曝気室17と排出室19を左右に区画して形成する隔壁20を設けている。この隔壁20は曝気室17の容量を排出室19の容量より大きくする位置に設けられ、その下辺に原水の対流方向を案内すると共に第2曝気槽11側への流入移動を規制して導く誘導壁21を形成している。
Further, the partition wall 12 is provided with a delivery pipe 16 serving as a delivery outlet at a position slightly below the connection pipe 13 so that the first aeration tank 10 and the second aeration tank 11 on the downstream side are communicated with each other.
The second aeration tank 11 is provided with a partition wall 20 formed by dividing the aeration chamber 17 and the discharge chamber 19 into left and right sides. The partition wall 20 is provided at a position where the capacity of the aeration chamber 17 is larger than the capacity of the discharge chamber 19, and guides the convection direction of the raw water to the lower side of the partition wall 20 and guides the inflow movement toward the second aeration tank 11. A wall 21 is formed.

誘導壁21は曝気室17側に向けて緩やかに湾曲させ、その先端部と曝気タンク2の底壁とで形成する流入口(以下流入間隔と言う)22の高さを30ミリ〜50ミリ程度に設定している。これにより第1曝気槽10内の大きな夾雑物や底壁側に堆積する未処理の固形物は、排出室19側への直接的な流入が流入間隔22によって規制され、第1曝気槽10内で十分に処理される。   The guide wall 21 is gently curved toward the aeration chamber 17 side, and the height of the inflow port (hereinafter referred to as the inflow interval) 22 formed by the tip portion thereof and the bottom wall of the aeration tank 2 is about 30 mm to 50 mm. It is set to. As a result, large contaminants in the first aeration tank 10 and untreated solid matter deposited on the bottom wall side are restricted from flowing directly into the discharge chamber 19 by the inflow interval 22, and the first aeration tank 10 Is fully processed.

上記第2曝気槽11の曝気室17は、仕切壁12に設けた送出管16の近傍下方位置にエアを噴出する、前記エア管15と同様のエア管23を設けている。これにより第1曝気槽10から送出管16を介して供給される中間処理水は、第2曝気槽11内の上流側から噴出されるエアによって木材チップBと攪拌混合されながら曝気処理される。   The aeration chamber 17 of the second aeration tank 11 is provided with an air tube 23 similar to the air tube 15 for injecting air to a lower position in the vicinity of the delivery tube 16 provided on the partition wall 12. As a result, the intermediate treated water supplied from the first aeration tank 10 via the delivery pipe 16 is aerated while being mixed with the wood chips B by air jetted from the upstream side in the second aeration tank 11.

排出室19はタンク右壁の上部に、第2曝気槽11で処理された処理水(処理浄水)を排出する送出管25を前記送出管16と略同じ高さ位置に設けている。曝気タンク2内の第1曝気槽10と第2曝気槽11の液面高さは、接続管13より所定距離だけ下位において略一定高さ位置に維持される。   In the discharge chamber 19, a delivery pipe 25 that discharges treated water (treated water) treated in the second aeration tank 11 is provided at substantially the same height as the delivery pipe 16 at the upper part of the right wall of the tank. The liquid level heights of the first aeration tank 10 and the second aeration tank 11 in the aeration tank 2 are maintained at a substantially constant height position below the connection pipe 13 by a predetermined distance.

この排出室19は送出管25と隔壁20の間に、排出室19内の底部側にある中間処理水の一部を第1曝気槽10に返送する返送装置26を設置している。図示例の返送装置26は逆L字状の返送管27とエア管29とからなる。
上記返送管27は横管部を液面より上方に位置させて隔壁20と仕切壁12の中央部に嵌挿して支持すると共に、縦管部を隔壁20に近接して垂設し拡開状に形成した下端開口部を吸込口30とし、流入間隔22の近傍に臨ませている。
In the discharge chamber 19, a return device 26 is installed between the delivery pipe 25 and the partition wall 20 to return a part of the intermediate treated water on the bottom side in the discharge chamber 19 to the first aeration tank 10. The return device 26 in the illustrated example includes an inverted L-shaped return tube 27 and an air tube 29.
The return pipe 27 has a horizontal pipe portion positioned above the liquid level and is inserted into and supported by the central portion of the partition wall 20 and the partition wall 12, and a vertical pipe portion is provided close to the partition wall 20 so as to expand. The lower end opening formed in FIG. 4 is used as a suction port 30 and faces the vicinity of the inflow interval 22.

エア管29はその開口端を返送管27の吸込口30内に臨ませて支持しており、前記エア圧送装置からエアを開口部30内に勢いよく送り込むことができる。この構成により返送管27内に強い上昇流を発生させることができ、前記流入間隔22を介して排出室19側に流入した直後の中間処理水(第2処理水)の一部を導いて吸い上げ、第1曝気槽10に返送すると共に管路内で中間処理水を激しく攪拌し曝気処理を効果的に行う。   The air pipe 29 is supported with its open end facing the suction port 30 of the return pipe 27, and air can be vigorously fed into the opening 30 from the air pressure feeding device. With this configuration, a strong upward flow can be generated in the return pipe 27 and a part of the intermediate treated water (second treated water) immediately after flowing into the discharge chamber 19 through the inflow interval 22 is guided and sucked up. Then, the aeration tank is returned to the first aeration tank 10 and the intermediate treatment water is vigorously stirred in the pipe to effectively perform the aeration treatment.

この実施形態においては、仕切壁12と曝気タンク2の右壁に略同じ高さ位置に取付支持される、横向きパイプからなる送出管16と送出管25は、それぞれの送り込み側に縦向きパイプの中途部を接続しT型管を構成している。この構成により送出管16と送出管25が有する縦管は、下部縦管部31の開口部を液面(水面)から60cm程度の深さ位置から、浮遊物の混入を防止して汲み出すように送水することができる。   In this embodiment, the delivery pipe 16 and the delivery pipe 25 made of horizontal pipes, which are mounted and supported at substantially the same height position on the partition wall 12 and the right wall of the aeration tank 2, are provided with vertical pipes on the respective feeding sides. The middle part is connected to form a T-shaped tube. With this configuration, the longitudinal pipes of the delivery pipe 16 and the delivery pipe 25 are designed to pump out the opening of the lower longitudinal pipe section 31 from a depth position of about 60 cm from the liquid surface (water surface) while preventing the entry of suspended matter. Can be sent to the water.

また上部縦管部32の開口部は水面から略25cm程度の高さに設定することにより、水面の変動や波立ちに対しても浮遊物の侵入を規制することができる。
さらに下部縦管部31と上部縦管部32は上下にストレートに開口させるので、上方から管内及び送出管16,送出管25の清掃等を簡単に行うことができる。
In addition, by setting the opening of the upper vertical pipe portion 32 at a height of about 25 cm from the water surface, it is possible to regulate the invasion of suspended matter even when the water surface fluctuates or waves.
Further, since the lower vertical pipe portion 31 and the upper vertical pipe portion 32 are opened straight up and down, the inside of the pipe and the delivery pipe 16 and the delivery pipe 25 can be easily cleaned from above.

尚、送出管16と送出管25の設置数と位置は、曝気タンク2の大きさ及び形状並びに処理量に応じて適宜に設定することができる。また各管路の直径は10cm程度以上であることが望ましい。また返送装置26は返送管27内にエアを圧送し上昇流を発生させる方式としたが、第2曝気槽11内の中間処理水を別方式のポンプ装置によって第1曝気槽10に返送することもできる。   The number and positions of the delivery pipes 16 and delivery pipes 25 can be appropriately set according to the size and shape of the aeration tank 2 and the processing amount. Moreover, it is desirable that the diameter of each pipe line is about 10 cm or more. In addition, the return device 26 is a method in which air is pumped into the return pipe 27 to generate an upward flow, but the intermediate treated water in the second aeration tank 11 is returned to the first aeration tank 10 by another type of pump device. You can also.

また図示例のように構成した曝気タンク2は、比較的小型の場合には一般的に市販されて家庭用或いは業務用等として使用される糞尿処理タンク(浄化槽)を利用することができる。この場合には、糞尿処理タンク内に仕切壁12及び隔壁20,返送装置26等を追加加工をする等の簡単な改造手段によって、第1曝気槽10及び第2曝気槽11等を浄化槽内に纏めて廉価に製造でき、また部分改良型によって設置工事等も行い易くなる等の利点がある。   Further, when the aeration tank 2 configured as shown in the drawing is relatively small, a manure processing tank (septic tank) that is generally marketed and used for home use or business use can be used. In this case, the first aeration tank 10, the second aeration tank 11, etc. are put into the septic tank by simple modification means such as additional processing of the partition wall 12, the partition wall 20, the return device 26, etc. in the manure processing tank. There are advantages such that they can be manufactured together at low cost, and the installation work etc. can be easily performed by the partial improvement type.

また曝気タンク2内を仕切壁12によって区画し第1曝気槽10と第2曝気槽11を横向きの一体構造によって製造される曝気タンク2は、第1曝気槽10と第2曝気槽11との上壁側に、それぞれ開閉可能な蓋を有する作業口33,33を設けている。
これにより横長で高さを低くすることができる曝気タンク2は、各作業口33から対応する内部の清掃や点検等のメンテナンス作業を簡単に行うことができる。
さらに上記大きさ程度以上の曝気タンク2或いは特殊な設置方式の曝気タンク2を構成したい場合には、防水構造のコンクリート製又はFRP製によって製造することができ、また第1曝気槽10と第2曝気槽11を分離した構造によって製造するときは、両者はパイプによって接続される。
In addition, the aeration tank 2 that is partitioned by the partition wall 12 and is manufactured by the horizontal integrated structure of the first aeration tank 10 and the second aeration tank 11 includes the first aeration tank 10 and the second aeration tank 11. Working ports 33 and 33 each having a lid that can be opened and closed are provided on the upper wall side.
Accordingly, the aeration tank 2 that is horizontally long and can be lowered in height can easily perform maintenance work such as internal cleaning and inspection from each work port 33.
Further, when it is desired to configure the aeration tank 2 having the above size or a special installation type aeration tank 2, it can be manufactured by waterproof concrete or FRP, and the first aeration tank 10 and the second aeration tank 10 When manufacturing the aeration tank 11 by the structure which isolate | separated, both are connected by the pipe.

以上のように構成される曝気タンク2には、第1曝気槽10と第2曝気槽11に木材チップBが所定の割合で混入される。この実施形態では木材チップBの混入割合は、水の容量に対し10%程度にすることが望ましく、この場合に原水及び木質細片の攪拌対流を損なうことなく流動性を有し曝気処理を好適に行うことができる。   In the aeration tank 2 configured as described above, the wood chips B are mixed in the first aeration tank 10 and the second aeration tank 11 at a predetermined ratio. In this embodiment, the mixing ratio of the wood chips B is preferably about 10% with respect to the volume of water. In this case, the aeration process is suitable because it has fluidity without impairing the stirring convection of the raw water and the wood chips. Can be done.

先ず投入槽5から接続管13を介し原水が第1曝気槽10内に供給され、エア管15から圧送エアが噴出され浄水処理が開始される。これにより第1曝気槽10内で送出管16で設定される水面高さに貯留される原水は、一側(左側)の下部から吹き出して上昇するエアによって曝気作用が付与され、この上昇流によって矢印方向に対流を生じ、木材チップBを攪拌しながら循環する。   First, raw water is supplied from the charging tank 5 through the connecting pipe 13 into the first aeration tank 10, and pressure-feed air is ejected from the air pipe 15 to start the water purification process. As a result, the raw water stored at the water level set by the delivery pipe 16 in the first aeration tank 10 is given an aeration action by the air that blows out from the lower part on one side (left side), and this upward flow causes Convection occurs in the direction of the arrow, and the wood chip B is circulated with stirring.

このとき大容量の第1曝気槽10では、多量の原水が木材チップBと均質な攪拌が繰り返され且つ十分な処理時間をかけて処理され、第2曝気槽11での処理負荷を軽減することができる。また逐次又は間欠的に供給される原水の供給により、第1曝気槽10内の原水が一定の水位を越える量になると、下部縦管部31を介して送出管16から溢流し、第1曝気槽10による1次処理が行われた中間処理水として、第2曝気槽11の曝気室17内に供給される。   At this time, in the first aeration tank 10 having a large capacity, a large amount of raw water is repeatedly agitated with the wood chip B and treated with sufficient processing time, thereby reducing the processing load in the second aeration tank 11. Can do. Further, when the raw water in the first aeration tank 10 exceeds a certain level due to the supply of the raw water supplied sequentially or intermittently, it overflows from the delivery pipe 16 via the lower vertical pipe section 31 and the first aeration. The intermediate treated water subjected to the primary treatment by the tank 10 is supplied into the aeration chamber 17 of the second aeration tank 11.

そして、第2曝気槽11に供給される中間処理水は送出管25で設定される水位に達しながら、曝気室17内でエア管23から供給されるエアによる曝気作用を受ける。これにより中間処理水は木材チップBと共に曝気室17内で、前記第1曝気槽10と同様に対流を生じ循環する。   The intermediate treated water supplied to the second aeration tank 11 is subjected to the aeration action by the air supplied from the air pipe 23 in the aeration chamber 17 while reaching the water level set by the delivery pipe 25. As a result, the intermediate treated water is circulated in the aeration chamber 17 together with the wood chips B by convection in the same manner as in the first aeration tank 10.

上記中間処理水は矢印方向の対流によって隔壁20に沿って下降し誘導壁21に案内されて、曝気室17の底壁より高い位置で上流側(前側)のエア管23側に確実に方向変更するように案内し循環流を形成することができる。そして、上記形成される循環流は曝気室17の底壁に堆積しようとする夾雑物等を前側に移動させて、エア管23との間に山状をなすように一時的に堆積させることができる。   The intermediate treated water descends along the partition wall 20 by convection in the direction of the arrow and is guided to the guide wall 21, and the direction of the intermediate treated water is reliably changed to the upstream (front) air pipe 23 side at a position higher than the bottom wall of the aeration chamber 17. In this way, a circulating flow can be formed. Then, the circulating flow formed can be temporarily deposited so as to form a mountain shape with the air pipe 23 by moving the contaminants and the like to be deposited on the bottom wall of the aeration chamber 17 to the front side. it can.

従って、流入間隔22内及びその直前での夾雑物の堆積が防止され、流入間隔22から入り込む中間処理水が底壁に堆積する未処理の夾雑物等の排出室19内への排出移動を抑制し、且つ排出室19内での処理負荷を軽減することができる。
また排出室19内に流入した夾雑物は、流入間隔22の下手側に吸込口30を開口させた返送装置26の吸い込み流に導かれ、返送管27内に吸い上げられて管内の曝気処理を経ながら第1曝気槽10に返送される。
Accordingly, accumulation of contaminants in the inflow interval 22 and immediately before the inflow interval 22 is prevented, and the movement of discharge of untreated contaminants and the like accumulated in the bottom wall from the inflow interval 22 into the discharge chamber 19 is suppressed. In addition, the processing load in the discharge chamber 19 can be reduced.
Further, the foreign matter that has flowed into the discharge chamber 19 is guided to the suction flow of the return device 26 having the suction port 30 opened on the lower side of the inflow interval 22, sucked into the return tube 27, and subjected to aeration processing in the tube. While being returned to the first aeration tank 10.

そして、返送装置26によって夾雑物が除去された状態の排出室19内の中間処理水は、流入間隔22から入り込む中間処理水によって水位を押し上げら送出管25側に至る。
また中間処理水は返送管27内の送り込みエアによる攪拌や上昇流等の影響を受けることのない静置状態にすることができる。従って、返送装置26の設置に支障されず静的環境となる排出室19内で、中間処理水の沈降作用が促進され上方の送出管25から浮遊物の混入を規制したきれいな処理浄水を送り出すことができる。
Then, the intermediate treated water in the discharge chamber 19 in a state where the contaminants have been removed by the return device 26 is pushed up by the intermediate treated water entering from the inflow interval 22 and reaches the delivery pipe 25 side.
Further, the intermediate treated water can be placed in a stationary state without being affected by stirring, upward flow or the like caused by the air fed in the return pipe 27. Accordingly, in the discharge chamber 19 which is not disturbed by the installation of the return device 26 and becomes a static environment, the settling action of the intermediate treated water is promoted, and clean treated water with regulated mixing of floating substances is sent out from the upper delivery pipe 25. Can do.

即ち、排出室19では返送装置26の吸い込みによって、未処理の夾雑物及び固体(有機物)等が速やかに沈降して底壁に至り、第1曝気槽10への夾雑物除去返送と返送管27内での曝気処理が繰り返され、堆積物や浮遊物の残留を少なくした状態で分解処理を促進することができる。尚、吸込口30は図3の点線で示すように流入間隔22の下流側に沿って広幅に形成すると、1本の返送管27によっても大型の第2曝気槽11に対して廉価に対応させることができる。   That is, in the discharge chamber 19, untreated contaminants and solids (organic matter) are quickly settled down to the bottom wall by suction of the return device 26, and the contaminant removal return to the first aeration tank 10 and the return pipe 27 are performed. The aeration process in the inside is repeated, and the decomposition process can be promoted in a state where the deposits and the suspended matter are reduced. If the suction port 30 is formed wide along the downstream side of the inflow interval 22 as shown by the dotted line in FIG. 3, the single return pipe 27 can correspond to the large second aeration tank 11 at low cost. be able to.

また曝気タンク2は従来のもののように、浮遊物や堆積物等を曝気タンク2の外に廃棄する分離装置等の設置を必要とすることなく、簡潔な構成によって送出管25から次工程の反応槽4等への直接的な送水を可能にすることができる。従って、処理施設の簡単な循環系を構成することができる等の利点がある。   Further, the aeration tank 2 does not require the installation of a separation device or the like for discarding suspended matter or deposits to the outside of the aeration tank 2, unlike the conventional one, and the reaction of the next process is performed from the delivery pipe 25 with a simple configuration. It is possible to enable direct water supply to the tank 4 or the like. Therefore, there is an advantage that a simple circulation system of the treatment facility can be configured.

上記のように構成され汚泥水を処理することができる曝気タンク2は、図1で示すように複数台のものを直列的に接続することにより、処理上手側から供給される処理水を処理下手側に接続される各曝気タンク2によって、順次処理を重ね最終段の曝気タンク2から綺麗な処理浄水を取り出すことができる。尚、後述する実験例で示すように送水パイプ37を介して取り出した処理浄水は、原水が十分に浄水処理されて1次処理レベルでありながら、異臭もなく殆ど無臭にすることができた。   The aeration tank 2 configured as described above and capable of treating sludge water is connected to a plurality of tanks in series as shown in FIG. With each aeration tank 2 connected to the side, it is possible to take out the treated clean water from the aeration tank 2 at the final stage by sequentially repeating the treatment. In addition, as shown in the experiment example mentioned later, the process purified water taken out via the water supply pipe 37 was able to be made almost odorless without a strange smell, although raw water was fully purified and was a primary treatment level.

さらに図示例のように、例えば4台の曝気タンク2を直列的に接続し処理浄水を反応槽4に供給する場合、第1曝気槽10と第2曝気槽11は曝気タンク2内に一体的に構成することが望ましく、且つ曝気タンク2は互いに逆向き平行状に並べると、上流側の排出室19を下流側の第1曝気槽10に対面させることができ、該排出室19の送出管25を接続管として両者を短い管路で接続することができる。そして、最終段の曝気タンク2の排出室19には送水ポンプ35を設置し、処理浄水を切換バルブ36及び送水パイプ37,37を介して反応槽4に供給するように配管することができる。   Further, as shown in the illustrated example, for example, when four aeration tanks 2 are connected in series and treated water is supplied to the reaction tank 4, the first aeration tank 10 and the second aeration tank 11 are integrated into the aeration tank 2. If the aeration tanks 2 are preferably arranged in parallel and opposite directions, the upstream discharge chamber 19 can face the first aeration tank 10 on the downstream side, and the delivery pipe of the discharge chamber 19 is provided. Both can be connected by a short pipe line with 25 as a connecting pipe. A water feed pump 35 is installed in the discharge chamber 19 of the final stage aeration tank 2, and the treated purified water can be piped so as to be supplied to the reaction tank 4 via the switching valve 36 and the water feed pipes 37 and 37.

また4台分の曝気タンク2からなる1次処理装置3は、全体として平面視で方形状に纏めて設置することができ、且つ最上手側の曝気タンク2の長手方向(左右長さ)内に貯水槽6及び投入槽5を収めると、処理施設1の設置スペースの効率を高めることができる。
さらに1次処理装置3の両側にユンボ等の作業車両を走行させる通路38を、広巾で作業性のよい直線状に形成することができ、また通路38に沿って反応槽4を平行状に設置することができる。
Further, the primary processing device 3 composed of the four aeration tanks 2 can be installed in a square shape as a whole in plan view, and is within the longitudinal direction (left and right length) of the uppermost aeration tank 2. If the water storage tank 6 and the charging tank 5 are housed in the storage space 1, the efficiency of the installation space of the processing facility 1 can be increased.
Furthermore, a passage 38 for running a work vehicle such as a yumbo can be formed on both sides of the primary processing apparatus 3 in a straight line having a wide width and good workability, and the reaction tank 4 is installed in parallel along the passage 38. can do.

そして、投入槽5等を含む1次処理装置3と反応槽4は前後長さを等しくすることが容易で、処理施設1の全体を平面視で方形状にすることができる。この際反応槽4の前後長さは該反応槽4の左右巾を調整することにより、処理能力を確保しながら前記1次処理装置3と一致させることができ、土地の有効利用及び配管構造並びに施工作業等を簡単にすることができる。   The primary processing apparatus 3 including the charging tank 5 and the reaction tank 4 can easily have the same length in the front-rear direction, and the entire processing facility 1 can be formed in a square shape in plan view. At this time, the front and rear length of the reaction tank 4 can be matched with the primary treatment apparatus 3 while ensuring the processing capacity by adjusting the left and right width of the reaction tank 4, and the effective use of land, the piping structure, and Construction work and the like can be simplified.

次に図4を参照し曝気タンク2の別実施形態について説明する。尚、上記実施形態のものと同様な構成及び作用については説明を省略する。この曝気タンク2は1次処理装置3と第2曝気槽11を区画する仕切壁12は、水位レベルとなる上方を開放することにより、送出口16をタンク幅に形成し前記パイプからなる送出管を省略している。この仕切壁12は上辺の高さを前記曝気タンク2の送出管16と略同じ位置にすると共に、上辺を1次処理装置3の上流側に向けて湾曲状に屈曲させた送出辺14を形成している。   Next, another embodiment of the aeration tank 2 will be described with reference to FIG. In addition, description is abbreviate | omitted about the structure and effect | action similar to the thing of the said embodiment. The aeration tank 2 has a partition wall 12 that divides the primary treatment device 3 and the second aeration tank 11 by opening the upper part at the water level, thereby forming a delivery port 16 in the tank width, and a delivery pipe comprising the pipe. Is omitted. The partition wall 12 has an upper side whose height is substantially the same as that of the delivery pipe 16 of the aeration tank 2, and a delivery side 14 that is bent in a curved shape toward the upstream side of the primary processing device 3. is doing.

これにより仕切壁12を備える第1曝気槽10は、接続管13から供給され貯留する原水の上限水位を送出辺14の上端高さに規制し、送出辺14を越える曝気処理された処理原水を第2曝気槽11に送水することができる。また第2曝気槽11内に供給された中間処理水の水位は、仕切壁12の送出辺14よりやや低い位置に設置されている送出管25の位置で規制され、送出管25から送水することができる。   Thus, the first aeration tank 10 provided with the partition wall 12 regulates the upper limit water level of the raw water supplied and stored from the connection pipe 13 to the upper end height of the delivery side 14, and the treated raw water subjected to the aeration process exceeding the delivery side 14. Water can be supplied to the second aeration tank 11. Further, the level of the intermediate treated water supplied into the second aeration tank 11 is regulated at the position of the delivery pipe 25 installed at a position slightly lower than the delivery side 14 of the partition wall 12, and water is fed from the delivery pipe 25. Can do.

このとき送出辺14は上流側に向けて屈曲された先端部によって、第1曝気槽10側の原水をより上流側において浮遊物の流入を規制し送水させることができる。このときエア管15の曝気作用によって矢印方向に対流している原水は、送出辺14の形状に沿って下向きに案内されて浮遊物を下方に導き循環処理される。   At this time, the sending edge 14 can feed the raw water on the first aeration tank 10 side by regulating the inflow of floating substances on the upstream side by the tip portion bent toward the upstream side. At this time, the raw water convected in the direction of the arrow by the aeration action of the air pipe 15 is guided downward along the shape of the delivery side 14 to guide the suspended matter downward to be circulated.

尚、返送管27は送出辺14の上方を通し、その開口部を1次処理装置3の中途部上方に臨ませ第2曝気槽11の中間処理水を返送する構成としている。
また処理施設1の原水供給及び水位のコントロール等は、管理施設側から各種ポンプや切換バルブ等を自動及び手動操作によって任意に制御することができる。
The return pipe 27 is configured to pass through the upper side of the delivery side 14 and return the intermediate treated water in the second aeration tank 11 with the opening facing the middle part of the primary treatment device 3.
Further, the raw water supply and water level control of the treatment facility 1 can be arbitrarily controlled from the management facility by various automatic and manual operations of various pumps and switching valves.

次に図1,図5を参照し反応槽4について説明する。この反応槽4は縦横の長さを前記程度に設定し、且つ高さ(深さ)を300cm程度にしており、この場合高さの2分の1程度を地盤を掘削して埋設施工し、地表に突出する周壁40の外側に盛土部41を施工して囲うことが望ましい。   Next, the reaction tank 4 will be described with reference to FIGS. This reaction tank 4 has the vertical and horizontal lengths set to the above-mentioned levels, and the height (depth) is set to about 300 cm. In this case, about half of the height is excavated from the ground and buried. It is desirable to construct and fill the embankment 41 on the outside of the peripheral wall 40 protruding to the ground surface.

また反応槽4は長手方向上手側(処理方向上手側)に前記送水パイプ37が接続され、処理方向下手側の適所に取出槽42が設置される。
取出槽42は反応槽4より深くなるように井戸状に区画形成されており、下り傾斜状に形成された反応槽4の底部43から管路44を介して接続している。取出槽42は内部に吸水ポンプ45の吸水管46を底部に近接させて設け、吸水ポンプ45の送水管47を貯水槽6に接続している。
Further, the water tank 37 is connected to the reaction tank 4 on the upper side in the longitudinal direction (upper side in the processing direction), and the take-out tank 42 is installed at an appropriate position on the lower side in the processing direction.
The take-out tank 42 is partitioned and formed in a well shape so as to be deeper than the reaction tank 4, and is connected via a conduit 44 from the bottom 43 of the reaction tank 4 formed in a downward inclined shape. The take-out tank 42 is provided inside with a water absorption pipe 46 of the water absorption pump 45 close to the bottom, and a water supply pipe 47 of the water absorption pump 45 is connected to the water storage tank 6.

以上のように構成される反応槽4は、例えば深さを300cm程度にする場合、微生物の菌床材となる前記木材チップAが、底部43側から250cm程度の層厚をなすチップ処理層を形成するように供給され敷き詰めた状態で充填される。
反応槽4に対する木材チップAの供給作業は、図示しないユンボを通路38を走行移動させて簡単に投入作業することができ、投入される木材チップAは逐次踏み固められながら全体が均質な密度となるように充填される。
In the reaction tank 4 configured as described above, for example, when the depth is set to about 300 cm, the wood chip A serving as a microbial bed material has a chip treatment layer having a layer thickness of about 250 cm from the bottom 43 side. It is supplied to form and filled in a spread state.
The supply operation of the wood chips A to the reaction tank 4 can be performed easily by moving a jumbo (not shown) through the passage 38, and the wood chips A to be input are made to have a uniform density as a whole while being sequentially stepped and compacted. It is filled to become.

木材チップAが充填された反応槽4は、前記中間処理水を処理した処理浄水が送水パイプ37から供給され、反応槽用の原水(被処理水)としてチップ処理層の表面に散水することができる。尚、送水パイプ37には点線で示すように散水パイプ39が設けられ、広い表面に対し均一な散水を行うことができる。   In the reaction tank 4 filled with the wood chips A, treated purified water obtained by treating the intermediate treated water is supplied from the water supply pipe 37 and sprayed on the surface of the chip treatment layer as raw water for the reaction tank (treated water). it can. The water supply pipe 37 is provided with a water spray pipe 39 as shown by a dotted line, and uniform water spray can be performed on a wide surface.

これによりチップ処理層は原水を表面側から均質に濾過させて通すことができ、原水が下方に至るに従い木材チップAによる浄水処理を行う。このように浄水処理が行われるに伴い、チップ処理層は原水の分解並びに微生物作用によって、後述する好気性嫌気性処理層50を底部43側から190cm程度の層厚となして形成し、且つ好気性嫌気性処理層50の上方に好気性処理層51を60cm程度の層厚で形成することができる。   Thereby, the chip treatment layer can filter the raw water from the surface side and pass it through, and performs the water purification treatment with the wood chip A as the raw water reaches the lower side. As the water purification treatment is performed in this way, the chip treatment layer is formed by forming the aerobic anaerobic treatment layer 50 described later with a layer thickness of about 190 cm from the bottom 43 side by decomposition of the raw water and microbial action. The aerobic treatment layer 51 can be formed with a layer thickness of about 60 cm above the aerobic anaerobic treatment layer 50.

また原水は好気性処理層51から好気性嫌気性処理層50を、浄水処理に必要とされる適正な処理時間を経て通る間に浄水処理された浄水となり底部43に至る。そして、処理済の浄水は底部43の下り傾斜に案内され停滞することなく、管路44から取出槽42に流入し貯留される。   Further, the raw water becomes purified water that has been subjected to water purification treatment from the aerobic treatment layer 51 through the aerobic anaerobic treatment layer 50 through an appropriate treatment time required for water purification treatment, and reaches the bottom 43. Then, the treated purified water is guided by the downward slope of the bottom 43 and flows into the take-out tank 42 from the pipeline 44 without stagnation.

次いで取出槽42に溜まる浄水は、吸水管46を介し吸水ポンプ45によって適時に汲み上げられ貯水槽6に貯留される。この貯水槽6に溜められる浄水は外部に取り出して任意な用途に有効利用することができると共に、浄水の一部を曝気タンク2側の原水を希釈する希釈水として投入槽5内に供給して循環利用される。尚、上記浄水は反応槽4からそのまま放流することもできる。   Next, the purified water collected in the take-out tank 42 is pumped up in time by the water absorption pump 45 through the water absorption pipe 46 and stored in the water storage tank 6. The purified water stored in the water storage tank 6 can be taken out and used effectively for any purpose, and a part of the purified water is supplied into the input tank 5 as dilution water for diluting the raw water on the aeration tank 2 side. It is recycled. The purified water can also be discharged from the reaction tank 4 as it is.

この反応槽4に充填する木材チップAは、前記特許文献2で示されるものと同様の木質細片をチップ処理層用の濾過材として利用したので、微生物並びに細菌類が各々その種類に応じそれぞれの生育や繁殖に適応する固有の条件を有し、原水の供給に伴う環境におけるph値や栄養分,温度等の変化に適応して増殖する。   Since the wood chip A filled in the reaction tank 4 uses the same wood chips as those shown in Patent Document 2 as a filter medium for the chip treatment layer, microorganisms and bacteria are each in accordance with the type thereof. It has a unique condition that adapts to the growth and reproduction of the fish, and adapts to changes in the ph value, nutrients, temperature, etc. in the environment accompanying the supply of raw water.

また木材チップAからなるチップ処理層は原水反応処理槽として大きな表面積を形成することができ、且つ保湿,保温性に優れ有機汚泥の生物学的処理を促進する。さらにチップ処理層は長期間の処理に際しても、木材チップAが木質本来の有機的な生体組織を長期間に渡って維持するので、目詰まりを生じ難く濾過材の交換や清掃等のメンテナンス作業を省力できる、浄水処理を安定的に高性能に行うことができる。   In addition, the chip treatment layer made of wood chips A can form a large surface area as a raw water reaction treatment tank, and is excellent in moisture retention and heat retention and promotes biological treatment of organic sludge. Furthermore, since the chip processing layer maintains the original organic living tissue of wood for a long period of time even during long-term processing, maintenance work such as replacement or cleaning of filter media is difficult to cause clogging. Water-saving treatment can be performed stably and with high performance.

そして、木材チップAを充填した反応槽4は、浄水処理を行うに伴い上層のチップ処理層に好気性菌が主体として棲息する好気性処理層51と、下層の深層に至るに従い木材チップAに好気性菌と嫌気性が混在した状態で嫌気性菌が増大する好気性嫌気性処理層50とを前記層厚の割合で形成することができる。   And the reaction tank 4 filled with the wood chip A has an aerobic treatment layer 51 in which aerobic bacteria mainly reside in the upper chip treatment layer as the water purification process is performed, and the wood chip A as it reaches the lower layer. An aerobic anaerobic treatment layer 50 in which anaerobic bacteria increase in a state where aerobic bacteria and anaerobic coexist can be formed at a ratio of the layer thickness.

これによりチップ処理層の表面に散水供給される原水は、先ず好気性処理層51に棲息する好気性菌によって好気性処理されたのち、好気性嫌気性処理層50を通過する間に好気菌と嫌気性菌が混在し下層に至るに従い嫌気性菌が増大する、両性菌による浄水処理が好適に行なわれて浄水にすることができる。   As a result, the raw water supplied to the surface of the chip treatment layer is first subjected to aerobic treatment by aerobic bacteria living in the aerobic treatment layer 51 and then passed through the aerobic anaerobic treatment layer 50. An anaerobic bacterium is mixed and the anaerobic bacterium increases as it reaches the lower layer, and water purification treatment with the amphoteric bacterium is suitably performed to obtain purified water.

次に図1で示す方式の処理施設1によって、豆腐製造時に生ずるオカラ汚泥水を浄水処理した実験例について説明する。この例では投入槽5に投入したオカラを反応槽4から回収した前記浄水で希釈させたオカラ廃棄汚泥水を原水とした。また使用する曝気タンク2は液体貯留容量が4トン程度の大きさであり、木材チップBを前記割合で混入した。   Next, an experimental example in which the okara sludge water produced during the production of tofu is purified by the treatment facility 1 of the method shown in FIG. 1 will be described. In this example, the okara waste sludge water obtained by diluting the okara charged in the charging tank 5 with the purified water recovered from the reaction tank 4 was used as raw water. Moreover, the aeration tank 2 to be used has a liquid storage capacity of about 4 tons, and the wood chips B are mixed in the above ratio.

そして、1次処理装置3は3台分の曝気タンク2を前記構成によって直列的に接続した構成とし、投入槽5内の原水を上流側の曝気タンク2に供給し最下流側の曝気タンク2から、処理済の処理浄水を送水パイプ37によって反応槽4に供給した。反応槽4は前記実施形態のものと同様に高さが300cm程度で、内部に充填する木材チップAの量を60m3程度としてチップ処理層を形成した。 The primary processing apparatus 3 has a configuration in which three aeration tanks 2 are connected in series according to the above-described configuration, and the raw water in the charging tank 5 is supplied to the upstream aeration tank 2 to supply the most downstream aeration tank 2. Then, treated treated water was supplied to the reaction tank 4 through a water pipe 37. The reaction tank 4 had a height of about 300 cm as in the previous embodiment, and the chip processing layer was formed with the amount of wood chips A filled therein being about 60 m 3 .

上記実験値を表1に示す。尚、表中において浄水処理前に計量した試料は投入槽5内の原水であり、処理後に計量した試料は貯水槽6に回収された浄水である。また曝気処理後に計量した試料は最下流側の曝気タンク2から送水パイプ37を介して取り出した処理浄水である。   The experimental values are shown in Table 1. In the table, the sample weighed before the water purification treatment is the raw water in the charging tank 5, and the sample weighed after the treatment is the purified water collected in the water storage tank 6. The sample weighed after the aeration treatment is treated purified water taken out from the most downstream aeration tank 2 through the water supply pipe 37.

Figure 2006326387
Figure 2006326387

上記のように処理されて得られる浄水は、下水への放流基準値及び河川放流基準値を何れも大幅にクリヤーする好結果が確認された。また浮遊物等を予め除去する特別な分離装置を必要としない曝気タンク2を備えた簡単な1次処理装置3によって、計量対象値を廉価に低減することも確認できた。また従来浄水処理を行うことが困難とされているオカラ汚泥水の処理にも有効であることが明らかとなった。同様に牛乳加工廃液等に対しても応用可能であると考えられる。   The purified water obtained by the treatment as described above was confirmed to have a clear result that both the discharge standard value to the sewage and the river discharge standard value were significantly cleared. It was also confirmed that the measurement target value can be reduced at a low cost by the simple primary processing device 3 provided with the aeration tank 2 that does not require a special separation device for removing suspended matters or the like in advance. Moreover, it became clear that it is effective also for the treatment of Okara sludge water, which has been conventionally difficult to purify. Similarly, it can be applied to milk processing waste liquids and the like.

また反応槽4は曝気タンク2によって前処理された処理水を木材チップAからなるチップ処理層を通して浄水処理し貯水槽6に貯留するので、浄水の排水や液肥製造或いは作物栽培等への排水利用を行い易くすることができる。   Moreover, since the reaction tank 4 purifies the treated water pretreated by the aeration tank 2 through the chip treatment layer made of wood chips A and stores it in the water storage tank 6, the drainage of purified water, the production of liquid fertilizer or the use of wastewater for crop cultivation, etc. Can be made easier.

本発明に係わる処理装置の構成を示す平面図である。It is a top view which shows the structure of the processing apparatus concerning this invention. 曝気タンクの構成を示す側断面図である。It is a sectional side view showing the composition of an aeration tank. 図2の平断面図である。FIG. 3 is a plan sectional view of FIG. 2. 曝気タンクの別実施形態の構成を示す側断面図である。It is a sectional side view which shows the structure of another embodiment of an aeration tank. 反応槽の構成を示す正断面図である。It is front sectional drawing which shows the structure of a reaction tank.

符号の説明Explanation of symbols

1 処理装置(処理施設)
2 曝気タンク
3 1次処理装置
4 反応槽
5 投入槽
6 貯水槽
10 第1曝気槽
11 第2曝気槽
12 仕切壁
13 供給口(接続管)
15,23,29 エア管
16,25 送出口(送出管)
20 隔壁
21 誘導壁
22 流入口(流入間隔)
26 返送装置
27 返送管
30 吸込口
31 下部縦管部
32 上部縦管部
37 送水パイプ
A,B 木材チップ(木質細片)
1 processing equipment (processing facility)
2 Aeration tank 3 Primary treatment device 4 Reaction tank 5 Input tank 6 Water storage tank 10 First aeration tank 11 Second aeration tank 12 Partition wall 13 Supply port (connection pipe)
15, 23, 29 Air pipe 16, 25 Outlet (delivery pipe)
20 Bulkhead 21 Guide wall 22 Inlet (inflow interval)
26 Return device 27 Return tube 30 Suction port 31 Lower vertical tube portion 32 Upper vertical tube portion 37 Water supply pipes A and B Wood chips (woody fine pieces)

Claims (5)

貯留する原水を曝気処理して送出口(16)から流出させる第1曝気槽(10)と、第1曝気槽(10)から流入する中間処理水を曝気処理し送出口(25)から外部に流出させる第2曝気槽(11)からなる曝気タンク(2)において、前記第2曝気槽(11)の送出口(25)側のタンク底壁に吸込口(30)を近接させて開口する返送装置(26)の返送管(27)を設け、第2曝気槽(11)の中間処理水を吸込口(30)から返送管(27)を介し第1曝気槽(10)に返送する構成とした曝気タンク構造。   The first aeration tank (10) for aerating the stored raw water to flow out from the delivery port (16), and the intermediate treated water flowing in from the first aeration tank (10) is aerated and sent from the delivery port (25) to the outside. In the aeration tank (2) composed of the second aeration tank (11) to be discharged, the return is opened by bringing the suction port (30) close to the tank bottom wall on the delivery port (25) side of the second aeration tank (11). A structure in which a return pipe (27) of the device (26) is provided, and intermediate treated water in the second aeration tank (11) is returned from the suction port (30) to the first aeration tank (10) through the return pipe (27). Aeration tank structure. 第2曝気槽(11)内の上流側と下流側にエア管(15)と返送管(27)を設け、該エア管(15)と返送管(27)の間に隔壁(20)を設けて、上流側の曝気室(17)と下流側の排出室(19)を区画して形成すると共に、隔壁(20)の下辺を上流側に屈曲して形成した誘導壁(21)とタンク底壁との間に、曝気室(17)と排出室(19)を連通させる流入間隔(22)を形成した請求項1の曝気タンク構造。   An air pipe (15) and a return pipe (27) are provided upstream and downstream in the second aeration tank (11), and a partition wall (20) is provided between the air pipe (15) and the return pipe (27). In addition, the upstream aeration chamber (17) and the downstream discharge chamber (19) are partitioned and formed, and the guide wall (21) formed by bending the lower side of the partition wall (20) upstream and the tank bottom 2. The aeration tank structure according to claim 1, wherein an inflow interval (22) is formed between the wall and the aeration chamber (17) and the discharge chamber (19). 返送管(27)の吸込口(30)内にエアを噴出するエア管(29)を設け、該エアによって返送管(27)内に上昇流を発生させ、排出室(19)底壁側の中間処理水を導き第1曝気槽(10)に返送する請求項1又は2の曝気タンク構造。   An air pipe (29) for ejecting air is provided in the suction port (30) of the return pipe (27), and an upward flow is generated in the return pipe (27) by the air, and the discharge chamber (19) on the bottom wall side The aeration tank structure according to claim 1 or 2, wherein the intermediate treated water is guided and returned to the first aeration tank (10). 曝気タンク(2)内で送出口(16)を備える仕切壁(12)によって、第1曝気槽(10)と第2曝気槽(11)を区画形成し、第1曝気槽(10)と第2曝気槽(11)の上部にメンテナンス作業用の作業口(33)を設けた請求項1又は2又は3の曝気タンク構造。   The first aeration tank (10) and the second aeration tank (11) are partitioned by the partition wall (12) having the delivery port (16) in the aeration tank (2), and the first aeration tank (10) and the first aeration tank (10) The aeration tank structure according to claim 1, 2 or 3, wherein a work port (33) for maintenance work is provided in an upper part of the two aeration tanks (11). 送出口(16)又は送出口(25)を横向きのパイプからなる送出管で形成し、送出管の送り込み側に下部縦管部(31)と上部縦管部(32)を形成する縦向きパイプの中途部を連結し、下部縦管部(31)と上部縦管部(32)の開口部を、それぞれ液面から所定の深さ及び高さに位置させる請求項1又は2又は3又は4の曝気タンク構造。   A longitudinal pipe in which the delivery port (16) or the delivery port (25) is formed by a delivery pipe made of a horizontal pipe, and a lower longitudinal pipe part (31) and an upper longitudinal pipe part (32) are formed on the feeding side of the delivery pipe. The intermediate part is connected, and the opening part of a lower vertical pipe part (31) and an upper vertical pipe part (32) is each located in predetermined depth and height from a liquid level, Claim 1, 2 or 3 or 4 Aeration tank structure.
JP2005149354A 2005-05-23 2005-05-23 Aeration tank structure Expired - Fee Related JP4848139B2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012193506A (en) * 2011-03-15 2012-10-11 Morita Holdings Corp Tank and sludge collecting vehicle loaded with tank
CN108911115A (en) * 2018-08-24 2018-11-30 中国海洋大学 High efficient solid and liquid separation biofilter
KR102209325B1 (en) * 2020-10-28 2021-01-29 주식회사 대한엔지니어링 Reactor for advanced treatment equipment with a structure to secure microbial residence time to improve river water quality

Citations (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5522325A (en) * 1978-08-07 1980-02-18 Nippon Steel Chem Co Ltd Waste liquid treatment using active sludge
JPS5522324A (en) * 1978-08-07 1980-02-18 Nippon Steel Chem Co Ltd Waste liquid treatment using active sludge
JPS5621692A (en) * 1979-07-31 1981-02-28 Nikko Kk Purifying tank
JPS6363194A (en) * 1986-09-02 1988-03-19 Sony Corp Driving device for sense amplifier for dynamic ram
JPH02218498A (en) * 1989-02-17 1990-08-31 Toyo Baioriakutaa Kk Packing body for purifying tank
JPH06238287A (en) * 1993-02-19 1994-08-30 Toto Ltd Membrane treatment device for purification tank and purification tank
JPH07124582A (en) * 1993-10-29 1995-05-16 Ebara Res Co Ltd Aerobic treatment tank and soil water treatment process using tank
JPH07171582A (en) * 1993-12-22 1995-07-11 Kanae:Kk Purifying tank for combination treatment
JPH09285796A (en) * 1996-04-22 1997-11-04 Daiichi Kankyo Kk Purifier
JPH1034180A (en) * 1996-07-23 1998-02-10 Souwa Eng:Kk Apparatus for biological treatment of waste water
JPH10290990A (en) * 1997-04-22 1998-11-04 Matsushita Electric Works Ltd Combined septic tank
JPH11165172A (en) * 1997-12-05 1999-06-22 Inax Corp Membrane separation purification tank and drainage treatment method using the tank
JP2002362493A (en) * 2001-03-27 2002-12-18 Evac Internatl Oy Sewage treatment device

Patent Citations (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5522325A (en) * 1978-08-07 1980-02-18 Nippon Steel Chem Co Ltd Waste liquid treatment using active sludge
JPS5522324A (en) * 1978-08-07 1980-02-18 Nippon Steel Chem Co Ltd Waste liquid treatment using active sludge
JPS5621692A (en) * 1979-07-31 1981-02-28 Nikko Kk Purifying tank
JPS6363194A (en) * 1986-09-02 1988-03-19 Sony Corp Driving device for sense amplifier for dynamic ram
JPH02218498A (en) * 1989-02-17 1990-08-31 Toyo Baioriakutaa Kk Packing body for purifying tank
JPH06238287A (en) * 1993-02-19 1994-08-30 Toto Ltd Membrane treatment device for purification tank and purification tank
JPH07124582A (en) * 1993-10-29 1995-05-16 Ebara Res Co Ltd Aerobic treatment tank and soil water treatment process using tank
JPH07171582A (en) * 1993-12-22 1995-07-11 Kanae:Kk Purifying tank for combination treatment
JPH09285796A (en) * 1996-04-22 1997-11-04 Daiichi Kankyo Kk Purifier
JPH1034180A (en) * 1996-07-23 1998-02-10 Souwa Eng:Kk Apparatus for biological treatment of waste water
JPH10290990A (en) * 1997-04-22 1998-11-04 Matsushita Electric Works Ltd Combined septic tank
JPH11165172A (en) * 1997-12-05 1999-06-22 Inax Corp Membrane separation purification tank and drainage treatment method using the tank
JP2002362493A (en) * 2001-03-27 2002-12-18 Evac Internatl Oy Sewage treatment device

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012193506A (en) * 2011-03-15 2012-10-11 Morita Holdings Corp Tank and sludge collecting vehicle loaded with tank
CN108911115A (en) * 2018-08-24 2018-11-30 中国海洋大学 High efficient solid and liquid separation biofilter
KR102209325B1 (en) * 2020-10-28 2021-01-29 주식회사 대한엔지니어링 Reactor for advanced treatment equipment with a structure to secure microbial residence time to improve river water quality

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