JPH08103780A - Biological treatment device - Google Patents

Biological treatment device

Info

Publication number
JPH08103780A
JPH08103780A JP6266098A JP26609894A JPH08103780A JP H08103780 A JPH08103780 A JP H08103780A JP 6266098 A JP6266098 A JP 6266098A JP 26609894 A JP26609894 A JP 26609894A JP H08103780 A JPH08103780 A JP H08103780A
Authority
JP
Japan
Prior art keywords
tank
biofilm
raw water
contact aeration
filter
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
JP6266098A
Other languages
Japanese (ja)
Inventor
Mikio Kitagawa
幹夫 北川
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water 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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP6266098A priority Critical patent/JPH08103780A/en
Publication of JPH08103780A publication Critical patent/JPH08103780A/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)
  • Filtration Of Liquid (AREA)

Abstract

PURPOSE: To treat the waste water of medium concentration with high degree of performance under heavy loads by effecting, in one treatment tank, contact aeration and filtration by means of floating filter medium. CONSTITUTION: The interior of a treatment tank 10, in which raw water is supplied to the bottom thereof and the raw water flows upward, is divided into an upper section 14 and a lower section 12, and packing materials 13 or which biomembranes are deposited are provided in the lower section 12 and a filter layer 16 comprising floating filter medium is provided in the upper section 14.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、産業廃水(原水)を
生物膜によって接触曝気処理し、次いでその処理水を濾
過、又は生物濾過する生物処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biological treatment apparatus for subjecting industrial wastewater (raw water) to contact aeration treatment with a biofilm and then filtering or biofiltering the treated water.

【0002】[0002]

【従来の技術】塩化ビニリデンや、塩化ビニール、ナイ
ロン等の化学繊維を紐状又は環状に加工した加工物や、
プラスチックの板片等に生物膜を付着、増殖させ、これ
を充填材にして原水を接触曝気処理し、原水中の溶解性
有機物成分を除去してBODを低減することは従来から
一般に行われている。又、ポリスチレンや、ポリプロピ
レン、ウレタン樹脂等を直径3〜10mm程度の球状や
不定形状に発泡成形した比重が1以下の極めて小さい浮
上性濾材に生物膜を付着させて濾層を構成し、これに原
水を上向流で通水し、同様に原水中の溶解性有機物成分
を除去してBODを低減する生物膜濾過も公知である。
2. Description of the Related Art Processed products obtained by processing chemical fibers such as vinylidene chloride, vinyl chloride, nylon, etc. into a string or ring,
It has been generally practiced in the past to reduce the BOD by attaching and growing a biofilm on a plastic plate or the like, using this as a filler, and subjecting raw water to contact aeration treatment to remove soluble organic components in the raw water. There is. In addition, a biological membrane is attached to an extremely small floating filter medium having a specific gravity of 1 or less, which is formed by foaming polystyrene, polypropylene, urethane resin or the like into a spherical or irregular shape having a diameter of about 3 to 10 mm to form a filter layer. Biofilm filtration is also known, in which raw water is passed in an upward flow, and similarly, soluble organic components in the raw water are removed to reduce BOD.

【0003】[0003]

【発明が解決しようとする課題】上記接触曝気処理の課
題は、充填材に過剰に付着した生物膜による充填材同志
の間隙の閉塞である。充填材に付着する生物膜の膜厚を
一定に調整することができれば、接触曝気の適用排水の
BOD濃度は中濃度域まで拡大し、高負荷運転が可能に
なるが、現状では好適な膜厚調整手段が無いため、接触
曝気は主にBODが100mg/立以下の低濃度排水を
対象とし、BOD負荷量1kg/m3 ・日以下の低負荷
領域が適用範囲になっている。そして100mg/立以
上の中濃度排水に適用したり、又は高負荷域で運転する
と、充填材に付着する生物膜の膜厚が増加し、充填材同
志の間隙が閉塞したり、生物膜への酸素の供給が不十分
になり、その結果、処理水の水質が大幅に悪化する危険
がある。
The problem of the above contact aeration process is the blockage of the gap between the fillers by the biofilm excessively attached to the filler. If the film thickness of the biofilm adhering to the packing material can be adjusted to a constant value, the BOD concentration of the wastewater to which contact aeration is applied will expand to the middle concentration range, and high load operation will be possible. Since there is no adjustment means, contact aeration mainly targets low-concentration wastewater with a BOD of 100 mg / cubic or less, and the applicable range is the low-load region with a BOD load of 1 kg / m 3 · day or less. When applied to medium-concentration drainage of 100 mg / stand or more, or when operated in a high load area, the film thickness of the biofilm adhering to the packing material increases, the gap between the packing materials is blocked, and There is a risk that the supply of oxygen will be insufficient, and as a result, the quality of the treated water will deteriorate significantly.

【0004】又、生物膜濾過の課題は濾層の洗浄であ
り、洗浄時間が短く、洗浄排水量の少ない効率的な洗浄
方法が開発されれば、生物膜濾過の対象排水のBOD濃
度を中濃度域まで拡大することが可能であるが、有効な
洗浄方法がないため、BOD負荷量2〜5kg/m3
日の負荷で運転して居り、対象排水は接触曝気と同じく
低濃度排水であって、BOD100mg/立以上の中濃
度排水を対象にすると洗浄頻度が増加して効率的な運転
ができなくなったり、接触曝気と同じく浮上性濾材同志
の間隙の閉塞や、処理水の水質の悪化が生じる。
Further, the problem of biofilm filtration is to wash the filter layer. If an efficient cleaning method with a short cleaning time and a small amount of cleaning wastewater is developed, the BOD concentration of the wastewater to be subjected to the biofilm filtration will be a medium concentration. It is possible to expand to the range, but since there is no effective cleaning method, the BOD load amount is 2 to 5 kg / m 3 ·
We are operating on a daily load, and the target wastewater is low-concentration wastewater as well as contact aeration, and if we target medium-concentration wastewater with a BOD of 100 mg / stand or more, the cleaning frequency will increase and efficient operation will not be possible, Similar to contact aeration, the gap between the floatable filter media will be blocked and the quality of treated water will deteriorate.

【0005】[0005]

【課題を解決するための手段】この発明は、接触曝気
と、濾過又は生物濾過の従来の問題点を同時に解消する
ことを目的に開発されたのであって、槽底に原水が供給
され、原水が上向流する処理槽の内部を上部と下部に区
分し、下部に生物膜が付着した充填材を設け、上部に浮
上性濾材による濾層を設けたことを特徴とする。
The present invention was developed for the purpose of simultaneously solving the conventional problems of contact aeration and filtration or biological filtration, and the raw water is supplied to the bottom of the tank to obtain the raw water. Is divided into an upper part and a lower part, a filler having a biofilm attached thereto is provided at the lower part, and a filter layer made of a floating filter material is provided at the upper part.

【0006】[0006]

【実施例】図示の実施例において、10は処理槽で、原
水は給水管11で槽底に供給され、槽内を上向流する。
槽内を下部12と上部14に区分し、下部には接触曝気
用の紐状充填材13を多数本、縄ノレン状に吊り下げ
た。紐状充填材の設置量は、充填材の形状にもよるが、
紐の直径が10〜30mmでは槽の1m3 当り50〜2
00mが適当であり、表面には生物膜が付着してある。
In the illustrated embodiment, 10 is a treatment tank, and raw water is supplied to the bottom of the tank by a water supply pipe 11 and flows upward in the tank.
The inside of the tank was divided into a lower part 12 and an upper part 14, and a large number of cord-like fillers 13 for contact aeration were suspended in the lower part in a rope-like shape. The installation amount of the string-shaped filler depends on the shape of the filler,
If the diameter of the string is 10 to 30 mm, 50 to 2 per 1 m 3 of the tank
00m is suitable and has a biofilm attached to the surface.

【0007】槽内の上方には金網などのストレーナ15
を設置し、その下に浮上性濾材による濾層16を設け
る。浮上性濾材は浮力でストレーナの下に密集して処理
槽内の上部14に濾層16を構成する。濾層の高さは、
接触曝気用の充填材13よりも高くする。又、槽底には
散気管17を敷設する。
A strainer 15 such as a wire mesh is provided above the tank.
Is installed, and a filter layer 16 made of a floatable filter material is provided below the filter. The buoyant filter media is buoyantly concentrated under the strainer to form a filter layer 16 on the upper portion 14 in the processing tank. The height of the filter layer is
It is made higher than the filler 13 for contact aeration. An air diffuser 17 is laid on the bottom of the tank.

【0008】処理を行うには給水管で処理槽の底部に原
水を供給して処理槽内を上向流させると同時に、散気管
17から空気を供給し、充填材13に付着する生物膜の
活性を維持する。原水は処理槽の下部を上向流する際に
充填材13に付着した生物膜と接触し、原水中の溶解性
有機物は生物膜で分解処理される。
In order to carry out the treatment, raw water is supplied to the bottom of the treatment tank by a water supply pipe to cause an upward flow in the treatment tank, and at the same time, air is supplied from the diffuser pipe 17 to remove biofilms adhering to the packing material 13. Stay active. When the raw water flows upward in the lower part of the treatment tank, it comes into contact with the biofilm attached to the packing material 13, and the soluble organic substances in the raw water are decomposed by the biofilm.

【0009】原水が処理槽の上部の浮上性濾材による濾
層中を上向流する際、原水中のSSや、充填材13に付
着した生物膜の過剰に成長し、生物膜から剥れた汚泥は
濾層に捕捉される。
When the raw water flows upward in the filter layer formed by the floating filter material in the upper part of the treatment tank, SS in the raw water and the biofilm adhering to the packing material 13 excessively grow and are separated from the biofilm. Sludge is captured in the filter bed.

【0010】濾層を構成する浮上性濾材に生物膜を付着
させておいてもよく、その場合は充填材との接触曝気で
処理されなかった原水中の未分解の有機物を浮上性濾材
に付着した生物膜で分解処理することができる。
A biofilm may be adhered to the buoyant filter medium constituting the filter layer, in which case undecomposed organic matter in the raw water which has not been treated by contact aeration with the filler is adhered to the buoyant filter medium. The biofilm can be decomposed.

【0011】接触曝気部、浮上性濾材の濾層で処理され
た処理水は処理槽の上端の取出管18から取出す。
The treated water treated by the contact aeration unit and the filter layer of the floatable filter medium is taken out from the take-out pipe 18 at the upper end of the treatment tank.

【0012】処理槽内の下部の接触曝気部の充填材13
に過剰に生物膜が付着したり、上部の浮上性濾材による
濾層にSSや汚泥が過剰に捕捉されて濾層の圧力損失が
増加した際は洗浄を行う。洗浄は原水の通水を停止した
後、槽内の液の一部を槽底部の排水管19から引き抜
き、濾層の高さを接触曝気部の位置まで下げる(図2参
照)。この状態で、槽底部の散気管から空気を供給し、
濾層の浮上性濾材を空気で攪拌し流動させる。この浮上
性濾材の流動時に、充填材13の表面に浮上性濾材が衝
突したり接触することにより、濾層に過剰に捕捉されて
いた汚泥やSSが剥離すると共に、充填材13の表面か
らも過剰な生物膜が剥離される。
Filler 13 in the lower contact aeration section in the processing tank
When excessive biofilm adheres to the filter or SS or sludge is excessively trapped in the filter layer formed by the floating filter material on the upper side and pressure loss of the filter layer increases, cleaning is performed. For cleaning, after stopping the passage of raw water, a part of the liquid in the tank is pulled out from the drain pipe 19 at the bottom of the tank, and the height of the filter layer is lowered to the position of the contact aeration section (see FIG. 2). In this state, supply air from the air diffuser at the bottom of the tank,
The floatable filter medium in the filter layer is agitated with air to flow. During the flow of the buoyant filter medium, the buoyant filter medium collides with or comes into contact with the surface of the filler 13, whereby the sludge and SS excessively trapped in the filter layer are peeled off, and also from the surface of the filler 13. Excess biofilm is stripped.

【0013】散気管からの空気による浮上性濾材の流動
を行ったら空気の供給を停止し、排水管19の弁を開い
て槽に残った液を排出する。剥離した汚泥やSSはその
液と一緒に槽外に排出される。
When the buoyant filter medium is caused to flow by the air from the air diffuser, the air supply is stopped, the valve of the drain pipe 19 is opened, and the liquid remaining in the tank is discharged. The sludge and SS that have peeled off are discharged outside the tank together with the liquid.

【0014】槽内液の排出が終ったら排水管の弁を閉
じ、槽内に上から工業用水や、処理水を供給管20で供
給して元通り水を張り、給水管11から原水を槽底に供
給して運転を再開する。
When the discharge of the liquid in the tank is completed, the valve of the drain pipe is closed, industrial water or treated water is supplied into the tank from above by the supply pipe 20, and the original water is filled. Supply to the bottom and restart operation.

【0015】尚、一回の洗浄で十分に汚泥やSSの剥
離、排出が行えなかった場合は、水張り後に再度洗浄を
行う。
If the sludge and SS cannot be sufficiently peeled and discharged in one washing, the washing is performed again after water filling.

【0016】図1の装置により通水試験と逆洗試験を行
った。接触曝気の充填材には、市販の紐状バイオループ
(クレハ化学製、素材は塩化ビニリデン)を用い、生物
濾過の浮上性濾材には、発泡ポリプロピレン製の粒径が
3〜5mm、比重が乾燥状態で0.3〜0.5の微細粒
子を用いた。処理槽には直径400mm、高さ3000
mmの透明カラムを用い、装置底部から曝気用空気と原
水を供給し、カラム上部には開口部が2mm以下の網を
設置し、その網の下に発泡ポリプロピレン製の上記浮上
性濾材を高さ1000mm投入した。装置底部から50
0mm上に、高さ1000mmにわたって、長さ100
0mmのバイオループを10本、上下方向に設置した。
各バイオループは互いに接触したり絡まない構造とし
た。グルコースを主基質としたBOD300〜1000
mg/立の合成基質を、全処理槽容量(370L)当り
3〜8kg−BOD/m3 ・日の負荷量で通水し、接触
曝気部の紐状バイオループ表面に生物膜を付着させ、上
部の浮上性濾材に汚泥を付着させた。バイオループに付
着した生物膜量は、8〜12g−VSS/mであり、浮
上性濾材に捕捉された汚泥量は5.5〜7g−VSS/
3 であった。洗浄は1日に1回、原水の供給を停止
し、槽内液を底部から1500mmの位置まで引き抜
き、曝気用散気管から空気を供給し、発泡ポリプロピレ
ンを流動させ過剰な汚泥を剥離した後、槽内残存水を排
出後、槽上部から工業用水を注入した。この洗浄によ
り、過剰な汚泥や生物膜の排出は良好であった。これら
の運転により、合成基質のBOD濃度が1000mg/
立の中濃度で、BOD負荷量8kg/m3 ・日の高負荷
域において、BOD10〜15mg/立、SS15mg
/立以下の高度な処理水が安定して得られた。高度な処
理水が得られた要因は、槽下部の接触曝気部の紐状充填
材に付着した生物膜を活性の高い一定な膜厚に調整でき
たため、接触曝気部で90〜95%のBOD除去が可能
となったこと、又、槽上部の生物膜濾過で、接触曝気部
から発生した浮遊性の汚泥をほゞ完璧に捕捉すると共
に、接触曝気部で残留した僅かなBODを捕捉汚泥で処
理できたことによる。
A water flow test and a backwash test were conducted by the apparatus shown in FIG. A commercially available string-like bioloop (made by Kureha Chemical Co., Ltd., the material is vinylidene chloride) is used as the contact aeration filler, and the floatable filter material for biological filtration is made of expanded polypropylene and has a particle size of 3 to 5 mm and a specific gravity of dry. Fine particles of 0.3 to 0.5 were used in the state. The processing tank has a diameter of 400 mm and a height of 3000
A transparent column of mm is used, aeration air and raw water are supplied from the bottom of the device, a net with an opening of 2 mm or less is installed at the top of the column, and the floating filter material made of expanded polypropylene is placed under the net. 1000 mm was thrown in. 50 from the bottom of the device
0 mm above, over a height of 1000 mm, length 100
Ten 0 mm bioloops were installed vertically.
Each bioloop had a structure in which it did not touch or entangle with each other. BOD 300 to 1000 using glucose as a main substrate
mg / vertical synthetic substrate was passed through with a load of 3 to 8 kg-BOD / m 3 · day per total treatment tank capacity (370 L) to attach a biofilm to the surface of the string-like bioloop of the contact aeration unit, Sludge was adhered to the floatable filter medium on the upper part. The amount of biofilm attached to the bioloop is 8 to 12 g-VSS / m, and the amount of sludge captured on the floating filter medium is 5.5 to 7 g-VSS / m.
It was m 3 . The washing was stopped once a day, the raw water supply was stopped, the liquid in the tank was drawn to the position of 1500 mm from the bottom, air was supplied from the aeration pipe for aeration, and the expanded polypropylene was made to flow to remove excess sludge. After draining the residual water in the tank, industrial water was injected from the upper part of the tank. By this washing, excess sludge and biofilm were discharged well. By these operations, the BOD concentration of the synthetic substrate was 1000 mg /
BOD10-15mg / stand, SS15mg in the high concentration range of BOD load 8kg / m 3 · day at medium concentration
/ Highly treated water below the vertical was stably obtained. The reason why highly treated water was obtained was that the biofilm adhering to the string-like packing material in the contact aeration section at the bottom of the tank could be adjusted to a constant film thickness with high activity. It is possible to remove it, and the biofilm filtration at the top of the tank captures almost completely the floating sludge generated from the contact aeration section, and captures a small amount of BOD remaining in the contact aeration section. It depends on what could be processed.

【0017】[0017]

【発明の効果】以上で明らかなように、本発明によれ
ば、処理槽の下部の接触曝気部では、高負荷域でのBO
D分解、上部の生物膜濾過部では残留BODの分解と、
汚泥やSSを濾過により捕捉し、この機能の異なる処理
の組合せ効果により、中濃度排水を高負荷で高度な処理
が可能になった。そして、槽下部の接触曝気の充填材を
洗浄することにより、中濃度排水を高負荷で処理しても
充填材が閉塞しないため、適用可能な排水濃度と、負荷
量が拡大される。更に、浮上性濾材を用いた生物膜濾過
を組み合わせているため、槽下部の接触曝気で残留した
BODや、洗浄で排出できなかったSSや、生物膜汚泥
が生物膜濾過で分解、捕捉されるため、高度な処理水が
得られる。
As is apparent from the above, according to the present invention, in the contact aeration section at the lower part of the processing tank, the BO in the high load region is increased.
D decomposition, decomposition of residual BOD in the upper biofilm filtration section,
Sludge and SS are captured by filtration, and due to the combined effect of treatments with different functions, medium-concentration wastewater can be treated highly under high load. By cleaning the contact aeration filler in the lower part of the tank, the filler does not clog even when the medium-concentration wastewater is treated under high load, so that the applicable wastewater concentration and the load amount can be expanded. Furthermore, since biofilm filtration using a floatable filter medium is combined, BOD remaining due to contact aeration at the bottom of the tank, SS that could not be discharged by washing, and biofilm sludge are decomposed and captured by biofilm filtration. Therefore, highly treated water can be obtained.

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

【図1】この発明の一実施例の運転時の断面図である。FIG. 1 is a sectional view of an embodiment of the present invention during operation.

【図2】図1の装置の洗浄状態の断面図である。FIG. 2 is a cross-sectional view of the apparatus of FIG. 1 in a cleaned state.

【符号の説明】[Explanation of symbols]

10 処理槽 11 原水の給水管 12 槽の下部 13 接触曝気用充填材 14 処理槽の上部 15 ストレーナ 16 浮上性濾材による濾層 17 散気管 18 処理水の取出管 19 洗浄水の排水管 20 水張り用の供給管 10 Treatment tank 11 Raw water supply pipe 12 Lower part of tank 13 Contact aeration filler 14 Upper part of treatment tank 15 Strainer 16 Filter layer with floating filter material 17 Air diffuser pipe 18 Treated water extraction pipe 19 Wash water drain pipe 20 For water filling Supply pipe

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/10 ZAB A B01D 29/08 540 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI technical display location C02F 3/10 ZAB A B01D 29/08 540 A

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 槽底に原水が供給され、原水が上向流す
る処理槽の内部を上部と下部に区分し、下部に生物膜が
付着した充填材を設け、上部に浮上性濾材による濾層を
設けたことを特徴とする生物処理装置。
1. A raw water is supplied to the bottom of the tank, and the inside of the treatment tank in which the raw water flows upward is divided into an upper part and a lower part, a filler having a biofilm attached to the lower part, and a filter with a floating filter material on the upper part. A biological treatment device having a layer.
JP6266098A 1994-10-06 1994-10-06 Biological treatment device Pending JPH08103780A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6266098A JPH08103780A (en) 1994-10-06 1994-10-06 Biological treatment device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6266098A JPH08103780A (en) 1994-10-06 1994-10-06 Biological treatment device

Publications (1)

Publication Number Publication Date
JPH08103780A true JPH08103780A (en) 1996-04-23

Family

ID=17426297

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6266098A Pending JPH08103780A (en) 1994-10-06 1994-10-06 Biological treatment device

Country Status (1)

Country Link
JP (1) JPH08103780A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000066502A1 (en) * 1999-04-30 2000-11-09 Dautais Jean Pierre Active purifying structures for lining and forming compact physico-biological filters
CN110526426A (en) * 2019-08-30 2019-12-03 佛山市大新农生物技术股份有限公司 A kind of fluidized bed for sewage treatment

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000066502A1 (en) * 1999-04-30 2000-11-09 Dautais Jean Pierre Active purifying structures for lining and forming compact physico-biological filters
CN110526426A (en) * 2019-08-30 2019-12-03 佛山市大新农生物技术股份有限公司 A kind of fluidized bed for sewage treatment

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