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JPS5915714B2 - Wastewater treatment method - Google Patents
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JPS5915714B2 - Wastewater treatment method - Google Patents

Wastewater treatment method

Info

Publication number
JPS5915714B2
JPS5915714B2 JP53050743A JP5074378A JPS5915714B2 JP S5915714 B2 JPS5915714 B2 JP S5915714B2 JP 53050743 A JP53050743 A JP 53050743A JP 5074378 A JP5074378 A JP 5074378A JP S5915714 B2 JPS5915714 B2 JP S5915714B2
Authority
JP
Japan
Prior art keywords
amount
wastewater
circulating water
aeration chamber
module
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.)
Expired
Application number
JP53050743A
Other languages
Japanese (ja)
Other versions
JPS54144758A (en
Inventor
則夫 塩地
俊夫 船越
清 菅田
徹 沢井
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP53050743A priority Critical patent/JPS5915714B2/en
Publication of JPS54144758A publication Critical patent/JPS54144758A/en
Publication of JPS5915714B2 publication Critical patent/JPS5915714B2/en
Expired 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)

Description

【発明の詳細な説明】 この発明は廃水を生物学的に浄化する装置、特に固着生
物膜による廃水処理装置の酸素供給方法および水の循環
方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for biologically purifying wastewater, and in particular to a method for supplying oxygen and a method for circulating water in a wastewater treatment apparatus using fixed biofilms.

従来からの生物学的廃水処理法として、活性汚泥法およ
び散水P床法などが代表的なものとじて知られている。
As conventional biological wastewater treatment methods, the activated sludge method and the sprinkling P bed method are known as representative methods.

しかしながら、これらの方法には次のような問題点があ
った。
However, these methods have the following problems.

(1)運転、管理に高度の技術と熟練が必要であり、殊
に活性汚泥法では返送汚泥の厳密な管理が必要である。
(1) Operation and management require a high degree of skill and skill, and especially in the activated sludge method, strict control of returned sludge is required.

(2)活性汚泥法ではバルキングを起こし易い等の問題
があり、また散水f床法ではF床バエの発生や臭気の問
題がある。
(2) The activated sludge method has problems such as the tendency to cause bulking, and the sprinkled F-bed method has problems such as generation of F-bed flies and odor.

(3)BOD、アンモニアについてはそれらが20pp
m以下の処理水を得ることは難かしい。
(3) Regarding BOD and ammonia, they are 20pp
It is difficult to obtain treated water of less than m.

上記の活性汚泥法、散水P床法のもつ問題点を解決した
浸漬型固着生物膜法も知られており、この方法は廃水を
、微生物を付着したモジュール部を通過させ、その際空
気を同時に送って廃水中のBODまたは窒素成分の酸化
に必要な酸素を供給して廃水の生物的処理を行なうもの
である。
The immersion-type fixed biofilm method is also known, which solves the problems of the activated sludge method and the sprinkled P bed method described above. The biological treatment of wastewater is carried out by supplying the oxygen necessary for oxidizing BOD or nitrogen components in the wastewater.

この装置の代表的なものは第1図に示すようなもので、
本体1内にモジュール2、曝気室3が設けてあり、原水
注入ライン4、処理水排出ライン5、空気注入ライン6
というような構造となっている。
A typical example of this device is shown in Figure 1.
A module 2 and an aeration chamber 3 are provided in the main body 1, a raw water injection line 4, a treated water discharge line 5, and an air injection line 6.
The structure is as follows.

生物を固着させるモジュールとしては小石、プラスチッ
ク板、プラスチック・チューブ等が用いられる。
Pebbles, plastic plates, plastic tubes, etc. are used as modules for attaching organisms.

モジュール内の水の循環はモジュールの中心部または側
面に曝気室を設け、曝気室の下部から空気を送入するこ
とによるエアーリフトポンプの効果により行なう。
Circulation of water within the module is achieved by providing an aeration chamber in the center or side of the module, and by introducing air from the lower part of the aeration chamber to achieve the effect of an air lift pump.

この循環される廃水とモジュール表面に付着した微生物
とを接触させることにより廃水の浄化処理を行なうもの
である。
The wastewater is purified by bringing the circulated wastewater into contact with microorganisms attached to the module surface.

しかしながら、従来の浸漬型固着生物膜法には下記に示
す欠点があった。
However, the conventional immersion type fixed biofilm method had the following drawbacks.

(a循環水流に対し抵抗の小さいモジュールを使用する
と偏流を起こし易く、その結果モジュールのデッドスペ
ース(死空間)が犬となり、処理性能が悪化して(る場
合がある。
(a) If a module with low resistance to the circulating water flow is used, it tends to cause drifting, and as a result, the dead space of the module becomes a dog, which may deteriorate the processing performance.

(b)循環水流に対し抵抗の大きいモジュールを使用す
ると目詰りを起こし易く、水の循環がし難くなって処理
効率が低下してくる場合があり、水質に応じたモジュー
ルを選択することが非常に難かしい。
(b) If a module with high resistance to circulating water flow is used, it may easily become clogged, making water circulation difficult and reducing treatment efficiency, so it is very important to select a module that is appropriate for the water quality. It's difficult.

(c)廃水の処理量が多くなった場合、酸素供給量も多
く必要となる。
(c) When the amount of wastewater to be treated increases, a large amount of oxygen is required to be supplied.

しかし酸素供給を多くするために空気送風量を多くする
と水の循環速度も速くなり、その結果、モジュールに付
着した微生物がはがれ易くなり処理効率が悪化する場合
がある。
However, if the air flow rate is increased in order to increase the oxygen supply, the water circulation speed will also increase, and as a result, microorganisms attached to the module may be easily peeled off and the processing efficiency may deteriorate.

このように廃水の水質、水量に対し空気送風量、循環水
量のコントロールがかなり難かしい。
In this way, it is quite difficult to control the quality and quantity of wastewater, the amount of air blowing, and the amount of circulating water.

そこで本発明者等は浸漬型固着生物膜法における上記の
ような欠点、特に(c)の欠点を解消すべ(研究を重ね
た結果、廃水中のアンモニア濃度および廃水流量を自動
検知し、空気量および循環水量の制御を行なうことによ
り廃水中のアンモニア濃度、水量の変動があっても安定
した水質を得る方法を見出し、本発明を完成したもので
ある。
Therefore, the present inventors aimed to eliminate the above-mentioned drawbacks of the immersion-type fixed biofilm method, especially the drawback (c). The present invention has been completed by discovering a method for obtaining stable water quality even when there are fluctuations in the ammonia concentration in wastewater and the amount of water by controlling the amount of circulating water.

即ち、本発明はモジュール充填部と曝気室とが別体であ
る固着生物膜式廃水処理装置により廃水処理する方法に
おいて、原廃水のアンモニア濃度および流量の検知に基
づいて曝気室への送入空気量の調整を行うと共に、モジ
ュール充填部から曝気室への循環水ラインに設けられた
流量指示調節計により循環水量を一定値に制御すること
を特徴とする廃水処理方法に関するものである。
That is, the present invention provides a method for treating wastewater using a fixed biofilm type wastewater treatment device in which a module filling part and an aeration chamber are separate bodies, in which the amount of air sent to the aeration chamber is adjusted based on the detection of the ammonia concentration and flow rate of raw wastewater. The present invention relates to a wastewater treatment method characterized in that the amount of circulating water is adjusted and the amount of circulating water is controlled to a constant value by a flow rate indicating controller installed in a circulating water line from a module filling section to an aeration chamber.

第2図にしたがって本発明を更に詳しく説明する。The present invention will be explained in more detail with reference to FIG.

浸漬型固着生物膜装置は曝気室1、本体2、モジュール
3、散気装置4、モジュール支持板5により構成されて
いる。
The immersion type fixed biofilm device is composed of an aeration chamber 1, a main body 2, a module 3, an aeration device 4, and a module support plate 5.

原廃水はラインP1 より曝気室1に注入され、ブロ
ワ−B1 からラインP5を経て供給される空気のエア
ーリフトポンプの効果により、ラインP2を経由して装
置本体2に流入し、モジュール部3を下向流で通過する
The raw wastewater is injected into the aeration chamber 1 from line P1, and due to the effect of the air lift pump of air supplied from blower B1 through line P5, it flows into the main body 2 of the device through line P2, and the module section 3 is It passes in a downward flow.

このときモジュールに付着した微生物の作用により廃水
が浄化される。
At this time, the wastewater is purified by the action of microorganisms attached to the module.

モジュールを通過した廃水はラインP3を経由して再び
曝気室1に流入し、散気装置4から酸素供給を受けたの
ち装置本体2に流入し、ある一定時間、曝気室1と装置
本体を循環して浄化処理された後、処理水流出ラインP
4から系外に流出する。
The wastewater that has passed through the module flows into the aeration chamber 1 again via line P3, receives oxygen supply from the aeration device 4, flows into the device body 2, and circulates between the aeration chamber 1 and the device body for a certain period of time. After being purified, the treated water outflow line P
4 leaks out of the system.

本発明は上記の浸漬型固着生物膜装置に次のような制御
方式を組み込むことから成っている。
The present invention consists of incorporating the following control system into the above-mentioned immersion type fixed biofilm device.

すなわち、原廃水中のアンモニア濃度をアンモニア濃度
検知器AEにより検知し濃度指示計AIにより示された
数値は演算器CCに入る。
That is, the ammonia concentration in the raw wastewater is detected by the ammonia concentration detector AE, and the numerical value indicated by the concentration indicator AI is input to the calculator CC.

次に原廃水の流入量を流量検出計FBIにより検知し、
流量指示計FIにより示された数値は演算器CCに入る
Next, the flow rate detector FBI detects the inflow of raw wastewater,
The numerical value indicated by the flow rate indicator FI is input to the calculator CC.

アンモニア濃度と流量の関係から演算器CCでは必要空
気量を演算し、その信号は空気調節バルブV−1に送ら
れ空気量の調節を行なう。
A calculation unit CC calculates the required amount of air from the relationship between the ammonia concentration and the flow rate, and the signal is sent to the air adjustment valve V-1 to adjust the amount of air.

空気量が変化すると曝気室の水流速が変化し、その結果
、循環水量も変化する。
When the amount of air changes, the water flow rate in the aeration chamber changes, and as a result, the amount of circulating water also changes.

この関係を式で示すと次のようになる。This relationship is expressed as follows.

q二(V+△V)・S・ε ■ Q−v−8・(1−ε) ■ q:空気量 V:曝気室の水流速 S:曝気室面積 △V:気泡の上昇速度 ε:ボイド比 Q:循環水量 循環水量の調節は循環水ラインP3に流量検出器FE2
を設は流量指示調節計FICによりバルブV−2の制御
を行なうことにより循環水量をある一定値に保つもので
ある。
q2 (V+△V)・S・ε ■ Q−v−8・(1−ε) ■ q: Air volume V: Water flow rate in the aeration chamber S: Aeration chamber area △V: Rising speed of bubbles ε: Void Ratio Q: Circulating water amount To adjust the circulating water amount, use the flow rate detector FE2 in the circulating water line P3.
The system is designed to maintain the amount of circulating water at a certain constant value by controlling valve V-2 using a flow rate indicator controller FIC.

即ち、本発明では空気量はどれだけ変っても循環水量は
変化させないというものである。
That is, in the present invention, no matter how much the amount of air changes, the amount of circulating water does not change.

本発明により次のような効果が奏せられる。The present invention provides the following effects.

(1) 原水のアンモニア濃度や水量の変動に対して
も常に安定した水質が得られる。
(1) Stable water quality can always be obtained despite fluctuations in the ammonia concentration and water volume of raw water.

(2)運転を自動化したことにより装置管理に要する労
力が大幅に削減される。
(2) By automating the operation, the labor required for equipment management is significantly reduced.

(3)循環水量をコントロールできるため、モジュール
に付着した微生物がはがれ処理効率が悪化する心配がな
くなる。
(3) Since the amount of circulating water can be controlled, there is no need to worry about microorganisms attached to the module coming off and deteriorating treatment efficiency.

実施例 原水アンモニア濃度30〜100 ppmの生活廃水を
、水温10〜30℃、処理水量1rrL′/時間で、次
のような構造の浸漬型固着生物膜装置で処理した。
Example Domestic wastewater having a raw water ammonia concentration of 30 to 100 ppm was treated at a water temperature of 10 to 30 DEG C. and a treatment rate of 1 rrL'/hour using a submerged fixed biofilm device having the following structure.

空気送風量は次のようにして制御した。The air flow rate was controlled as follows.

循環水量は次のようにして制御した。The amount of circulating water was controlled as follows.

試験結果 ■空気量・循環水量の制 御をしなかった場合 上記試験結果を比較してわかるように、原水のアンモニ
ア濃度の変動に対し空気量、循環水量の制御を行った場
合の効果が非常に大きいことがわかる。
Test results - When air volume and circulating water volume were not controlled As can be seen by comparing the test results above, controlling air volume and circulating water volume was extremely effective against fluctuations in the ammonia concentration of raw water. You can see that it's big.

■制御を行なった場合■When controlling

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

第1図は浸漬型固着生物処理装置の概要を示し、第2図
は本発明方法の概要を示すものである。
FIG. 1 shows an overview of the immersion type sessile biological treatment apparatus, and FIG. 2 shows an overview of the method of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 モジュール充填部と曝気室とが別体である固着生物
膜式廃水処理装置により廃水処理する方法において、原
廃水のアンモニア濃度および流量の検知に基づいて曝気
室への送入空気量の調整を行うと共に、モジュール充填
部から曝気室への循環水ラインに設けられた流量指示調
節計により循環水量を一定値に制御することを特徴とす
る廃水処理方法。
1 In a wastewater treatment method using a fixed biofilm wastewater treatment device in which the module filling part and the aeration chamber are separate, the amount of air fed to the aeration chamber is adjusted based on the detection of the ammonia concentration and flow rate of raw wastewater. A wastewater treatment method characterized in that the amount of circulating water is controlled to a constant value by a flow rate indicating controller installed in a circulating water line from a module filling part to an aeration chamber.
JP53050743A 1978-05-01 1978-05-01 Wastewater treatment method Expired JPS5915714B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53050743A JPS5915714B2 (en) 1978-05-01 1978-05-01 Wastewater treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53050743A JPS5915714B2 (en) 1978-05-01 1978-05-01 Wastewater treatment method

Publications (2)

Publication Number Publication Date
JPS54144758A JPS54144758A (en) 1979-11-12
JPS5915714B2 true JPS5915714B2 (en) 1984-04-11

Family

ID=12867312

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53050743A Expired JPS5915714B2 (en) 1978-05-01 1978-05-01 Wastewater treatment method

Country Status (1)

Country Link
JP (1) JPS5915714B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109467283B (en) * 2018-12-25 2020-09-08 湖南智水环境工程有限公司 Sewage treatment equipment suitable for multi-household domestic sewage treatment

Also Published As

Publication number Publication date
JPS54144758A (en) 1979-11-12

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