JP3374766B2 - Anaerobic treatment equipment for organic wastewater - Google Patents

Anaerobic treatment equipment for organic wastewater

Info

Publication number
JP3374766B2
JP3374766B2 JP29516298A JP29516298A JP3374766B2 JP 3374766 B2 JP3374766 B2 JP 3374766B2 JP 29516298 A JP29516298 A JP 29516298A JP 29516298 A JP29516298 A JP 29516298A JP 3374766 B2 JP3374766 B2 JP 3374766B2
Authority
JP
Japan
Prior art keywords
section
sludge
wall
settling
baffle
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 - Lifetime
Application number
JP29516298A
Other languages
Japanese (ja)
Other versions
JP2000117285A (en
Inventor
元之 依田
康雄 武田
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 JP29516298A priority Critical patent/JP3374766B2/en
Priority to TW88117220A priority patent/TW475920B/en
Priority to CNB991222016A priority patent/CN1182050C/en
Priority to KR19990044420A priority patent/KR100595109B1/en
Publication of JP2000117285A publication Critical patent/JP2000117285A/en
Application granted granted Critical
Publication of JP3374766B2 publication Critical patent/JP3374766B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2846Anaerobic digestion processes using upflow anaerobic sludge blanket [UASB] reactors
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2866Particular arrangements for anaerobic reactors
    • C02F3/2873Particular arrangements for anaerobic reactors with internal draft tube circulation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Microbiology (AREA)
  • Chemical & Material Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Organic Chemistry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

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

【0001】[0001]

【発明の属する技術分野】この発明は有機性排水中の有
機物を、沈積層を構成する嫌気性微生物からなるグラニ
ュールや、その前駆体(小粒径のグラニュール)である
自己造粒汚泥(単に汚泥とも記す。)で最終的にメタン
と二酸化炭素を主成分とする嫌気性ガスに分解して有機
物を除去し、有機物の分解が済んだ処理水を、発生した
嫌気性ガス、及び汚泥から分離して取出すUASB式
(上向流スラッジブランケット式)嫌気性処理装置に関
する。
TECHNICAL FIELD The present invention relates to granules composed of anaerobic microorganisms forming sedimentation layers and self-granulating sludge (precursor of small particle size) for organic matter in organic wastewater. It is also referred to simply as sludge.) Finally, it decomposes into anaerobic gas consisting mainly of methane and carbon dioxide to remove organic matter, and the treated water after decomposition of organic matter is removed from the generated anaerobic gas and sludge. The present invention relates to a UASB type (upflow sludge blanket type) anaerobic treatment device that is separated and taken out.

【0002】[0002]

【従来の技術】本特許出願人は、特願平10−1024
91号により底部に嫌気性汚泥層と、該汚泥層中に有機
性排水を上向流で供給する給水管とを有する反応部を備
えた処理槽の内部の上記反応部の上の水中に、尖端部を
下に向けた錐形の沈殿部を浸漬して配置すると共に、上
記沈殿部の回りに上端部が槽内の液面上に突出し、下端
部が上記沈殿部の高さの途中の水中に位置する直立筒壁
と、この直立筒壁の下端部から前記沈殿部の下端に向か
って近付く傾斜壁と、前記沈殿部の上の直立筒壁の内部
には下向きに窄って下端が沈殿部の内部に上から浅く突
入すると共に、上部に槽内の液面から処理水が溢入する
溢入樋を備えた仕切壁と、前記沈殿部の外面に設けら
れ、直立筒壁の下端部内面に向かって斜め下向きに突出
する邪魔板と、前記沈殿部の底に溜まる汚泥を沈殿部の
外に排出して反応部に返送する返送ポンプを接続した汚
泥返送管とを設けた有機性排水の嫌気性処理装置を提案
した。
2. Description of the Related Art The applicant of the present patent application is Japanese Patent Application No. 10-1024.
No. 91 anaerobic sludge layer at the bottom, and in the water above the reaction section inside the treatment tank having a reaction section having a water supply pipe for supplying organic wastewater in the sludge layer in an upward flow, While arranging by immersing the conical precipitation part with the pointed part facing downward, the upper end projects above the liquid surface in the tank around the precipitation part, and the lower end part is in the middle of the height of the precipitation part. An upright tubular wall located in water, an inclined wall approaching from the lower end of the upright tubular wall toward the lower end of the settling section, and an upright tubular wall above the settling section is constricted downward and the lower end is A partition wall equipped with an overflow gutter that rushes into the settling section shallowly from above and at the top of which the treated water overflows from the liquid level in the tank, and the lower end of the upright cylindrical wall provided on the outer surface of the settling section. Baffle plate that projects obliquely downward toward the inner surface of the part, and sludge that accumulates at the bottom of the settling part is discharged to the outside of the settling part and the reaction part Proposed anaerobic treatment apparatus of the organic waste water having a sludge return pipe which connects the return pump to return.

【0003】[0003]

【発明が解決しようとする課題】上記先行装置では尖端
部を下に向けた錐形の沈殿部の底に沈降した汚泥は、返
送ポンプを接続した汚泥返送管を使用し、返送ポンプの
運転により反応部に返送しているが、沈殿部内への汚泥
の流入が増加すると返送ポンプでは排除しきれず、沈殿
部の空間が沈降分離に有効に利用できなくなる可能性が
ある。そのためにはポンプの稼働台数、稼働時間、頻度
調整を行って沈殿部に汚泥をできるだけ貯めこないよう
に運転を行わねばならず、運転が煩雑になる。
In the above-mentioned prior device, sludge settled on the bottom of the pyramid-shaped settling part with the pointed tip facing downward uses the sludge return pipe connected to the return pump, and the sludge return pipe is operated by the operation of the return pump. Although it is returned to the reaction section, if the flow of sludge into the settling section increases, it cannot be completely removed by the return pump, and the space in the settling section may not be effectively used for sedimentation separation. For that purpose, the number of operating pumps, the operating time, and the frequency must be adjusted so that the sludge is not stored in the sedimentation section as much as possible, and the operation becomes complicated.

【0004】[0004]

【課題を解決するための手段】本発明は上述した問題点
を解消するために開発されたもので、請求項1の有機性
排水の嫌気性処理装置は、底部に嫌気性汚泥層と、該汚
泥層中に有機性排水を上向流で供給する給水管とを有す
る反応部を備えた処理槽の内部の上記反応部の上の水中
に、尖端部を下に向けた錐形の沈殿部を浸漬して配置す
ると共に、上記沈殿部の回りに上端部が槽内の液面上に
突出し、下端部が上記沈殿部の高さの途中の水中に位置
する直立筒壁と、この直立筒壁の下端部から前記沈殿部
の下端に向かって近付く傾斜壁と、前記沈殿部の上の直
立筒壁の内部には下向きに窄って下端が沈殿部の内部に
上から浅く突入すると共に、上部に槽内の液面から処理
水が溢入する溢入樋を備えた仕切壁と、前記沈殿部の外
面に設けられ、直立筒壁の下端部内面に向かって斜め下
向きに突出する邪魔板とを設けた有機性排水の嫌気性処
理装置において、上記沈殿部の下端に山形断面のバッフ
ルを配置したことを特徴とする。又、請求項2の有機性
排水の嫌気性処理装置は、請求項1に記載の有機性排水
の嫌気性処理装置において、上記沈殿部の底の内部に一
端が開口し、他端部は槽内の液面上に突出したのち下向
きに折返し、仕切壁の外で槽内の液面中に突入する汚泥
の返送管と、前記山形断面のバッフルの頂部の内部に下
端が開口し、上端は上記汚泥の返送管の途中に接続した
上向きのガス抜き管とを設け、前記反応部で発生してバ
ッフルで捕集された嫌気性ガスを上記ガス抜き管により
汚泥返送管に供給し、汚泥返送管内に生じるガスリフト
作用でバッフルに捕集された汚泥と、沈殿部の底に沈降
した汚泥とを反応部に返送するようにしたことを特徴と
する。
The present invention was developed in order to solve the above-mentioned problems. An anaerobic treatment apparatus for organic wastewater according to claim 1 has an anaerobic sludge layer at the bottom, and A pyramidal sedimentation part with the tip facing downward in water above the reaction part inside the treatment tank having a reaction part having a water supply pipe for supplying organic wastewater in an upward flow into the sludge layer While arranging by immersing, the upper end portion projects above the liquid surface in the tank around the settling section, and the lower end section is positioned in the water in the middle of the height of the settling section, and the upright tube. An inclined wall approaching from the lower end of the wall toward the lower end of the settling section, and the inside of the upright cylindrical wall above the settling section is constricted downward and the lower end rushes into the inside of the settling section shallowly from above, A partition wall with an overflow gutter at the top where treated water overflows from the liquid level inside the tank, and an outer surface of the settling section. In anaerobic treatment apparatus of the organic waste water which is provided a baffle plate which projects obliquely downward toward the lower end portion inner surface of the cylindrical wall, characterized in that a baffle of chevron cross-section at the lower end of the precipitation section. The anaerobic treatment apparatus for organic wastewater according to claim 2 is the anaerobic treatment apparatus for organic wastewater according to claim 1, wherein one end is opened inside the bottom of the settling section and the other end is a tank. Inside of the baffle with the chevron cross section, the lower end opens, and the upper end is the upper end of the baffle with the chevron cross section, and the sludge return pipe that protrudes above the inner liquid surface and then folds downward and projects into the liquid surface inside the tank outside the partition wall. An upward gas vent pipe connected in the middle of the sludge return pipe is provided, and the anaerobic gas generated in the reaction section and collected by the baffle is supplied to the sludge return pipe by the gas vent pipe, and sludge return is performed. It is characterized in that the sludge collected by the baffle by the gas lift action generated in the pipe and the sludge settled at the bottom of the settling section are returned to the reaction section.

【0005】[0005]

【発明の実施の形態】図1,2、及び図3の各実施形態
において、10は頂部にガス抜き管10′を有する有蓋
の処理槽、12は処理槽の内部に形成された汚泥からな
る嫌気性汚泥層、13は上記嫌気性汚泥層中に原水(有
機性排水)を供給して上向流させる給水管であり、嫌気
性汚泥層を構成する汚泥は上向流する原水により処理槽
の高さの中程まで流動状態に展開する。原水の給水管1
3と、流動状態に展開する嫌気性汚泥層12とにより処
理槽内の下半部に反応部11が構成される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS In each of the embodiments of FIGS. 1, 2 and 3, 10 is a covered treatment tank having a gas vent pipe 10 'at the top, and 12 is sludge formed inside the treatment tank. An anaerobic sludge layer, 13 is a water supply pipe for supplying raw water (organic wastewater) into the anaerobic sludge layer for upward flow, and the sludge constituting the anaerobic sludge layer is treated by upward flow raw water. Deploys in a fluid state up to the middle of the height. Raw water supply pipe 1
3 and the anaerobic sludge layer 12 that develops in a fluidized state constitute a reaction section 11 in the lower half of the treatment tank.

【0006】処理槽10の内部の上記反応部11の上の
水中に、尖端部を下に向けた錐形の中空の沈殿部14を
浸漬して配置すると共に、処理槽は、上記沈殿部の回り
に上端部が槽内の液面W上に突出し、下端部が上記沈殿
部の高さの途中の水中に位置する直立筒壁15と、この
直立筒壁の下端部から前記沈殿部の下端に向かって近付
く傾斜壁16と、前記沈殿部の上の直立筒壁15の内部
に下半部が下向きに窄って下端が沈殿部の内部に上から
浅く突入する仕切壁17と、この仕切壁17の内側に沿
って立ち、仕切壁との間に処理水の溢入樋19を形成す
る起立壁18と、前記沈殿部の外面に設けられ、直立筒
壁の下端部内面に向かって斜め下向きに突出する邪魔板
20を備えている。
A pyramidal hollow settling section 14 with its tip facing downward is disposed by being immersed in water above the reaction section 11 inside the processing tank 10, and the treatment tank is An upright cylindrical wall 15 having an upper end projecting above the liquid surface W in the tank and a lower end located in water halfway along the height of the settling section, and a lower end of the upright tubed wall to a lower end of the settling section. An inclined wall 16 approaching toward the bottom of the settling section, a partition wall 17 in which the lower half portion is narrowed downward and the lower end is projected into the inside of the settling section from above from the upper part of the upright tubular wall 15 and the partition wall 17. Standing along the inside of the wall 17, a standing wall 18 that forms a treated water overflow gutter 19 with the partition wall and an outer surface of the settling portion, which is slanted toward the inner surface of the lower end portion of the upright tubular wall. The baffle plate 20 that projects downward is provided.

【0007】仕切壁17の上端は液面W上に突出してい
るが、下向きに深いV形切込み17′を有するので仕切
壁の外の液は上記V形切欠きを通って溢入樋19に入
る。又、起立壁18の上端は仕切壁よりも低く、液面と
ほゞ同レベルであるが浅いV形切込み18′を有するの
で起立壁18の内側の液はV形切込みを通って溢入樋1
9に入る。溢入樋19に入った液は処理水として処理槽
10の外に排水管21で排水される。
The upper end of the partition wall 17 projects above the liquid surface W, but since it has a deep V-shaped cutout 17 'facing downward, the liquid outside the partition wall passes through the V-shaped cutout and flows into the overflow trough 19. enter. Further, since the upper end of the standing wall 18 is lower than the partition wall and has a shallow V-shaped cut 18 'which is almost at the same level as the liquid surface, the liquid inside the standing wall 18 overflows the trough through the V-shaped cut. 1
Enter 9. The liquid that has entered the overflow gutter 19 is discharged as treated water outside the treatment tank 10 through a drain pipe 21.

【0008】尚、直立筒壁15は適宜の手段、例えば支
持アームなどで処理槽の内壁に固定する。処理槽は円筒
槽でも、多角筒槽でもよい。
The upright cylindrical wall 15 is fixed to the inner wall of the processing tank by an appropriate means such as a support arm. The treatment tank may be a cylindrical tank or a polygonal cylinder tank.

【0009】直立筒壁15は平面形状が正方形又は長方
形の四角筒で、その左右の側壁15a,15aの内側に
沿い、各端部を直立筒壁の相対向した端壁15b,15
bに固定して左右の仕切壁17、起立壁18が設けてあ
る。これにより溢入樋19は左右に独立して2つ形成さ
れるため、処理水の排水管21は各溢入樋19に対して
設ける。
The upright tube wall 15 is a square tube having a square or rectangular shape in plan view and extends along the inner sides of the left and right side walls 15a, 15a, with its end portions facing end walls 15b, 15 of the upright tube wall.
Left and right partition walls 17 and standing walls 18 are provided by fixing to b. As a result, two overflow gutters 19 are independently formed on the left and right sides, and therefore a drain pipe 21 for treated water is provided for each overflow gutter 19.

【0010】左右の仕切壁17の下向きに窄った下端部
が上から浅く突入する沈殿部14も、逆ハ字形の左右の
上部14′,14′を直立筒壁の相対向した端壁15
b,15bに固定されている。そして、沈殿部14は上
記左右の上部14′,14′、及び端壁15b,15b
から下向きに延長した中空の四角錐になっている。
Also in the settling portion 14 in which the lower end portions of the left and right partition walls 17 which are narrowed downward are projected from above, the left and right upper portions 14 ', 14' of the inverted C-shape are opposed to each other by the end walls 15 of the upright cylindrical wall.
It is fixed to b and 15b. The settling portion 14 includes the left and right upper portions 14 ', 14' and the end walls 15b, 15b.
It is a hollow quadrangular pyramid that extends downward from.

【0011】又、沈殿部の外面に設けれ、直立筒壁15
の下端部内面に向かって斜め下向きに突出する左右の邪
魔板20も、沈殿部の上部14′,14′と一緒に各端
部を直立筒壁の相対向した端壁15b,15bにハ字形
に固定されている。
The upright cylindrical wall 15 is provided on the outer surface of the sedimentation portion.
The left and right baffle plates 20 projecting obliquely downward toward the inner surface of the lower end of each of the end portions together with the upper portions 14 ', 14' of the settling portion are formed in a square shape on opposite end walls 15b, 15b of the upright cylindrical wall. It is fixed to.

【0012】そして、直立筒壁15の下端部から沈殿部
14の下端に向かって近付く左右の傾斜壁16,16
は、直立筒壁15の左右の側壁15a,15aが斜め下
向きに延びて形成されている。
Then, the left and right inclined walls 16, 16 approaching from the lower end of the upright cylindrical wall 15 toward the lower end of the settling portion 14.
The left and right side walls 15a, 15a of the upright cylindrical wall 15 are formed to extend obliquely downward.

【0013】直立筒壁の相対向した端壁15b,15b
には、左右の傾斜壁16,16の下端から左右の邪魔板
20,20、及び四角錐の沈殿部14の上端の相対向し
た端壁14a,14aに沿って切欠き22が形成されて
いる。
End walls 15b, 15b of the upright cylindrical wall which face each other.
A notch 22 is formed along the left and right baffle plates 20, 20 from the lower ends of the left and right inclined walls 16, 16 and the opposite end walls 14a, 14a of the upper end of the quadrangular pyramid settling portion 14. .

【0014】この実施形態では、図示してないが平面形
状が正方形の角形の処理槽10の中央部にそれよりも小
さい正方形の直立筒壁15を有する1つの処理部を設置
してあるが、処理部の設置数は任意であって処理槽10
の平面形状の大きさに応じ適宜定めればよい。
In this embodiment, although not shown, one processing section having a square upright cylindrical wall 15 smaller than that is installed in the central portion of a rectangular processing tank 10 having a square planar shape. The number of processing units installed is arbitrary and the processing tank 10
It may be determined as appropriate according to the size of the plane shape.

【0015】頂部を下に向けた中空な四角錐の沈殿部1
4の、下向き頂部の下端には頂部を上に向けた山形断面
のバッフル23を設ける。図1,2の実施形態のバッフ
ル23は中空の四角錐であるが、図2の四角錐の左右の
端は15bの距離に等しいか、それ以上とする。そし
て、図3に示したようにバッフルは中空な切妻屋根形で
もよい。この切妻屋根形バッフルの妻板と妻板の間の距
離は直立筒壁の端壁15b,15b間の距離に等しい
か、それよりも長くすることが好ましい。
Hollow quadrangular pyramid settling section 1 with the top facing down
4, a baffle 23 having a chevron section with the top facing upward is provided at the lower end of the downward facing top. Although the baffle 23 of the embodiment of FIGS. 1 and 2 is a hollow quadrangular pyramid, the left and right ends of the quadrangular pyramid of FIG. 2 are equal to or greater than a distance of 15b. And, as shown in FIG. 3, the baffle may have a hollow gable roof shape. The distance between the gable plates of the gable roof baffle is preferably equal to or longer than the distance between the end walls 15b and 15b of the upright cylindrical wall.

【0016】給水管13から処理槽内に供給されて反応
部11を上向流する原水(有機性汚水)は、嫌気性汚泥
層12を流動状態に展開して汚泥と接触し、含有する有
機物を嫌気性微生物で分解されて処理水となり、この処
理水は分解により生成して浮上する嫌気性のガスに随伴
し、一部の汚泥を伴って反応部11から更に上向流す
る。
Raw water (organic sewage), which is supplied from the water supply pipe 13 into the treatment tank and flows upward in the reaction section 11, spreads the anaerobic sludge layer 12 into a fluid state and comes into contact with the sludge to contain the organic matter. Is decomposed by anaerobic microorganisms into treated water, and the treated water accompanies the anaerobic gas that is generated by the decomposition and floats, and further flows upward from the reaction section 11 together with some sludge.

【0017】上向流するガスと汚泥を含んだ処理水の一
部はバッフル23に捕集される。残りの汚泥を含んだ処
理水とガスはバッフル23の回りを上向流し、その一部
は直立筒壁15の下端を狭くしている左右の傾斜壁1
6,16で導かれ、直立筒壁の回り、つまり該筒壁の左
右の側壁15a,15aと処理槽の内壁との間の上昇水
路25,25と、端壁15b,15bと処理槽の内壁と
の間の上昇水路26,26と、処理部を複数設けた場合
は隣接した直立筒壁の壁15a,15aや15b,15
bの間の上昇水路を上昇し、ガスは液面に浮上してガス
抜き管10′から外に放出される。残りの処理水とガス
は左右の傾斜壁16,16の下端と沈殿部14との間、
及び直立筒壁の相対向した端壁15b,15bに形成さ
れた切欠き22,22を通り、直立筒壁15と邪魔板2
0の間を通り抜けて上昇し、一部のガスは邪魔板20で
捕捉される。処理水とガスの一部は仕切壁17と直立筒
壁15との間を上向し、ガスは液面上に浮上してガス抜
き管から放出され、処理水は仕切壁17の切欠き17′
から溢入樋19,19に流入し、排水管21,21で系
外に排水される。
A part of the treated water containing upward gas and sludge is collected by the baffle 23. The treated water and the gas containing the remaining sludge flow upward around the baffle 23, and a part of the treated water and gas narrow the lower end of the upright cylindrical wall 15 and the left and right inclined walls 1
6, 16 and the rising water channels 25 and 25 around the upright cylindrical wall, that is, between the left and right side walls 15a and 15a of the cylindrical wall and the inner wall of the treatment tank, and the end walls 15b and 15b and the inner wall of the treatment tank. Between the rising water channels 26, 26 and adjacent walls 15a, 15a and 15b, 15 of the upright cylindrical wall when a plurality of processing units are provided.
Ascending in the ascending water channel between b, the gas floats on the liquid surface and is discharged to the outside from the degassing pipe 10 '. The remaining treated water and gas flow between the lower ends of the left and right inclined walls 16 and 16 and the sedimentation section 14,
And the upright cylinder wall 15 and the baffle plate 2 through the notches 22 and 22 formed in the end walls 15b and 15b of the upright cylinder wall facing each other.
Ascending through 0 and rising, some gas is trapped by baffle plate 20. A part of the treated water and the gas is directed upward between the partition wall 17 and the upright cylindrical wall 15, the gas floats above the liquid surface and is discharged from the degassing pipe, and the treated water is cut into the notch 17 of the partition wall 17. ′
Flows into the overflow gutters 19 and 19 and is discharged to the outside of the system by the drain pipes 21 and 21.

【0018】直立筒壁15と邪魔板20,20間を通り
抜けて上昇するガスと処理水の残部は仕切壁17,17
の下端部と沈殿部の上部14′,14′との間の隙間2
8,28を下向きに通り抜けて左右の仕切壁17,17
の間に流入するが、上昇流速と汚泥の沈降速度の差から
汚泥は沈殿部14に沈降し、ガスは液面に浮上してガス
抜き管で放出され、処理水は起立壁18,18に設けた
切欠き18′から溢入樋19,19に溢入し、排水管2
1,21が系外に排水される。
The balance of the gas and treated water that rises through the space between the upright cylindrical wall 15 and the baffles 20 and 20 is the partition walls 17 and 17.
Between the lower end of the bottom and the upper part 14 ', 14' of the settling part 2
Left and right partition walls 17, 17 passing downward through 8, 28
However, due to the difference between the ascending velocity and the sedimentation velocity of the sludge, the sludge settles in the sedimentation section 14, the gas floats to the liquid surface and is discharged through the degassing pipe, and the treated water flows into the standing walls 18 and 18. The overflow pipes 19 and 19 overflow from the notch 18 'provided, and the drain pipe 2
1, 21 are drained out of the system.

【0019】こうして、反応部から嫌気性ガスに伴って
上向流する処理水に含まれた汚泥の一部と、嫌気性ガス
の一部はバッフル23に捕集される。従って、沈殿部1
4に沈降する汚泥の量は少なくなると共に、処理水に混
ざって溢入樋19,19に流出する汚泥も少なくなるの
で水質のよい処理水が得られる。
In this manner, a part of the sludge contained in the treated water flowing upward from the reaction section along with the anaerobic gas and a part of the anaerobic gas are collected by the baffle 23. Therefore, the precipitation part 1
The amount of sludge settling in No. 4 is small and the amount of sludge mixed with the treated water and flowing out to the overflow gutters 19 and 19 is also small, so that treated water with good water quality can be obtained.

【0020】バッフル23に捕集された汚泥、沈殿部1
4に沈降した汚泥を反応部11に返送するため、沈殿部
14の底の内部に一端が開口し、他端部は槽内の液面上
に突出したのち下向きに折返し、仕切壁17の外で槽内
の液面上に開口しているか、又は液面中に突入する汚泥
の返送管29と、バッフル23の頂部の内部に下端が開
口し、沈殿部14の壁を貫通して上端が上記汚泥の返送
管29の途中に接続したガス抜き管30を設ける。これ
によりバッフルで捕集された嫌気性のガスはガス抜き管
30を上昇して汚泥の返送管29に流入し、仕切壁17
の外で槽内に戻される。この嫌気性ガスのエアリフト作
用によりバッフルに捕集された汚泥、沈殿部に沈降した
汚泥を反応部11に戻すことができる。汚泥の返送管2
9には、ガス抜き管30が接続した位置の上流に、タイ
マにより開閉作動を制御される自動弁Vを設けもよい。
又、ガスリスト効率を高めるために、返送管29の立ち
上がり最高部に受槽(図示せず)を設けることもでき
る。
Sludge collected in the baffle 23, sedimentation section 1
In order to return the sludge settled to No. 4 to the reaction section 11, one end is opened inside the bottom of the settling section 14 and the other end is projected above the liquid level in the tank and then folded back to the outside of the partition wall 17. At the bottom of the baffle 23, a return pipe 29 for sludge that is open on the liquid surface in the tank or that rushes into the liquid surface is opened at the bottom, and the top of the baffle 23 is penetrated through the wall of the sedimentation portion 14. A gas vent pipe 30 connected to the sludge return pipe 29 is provided. As a result, the anaerobic gas collected by the baffle rises in the gas vent pipe 30 and flows into the sludge return pipe 29, and the partition wall 17
It is returned to the tank outside. The sludge collected in the baffle and the sludge settled in the settling section can be returned to the reaction section 11 by the airlift action of the anaerobic gas. Sludge return pipe 2
An automatic valve V whose opening / closing operation is controlled by a timer may be provided at 9 upstream of the position to which the gas vent pipe 30 is connected.
Further, in order to improve the gas list efficiency, a receiving tank (not shown) may be provided at the highest rising portion of the return pipe 29.

【0021】[0021]

【発明の効果】請求項1の発明によりバッフルが嫌気性
ガスと上向流する処理水中の汚泥を捕集するため沈殿部
への汚泥の流入は少なくなり、沈殿部の空間を沈降分離
に有効に利用できる。又、請求項2の発明により、バッ
フルが捕集した嫌気性ガスのエアリフト作用でバッフル
に捕集された汚泥と、沈殿部に沈降した汚泥を反応部に
返送することができる。従って、ポンプを使用する必要
がないので設備コスト、ランニングコストは低減する。
According to the invention of claim 1, since the baffle collects sludge in the treated water flowing upward with the anaerobic gas, the sludge inflow to the settling section is reduced, and the space in the settling section is effective for settling separation. Available for Further, according to the invention of claim 2, the sludge collected in the baffle and the sludge settled in the sedimentation part can be returned to the reaction part by the airlift action of the anaerobic gas collected in the baffle. Therefore, since it is not necessary to use a pump, equipment cost and running cost are reduced.

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

【図1】この発明の嫌気性処理装置の一実施形態の縦断
正面図である。
FIG. 1 is a vertical sectional front view of an embodiment of an anaerobic treatment apparatus of the present invention.

【図2】図1の処理装置の縦断側面図である。2 is a vertical side view of the processing apparatus of FIG. 1. FIG.

【図3】この発明の処理装置の他の実施形態の図2と同
様な縦断側面図である。
FIG. 3 is a vertical sectional side view similar to FIG. 2 of another embodiment of the processing apparatus of the present invention.

【符号の説明】[Explanation of symbols]

10 有蓋の処理槽 10′ ガス抜き管 11 反応部 12 反応部の嫌気性汚泥層 13 反応部の原水給水管 14 沈殿部 15 直立筒壁 15a 直立筒壁の側壁 15b 直立筒壁の端壁 16 傾斜壁 17 仕切壁 17′ 仕切壁のV形切込み 18 起立壁 18′ 起立壁のV形切込み 19 溢入樋 20 邪魔板 21 処理水の排水管 22 直立筒壁の端壁の切欠き 23 バッフル 25 上昇水路 26 上昇水路 29 汚泥の返送管 30 ガス抜き管 10 Treated tank with a lid 10 'degassing tube 11 Reaction part 12 Anaerobic sludge layer in the reaction section 13 Raw water supply pipe of reaction section 14 sedimentation part 15 Upright cylinder wall 15a Side wall of upright cylinder wall 15b End wall of upright cylinder wall 16 inclined wall 17 partition walls 17 'V-shaped cut in partition wall 18 standing wall 18 'V-shaped notch on upright wall 19 overflow gutter 20 baffle 21 Drainage pipe for treated water 22 Notch in end wall of upright cylinder wall 23 baffle 25 ascending canal 26 ascending canal 29 Sludge return pipe 30 degassing tube

フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C02F 3/28 - 3/34 Continuation of front page (58) Fields surveyed (Int.Cl. 7 , DB name) C02F 3/28-3/34

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 底部に嫌気性汚泥層と、該汚泥層中に有
機性排水を上向流で供給する給水管とを有する反応部を
備えた処理槽の内部の上記反応部の上の水中に、尖端部
を下に向けた錐形の沈殿部を浸漬して配置すると共に、
上記沈殿部の回りに上端部が槽内の液面上に突出し、下
端部が上記沈殿部の高さの途中の水中に位置する直立筒
壁と、この直立筒壁の下端部から前記沈殿部の下端に向
かって近付く傾斜壁と、前記沈殿部の上の直立筒壁の内
部には下向きに窄って下端が沈殿部の内部に上から浅く
突入すると共に、上部に槽内の液面から処理水が溢入す
る溢入樋を備えた仕切壁と、前記沈殿部の外面に設けら
れ、直立筒壁の下端部内面に向かって斜め下向きに突出
する邪魔板とを設けた有機性排水の嫌気性処理装置にお
いて、上記沈殿部の下端に山形断面のバッフルを配置し
たことを特徴とする有機性排水の嫌気性処理装置。
1. Water above the reaction section inside a treatment tank having a reaction section having an anaerobic sludge layer at the bottom and a water supply pipe for supplying organic wastewater into the sludge layer in an upward flow. In, place the cone-shaped precipitation part with the tip facing downward, and place it,
An upright cylindrical wall having an upper end projecting above the liquid surface in the tank around the settling section and a lower end located in the water in the middle of the height of the settling section, and the settling section from the lower end of the upright tube wall. The slanted wall approaching toward the lower end of the settling wall, and the inside of the upright cylindrical wall above the settling section is narrowed downward and the lower end is projected into the settling section from the top at a shallow depth. A partition wall provided with an overflow gutter for the treated water to overflow, and a baffle plate that is provided on the outer surface of the settling section and that projects obliquely downward toward the inner surface of the lower end portion of the upright tubular wall. An anaerobic treatment apparatus for organic wastewater, wherein a baffle having a chevron cross section is arranged at the lower end of the precipitation section.
【請求項2】 請求項1に記載の有機性排水の嫌気性処
理装置において、上記沈殿部の底の内部に一端が開口
し、他端部は槽内の液面上に突出したのち下向きに折返
し、仕切壁の外で槽内の液面中に突入する汚泥の返送管
と、前記山形断面のバッフルの頂部の内部に下端が開口
し、上端は上記汚泥の返送管の途中に接続した上向きの
ガス抜き管とを設け、前記反応部で発生してバッフルで
捕集された嫌気性ガスを上記ガス抜き管により汚泥返送
管に供給し、汚泥返送管内に生じるガスリフト作用でバ
ッフルに捕集された汚泥と、沈殿部の底に沈降した汚泥
とを反応部に返送するようにしたことを特徴とする有機
性排水の嫌気性処理装置。
2. The apparatus for anaerobic treatment of organic wastewater according to claim 1, wherein one end has an opening inside the bottom of the settling section, and the other end projects downward on the liquid surface in the tank. A sludge return pipe that folds back and plunges into the liquid level in the tank outside the partition wall, and a lower end opens inside the top of the baffle with the chevron cross section, and the upper end connects upwards in the middle of the sludge return pipe. And a bleeder tube for the anaerobic gas generated in the reaction section and collected in the baffle is supplied to the sludge return pipe by the gas bleeder tube, and is collected in the baffle by the gas lift action generated in the sludge return pipe. An anaerobic treatment apparatus for organic wastewater, wherein the sludge and the sludge settled to the bottom of the settling section are returned to the reaction section.
JP29516298A 1998-10-16 1998-10-16 Anaerobic treatment equipment for organic wastewater Expired - Lifetime JP3374766B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP29516298A JP3374766B2 (en) 1998-10-16 1998-10-16 Anaerobic treatment equipment for organic wastewater
TW88117220A TW475920B (en) 1998-10-16 1999-10-06 An anaerobic processing equipment for organic waste water
CNB991222016A CN1182050C (en) 1998-10-16 1999-10-12 Anaerobic treatment device for organic waste water
KR19990044420A KR100595109B1 (en) 1998-10-16 1999-10-13 anaerobic treatment apparatns of organic drainage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29516298A JP3374766B2 (en) 1998-10-16 1998-10-16 Anaerobic treatment equipment for organic wastewater

Publications (2)

Publication Number Publication Date
JP2000117285A JP2000117285A (en) 2000-04-25
JP3374766B2 true JP3374766B2 (en) 2003-02-10

Family

ID=17817058

Family Applications (1)

Application Number Title Priority Date Filing Date
JP29516298A Expired - Lifetime JP3374766B2 (en) 1998-10-16 1998-10-16 Anaerobic treatment equipment for organic wastewater

Country Status (4)

Country Link
JP (1) JP3374766B2 (en)
KR (1) KR100595109B1 (en)
CN (1) CN1182050C (en)
TW (1) TW475920B (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4620383B2 (en) * 2004-06-07 2011-01-26 株式会社エイブル Methane fermentation treatment method
CN100506721C (en) * 2006-07-20 2009-07-01 清华大学 Method and device for improving three phase separating efficiency of baffle type anaerobic biological reactor
JP2008221181A (en) * 2007-03-15 2008-09-25 Ebara Corp Anaerobic treatment device and treatment method
JP5176384B2 (en) * 2007-05-11 2013-04-03 栗田工業株式会社 Bioreactor
KR100893377B1 (en) * 2008-10-31 2009-04-17 (주)화인이테크 Apparatus for aerobic treatment of organic waste
KR101351005B1 (en) * 2012-07-02 2014-01-14 서준용 Anaerobic container and apparatus for producing biogas using it
KR101384782B1 (en) * 2012-08-01 2014-04-21 창원대학교 산학협력단 Self-supporting sludge free energy device for treating sewage
JP7206406B2 (en) * 2019-09-27 2023-01-17 株式会社フジタ Biogas generator, biogas generation system, and biogas generation method
CN115215496B (en) * 2022-08-15 2023-08-29 南京柯若环境技术有限公司 Sewage pretreatment method and equipment with biological clarification tank function

Also Published As

Publication number Publication date
CN1251354A (en) 2000-04-26
JP2000117285A (en) 2000-04-25
KR20000029049A (en) 2000-05-25
TW475920B (en) 2002-02-11
KR100595109B1 (en) 2006-07-03
CN1182050C (en) 2004-12-29

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