JPH04330996A - Anaerobic water treating device - Google Patents

Anaerobic water treating device

Info

Publication number
JPH04330996A
JPH04330996A JP3100901A JP10090191A JPH04330996A JP H04330996 A JPH04330996 A JP H04330996A JP 3100901 A JP3100901 A JP 3100901A JP 10090191 A JP10090191 A JP 10090191A JP H04330996 A JPH04330996 A JP H04330996A
Authority
JP
Japan
Prior art keywords
reactor
fluidized bed
level
carrier
flow rate
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
Application number
JP3100901A
Other languages
Japanese (ja)
Inventor
Shigeru Kobayashi
小 林   茂
Kazuo Shibazaki
柴 崎 和 夫
Nobuyuki Ashikaga
足 利 伸 行
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toshiba Corp
Original Assignee
Toshiba Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Toshiba Corp filed Critical Toshiba Corp
Priority to JP3100901A priority Critical patent/JPH04330996A/en
Publication of JPH04330996A publication Critical patent/JPH04330996A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE:To keep the amt. of bacteria in a reactor at a high concn. and to prevent the outflow of a carrier into treated water by maintaining the level of the fluidized bed of the carrier at a preset level. CONSTITUTION:The water treating device is provided with a reactor 3 having the fluidized bed 9a of a carrier deposited with anaerobes, a raw water pump 2 connected to the bottom of the reactor 3 and used for introducing waste water into the reactor 3 and a circulating pump 5 connected to the bottom of the reactor 3 and used for introducing a part of treated water into the reactor 3. A detector 6 is furnished in the reactor 3 to detect the level of the fluidized bed 9a of the carrier. An arithmetic controller 7 is furnished to output a flow rate control signal to the circulating pump 5 based on the level signal from the detector 7 and the flow rate signal from the raw water pump 2 so that the level of the fluidized bed 9a is controlled to a set level.

Description

【発明の詳細な説明】[Detailed description of the invention]

【0001】0001

【産業上の利用分野】本発明は、下水や産業廃水などの
廃水を嫌気的に処理する嫌気性水処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an anaerobic water treatment apparatus for anaerobically treating wastewater such as sewage and industrial wastewater.

【0002】0002

【従来の技術】嫌気性細菌であるメタン菌を利用した嫌
気性水処理方法は、有機物の分解速度が遅いため廃水処
理に時間がかかるなどの問題があった。しかし、このよ
うな問題を解決するために、嫌気性菌体(メタン菌)を
付着させた大きさ0.1〜1mm程度の担体をリアクタ
内に充填し、リアクタの下部から導入された廃水とリア
クタによって処理された循環水によって担体を流動させ
て廃水処理を行う流動床型嫌気性水処理装置が提案され
ている。この流動床型嫌気性水処理装置は、多量の菌体
を担体に付着させることができるため、短時間の滞留時
間で良好な廃水処理が可能となる。
BACKGROUND OF THE INVENTION Anaerobic water treatment methods using methane bacteria, which are anaerobic bacteria, have problems such as the slow decomposition rate of organic matter and the time it takes to treat wastewater. However, in order to solve this problem, a carrier with a size of about 0.1 to 1 mm to which anaerobic bacterial cells (methane bacteria) are attached is filled into the reactor, and the wastewater introduced from the bottom of the reactor is mixed with the carrier. A fluidized bed type anaerobic water treatment device has been proposed in which wastewater treatment is performed by fluidizing a carrier using circulating water treated by a reactor. This fluidized bed type anaerobic water treatment device is capable of attaching a large amount of bacterial cells to the carrier, so that good wastewater treatment is possible with a short residence time.

【0003】このような流動床型嫌気性水処理装置は、
担体の表面に多量の菌体が付着するまでに数ヵ月の長い
期間を要するため、その間は低い負荷で運転しなければ
ならない。一方、担体表面に多量の菌体が付着した後は
、担体粒径が徐々に大きくなり密度が小さくなるため、
沈降速度が減少してゆく。沈降速度が減少すると菌体の
付着した担体の流動層のレベルが高くなり、ついにはリ
アクタ内から菌体が付着した担体が処理水とともに流出
して処理水を悪化させる。このような担体の流出を防ぐ
ため、攪はん機等をリアクタ内に入れて担体表面から菌
体を剥離したり、粒径の肥大した菌体付着の担体をリア
クタから引き抜いている。
[0003] Such a fluidized bed type anaerobic water treatment equipment is
Since it takes several months for a large amount of bacterial cells to adhere to the surface of the carrier, the system must be operated at a low load during that time. On the other hand, after a large number of bacterial cells adhere to the carrier surface, the carrier particle size gradually increases and the density decreases.
The sedimentation rate decreases. As the sedimentation rate decreases, the level of the fluidized bed of carriers with bacterial bodies attached increases, and eventually the carriers with bacterial bodies attached flow out of the reactor together with the treated water, deteriorating the treated water. In order to prevent such carriers from flowing out, a stirrer or the like is placed inside the reactor to peel off the microbial cells from the surface of the carrier, or carriers with enlarged particle sizes and attached microbial cells are pulled out from the reactor.

【0004】0004

【発明が解決しようとする課題】しかしながら、攪はん
機により菌体を担体から剥離したり、菌体付着の担体を
リアクタから引き抜くことは、リアクタ内の菌体量を減
少させることになる。前述のように嫌気性処理において
は、リアクタ内に大量の菌体を保持することが、良好な
廃水処理を行うために重要である。従って、菌体を担体
から剥離したり、菌体付着の担体をリアクタから過剰に
引き抜くことは、廃水処理の悪化を招くことになる。
[Problems to be Solved by the Invention] However, using a stirrer to separate the bacterial cells from the carrier or to pull out the carrier to which the bacterial cells are attached from the reactor reduces the amount of bacterial cells in the reactor. As mentioned above, in anaerobic treatment, it is important to maintain a large amount of bacterial cells in the reactor in order to perform good wastewater treatment. Therefore, peeling off the bacterial cells from the carrier or excessively pulling out the carrier to which the bacterial cells are attached from the reactor will lead to deterioration of wastewater treatment.

【0005】本発明はこのような問題点を考慮してなさ
れたものであり、担体の流出を防止するとともに、菌体
の剥離や引き抜き量を減らし、リアクタ内の菌体量を高
めて処理水の水質向上を図ることができる嫌気性水処理
装置を提供することを目的とする。
[0005] The present invention was made in consideration of these problems, and it prevents the outflow of carriers, reduces the amount of peeling and pulling out of bacterial cells, increases the amount of bacterial cells in the reactor, and improves the efficiency of treated water. The purpose of the present invention is to provide an anaerobic water treatment device that can improve water quality.

【0006】[0006]

【課題を解決するための手段】本発明は、嫌気性菌体を
付着させた担体の流動層を有するリアクタと、このリア
クタ底部に接続され廃水を前記リアクタ内に上向流で流
入させる原水ポンプと、前記リアクタ底部に接続され前
記リアクタによって処理された処理水の一部を前記リア
クタ内に上向流で流入させる循環ポンプとを備え、前記
リアクタ内に前記担体の流動層の流動層レベルを検知す
る検知器を設け、この検知器からのレベル信号と前記原
水ポンプからの流量信号に基づいて前記担体の流動層レ
ベルが予め設定した設定レベルとなるよう前記循環ポン
プに流量制御信号を出力する演算制御装置を設けたこと
を特徴とする嫌気性水処理装置である。
[Means for Solving the Problems] The present invention provides a reactor having a fluidized bed of carriers to which anaerobic bacterial cells are attached, and a raw water pump connected to the bottom of the reactor to flow wastewater into the reactor in an upward flow. and a circulation pump connected to the bottom of the reactor to flow a portion of the treated water treated by the reactor into the reactor in an upward flow, the fluidized bed level of the fluidized bed of the carrier being maintained in the reactor. A detector is provided for detection, and a flow rate control signal is output to the circulation pump so that the fluidized bed level of the carrier reaches a preset level based on the level signal from the detector and the flow rate signal from the raw water pump. This is an anaerobic water treatment device characterized by being equipped with an arithmetic and control device.

【0007】[0007]

【作用】本発明によれば、検知器によって担体の流動層
レベルが検知され、検知器からのレベル信号が演算制御
装置に出力されるとともに、原水ポンプからの流量信号
が演算制御装置に出力され、演算制御装置は検知器から
のレベル信号と原水ポンプからの流量信号に基づいて、
担体の流動層レベルが予め設定した設定レベルとなるよ
う循環ポンプの流量制御を行う。
[Operation] According to the present invention, the level of the fluidized bed of the carrier is detected by the detector, the level signal from the detector is output to the arithmetic and control device, and the flow rate signal from the raw water pump is output to the arithmetic and control device. , the arithmetic and control unit uses the level signal from the detector and the flow rate signal from the raw water pump to
The flow rate of the circulation pump is controlled so that the fluidized bed level of the carrier becomes a preset level.

【0008】[0008]

【実施例】以下、図面を参照して本発明の実施例につい
て説明する。図1は本発明による嫌気性水処理装置の一
実施例を示す図である。
Embodiments Hereinafter, embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a diagram showing an embodiment of an anaerobic water treatment apparatus according to the present invention.

【0009】図1において、嫌気性水処理装置は、嫌気
性菌体を付着させた担体を含む流動層9aを内部に有す
るリアクタ3を備えており、リアクタ3内の流動層9a
より上部側は処理層9bとなっている。またリアクタ3
の底部には、原水タンク1に一次的に貯留された廃水を
リアクタ3内に上向流で流入させる原水ポンプ2が接続
されている。さらに、リアクタ3の上部から溢流する処
理水は、処理水槽4内に流入するようになっている。ま
た処理槽4内の処理水の一部(循環水)は、循環ポンプ
5によってリアクタ3の底部からリアクタ3内に上向流
で流入するようになっている。リアクタ3内の担体に付
着された菌体はメタン菌群からなり、廃水中の有機物を
低級脂肪酸を経てメタン、二酸化炭素にまで分解するよ
うになっている。
In FIG. 1, the anaerobic water treatment apparatus is equipped with a reactor 3 having a fluidized bed 9a inside thereof containing a carrier to which anaerobic bacteria are attached.
The upper side is a processing layer 9b. Also reactor 3
A raw water pump 2 is connected to the bottom of the reactor 3, which causes wastewater temporarily stored in the raw water tank 1 to flow upward into the reactor 3. Furthermore, the treated water overflowing from the upper part of the reactor 3 flows into the treated water tank 4. Further, a part of the treated water (circulated water) in the treatment tank 4 is caused to flow upward into the reactor 3 from the bottom of the reactor 3 by the circulation pump 5. The bacterial cells attached to the carrier in the reactor 3 are composed of a group of methane bacteria, and are designed to decompose organic matter in wastewater into methane and carbon dioxide via lower fatty acids.

【0010】また、リアクタ3内には、リアクタ3内の
担体の流動層9aの流動層レベルを検知する検知器6が
取付けられ、検知器6には演算制御装置7が接続されて
いる。さらに原水ポンプ2も演算制御装置7に接続され
ている。この演算制御装置7は、検知器6からのレベル
信号と原水ポンプ2からの流量信号とに基づいて、循環
ポンプ5に流量制御信号を出力するようになっている。 すなわち、リアクタ3の底部には、原水ポンプ2からの
廃水と循環ポンプ5からの循環水が流入し、これら廃水
と循環水の流量の和によって担体を押し上げ流動層9a
のレベルを維持している。このため廃水と循環水の流量
の和が、予め設定した流動層9aの設定レベルを維持す
る流量となるよう循環ポンプ5に流量制御信号を出力す
る。
A detector 6 is installed inside the reactor 3 to detect the level of the fluidized bed 9a of the carrier in the reactor 3, and an arithmetic and control unit 7 is connected to the detector 6. Furthermore, the raw water pump 2 is also connected to the arithmetic and control device 7. This arithmetic and control device 7 is configured to output a flow rate control signal to the circulation pump 5 based on the level signal from the detector 6 and the flow rate signal from the raw water pump 2. That is, wastewater from the raw water pump 2 and circulating water from the circulation pump 5 flow into the bottom of the reactor 3, and the sum of the flow rates of these wastewater and circulating water pushes up the carrier and forms the fluidized bed 9a.
maintains the level of Therefore, a flow rate control signal is output to the circulation pump 5 so that the sum of the flow rates of waste water and circulating water becomes a flow rate that maintains a preset level of the fluidized bed 9a.

【0011】次にこのような構成からなる本実施例の作
用について説明する。
Next, the operation of this embodiment having such a configuration will be explained.

【0012】廃水は原水タンク1に一度貯留された後、
原水ポンプ2によりリアクタ3の底部から内部へと導入
される。そして担体に付着され高濃度に保持されている
菌体(メタン菌群)により、廃水中の有機物が低級脂肪
酸を経てメタン、二酸化炭素にまで分解される。浄化さ
れた処理水は、リアクタ3の上部より溢流し、処理水槽
4を経て排出される。また、浄化された処理水の一部は
、循環水となって循環ポンプ5によりリアクタ3の底部
へと返送される。
[0012] After the wastewater is once stored in the raw water tank 1,
Raw water is introduced into the reactor 3 from the bottom by the pump 2 . The organic matter in the wastewater is then decomposed into methane and carbon dioxide through lower fatty acids by the bacteria (methane bacteria group) attached to the carrier and maintained at a high concentration. The purified treated water overflows from the upper part of the reactor 3 and is discharged through the treated water tank 4. Further, a part of the purified treated water becomes circulating water and is returned to the bottom of the reactor 3 by the circulation pump 5.

【0013】リアクタ3の内部の流動層の流動層レベル
は、検知器6により随時検知され、演算制御装置7によ
り流動層レベルの変化を監視している。また、演算制御
装置7は原水ポンプ2からの流量信号によりその流量の
変化を監視している。ここで、リアクタ3内に流入され
る流量は、原水ポンプ2からの廃水と循環ポンプ5から
の循環水の流量の和で表わされる。従って、演算制御装
置7は、循環ポンプ5の流量と原水ポンプ2の流量の和
が、設定した流動層レベルを維持する流量となるように
循環ポンプ5に流量制御信号を出力してこれを制御する
。すなわち、流動層レベルの変化量が設定値を越えた場
合、予め設定した流動層レベルになるまで循環ポンプ5
の流量を演算制御装置7により減少させる。
The fluidized bed level of the fluidized bed inside the reactor 3 is detected by a detector 6 at any time, and changes in the fluidized bed level are monitored by an arithmetic and control unit 7. Further, the arithmetic and control device 7 monitors changes in the flow rate based on the flow rate signal from the raw water pump 2. Here, the flow rate flowing into the reactor 3 is represented by the sum of the flow rates of waste water from the raw water pump 2 and circulating water from the circulation pump 5. Therefore, the arithmetic and control device 7 outputs a flow rate control signal to the circulation pump 5 to control it so that the sum of the flow rate of the circulation pump 5 and the flow rate of the raw water pump 2 becomes a flow rate that maintains the set fluidized bed level. do. In other words, when the amount of change in the fluidized bed level exceeds the set value, the circulation pump 5 is operated until the fluidized bed level reaches the preset value.
The arithmetic and control device 7 reduces the flow rate.

【0014】循環ポンプ5の制御について更に詳述する
と、一定時間ごとにリアクタ3内を上下する検知器6に
より流動層レベルが検知され、演算制御装置7により、
各時間ごとの流動層レベルと予め設定した流動層レベル
との差が求められる。この差が正の値であり、かつ絶対
値が予め設定された値を上回った場合、流動層レベルが
上昇して担体流出の可能性があると判断して、演算制御
装置7により循環ポンプ5の流量を下げる。逆に、この
差が負の値であり、かつ絶対値が予め設定された値を上
回った場合、流動層レベルが設定したレベルを下回り担
体が下方にかたまるため処理効率が低下すると判断して
、演算制御装置7により循環ポンプ5の流量を上げる。 このようにして循環ポンプ5の流量調整後の流動層レベ
ルを予め設定した設定レベルに近づけることができる。
To explain in more detail the control of the circulation pump 5, the fluidized bed level is detected by the detector 6 that moves up and down inside the reactor 3 at regular intervals, and the arithmetic and control unit 7 detects the level of the fluidized bed.
The difference between the fluidized bed level for each hour and the preset fluidized bed level is determined. If this difference is a positive value and the absolute value exceeds a preset value, it is determined that the fluidized bed level has risen and there is a possibility of carrier outflow, and the arithmetic and control unit 7 controls the circulation pump 5. lower the flow rate. On the other hand, if this difference is a negative value and the absolute value exceeds a preset value, it is determined that the fluidized bed level falls below the set level and the carriers clump downward, resulting in a decrease in processing efficiency. The flow rate of the circulation pump 5 is increased by the arithmetic and control device 7. In this way, the fluidized bed level after adjusting the flow rate of the circulation pump 5 can be brought close to a preset level.

【0015】本実施例によれば、リクアタ3からの担体
の流出を防止するとともに、菌体の剥離や担体の引き抜
き量を減らすことができるため、リアクタ内の菌体量を
高濃度に維持して処理水の水質向上を図ることが可能と
なる。
According to this embodiment, it is possible to prevent the carrier from flowing out from the reactor 3 and to reduce the amount of detachment of bacterial cells and the amount of carriers pulled out, so that the amount of bacterial cells in the reactor can be maintained at a high concentration. This makes it possible to improve the quality of treated water.

【0016】なお、流動層レベルの設定値は、菌体の増
殖速度、リアクタの流動特性、菌体の剥離特性等により
決定されるため、予備実験で決定することが望ましい。 また、本発明は流動床型リアクタ3に適用されるので、
リアクタ内の流動状態を適切に維持するために循環ポン
プ5の流量はある程度必要となる。この循環ポンプ5の
流量下限は、用いる担体の大きさや密度およびリアクタ
3の流動特性により決定されるが、リアクタ3内の流体
の上昇速度が概ね2m/H程度となるよう循環ポンプ5
の流量下限が定められる。
[0016] Since the set value of the fluidized bed level is determined by the growth rate of the bacterial cells, the flow characteristics of the reactor, the peeling characteristics of the bacterial cells, etc., it is desirable to determine it through preliminary experiments. Furthermore, since the present invention is applied to the fluidized bed reactor 3,
A certain amount of flow rate of the circulation pump 5 is required to maintain an appropriate flow state in the reactor. The lower limit of the flow rate of the circulation pump 5 is determined by the size and density of the carrier used and the flow characteristics of the reactor 3, but the circulation pump 5
The lower limit of the flow rate is determined.

【0017】[0017]

【発明の効果】以上説明したように、本発明によれば菌
体の剥離や菌体が付着した担体の引き抜きを行うことな
く、流動層レベルを予め設定した設定レベルに維持する
ことができる。このため、リアクタ内の菌体量を高濃度
に維持するとともに処理水中への担体の流出を防止する
ことができ、処理水の水質向上を図ることができる。
As explained above, according to the present invention, the fluidized bed level can be maintained at a preset level without peeling off the bacterial cells or pulling out the carrier to which the bacterial cells are attached. Therefore, the amount of bacterial cells in the reactor can be maintained at a high concentration, and the carrier can be prevented from flowing out into the treated water, and the quality of the treated water can be improved.

【図面の簡単な説明】[Brief explanation of drawings]

【図1】本発明による嫌気性水処理装置の一実施例を示
す概略系統図。
FIG. 1 is a schematic system diagram showing an embodiment of an anaerobic water treatment apparatus according to the present invention.

【符号の説明】[Explanation of symbols]

2  原水ポンプ 3  リアクタ 5  循環ポンプ 6  検知器 7  演算制御装置 9a  担体の流動層 2 Raw water pump 3 Reactor 5 Circulation pump 6 Detector 7 Arithmetic control unit 9a Fluidized bed of carrier

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】嫌気性菌体を付着させた担体の流動層を有
するリアクタと、このリアクタ底部に接続され廃水を前
記リアクタ内に上向流で流入させる原水ポンプと、前記
リアクタ底部に接続され前記リアクタによって処理され
た処理水の一部を前記リアクタ内に上向流で流入させる
循環ポンプとを備え、前記リアクタ内に前記担体の流動
層の流動層レベルを検知する検知器を設け、この検知器
からのレベル信号と前記原水ポンプからの流量信号に基
づいて前記担体の流動層レベルが予め設定した設定レベ
ルとなるよう前記循環ポンプに流量制御信号を出力する
演算制御装置を設けたことを特徴とする嫌気性水処理装
置。
1. A reactor having a fluidized bed of carriers to which anaerobic bacterial cells are attached; a raw water pump connected to the bottom of the reactor for causing wastewater to flow upward into the reactor; and a raw water pump connected to the bottom of the reactor. a circulation pump for flowing a portion of the treated water treated by the reactor into the reactor in an upward flow; a detector for detecting a fluidized bed level of the fluidized bed of the carrier is provided in the reactor; A calculation and control device is provided that outputs a flow rate control signal to the circulation pump so that the fluidized bed level of the carrier reaches a preset level based on the level signal from the detector and the flow rate signal from the raw water pump. Features of anaerobic water treatment equipment.
JP3100901A 1991-05-02 1991-05-02 Anaerobic water treating device Pending JPH04330996A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3100901A JPH04330996A (en) 1991-05-02 1991-05-02 Anaerobic water treating device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3100901A JPH04330996A (en) 1991-05-02 1991-05-02 Anaerobic water treating device

Publications (1)

Publication Number Publication Date
JPH04330996A true JPH04330996A (en) 1992-11-18

Family

ID=14286251

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3100901A Pending JPH04330996A (en) 1991-05-02 1991-05-02 Anaerobic water treating device

Country Status (1)

Country Link
JP (1) JPH04330996A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102144117B1 (en) * 2019-08-05 2020-08-12 주식회사 디에스엔지니어스 Reactor using anaerobic microorganisms with low initial investment and high volume loading and purification efficiency

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR102144117B1 (en) * 2019-08-05 2020-08-12 주식회사 디에스엔지니어스 Reactor using anaerobic microorganisms with low initial investment and high volume loading and purification efficiency

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