JPS6320596B2 - - Google Patents

Info

Publication number
JPS6320596B2
JPS6320596B2 JP55088831A JP8883180A JPS6320596B2 JP S6320596 B2 JPS6320596 B2 JP S6320596B2 JP 55088831 A JP55088831 A JP 55088831A JP 8883180 A JP8883180 A JP 8883180A JP S6320596 B2 JPS6320596 B2 JP S6320596B2
Authority
JP
Japan
Prior art keywords
cleaning
water
wastewater
air
less
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
JP55088831A
Other languages
Japanese (ja)
Other versions
JPS5715889A (en
Inventor
Juichi Fuchu
Yoshiro Hayashi
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.)
Ebara Corp
Original Assignee
Ebara Infilco Co 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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP8883180A priority Critical patent/JPS5715889A/en
Publication of JPS5715889A publication Critical patent/JPS5715889A/en
Publication of JPS6320596B2 publication Critical patent/JPS6320596B2/ja
Granted 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】[Detailed description of the invention]

〔産業上の利用分野〕 本発明は、下水、産業廃水その他の汚水などの
有機性汚水を浄化処理するために、好気性微生物
を生成させ汚水中の汚濁物質を吸着酸化分解させ
る好気性生物処理方法に関するものである。 〔従来の技術〕 一般に砂、アンスラサイト、活性炭、プラスチ
ツクろ材などの粒状充填材表面に好気性微生物を
付着させ有機性汚水を浄化する方法は、昨今各種
検討されている。中でも固定床状態で汚水と空気
または酸素を粒状充填層内で接触させ、間欠的に
洗浄して系外に汚泥を排水する方法は、汚泥また
は水を循環することなく処理できること、バルキ
ングが生じないこと、汚泥の閉塞を防止できるこ
と、ろ過作用があり沈降分離部が不要なこと、送
気による撹拌を期待しないためBOD除去に必要
な送気量だけで良いことなどの利点があり注目を
あびている。 この生物処理方法は粒状充填材層を固定床状態
で通水することにより、水処理で良く用いられて
いる清澄ろ過と類似している。従つて間欠的に行
う洗浄方法も清澄ろ過と同様な方法が行われてい
た。つまり、水逆洗(水逆洗速度:調和平均径3
〜4mmのアンスラサイトの場合1.3m3/m2・min)
により充填材層を30%程度膨張させ、充填材層の
流動化により充填材を洗浄する方法である。ま
た、マツトボールの発生を抑制するために、表洗
もしくは水逆洗前に空洗を行う方法もとられてい
る。 〔発明が解決しようとする問題点〕 しかしながら、生物処理法は清澄ろ過と基本的
にその原理を異にしており、清澄ろ過における洗
浄方法があてはまるとはとうてい考えられない。
実際に、清澄ろ過における洗浄方法を行つてみる
と、相当量の洗浄水量が必要となり、著しい場合
には処理水量の50%を越えることもしばしばあ
り、良好な洗浄方法とは言えず、ひいては効率的
な生物処理法とも言えないなど問題があつた。 本発明は、これら従来の問題点を配慮し、確実
で経済的かつ簡便な洗浄が可能で効率的な生物処
理を行いうる有効な方法を提供することを目的と
している。 〔問題点を解決するための手段〕 本発明は、汚水を各種の粒状媒体から選ばれた
一種または二種以上の比重2.2以下で粒径2〜10
mmの粒状媒体を充填した充填槽内で好気性生物処
理し、間欠的な粒状媒体の洗浄を行う際に、あら
かじめ1.5m3/m2・min以下の流速で空気洗浄を
行い、空気洗浄後1.5m3/m2・min以下の空気と
同時に0.6m3/m2・min以下の水を充填槽下部よ
り噴射し、その後0.6m3/m2・min以下の水で逆
洗浄し、洗浄排水を排出させる工程を少なくとも
2回以上行うことを特徴とする汚水の浄化方法で
ある。 〔実施例〕 本発明の実施態様を説明すると、まず中間捨水
を行い、比重2.2以下で粒径2〜10mmの粒状媒体
を充填した充填槽内の水位レベルを充填材層界面
より上に、好ましくは150〜300mmに配備した中間
捨水口まで低下させる。次に中間捨水弁を閉じ、
空気洗浄を行う。この空気洗浄は空気洗浄速度と
して1.5m3/m2・min以下で好ましくは0.6〜1.2
m3/m2・minであり空気洗浄時間は1〜5分が良
い。この操作では主に充填材層の表層部の生物膜
剥離を目的とする。引き続き空気洗浄を行いなが
ら、同時に水逆洗を行う。この水逆洗速度は0.6
m3/m2・min以下で好ましくは0.2〜0.6m3/m2
minである。空気・水同時洗浄時間は3分程度で
良い。この操作では空気と水のそれぞれの洗浄効
果を相乗的に利用し、充填材層全域の生物膜の剥
離及び剥離した生物膜の充填槽上部への移送を目
的とする。この操作中においては洗浄排水は充填
槽外部に排出しない。次に、空洗を停止し、水逆
洗のみとなる。水逆洗速度は前操作と同様で良
い。水逆洗時間は1〜3分が適当である。この操
作の目的は剥離した生物膜を充填材層から充填槽
上部への移送のためである。水逆洗終了後、中間
捨水弁を開とし、洗浄排水を系外に排出するが、
これら全工程を一単位としてこれを少なくとも2
回以上繰り返して行うものであるが、洗浄排水の
排出は中間捨水口に限らずオーバーフロータイプ
などの他の手法で行つてもよい。 なお前記空気又は水洗浄工程においては一般に
空気、水とも洗浄速度が高い方が洗浄効果も高
い。しかしながら1.5m3/m2・min以上の高い洗
浄速度で洗浄すると、粒状媒体と砂利などの支持
部材との混合が生じ、処理状況に悪影響を与え
る。空気・水同時洗浄時の最も効果的な洗浄速度
の組合せは、実験結果より空気:0.6〜1.5m3
m2・min、水:0.2〜0.6m3/m2・minであること
が判明した。また水洗浄速度を0.2〜0.6m3/m2
minとすると空気:水同時洗浄時に洗浄水を充填
槽外部に排出する必要もなくなり、かつ排出口に
特殊な形状のバツフルプレート等を配備しなくと
も良く、簡潔な充填槽となると同時に粒状媒体を
流出する弊害も全くなくなる。 また、空気単独洗浄時においても、空気・水同
時洗浄時の空気洗浄速度と同一の速度で、空気単
独洗浄の目的は十分達せられるし、水単独洗浄時
においても同様にその目的が達せられる。 従つて、本発明方法においては空気及び水洗浄
速度は常に一定の値で良く、それぞれの操作にお
いて特別な配慮はいらなくなる。 また洗浄回数については第1図に示すように1
回行うだけでは効果がうすい。逆つて少なくとも
2回、望むらくは3〜4回行つた方が良い。 なお本発明方法において用いられる粒状媒体と
しては、アンスラサイト、プラスチツクろ材、
砂、例えば人工骨材、人工ケイ砂、又は活性炭な
どの粒状媒体から選ばれた一種又は二種以上が用
いられ真比重2.2以下で粒径2〜10mmのものであ
る。 次に本発明方法と従来法とを比較してみると、
第1表の洗浄条件で第2表の結果となつた。 即ち、
[Industrial Application Field] The present invention is an aerobic biological treatment method in which aerobic microorganisms are generated to adsorb, oxidize, and decompose pollutants in wastewater in order to purify organic wastewater such as sewage, industrial wastewater, and other wastewater. It is about the method. [Prior Art] Various methods have recently been studied for purifying organic wastewater by attaching aerobic microorganisms to the surface of granular fillers such as sand, anthracite, activated carbon, and plastic filter media. Among these methods, methods in which sewage is brought into contact with air or oxygen in a granular packed bed in a fixed bed state, and the sludge is drained out of the system through intermittent cleaning, can be treated without circulating sludge or water and do not cause bulking. It is attracting attention because of its advantages, such as being able to prevent sludge clogging, having a filtration effect and not requiring a sedimentation separation section, and requiring only the amount of air that is needed to remove BOD since there is no expectation of stirring by air. . This biological treatment method is similar to clarifying filtration, which is often used in water treatment, by passing water through a bed of granular packing material in a fixed bed state. Therefore, the intermittent cleaning method was similar to clarifying filtration. In other words, water backwashing (water backwashing speed: harmonic mean diameter 3
~ 1.3m3 / m2・min for 4mm anthracite)
This method expands the filler layer by about 30% and washes the filler by fluidizing the filler layer. In addition, in order to suppress the occurrence of matte balls, a method of performing air washing before surface washing or water backwashing is also used. [Problems to be Solved by the Invention] However, the principle of the biological treatment method is fundamentally different from that of clarification filtration, and it is highly unlikely that the cleaning method used in clarification filtration would be applicable.
In fact, when the cleaning method used in clarification filtration is used, a considerable amount of cleaning water is required, and in extreme cases, it often exceeds 50% of the amount of treated water, so it cannot be said to be a good cleaning method, and it is not efficient. There were problems, such as the fact that it could not be called a biological treatment method. The present invention takes these conventional problems into consideration and aims to provide an effective method that enables reliable, economical, and simple cleaning and efficient biological treatment. [Means for Solving the Problems] The present invention provides wastewater with one or more granular media selected from various granular media with a specific gravity of 2.2 or less and a particle size of 2 to 10.
When conducting aerobic biological treatment in a tank filled with granular media of 1.5 mm and intermittent cleaning of the granular media, air cleaning is performed in advance at a flow rate of 1.5 m 3 /m 2 min or less, and after air cleaning is performed. Air of 1.5m 3 /m 2・min or less and water of 0.6m 3 /m 2・min or less are simultaneously injected from the bottom of the filling tank, and then backwashed with water of 0.6m 3 /m 2・min or less for cleaning. This method of purifying wastewater is characterized by performing the step of discharging wastewater at least twice. [Example] To explain the embodiment of the present invention, first, intermediate water is drained, and the water level in the packed tank filled with granular media with a specific gravity of 2.2 or less and a particle size of 2 to 10 mm is raised above the interface of the filler layer. Preferably, it is lowered to an intermediate drainage port located at 150 to 300 mm. Next, close the intermediate drainage valve,
Perform air cleaning. This air cleaning is performed at an air cleaning rate of 1.5 m 3 /m 2 ·min or less, preferably 0.6 to 1.2
m 3 /m 2 ·min, and the air cleaning time is preferably 1 to 5 minutes. This operation is mainly aimed at removing the biofilm from the surface layer of the filler layer. While continuing to clean the air, backwash with water at the same time. This water backwash rate is 0.6
m 3 /m 2 · min or less, preferably 0.2 to 0.6 m 3 /m 2 ·
It is min. The time required for simultaneous air and water cleaning is about 3 minutes. In this operation, the cleaning effects of air and water are used synergistically, and the purpose is to peel off the biofilm from the entire filling material layer and transfer the separated biofilm to the upper part of the filling tank. During this operation, cleaning waste water is not discharged to the outside of the filling tank. Next, air washing is stopped and only water backwashing is performed. The water backwashing speed may be the same as in the previous operation. A suitable time for water backwashing is 1 to 3 minutes. The purpose of this operation is to transfer the detached biofilm from the filler layer to the upper part of the fill tank. After water backwashing is completed, the intermediate drainage valve is opened and the cleaning wastewater is discharged out of the system.
All these processes are considered as one unit, and this is divided into at least 2
Although this process is repeated several times, the discharge of cleaning wastewater is not limited to the intermediate drainage port, and may be performed using other methods such as an overflow type. In addition, in the air or water cleaning step, generally speaking, the higher the cleaning speed of both air and water, the higher the cleaning effect. However, when cleaning at a high cleaning rate of 1.5 m 3 /m 2 ·min or higher, mixing of the granular media with supporting members such as gravel occurs, which adversely affects the treatment situation. According to experimental results, the most effective combination of cleaning speeds when simultaneously cleaning air and water is: air: 0.6 to 1.5 m 3 /
m 2 ·min, water: 0.2 to 0.6 m 3 /m 2 ·min. In addition, the water cleaning speed should be adjusted to 0.2 to 0.6 m3 / m2 .
If it is set to min, there is no need to discharge cleaning water outside the filling tank during simultaneous air/water cleaning, and there is no need to install a specially shaped buttful plate at the discharge port. The negative effects of leaking the data will also be completely eliminated. Furthermore, the purpose of air cleaning alone can be sufficiently achieved at the same speed as the air cleaning speed when air and water are simultaneously cleaned, and the purpose can be achieved similarly when cleaning water alone. Therefore, in the method of the present invention, the air and water cleaning rates can always be kept at constant values, and no special consideration is required in each operation. In addition, the number of washings is 1 as shown in Figure 1.
Just doing it once will not have much effect. It is better to do this at least twice, preferably three or four times. The granular media used in the method of the present invention include anthracite, plastic filter media,
One or more types of sand selected from granular media such as artificial aggregate, artificial silica sand, and activated carbon are used, and the sand has a true specific gravity of 2.2 or less and a particle size of 2 to 10 mm. Next, when comparing the method of the present invention and the conventional method,
The washing conditions shown in Table 1 resulted in the results shown in Table 2. That is,

【表】 注−1 本発明方法は2回繰り返す
−2 充填材層は1.5mである
−3 粒状媒体はアンスラサイト(調和平
均径3mm)を使用
[Table] Note-1 The method of the present invention is repeated twice.
-2 Filler layer is 1.5m
-3 The granular medium uses anthracite (harmonic mean diameter 3 mm)

〔発明の効果〕〔Effect of the invention〕

本発明は、微生物接触用充填材からなる充填材
層内に好気的状態下で汚水を流過させ汚水中の汚
濁物質を吸着酸化分解処理する方法において洗浄
水量も少なく確実で経済的な洗浄方法が可能とな
り、効率的な生物処理が行え、バルキングも生じ
ないし、しかも適宜に逆洗することができるので
汚泥の閉塞を防止できると共に、従来の問題点を
も解決でき、充填材を常に浸水して処理すれば防
臭対策が容易となり運転管理も簡易化できる。
The present invention provides reliable and economical cleaning with a small amount of washing water in a method of adsorbing, oxidizing and decomposing pollutants in wastewater by passing wastewater under aerobic conditions through a filler layer made of a filler for contact with microorganisms. This method enables efficient biological treatment, does not cause bulking, and can be backwashed as appropriate, which prevents sludge clogging and solves the conventional problems, allowing the filler to be constantly submerged in water. If this treatment is carried out, deodorizing measures can be easily taken and operation management can be simplified.

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

第1図は洗浄効果を示す洗浄率と洗浄工程回数
との関係線図である。
FIG. 1 is a diagram showing the relationship between the cleaning rate and the number of cleaning steps, showing the cleaning effect.

Claims (1)

【特許請求の範囲】 1 汚水を各種の粒状媒体から選ばれた一種また
は二種以上の比重2.2以下で粒径2〜10mmの粒状
媒体を充填した充填槽内で好気性生物処理し、間
欠的な粒状媒体の洗浄を行う際に、あらかじめ
1.5m3/m2・min以下の流速で空気洗浄を行い、
空気洗浄後1.5m3/m2・min以下の空気と同時に
0.6m3/m2・min以下の水を充填槽下部より噴射
し、その後0.6m3/m2・min以下の水で逆洗浄し、
洗浄排水を排出させる工程を少なくとも2回以上
行うことを特徴とする汚水の浄化方法。 2 前記粒状媒体が、アンスラサイト・プラスチ
ツクろ材・砂・活性炭等の粒状媒体から選ばれた
ものであつて、充填材層に気体を充填材層下部に
設けた散気装置から送入して好気的状態下を維持
して処理されるものである特許請求の範囲第1項
記載の汚水の浄化方法。 3 前記洗浄終了後の洗浄排水が前記充填材層界
面上部より排出されて処理されるものである特許
請求の範囲第1項又は第2項記載の汚水の浄化方
法。 4 前記洗浄工程が予め中間捨水を行つて充填槽
内の水位レベルを充填材層界面より上でその近傍
位置まで低下させて空気洗浄を行うものである特
許請求の範囲第2項又は第3項記載の汚水の浄化
方法。
[Scope of Claims] 1. Sewage is subjected to aerobic biological treatment in a tank filled with one or more types of granular media selected from various granular media with a specific gravity of 2.2 or less and a particle size of 2 to 10 mm, and is treated intermittently. When cleaning granular media,
Perform air cleaning at a flow rate of 1.5m 3 /m 2・min or less,
At the same time with air below 1.5m 3 /m 2・min after air cleaning
Water of 0.6m 3 /m 2・min or less is injected from the bottom of the filling tank, and then backwashed with water of 0.6m 3 /m 2・min or less.
A method for purifying sewage characterized by performing the step of discharging washing wastewater at least twice. 2. The granular medium is selected from granular media such as anthracite, plastic filter media, sand, activated carbon, etc., and the gas is preferably introduced into the filler layer from an aeration device provided at the bottom of the filler layer. A method for purifying wastewater according to claim 1, wherein the wastewater is treated while maintaining an air condition. 3. The wastewater purification method according to claim 1 or 2, wherein the cleaning wastewater after the cleaning is completed is discharged from the upper part of the interface of the filler layer and treated. 4. Claim 2 or 3, wherein the cleaning step is performed in advance by performing intermediate water drainage to lower the water level in the filling tank to a position above and near the filling material layer interface to perform air cleaning. Method for purifying sewage as described in section.
JP8883180A 1980-06-30 1980-06-30 Purification method for sewage Granted JPS5715889A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8883180A JPS5715889A (en) 1980-06-30 1980-06-30 Purification method for sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8883180A JPS5715889A (en) 1980-06-30 1980-06-30 Purification method for sewage

Publications (2)

Publication Number Publication Date
JPS5715889A JPS5715889A (en) 1982-01-27
JPS6320596B2 true JPS6320596B2 (en) 1988-04-28

Family

ID=13953881

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8883180A Granted JPS5715889A (en) 1980-06-30 1980-06-30 Purification method for sewage

Country Status (1)

Country Link
JP (1) JPS5715889A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0716672B2 (en) * 1986-02-27 1995-03-01 オルガノ株式会社 Immersion filter method cleaning method
JPH0683830B2 (en) * 1988-03-09 1994-10-26 栗田工業株式会社 Biological filtration device cleaning method
JPH0229491U (en) * 1988-08-15 1990-02-26
FR2639934B1 (en) * 1988-12-05 1991-03-22 Prod Indls Charbons Actifs BIOLOGICAL WATER PURIFICATION CONTACTOR FOR THE PRODUCTION OF DRINKING WATER AND ASSOCIATED PILOTAGE METHOD
KR20010010073A (en) * 1999-07-15 2001-02-05 윤덕용 Method for Removing of Excess Biomass in Packed Bed Biofilter
KR100492933B1 (en) * 2002-10-25 2005-06-02 ㈜유성이엔티 A drop off device of biofilter deodorizer and the drop off method

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5491960A (en) * 1977-12-29 1979-07-20 Omnium Assainissement Method of biologically purifying water

Also Published As

Publication number Publication date
JPS5715889A (en) 1982-01-27

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