JPH0824890A - Anaerobic treatment device - Google Patents
Anaerobic treatment deviceInfo
- Publication number
- JPH0824890A JPH0824890A JP16364394A JP16364394A JPH0824890A JP H0824890 A JPH0824890 A JP H0824890A JP 16364394 A JP16364394 A JP 16364394A JP 16364394 A JP16364394 A JP 16364394A JP H0824890 A JPH0824890 A JP H0824890A
- Authority
- JP
- Japan
- Prior art keywords
- magnetic powder
- pipe
- processing container
- extraction
- waste water
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- Y02W10/12—
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は有機性産業廃水を嫌気性
微生物によって生物学的に処理するための嫌気性処理装
置に係り、特に、高濃度の懸濁物を含む有機性産業廃水
を効果的に処理するための嫌気性処理装置に関するもの
である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an anaerobic treatment apparatus for biologically treating organic industrial wastewater with anaerobic microorganisms, and more particularly to organic industrial wastewater containing a high concentration of suspension. The present invention relates to an anaerobic treatment device for treating anaerobically.
【0002】[0002]
【従来の技術】従来、溶解性有機物を含む有機性産業廃
水を処理するための方法としては嫌気性微生物を用いた
方法がある。これは、有機性産業廃水中の溶解性有機物
をメタン生成細菌等の嫌気性微生物で生物学的に分解処
理するものであり、例えば、図4に示すような嫌気性処
理装置によって処理されている。この嫌気性処理装置
は、上記嫌気性微生物が高密度に集積したグラニュール
(図示せず)が収容された処理容器aの下端部に、上記
有機性産業廃水を導入するための流入配管bを接続する
と共に、その内部に気液分離手段c等を備えたものであ
り、流入配管bから導入された有機性産業廃水を上昇流
で流しつつ、上記嫌気性微生物によって有機性産業廃水
中の溶解性有機物を生物学的に分解処理し、CO2やメ
タンを主成分とするバイオガスと処理水とをその上端部
から排出するものである。2. Description of the Related Art Conventionally, as a method for treating organic industrial wastewater containing soluble organic substances, there is a method using anaerobic microorganisms. This is for biologically decomposing soluble organic substances in organic industrial wastewater with anaerobic microorganisms such as methanogenic bacteria. For example, it is treated by an anaerobic treatment apparatus as shown in FIG. . In this anaerobic treatment apparatus, an inflow pipe b for introducing the organic industrial wastewater is provided at a lower end portion of a treatment container a in which granules (not shown) in which the anaerobic microorganisms are densely accumulated are stored. In addition to being connected, it is equipped with gas-liquid separation means c and the like inside, and while the organic industrial wastewater introduced from the inflow pipe b is allowed to flow in an upward flow, it is dissolved in the organic industrial wastewater by the anaerobic microorganisms. The organic substance is biologically decomposed, and biogas containing CO2 and methane as main components and treated water are discharged from the upper end thereof.
【0003】[0003]
【発明が解決しようとする課題】ところで、この嫌気性
処理装置による処理対象廃水は溶解性有機物主体の廃水
に略限定されており、汚泥等の懸濁物(SS:通常、廃
水をフィルターで濾過して得られた残滓をいい、単位は
mg/lで表す)を含む廃水には殆ど用いられないのが
現状である。すなわち、このSSが処理容器a内に流入
すると、この処理容器a内の一定部分を占有してしま
い、微生物によるグラニュールや生物膜が出来難くくな
り、有機物の分解速度が大巾に低下してしまうからであ
る。そこで、雨天下水処理等で用いられる磁気分離法等
を応用し、このSS中にマグネタイト等の磁性粉等を混
入して高密度化させ、高密度化したSSのみを処理容器
aに流入する前に廃水bから抜き出すことも考えられる
が、そのためには、大量の磁性粉、あるいはSSから磁
性粉を回収するための装置等を新たに設ける必要がある
ため、設置スペースの拡大やコストの上昇を招いてしま
う不都合があった。By the way, the wastewater to be treated by this anaerobic treatment apparatus is almost limited to the wastewater mainly composed of soluble organic substances, and a suspension of sludge (SS: usually, the wastewater is filtered by a filter). It is the present condition that it is hardly used for the wastewater containing the residue obtained in this way, the unit of which is expressed in mg / l. That is, when this SS flows into the processing container a, it occupies a certain part of the processing container a, making it difficult for granules and biofilms to be formed by microorganisms, and the decomposition rate of organic matter is greatly reduced. This is because it will end up. Therefore, by applying a magnetic separation method or the like used in rainwater sewage treatment, etc., to mix magnetic powder such as magnetite into this SS to densify it, and only the densified SS flows into the processing container a. It is also possible to extract the waste water from the waste water b, but for that purpose, it is necessary to newly install a large amount of magnetic powder or a device for recovering the magnetic powder from the SS, thus increasing the installation space and increasing the cost. There was an inconvenience to invite.
【0004】そこで、本発明は上記の問題点を有効に解
決するために案出されたものであり、その目的は設置ス
ペースの拡大やコストの上昇を招くことなく、SSを含
んだ有機性廃水でも効率良く処理することができる新規
な嫌気性処理装置を提供するものである。The present invention has been devised in order to effectively solve the above problems, and its purpose is to increase the installation space and cost without increasing the organic wastewater containing SS. However, it is intended to provide a novel anaerobic treatment device capable of efficiently treating.
【0005】[0005]
【課題を解決するための手段】上記目的を達成するため
に本発明は、溶解性有機物を含む有機性産業廃水を、下
端部から導入して上昇流で流し、上端部からオーバーフ
ローさせる処理容器内部に、上記有機性産業廃水中の溶
解性有機物を分解するための嫌気性微生物等を収容した
嫌気性処理装置において、上記処理容器内に上記有機性
産業廃水中の懸濁物を高密度化させる磁性粉を混入する
と共に、その下部に、高密度化したSSを抜き出すため
のSS抜出し管をこれより斜め上方に分岐させて接続
し、そのSS抜出し管の下方に、上記SSをエアリフト
させてSSから磁性粉をひきはがしつつSSを抜出すた
めのSS抜出し手段を設けると共に、その上方に、抜出
されるSS中の磁性粉を吸着して回収するための磁性粉
回収手段を設けたものであり、また、上記磁性粉回収手
段としては上記SS抜出し管を囲繞して設けられた電磁
石と、上記処理容器からオーバーフローした処理水の一
部を上記SS抜出し管内に逆流させる洗浄手段とからな
るものである。In order to achieve the above object, the present invention is directed to the inside of a processing vessel in which an organic industrial wastewater containing soluble organic matter is introduced from the lower end portion, flowed in an upward flow, and overflowed from the upper end portion. In the anaerobic treatment apparatus containing anaerobic microorganisms for decomposing soluble organic matter in the organic industrial wastewater, the suspension in the organic industrial wastewater is densified in the treatment container. In addition to mixing the magnetic powder, an SS extraction pipe for extracting the densified SS is connected to the lower part of the SS branch by branching diagonally upward from this, and the SS is air-lifted below the SS extraction pipe to SS. In addition to providing an SS withdrawing means for removing the SS while removing the magnetic powder from above, a magnetic powder collecting means for adsorbing and collecting the magnetic powder in the extracted SS is provided above it. The magnetic powder recovery means includes an electromagnet surrounding the SS withdrawal pipe and a cleaning means for causing a part of the treated water overflowing from the treatment container to flow back into the SS withdrawal pipe. It is a thing.
【0006】[0006]
【作用】本発明は上述した構成により、処理容器内に流
入した廃水中のSSは磁性粉によって高密度化して比重
が増大して処理容器内に濃縮した状態で存在することに
なり、従って占有体積としては小さくなる。これによっ
て、処理容器内に占めるSSの割合が従来技術ほどには
増大することがなくなり、嫌気性微生物による廃水中の
有機物の分解処理能力が低下することがない。また、こ
のSS抜出し手段の下方に設けたエアリフトによりSS
から磁性粉をひきはがし、次にこのSS抜き出し手段の
上方に設けられた磁性粉回収手段の電磁石が、抜出され
るSS中の磁性粉のみを分離し、これを洗浄手段によっ
て再び処理容器内に回収することになるため、磁性粉が
減少してしまうことがなく、余剰のSSを抜き出すこと
ができる。またSS抜出し管を処理容器の底から離して
設けることにより、処理容器内では沈降しやすいグラニ
ュールを引き抜かず、SSを選択的に引き抜くこともで
きる。According to the present invention, due to the above-mentioned constitution, SS in the waste water flowing into the processing container is densified by the magnetic powder to increase the specific gravity and exists in the processing container in a concentrated state. The volume becomes smaller. As a result, the proportion of SS in the treatment container does not increase as much as in the prior art, and the ability of anaerobic microorganisms to decompose and treat organic substances in wastewater does not decrease. In addition, an SS is provided by an air lift provided below the SS extraction means.
Then, the magnetic powder is removed from the SS, and then the electromagnet of the magnetic powder recovery means provided above the SS extraction means separates only the magnetic powder in the SS to be extracted, and this is washed again into the processing container by the cleaning means. Since the magnetic powder is collected, the surplus SS can be extracted without reducing the magnetic powder. Further, by providing the SS withdrawal tube away from the bottom of the processing container, it is possible to selectively withdraw SS without extracting the granules that tend to settle in the processing container.
【0007】[0007]
【実施例】以下、本発明の一実施例を添付図面に基づい
て詳述する。An embodiment of the present invention will be described in detail below with reference to the accompanying drawings.
【0008】図1は本発明に係る嫌気性処理装置の一実
施例を示したものである。図示するように、この嫌気性
処理装置は従来と略同様な構成をしており、略円柱状を
した処理容器1の下端部にSSを含んだ有機性産業廃水
を導入するための流入配管2が接続されると共に、上端
部に処理水をオーバーフローする流出管3と、バイオガ
スを排気する排気管4がそれぞれ接続され、流入配管2
から流入した廃水を上昇流で流すようになっている。ま
た、この処理容器1の内部にはメタン酸化細菌等の嫌気
性微生物が集積したグラニュール(図示せず)及び気液
分離手段5が収容されており、流入配管2より導入され
た有機性産業廃水を上記微生物によって処理水とメタン
を主成分とするバイオガスとに生物学的に分解処理する
ようになっている。また、この処理容器1内には、例え
ば平均粒径が10μm以下の微細なマグネタイト等の磁
性粉が混入されており、処理容器1内に流れ込んできた
SSを付着させて高密度化させ、処理容器1内に濃縮さ
せるようになっている。FIG. 1 shows an embodiment of the anaerobic treatment apparatus according to the present invention. As shown in the figure, this anaerobic treatment apparatus has substantially the same structure as the conventional one, and an inflow pipe 2 for introducing an organic industrial wastewater containing SS to the lower end portion of a treatment container 1 having a substantially cylindrical shape. And an exhaust pipe 4 for exhausting the treated water and an exhaust pipe 4 for exhausting biogas are respectively connected to the upper end of the inflow pipe 2.
The wastewater that has flowed in from is flowed in an upward flow. Further, a granule (not shown) accumulating anaerobic microorganisms such as methane-oxidizing bacteria and a gas-liquid separating means 5 are housed inside the processing container 1, and the organic industry introduced through the inflow pipe 2 Waste water is biologically decomposed into treated water and biogas containing methane as a main component by the above microorganisms. In addition, magnetic powder such as fine magnetite having an average particle size of 10 μm or less is mixed in the processing container 1, and the SS that has flowed into the processing container 1 is adhered to increase the density. It is designed to be concentrated in the container 1.
【0009】また、この処理容器1の側壁部には、これ
より斜め上方に延びたSS抜出し管6が接続されてい
る。このSS抜出し管6は処理容器1に溜まったSSを
抜き出すものであり、その途中には下方から上方に向か
ってそれぞれSS抜出し手段7と、磁性粉回収手段8
と、SS受液容器9が設けられている。このSS抜出し
手段7は、先端部がSS抜出し管6を貫通してその内部
に臨んだ搬送ガス噴出し管10と、逆止弁11と、ポン
プ12とからなっており、ポンプ12から送り出される
空気などの搬送ガスによってSS抜出し管6内のSSを
磁性粉を分離しつつエアーリフトによって抜き出すよう
になっている。また、磁性粉回収手段8はSS抜出し管
6を囲繞するように設けられ、任意に励磁することがで
きる電磁石13と、この電磁石13の上方に設けられた
洗浄手段14とからなっており、SS抜出し管6内に磁
場を形成し、上昇するSS中の磁性粉Jのみを吸着して
再び処理容器1内に戻すようになっている。この洗浄手
段14は、電磁石13上方のSS抜出し管6と上記流出
管3間を接続する洗浄管15と、逆止弁16と、ポンプ
17とからなっており、上記流出管3内を流れる処理水
の一部を抜き出し、SS抜出し管6内に逆流させて上記
電磁石13に吸着された磁性粉Jを処理容器1内に圧送
させるようになっている。また、SS受液容器9は上方
に開放したSS抜出し管6の先端部を囲繞するように設
けられており、SS抜出し管6からオーバーフローした
SSを回収して図示しないSS処理手段に送るようにな
っている。尚、このSS抜出し管6の上端部は、SS抜
出し管6内の廃水が自然にオーバーフローしないように
処理容器1の流出管3の高さよりもやや高い位置に開口
している。Further, an SS extraction pipe 6 extending obliquely upward from the side wall of the processing container 1 is connected to the side wall. This SS withdrawing pipe 6 is for withdrawing SS accumulated in the processing container 1, and in the middle thereof, an SS withdrawing means 7 and a magnetic powder collecting means 8 are provided from the bottom to the top.
And an SS liquid receiving container 9 is provided. The SS extraction means 7 is composed of a carrier gas injection pipe 10 whose front end penetrates the SS extraction pipe 6 and faces the inside thereof, a check valve 11, and a pump 12, and is delivered from the pump 12. The SS in the SS extraction pipe 6 is extracted by an air lift while separating the magnetic powder by a carrier gas such as air. Further, the magnetic powder collecting means 8 is provided so as to surround the SS extraction pipe 6, and is composed of an electromagnet 13 which can be excited at will and a cleaning means 14 provided above the electromagnet 13, A magnetic field is formed in the extraction pipe 6, and only the rising magnetic powder J in SS is adsorbed and returned to the inside of the processing container 1. The cleaning means 14 is composed of a cleaning pipe 15 connecting the SS extraction pipe 6 above the electromagnet 13 and the outflow pipe 3, a check valve 16 and a pump 17, and a process for flowing in the outflow pipe 3. A part of the water is withdrawn, the water is withdrawn into the SS withdrawal pipe 6 and the magnetic powder J adsorbed by the electromagnet 13 is pressure-fed into the processing container 1. Further, the SS liquid receiving container 9 is provided so as to surround the tip end portion of the SS withdrawing pipe 6 opened upward, so that the SS overflowed from the SS withdrawing pipe 6 is collected and sent to an SS processing means (not shown). Has become. The upper end of the SS extraction pipe 6 is opened at a position slightly higher than the height of the outflow pipe 3 of the processing container 1 so that the waste water in the SS extraction pipe 6 does not naturally overflow.
【0010】次に、本実施例の作用を説明する。Next, the operation of this embodiment will be described.
【0011】先ず、流入配管2から処理容器1内に流れ
込んだ廃水は上昇流で処理容器1内を通過する際に、処
理容器1内の嫌気性微生物によって処理水とバイオガス
に分解処理され、処理水はオバーフローして流出管3か
ら流出し、バイオガスは気液分離手段5によって処理水
中から分離されて排気管4から排気される。この時、廃
水中のSSは、予め処理容器1内に投入された磁性粉に
よって図2に示すように、その周囲に凝集して高密度化
され、図1に示すように、処理容器1内に濃縮される。First, when the wastewater flowing into the processing container 1 from the inflow pipe 2 passes through the processing container 1 in an upward flow, it is decomposed by the anaerobic microorganisms in the processing container 1 into processed water and biogas. The treated water overflows and flows out from the outflow pipe 3, and the biogas is separated from the treated water by the gas-liquid separation means 5 and exhausted from the exhaust pipe 4. At this time, the SS in the waste water is aggregated and densified around the surroundings as shown in FIG. 2 by the magnetic powder previously charged into the processing container 1, and as shown in FIG. Is concentrated to.
【0012】そして、この高密度SSの占める割合は廃
水の導入と共に徐々に増加していくことになるが、その
液面が、例えばSS抜出し管6のSS抜出し手段7の高
さに達したならば、SS抜出し手段7のポンプ12を作
動させ、搬送ガス噴出し管10内に空気等の搬送ガスを
噴き出し、SS抜出し管6内のSSをエアリフトによっ
て上昇させる。これと同時に、磁性粉回収手段8の電磁
石13に通電して励磁させると、SS抜出し管6内を上
昇しているSS中の磁性粉Jがエアレーションで強く混
合されSSから離れると共に、電磁石13の磁力によっ
てSS中から分離し、SS抜出し管6の内壁面に吸着さ
れる。そして、磁性粉Jが分離されたSSはさらにSS
抜出し管6内を上昇し、その上端部からオーバーフロー
してSS受液容器9から抜き出されることになる。これ
によって、処理容器1内のSSの占める割合がこれ以上
増えることがなくなり、嫌気性微生物による分解処理能
力の低下を防止することができる。The proportion of the high-density SS gradually increases with the introduction of the wastewater, but if the liquid level reaches the height of the SS withdrawing means 7 of the SS withdrawing pipe 6, for example. For example, the pump 12 of the SS extraction means 7 is actuated, carrier gas such as air is ejected into the carrier gas ejection pipe 10, and SS in the SS ejection pipe 6 is raised by an air lift. At the same time, when the electromagnet 13 of the magnetic powder collecting means 8 is energized to be excited, the magnetic powder J in SS rising in the SS extraction tube 6 is strongly mixed by aeration and separated from SS, and at the same time, It is separated from the SS by magnetic force and adsorbed on the inner wall surface of the SS extraction pipe 6. The SS from which the magnetic powder J has been separated is further SS
It rises in the extraction pipe 6, overflows from the upper end thereof, and is extracted from the SS liquid receiving container 9. As a result, the proportion of SS in the processing container 1 does not increase any more, and it is possible to prevent the degradation of the decomposition processing capacity by anaerobic microorganisms.
【0013】次に、このような状態で処理容器1内のS
Sを抜き出すことにより、処理容器1内の磁性粉Jが減
少すると共に、減少した磁性粉Jが図1に示すように電
磁石13付近のSS抜出し管6内壁に徐々に堆積してく
ると、一旦、SS抜出し手段7によるSSの抜出しを停
止すると共に、電磁石13への通電を停止して非励磁状
態にする。その後、磁性粉回収手段8の洗浄管15に設
けられたポンプ17を駆動して、流出管3を流れる処理
水の一部を洗浄管15により導いてSS抜出し管6内に
逆流させると、SS抜出し管6内壁に堆積した磁性粉J
がSS抜出し管6内を逆流して処理容器1内に戻され、
再び処理容器1内のSSを高密度化させる凝集剤として
作用することになる。そして、一定時間経過後、再び上
述したようなSS抜出し作業及び磁性粉回収作業を繰り
返すことによって、次々と処理容器1内に流入してくる
SSのみを効率的に抜き出すことができる。Next, in such a state, the S in the processing container 1 is
By extracting S, the magnetic powder J in the processing container 1 decreases, and when the decreased magnetic powder J gradually accumulates on the inner wall of the SS extraction pipe 6 near the electromagnet 13 as shown in FIG. , SS extraction by the SS extraction means 7 is stopped, and energization to the electromagnet 13 is stopped to bring it into a non-excited state. After that, when the pump 17 provided in the cleaning pipe 15 of the magnetic powder collecting means 8 is driven to guide a part of the treated water flowing through the outflow pipe 3 by the cleaning pipe 15 and make it flow backward into the SS extraction pipe 6, SS Magnetic powder J deposited on the inner wall of the extraction pipe 6
Flows back in the SS extraction pipe 6 and is returned to the processing container 1,
Again, it acts as an aggregating agent for densifying the SS in the processing container 1. Then, after the elapse of a certain time, the SS withdrawing work and the magnetic powder collecting work as described above are repeated again, whereby only the SS flowing into the processing container 1 one after another can be efficiently withdrawn.
【0014】このように、本発明は磁性粉を混入して廃
水中のSSを高密度化させて処理容器内で占める容積を
小さくしたため、従来の嫌気性処理装置では殆ど処理す
ることができなかったSS混入有機廃水の処理を行うこ
とが可能となり、また、この高濃度SS中の磁性粉を磁
力を利用してSSの抜出しと同時に回収、再利用するよ
うにしたため、新たに磁性粉を添加する必要がなく、コ
ストの上昇も抑えることができる。尚、本実施例では磁
性粉を分離するために電磁石を用いたが、これに代えて
一般的な永久磁石を機械的にSS抜出し管に近付けた
り、離したりする形で用いても同様な効果を得ることが
でき、また、エアリフトに代えて、SS抜出し管内に攪
拌機を設けて、遠心力によって物理的にSS中の磁性粉
を分離するようにしても良い。また、図3に示すよう
に、SS抜出し管6の上端部に設けられたSS受液容器
9を密閉構造とし、SS受液容器9から抜出されるSS
のラインに電磁弁18などを設け、磁性粉回収作業中は
それを閉じてポンプ17を作動させることにより、図示
するように洗浄手段14による磁性粉の回収効果を向上
させることもできる。As described above, according to the present invention, since the magnetic powder is mixed to increase the density of SS in the waste water to reduce the volume occupied in the processing container, almost no processing can be performed by the conventional anaerobic processing apparatus. It is possible to treat SS-containing organic wastewater, and the magnetic powder in this high-concentration SS is collected and reused at the same time as SS is extracted by using magnetic force, so new magnetic powder is added. It is not necessary to do so, and the increase in cost can be suppressed. In the present embodiment, an electromagnet was used to separate the magnetic powder, but instead of this, a general permanent magnet may be used mechanically close to or away from the SS extraction tube to obtain the same effect. Alternatively, instead of the air lift, a stirrer may be provided in the SS withdrawal pipe to physically separate the magnetic powder in SS by centrifugal force. Further, as shown in FIG. 3, the SS liquid receiving container 9 provided at the upper end portion of the SS withdrawing pipe 6 has a closed structure, and the SS liquid receiving container 9 is withdrawn from the SS liquid receiving container 9.
It is also possible to improve the magnetic powder recovery effect by the cleaning means 14 as shown in the figure by providing a solenoid valve 18 or the like in the line and closing the magnetic valve during the magnetic powder recovery operation to operate the pump 17.
【0015】[0015]
【発明の効果】以上要するに本発明によれば、従来の嫌
気性処理装置では殆ど処理することができなかったSS
混入有機廃水の処理を行うことが可能となるため、廃水
の処理能力が向上すると共に、装置の大型化や付設設備
の設置に伴う設置スペースや製造コストの上昇を抑える
ことができる。また、この高濃度SS中の磁性粉をエア
リフトにより分離し、次に磁力を利用してSSの抜出し
と同時に回収、再利用するようにしたため、新たに磁性
粉を添加する必要がなくなり、SS抜出しに伴う磁性粉
のロスと補充によるコストの上昇も抑えることができる
等といった優れた効果を発揮することができる。In summary, according to the present invention, SS which can hardly be treated by the conventional anaerobic treatment apparatus.
Since it is possible to treat the mixed organic wastewater, it is possible to improve the treatment capacity of the wastewater and to suppress an increase in installation space and manufacturing cost associated with the increase in size of the apparatus and the installation of the attached equipment. In addition, since the magnetic powder in this high-concentration SS is separated by an air lift, and then the magnetic force is used to collect and reuse SS at the same time as it is taken out, there is no need to add new magnetic powder, and SS is taken out. It is possible to exert an excellent effect such that it is possible to suppress the loss of the magnetic powder and the increase in cost due to the replenishment due to the above.
【図1】本発明の一実施例を示す構成図である。FIG. 1 is a configuration diagram showing an embodiment of the present invention.
【図2】高濃度SSを示す概念図である。FIG. 2 is a conceptual diagram showing high concentration SS.
【図3】本発明の変形実施例を示す構成図である。FIG. 3 is a configuration diagram showing a modified embodiment of the present invention.
【図4】従来の嫌気性処理装置の構造を示す簡略図であ
る。FIG. 4 is a simplified diagram showing a structure of a conventional anaerobic treatment apparatus.
1 処理容器 6 SS抜出し管 7 SS抜出し手段 8 磁性粉回収手段 J 磁性粉 1 Processing Container 6 SS Extracting Tube 7 SS Extracting Means 8 Magnetic Powder Collecting Means J Magnetic Powder
Claims (2)
下端部から導入して上昇流で流し、上端部からオーバー
フローさせる処理容器内部に、上記有機性産業廃水中の
有機物を分解するための嫌気性微生物等を収容した嫌気
性処理装置において、上記処理容器内に上記有機性産業
廃水中の懸濁物(以下SSという)を高密度化させる磁
性粉を混入すると共に、その側面部に、処理容器に蓄積
したSSを抜き出すためのSS抜出し管をこれより斜め
上方に分岐させて接続し、そのSS抜出し管に、上記S
Sをエアリフトさせて抜き出すためのSS抜出し手段
と、このSS抜出し手段で抜き出されるSS中の磁性粉
を吸着して回収するための磁性粉回収手段とを設けたこ
とを特徴とする嫌気性処理装置。1. An organic industrial wastewater containing soluble organic matter,
Introduced from the lower end and flowing in an upward flow, overflowing from the upper end, inside the processing container, in the anaerobic processing apparatus containing anaerobic microorganisms for decomposing organic matter in the organic industrial wastewater, the processing container, A magnetic powder that densifies the suspension in the organic industrial waste water (hereinafter referred to as SS) is mixed therein, and an SS extraction pipe for extracting the SS accumulated in the processing container is provided on the side surface of the magnetic powder. Connect by branching diagonally upward, and then connecting the above S
Anaerobic treatment, characterized in that SS extraction means for air-lifting and extracting S and magnetic powder recovery means for adsorbing and recovering the magnetic powder in SS extracted by this SS extraction means are provided. apparatus.
を囲繞して設けられた電磁石と、上記処理容器からオー
バーフローした処理水の一部を上記SS抜出し管内に逆
流させる洗浄手段とからなることを特徴とする請求項1
記載の嫌気性処理装置。2. The magnetic powder recovery means comprises an electromagnet surrounding the SS extraction tube and a cleaning means for causing a part of the treated water overflowing from the processing container to flow back into the SS extraction tube. Claim 1 characterized by the above-mentioned.
Anaerobic treatment device described.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16364394A JPH0824890A (en) | 1994-07-15 | 1994-07-15 | Anaerobic treatment device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16364394A JPH0824890A (en) | 1994-07-15 | 1994-07-15 | Anaerobic treatment device |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0824890A true JPH0824890A (en) | 1996-01-30 |
Family
ID=15777851
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP16364394A Pending JPH0824890A (en) | 1994-07-15 | 1994-07-15 | Anaerobic treatment device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0824890A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6855254B1 (en) * | 2003-12-19 | 2005-02-15 | Shalom Recycling Inc. | Magerle metal waste recovery process |
JP2008100151A (en) * | 2006-10-18 | 2008-05-01 | Kobelco Eco-Solutions Co Ltd | Organic wastewater treatment method and organic waste water treatment device |
-
1994
- 1994-07-15 JP JP16364394A patent/JPH0824890A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6855254B1 (en) * | 2003-12-19 | 2005-02-15 | Shalom Recycling Inc. | Magerle metal waste recovery process |
JP2008100151A (en) * | 2006-10-18 | 2008-05-01 | Kobelco Eco-Solutions Co Ltd | Organic wastewater treatment method and organic waste water treatment device |
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