JP2012143673A - Fluidized bed type biological treatment apparatus - Google Patents

Fluidized bed type biological treatment apparatus Download PDF

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JP2012143673A
JP2012143673A JP2011002076A JP2011002076A JP2012143673A JP 2012143673 A JP2012143673 A JP 2012143673A JP 2011002076 A JP2011002076 A JP 2011002076A JP 2011002076 A JP2011002076 A JP 2011002076A JP 2012143673 A JP2012143673 A JP 2012143673A
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carrier
rotating plate
plate
biological treatment
fluidized bed
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JP5636968B2 (en
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Yuji Yasuike
友時 安池
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Kurita Water Industries Ltd
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Priority to JP2011002076A priority Critical patent/JP5636968B2/en
Priority to KR1020127012062A priority patent/KR101415077B1/en
Priority to CN201280000186.XA priority patent/CN102695681B/en
Priority to PCT/JP2012/050095 priority patent/WO2012093691A1/en
Priority to TW101100597A priority patent/TWI429601B/en
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    • 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
    • C02F3/02Aerobic processes
    • C02F3/08Aerobic processes using moving contact bodies
    • C02F3/085Fluidized beds
    • 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
    • C02F3/02Aerobic processes
    • C02F3/08Aerobic processes using moving contact bodies
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F27/00Mixers with rotary stirring devices in fixed receptacles; Kneaders
    • B01F27/80Mixers with rotary stirring devices in fixed receptacles; Kneaders with stirrers rotating about a substantially vertical axis
    • 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
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N11/00Carrier-bound or immobilised enzymes; Carrier-bound or immobilised microbial cells; Preparation thereof
    • C12N11/14Enzymes or microbial cells immobilised on or in an inorganic carrier
    • 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

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  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
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  • Biotechnology (AREA)
  • Biomedical Technology (AREA)
  • Biochemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a fluidized bed type biological treatment apparatus which can radiate adherent bubbles from a carrier while preventing or suppressing the peeling of a biofilm.SOLUTION: The fluidized bed type biological treatment apparatus 1 includes: a cylindrical tank body 2 with a cylinder axis direction as a vertical direction; a drive shaft 3 arranged at the shaft core position of the tank body 2; a rotary blade 4 stuck to the drive shaft 3; a fixed plate 8 provided at the upper part of the tank body 2; a rotary plate 7 provided at the drive shaft 3; and a treated water ejection trough 6 provided at the upper part of the tank body 2. The rotary plate 7 circles, a floated carrier is sandwiched between the rotary plate 7 and the lower part made of rubber of the fixed plate 8, and bubbles radiate.

Description

本発明は、排水を処理するための流動床式生物処理装置に係り、特に担体に付着した気泡を放散させる手段を備えた流動床式生物処理装置に関する。   The present invention relates to a fluidized bed biological treatment apparatus for treating wastewater, and more particularly to a fluidized bed biological treatment apparatus provided with means for diffusing bubbles attached to a carrier.

生物処理では、担体に微生物を付着させ、槽内のMLVSSを高く維持するようにした流動床式生物処理装置が広く用いられている。この流動床式生物処理装置においては、通常の場合、槽内に充填された担体が撹拌羽根による撹拌や上向流の水勢によって流動している。   In biological treatment, fluidized bed biological treatment apparatuses are widely used in which microorganisms are attached to a carrier and the MLVSS in the tank is kept high. In this fluidized bed biological treatment apparatus, in general, the carrier filled in the tank is fluidized by stirring with stirring blades or an upward flow of water.

この流動床式生物処理装置によって脱窒処理を行う場合においては、脱窒反応により窒素ガスが発生する。担体に形成された生物膜の内部に窒素ガスが内包されるために、ガスの浮力により浮上して水面に滞留するようになる。浮上担体の量が多くなると、担体と槽内液中の基質との接触が悪くなり、流動床式生物処理装置の処理効率が低下する。なお、窒素以外にも嫌気処理時のメタンなどのガスが担体に付着して担体が浮上することもある。   When denitrification is performed by this fluidized bed biological treatment apparatus, nitrogen gas is generated by the denitrification reaction. Since nitrogen gas is contained inside the biofilm formed on the carrier, it floats by the buoyancy of the gas and stays on the water surface. When the amount of the floating carrier is increased, the contact between the carrier and the substrate in the liquid in the tank is deteriorated, and the treatment efficiency of the fluidized bed biological treatment apparatus is lowered. In addition to nitrogen, gas such as methane during anaerobic treatment may adhere to the carrier and the carrier may float.

特開2006−218371には、槽内の中央に上下方向にドラフトチューブを設置し、このドラフトチューブ内にインペラ装置を設置し、インペラ装置によって担体を脱泡することが記載されている。即ち、気泡が付着することにより槽内を浮上した担体は、ドラフトチューブの上端から該ドラフトチューブ内に吸い込まれて循環されると共に、ドラフトチューブ内のインペラ装置を通過するときにインペラによって剪断力が与えられ、脱泡される(同公報0027段落)。   Japanese Patent Application Laid-Open No. 2006-218371 describes that a draft tube is installed vertically in the center of a tank, an impeller device is installed in the draft tube, and the carrier is defoamed by the impeller device. That is, the carrier that has floated in the tank due to the adhering of bubbles is sucked into the draft tube from the upper end of the draft tube and circulated. Given and degassed (paragraph 0027 of the publication).

特開2006−218371JP 2006-218371 A

上記特許文献1のようにインペラによって担体に剪断力を与えて付着気泡を脱泡させる場合、インペラが担体に与える剪断力が強過ぎるために、担体に付着している生物膜が剥離するおそれがある。   When applying a shearing force to the carrier by the impeller to defoam the attached bubbles as in the above-mentioned Patent Document 1, since the shearing force applied to the carrier by the impeller is too strong, the biofilm attached to the carrier may be peeled off. is there.

本発明は、生物膜の剥離を防止ないし抑制しつつ、担体から付着気泡を放散させることができる流動床式生物処理装置を提供することを目的とする。   It is an object of the present invention to provide a fluidized bed biological treatment apparatus that can dissipate attached bubbles from a carrier while preventing or suppressing biofilm peeling.

請求項1の流動床式生物処理装置は、槽内に粒状の担体が充填され、該担体を撹拌する撹拌手段と、担体に付着した気泡を放散させる気泡放散手段とを有する流動床式生物処理装置において、該気泡放散手段は、槽内で浮上した担体を回転板と定置板とで挟むことにより気泡を放散させるように構成されていることを特徴とするものである。   The fluidized bed biological treatment apparatus according to claim 1 is a fluidized bed biological treatment apparatus in which a tank is filled with a granular carrier, and has a stirring means for stirring the carrier and a bubble diffusing means for diffusing bubbles attached to the carrier. In the apparatus, the bubble diffusing means is configured to diffuse bubbles by sandwiching a carrier floating in the tank between a rotating plate and a stationary plate.

請求項2の流動床式生物処理装置は、請求項1において、該回転板は槽内の水面下で旋回するように駆動軸に取り付けられており、該定置板は、下部を水中に没するように該回転板の旋回領域に配置されており、該回転板が旋回して該回転板の上部が該定置板の下部に当接し、この際に回転板の上部と定置板の下部との少なくとも一方が退動することにより回転板が定置板の下側を通過するように構成されていることを特徴とするものである。   A fluidized bed biological treatment apparatus according to a second aspect is the fluidized bed biological treatment apparatus according to the first aspect, wherein the rotating plate is attached to a drive shaft so as to swivel below the water surface in the tank, and the stationary plate is submerged in water. The rotating plate rotates so that the upper portion of the rotating plate comes into contact with the lower portion of the stationary plate, and at this time, the upper portion of the rotating plate and the lower portion of the stationary plate are The rotating plate is configured to pass under the stationary plate when at least one of them is retracted.

請求項3の流動床式生物処理装置は、請求項2において、前記定置板の少なくとも下部が軟質材よりなり、前記回転板の上部が定置板の下部に当接したときに該定置板の下部が退動することを特徴とするものである。   The fluidized bed biological treatment apparatus according to claim 3 is the fluidized bed biological treatment apparatus according to claim 2, wherein at least a lower portion of the stationary plate is made of a soft material, and a lower portion of the stationary plate is in contact with a lower portion of the stationary plate. Is characterized by retreating.

請求項4の流動床式生物処理装置は、請求項3において、前記回転板は、上部ほど旋回進行方向の後方となるように傾斜していることを特徴とするものである。   A fluidized bed biological treatment apparatus according to a fourth aspect is characterized in that, in the third aspect, the rotating plate is inclined so that the upper part is rearward in the swivel direction.

本発明の流動床式生物処理装置では、槽内を浮上した担体を回転板と定置板とで挟むことにより、該担体に付着した気泡を放散させる。この気泡放散機構によると、担体に与える衝撃を小さくし、生物膜の剥離を防止ないし抑制しつつ気泡を放散させることができる。   In the fluidized bed biological treatment apparatus of the present invention, the carrier floating in the tank is sandwiched between the rotating plate and the stationary plate, so that the bubbles attached to the carrier are diffused. According to this bubble diffusing mechanism, the impact applied to the carrier can be reduced, and the bubbles can be radiated while preventing or suppressing biofilm peeling.

請求項2の流動床式生物処理装置では、回転板が水面下で旋回し、浮上した担体が該回転板の上部と定置板の下部との間で挟まれて担体から気泡が放散する。この回転板と定置板とが当接したときに、回転板の上部と定置板の下部との少なくとも一方が退動することにより、担体に与えられる衝撃が小さくなり、生物膜の剥離が防止ないし抑制される。   In the fluidized bed biological treatment apparatus according to the second aspect, the rotating plate swirls under the surface of the water, the floated carrier is sandwiched between the upper part of the rotating plate and the lower part of the stationary plate, and bubbles are diffused from the carrier. When the rotating plate and the stationary plate come into contact, at least one of the upper portion of the rotating plate and the lower portion of the stationary plate is retracted, so that the impact given to the carrier is reduced and the biofilm is prevented from peeling off. It is suppressed.

請求項3の流動床式生物処理装置では、定置板の下部を軟質材にて構成してあるので、回転板が定置板の下部に当接したときに定置板の下部が退動し、担体に与えられる衝撃が小さくなる。   In the fluidized bed biological treatment apparatus according to claim 3, since the lower part of the stationary plate is made of a soft material, the lower part of the stationary plate moves backward when the rotating plate comes into contact with the lower part of the stationary plate, The impact given to is reduced.

請求項4の流動床式生物処理装置では、回転板を傾斜させており、槽内水面付近の担体が、旋回している該回転板によってかき上げられるようにして回転板に沿って上方に移動し、回転板と定置板との間に挟まれて気泡が担体から放散する。   In the fluidized bed biological treatment apparatus according to claim 4, the rotating plate is inclined, and the carrier in the vicinity of the water surface in the tank moves upward along the rotating plate so as to be lifted up by the rotating rotating plate. Then, the air bubbles are diffused from the carrier by being sandwiched between the rotating plate and the stationary plate.

実施の形態に係る流動床式生物処理装置の縦断面図である。It is a longitudinal cross-sectional view of the fluidized bed type biological treatment apparatus which concerns on embodiment. 図1の気泡放散手段を示す斜視図である。It is a perspective view which shows the bubble diffusion means of FIG. 回転板及び定置板の縦断面図である。It is a longitudinal cross-sectional view of a rotating plate and a stationary plate.

以下、図面を参照して実施の形態について説明する。第1図は実施の形態に係る流動床式生物処理装置の縦断面図である。   Hereinafter, embodiments will be described with reference to the drawings. FIG. 1 is a longitudinal sectional view of a fluidized bed biological treatment apparatus according to an embodiment.

この流動床式生物処理装置1は、筒軸心方向を鉛直方向とした円筒形の槽体2と、該槽体2の軸心位置に配置された駆動軸3と、該駆動軸3に固着された回転翼(攪拌翼)4と、駆動軸3を回転させるモータ5と、槽体2の上部に設けられた担体流出防止スクリーン付きの処理水取出トラフ6を備えている。処理水取出トラフ6のオーバーフローレベルが槽体2内の水面位WLである。槽体2内の上部に、担体からの付着気泡の放散手段として、回転板7と定置板8とが設けられている。   The fluidized bed biological treatment apparatus 1 includes a cylindrical tank body 2 whose vertical direction is a cylinder axis direction, a drive shaft 3 disposed at the axial center position of the tank body 2, and an anchor to the drive shaft 3. A rotary blade (stirring blade) 4, a motor 5 for rotating the drive shaft 3, and a treated water extraction trough 6 with a carrier outflow prevention screen provided at the upper part of the tank body 2 are provided. The overflow level of the treated water extraction trough 6 is the water level WL in the tank body 2. A rotating plate 7 and a stationary plate 8 are provided in the upper part of the tank body 2 as means for diffusing attached bubbles from the carrier.

回転翼4は、この実施の形態では板面を鉛直方向とした平板状であり、駆動軸3から槽体2の直径方向に延在している。即ち、この実施の形態では回転翼4は180°反対方向に2枚設けられている。ただし、翼は放射方向に3枚以上設けられてもよく、通常は2〜4枚程度が好適である。担体を流動させれば良く、翼の形状は限定されない。   In this embodiment, the rotary blade 4 has a flat plate shape with the plate surface in the vertical direction, and extends from the drive shaft 3 in the diameter direction of the tank body 2. That is, in this embodiment, two rotor blades 4 are provided in the opposite direction of 180 °. However, three or more blades may be provided in the radial direction, and usually about 2 to 4 blades are suitable. What is necessary is just to make a support | carrier flow, and the shape of a wing | blade is not limited.

回転翼4の旋回直径(この実施の形態では2枚の回転翼4の先端同士の距離)は、槽体2の直径の20〜80%特に50〜70%程度が好適である。   The swirl diameter of the rotor blade 4 (the distance between the tips of the two rotor blades 4 in this embodiment) is preferably about 20 to 80%, particularly about 50 to 70% of the diameter of the tank body 2.

回転翼4は、槽体2の上下方向の中間付近に配置されている。回転翼4の上縁の高さ(槽体底面からの高さ。以下、同様)は、槽体水深の20〜80%特に50〜70%程度が好適である。回転翼4の上下幅は、槽体水深の5〜60%特に10〜40%程度が好適である。   The rotary blade 4 is disposed near the middle of the tank body 2 in the vertical direction. The height of the upper edge of the rotor blade 4 (height from the bottom surface of the tank body, hereinafter the same) is preferably about 20 to 80%, particularly about 50 to 70% of the tank body water depth. The vertical width of the rotary blade 4 is preferably about 5 to 60%, particularly about 10 to 40% of the tank body water depth.

なお、回転翼4は、この実施の形態では上下方向に1段のみ設けられているが、2段以上に設けられてもよい。   In this embodiment, only one stage of the rotary blade 4 is provided in the vertical direction, but it may be provided in two or more stages.

この実施の形態では、槽体2の底面に軸受部を設け、この軸受部によって駆動軸3の下端を支持するようにしている。   In this embodiment, a bearing portion is provided on the bottom surface of the tank body 2, and the lower end of the drive shaft 3 is supported by this bearing portion.

この槽体2内に粒状担体Cが収容されている。   A granular carrier C is accommodated in the tank body 2.

担体はどのような材質でも良いが、磨耗に強い高分子架橋体の粒状のものが好ましい。   The carrier may be any material, but is preferably a granular polymer crosslinked material that is resistant to wear.

担体の材料樹脂としては、例えばポリオレフィン、PVA、PEG、(ポリ)アクリルアミド、N置換アクリルアミド、(ポリ/メタ)アクリル酸またはそのアルカリ金属塩、アルギン酸、ポリアルキレンオキサイド、ジメチルアミノエチル(メタ)アクリレート(DAM)、ジアセトンアルコール(DAA)、ポリアルキレンオキサイド等が挙げられる。より具体的には、ポリアクリル酸ナトリウム、アクリル酸ナトリウムとアクリルアミドとのコポリマー、アクリル酸ナトリウムとアクリルアミド2−メチルプロパンスルホン酸ナトリウムとのコポリマー、アクリル酸ナトリウムとアクリルアミドとアクリルアミド2−メチルプロパンスルホン酸ナトリウムとのターポリマー、および、ジメチルアミノエチル(メタ)アクリレートの三級塩もしくは四級アンモニウムのホモポリマーまたはアクリルアミド等とのコポリマー等が例示される。   Examples of the carrier resin include polyolefin, PVA, PEG, (poly) acrylamide, N-substituted acrylamide, (poly / meth) acrylic acid or an alkali metal salt thereof, alginic acid, polyalkylene oxide, dimethylaminoethyl (meth) acrylate ( DAM), diacetone alcohol (DAA), polyalkylene oxide and the like. More specifically, sodium polyacrylate, copolymer of sodium acrylate and acrylamide, copolymer of sodium acrylate and sodium acrylamide 2-methylpropanesulfonate, sodium acrylate, acrylamide and sodium acrylamide 2-methylpropanesulfonate And a terpolymer of dimethylaminoethyl (meth) acrylate, a homopolymer of quaternary ammonium or a copolymer with acrylamide and the like.

担体の平均粒径としては1mm〜20mmが使用でき、1mm〜5mmが好ましく、特に好ましくは1.2mm〜3.5mmである。これより小さいと担体と水の分離が困難になり、大きいと流動の妨げとなる。   The average particle diameter of the carrier can be 1 mm to 20 mm, preferably 1 mm to 5 mm, particularly preferably 1.2 mm to 3.5 mm. If it is smaller than this, it will be difficult to separate the carrier and water, and if it is larger, flow will be hindered.

担体の空隙率は20〜50%が好ましく、特に30〜40%が望ましい。空隙率が低いと、汚泥の付着が少なく処理効率が低下し、高いとガスを内包しやすくなる。   The porosity of the carrier is preferably 20 to 50%, particularly preferably 30 to 40%. When the porosity is low, there is little adhesion of sludge and the processing efficiency is lowered, and when it is high, gas is easily included.

担体の密度としては、平均して0.96〜1.02g/cmであることが望ましく、80%以上の担体の密度が0.98〜1.01g/cm特に0.985〜1.00g/cmであることが好ましい。 The density of the carrier is desirably 0.96 to 1.02 g / cm 3 on average, and the density of the carrier of 80% or more is 0.98 to 1.01 g / cm 3, particularly 0.985 to 1. It is preferably 00 g / cm 3 .

担体の充填量は槽体2の水面位WL以下の容積に対して担体のかさ容積が5〜50%となる量であることが好ましい。これよりも担体の量が少ないと処理効率が低くなり、50%よりも多いと攪拌動力が過大となる。   The filling amount of the carrier is preferably such that the bulk volume of the carrier is 5 to 50% with respect to the volume below the water level WL of the tank body 2. If the amount of the carrier is less than this, the processing efficiency is lowered, and if it is more than 50%, the stirring power becomes excessive.

第2図は、この担体に付着した気泡を放散させるための回転板7及び定置板8の斜視図、第3図は回転板7が定置板8に当接しようとしている状態の縦断面図である。   FIG. 2 is a perspective view of the rotating plate 7 and the stationary plate 8 for diffusing air bubbles adhering to the carrier, and FIG. 3 is a longitudinal sectional view of the state where the rotating plate 7 is about to contact the stationary plate 8. is there.

回転板7は、駆動軸3から放射方向に延在するように2枚設けられている。枚数は2〜4枚程度が好適である。回転板7は、旋回進行方向に対し上部ほど後方となるように傾斜している。回転板7の前面の傾斜角度θは60°以下、特に30〜60°程度が好適である。なお、回転板7は、この傾斜角度を調整できるように駆動軸3に取り付けられることが望ましい。   Two rotating plates 7 are provided so as to extend in the radial direction from the drive shaft 3. The number of sheets is preferably about 2 to 4 sheets. The rotating plate 7 is inclined so as to be rearward toward the upper part with respect to the turning traveling direction. The inclination angle θ of the front surface of the rotating plate 7 is preferably 60 ° or less, particularly about 30 to 60 °. The rotating plate 7 is preferably attached to the drive shaft 3 so that the inclination angle can be adjusted.

回転板7の放射方向長さ即ち旋回半径は、循環流が弱く担体が集まってくる固体的回転半径の10〜100%特に20〜60%程度が好ましい。固体的回転半径(r)の計算式は次の通りである。
2r=1.23{0.57+0.35(d/D)}(b/D)0.036 0.116Re/(10+1.43Re)d
:固体的回転半径(m)
d:撹拌翼径(m)
D:槽径(m)
b:翼幅(m)
:翼の羽根枚数
Re:レイノルズ数
The radial length of the rotating plate 7, that is, the turning radius, is preferably about 10 to 100%, particularly about 20 to 60% of the solid turning radius where the circulating flow is weak and the carrier gathers. The formula for calculating the solid turning radius (r c ) is as follows.
2r c = 1.23 {0.57 + 0.35 (d / D)} (b / D) 0.036 n p 0.116 Re / (10 3 +1.43 Re) d
r c : solid turning radius (m)
d: Stirring blade diameter (m)
D: Tank diameter (m)
b: Wing width (m)
n p : number of blades of wings Re: Reynolds number

回転板7は、水中に没するように設けられるのが好ましい。回転板7の構成材料としては、金属、合成樹脂など任意であるが、定置板8と当接する上部の少なくとも表面(定置板8との接触面)については、柔軟な天然ゴム、合成ゴム(例えばシリコンゴム)などで構成されていることが望ましい。   The rotating plate 7 is preferably provided so as to be immersed in water. The constituent material of the rotating plate 7 is arbitrary, such as metal or synthetic resin, but at least the upper surface (contact surface with the stationary plate 8) that contacts the stationary plate 8 is flexible natural rubber or synthetic rubber (for example, It is desirable that it be made of silicon rubber).

定置板8は、その下部が回転板7の旋回領域の水中に没するように設置されている。この実施の形態では定置板8は駆動軸3を挟んで対称に2枚設置されているが、1枚〜4枚程度であればよい。定置板8は、板面が駆動軸3に対して放射方向となるように設置されている。定置板8の放射方向の幅は回転板7の旋回半径の20〜120%特に40〜100%程度が好ましい。   The stationary plate 8 is installed such that its lower part is submerged in water in the swivel region of the rotating plate 7. In this embodiment, two stationary plates 8 are installed symmetrically with the drive shaft 3 in between. The stationary plate 8 is installed such that the plate surface is in the radial direction with respect to the drive shaft 3. The radial width of the stationary plate 8 is preferably about 20 to 120%, particularly about 40 to 100% of the turning radius of the rotating plate 7.

定置板8の駆動軸3側の端部から駆動軸3までの距離は、回転板7の旋回半径の5〜40%特に10〜30%程度が好適である。定置板8の駆動軸3から遠い側の端部から駆動軸3までの距離は、回転板7の旋回半径の25〜130%特に50〜100%程度が好適である。   The distance from the end of the stationary plate 8 on the drive shaft 3 side to the drive shaft 3 is preferably about 5 to 40%, particularly about 10 to 30% of the turning radius of the rotating plate 7. The distance from the end of the stationary plate 8 on the side far from the drive shaft 3 to the drive shaft 3 is preferably about 25 to 130%, particularly about 50 to 100% of the turning radius of the rotary plate 7.

定置板8の下端から水面までの距離(水没深さ)Hは、30cm以下、特に5〜30cmとりわけ5〜10cm程度が好ましい。この定置板8の水没深さHは、回転板7の上縁の水没深さHよりも大きく、回転板7が旋回したときに回転板7の上部が定置板8の下部に当接するよう構成されている。定置板8の水没深さHは、回転板7の上縁の水没深さHの150〜1500%(1.5〜15倍)特に200〜500%(2〜5倍)程度であることが好ましい。定置板8の少なくとも下部は、回転板7と当接したときに回転板7に押されて退動変形するように柔軟なゴム(例えば天然ゴムやシリコンゴム等の合成ゴム)にて構成されていることが望ましい。 The distance (water immersion depth) H 1 from the lower end of the stationary plate 8 to the water surface is preferably 30 cm or less, particularly 5 to 30 cm, and particularly preferably about 5 to 10 cm. The submerged depth H 1 of the stationary plate 8 is larger than the submerged depth H 2 of the upper edge of the rotating plate 7, and the upper portion of the rotating plate 7 contacts the lower portion of the stationary plate 8 when the rotating plate 7 turns. It is configured as follows. The submergence depth H 1 of the stationary plate 8 is about 150 to 1500% (1.5 to 15 times), particularly 200 to 500% (2 to 5 times) of the submergence depth H 2 of the upper edge of the rotating plate 7. It is preferable. At least the lower part of the stationary plate 8 is made of a flexible rubber (for example, a synthetic rubber such as natural rubber or silicon rubber) so as to be pushed backward by the rotating plate 7 when it contacts the rotating plate 7. It is desirable.

このように構成された流動床式生物処理装置においては、回転翼4及び回転板7を回転させながらこの槽体2内に原水供給管9から原水(有機物含有排水)を槽体2内に供給し、生物処理を行う。   In the fluidized bed biological treatment apparatus configured as described above, raw water (organic matter-containing wastewater) is supplied into the tank body 2 from the raw water supply pipe 9 into the tank body 2 while rotating the rotor blades 4 and the rotating plate 7. And biological treatment.

回転翼4の駆動軸3の回転数はG値が50〜200特に80〜150となるように調節するのが好適である。   It is preferable to adjust the rotational speed of the drive shaft 3 of the rotor blade 4 so that the G value is 50 to 200, particularly 80 to 150.

槽体2内の液(被処理水と担体とが混合した液)は、回転翼4から受ける遠心力及び旋回力により槽体2の上下方向中間付近で放射方向かつ旋回方向に流れ、槽体2の内周面に当って上方に向う旋回流れと下方に向う旋回流れとに別れる。   The liquid in the tank body 2 (liquid in which the water to be treated and the carrier is mixed) flows in a radial direction and a swiveling direction in the vicinity of the middle in the vertical direction of the tank body 2 due to the centrifugal force and the turning force received from the rotor blades 4. 2 divides into a swirl flow that is directed upward and a swirl flow that is directed downward.

上方に向う旋回流れとなった液は、槽体2の内周面に沿って旋回しながら上昇する。この間に、液中の担体はほぐされる。液は、水面位WL付近に至ると求心方向に向きを変え、その後、渦巻状に流れて水面位付近の中央部付近に集まり、次いで、沈降し、回転翼4付近に戻る。   The liquid that turns into the upward swirling flow rises while swirling along the inner peripheral surface of the tank body 2. During this time, the carrier in the liquid is loosened. The liquid changes its direction in the centripetal direction when it reaches the vicinity of the water surface level WL, then flows in a spiral shape, collects in the vicinity of the center near the water surface level, and then settles and returns to the vicinity of the rotary blade 4.

一方、槽体2の上下方向の中間付近から下方に向う旋回流となった液は、槽体2の内周面に沿って旋回しながら下降し、槽体底面近くに達すると渦巻き状に流れて槽体2の底面中央付近に集まり、槽体2の中心付近を上昇して回転翼4に戻る。   On the other hand, the liquid that has turned downward from the middle in the vertical direction of the tank body 2 descends while swirling along the inner peripheral surface of the tank body 2, and flows in a spiral shape when reaching the bottom surface of the tank body 2. Then, they gather near the bottom center of the tank body 2, rise near the center of the tank body 2, and return to the rotary blade 4.

この実施の形態では、担体の比重が約1又はそれ以下であることが好ましい。この場合、担体の多くは上昇旋回流と共に槽体2の内周面に沿って旋回しながら上昇し、この間にほぐされる。そのため、水面位WL付近の求心方向の渦巻流に伴って水面位付近の周縁部(槽体2の内周面付近)から中央部に向ってスムーズに流れ、次いで水面位WL付近の中央部から下降流に伴って沈降する。このようにして担体が良好に槽体2内を循環するようになり、生物処理効率が向上する。   In this embodiment, the specific gravity of the carrier is preferably about 1 or less. In this case, most of the carrier rises while swirling along the inner peripheral surface of the tank body 2 together with the rising swirl flow, and is loosened during this time. Therefore, along with the spiral flow in the centripetal direction near the water surface level WL, it smoothly flows from the peripheral part (near the inner peripheral surface of the tank body 2) near the water level toward the central part, and then from the central part near the water level WL. Settling with downflow. In this way, the carrier circulates well in the tank body 2 and the biological treatment efficiency is improved.

担体に気泡が付着すると、担体は下降水流によって沈降せず、水面に浮上したままとなる。この実施の形態では、気泡が付着して水面に浮上した担体Cは、水面の中央付近に集まり、回転板7に押されて旋回し、回転板7の上部と定置板8の下部との間に挟まれ、担体Cに衝撃が与えられ、気泡が放散する。気泡が放散した担体Cは、下降水流と共に沈降し、槽体2内を循環する。   When bubbles adhere to the carrier, the carrier does not settle due to the descending water flow, but remains floating on the water surface. In this embodiment, the carrier C that has floated on the water surface due to bubbles adhering to it gathers in the vicinity of the center of the water surface, is pushed by the rotating plate 7 and swivels between the upper portion of the rotating plate 7 and the lower portion of the stationary plate 8. The carrier C is impacted and the bubbles are diffused. The carrier C from which the bubbles have diffused settles with the descending water flow and circulates in the tank body 2.

この実施の形態では、回転板7は傾斜板よりなるので、水面近くの担体も回転板7の旋回に伴い回転板7の板面に沿って上方に移動し、回転板7と定置板8とで挟まれて気泡が放散する。また、定置板8の少なくとも下部がゴム等の軟質材よりなるので、回転板7の上部が定置板8に当接したときに該定置板8の下部が回転板7に押されて退動変形する。そのため、担体Cに加えられる衝撃が適度なものとなり、担体に付着した生物膜の剥離が防止ないし抑制される。   In this embodiment, since the rotating plate 7 is an inclined plate, the carrier near the water surface moves upward along the plate surface of the rotating plate 7 as the rotating plate 7 turns, and the rotating plate 7 and the stationary plate 8 The air bubbles are diffused by being sandwiched between. Further, since at least the lower part of the stationary plate 8 is made of a soft material such as rubber, when the upper part of the rotating plate 7 abuts against the stationary plate 8, the lower part of the stationary plate 8 is pushed by the rotating plate 7 and retracts. To do. For this reason, the impact applied to the carrier C becomes moderate, and peeling of the biofilm attached to the carrier is prevented or suppressed.

上記実施の形態では、定置板8の下部を軟質材にて構成しているが、回転板7の上部を軟質材にて構成し、定置板8と当接したときに該上部が退動するよう構成してもよい。また、回転板7の上部及び定置板8の下部の双方を軟質材にて構成してもよい。   In the above embodiment, the lower portion of the stationary plate 8 is made of a soft material, but the upper portion of the rotating plate 7 is made of a soft material, and the upper portion retreats when contacting the stationary plate 8. You may comprise. Moreover, you may comprise both the upper part of the rotating plate 7, and the lower part of the stationary plate 8 with a soft material.

定置板8は、モータ5の設置ベースなど適宜の部材に取り付けて設置されるが、この取り付け部をヒンジにて構成し、定置板8が強く押されたときにはヒンジ部によって定置板8が回動し、定置板8に過大な応力が生じることを防止するようにしてもよい。   The stationary plate 8 is installed by being attached to an appropriate member such as an installation base of the motor 5. This mounting portion is configured by a hinge, and when the stationary plate 8 is strongly pressed, the stationary plate 8 is rotated by the hinge portion. Then, it may be possible to prevent an excessive stress from being generated on the stationary plate 8.

上記実施の形態では、回転翼4と回転板7とを共通の駆動軸3に取り付け、同一回転数にて回転させるよう構成しているが、例えば回転板7の回転軸を中空管状とし、この回転軸内に駆動軸3を通し、回転翼4については駆動軸3で回転させ、回転板7については管状回転軸によって回転翼4とは異なる回転速度で回転させるようにしてもよい。   In the above embodiment, the rotary blade 4 and the rotary plate 7 are attached to the common drive shaft 3 and are configured to rotate at the same rotational speed. For example, the rotary shaft of the rotary plate 7 is a hollow tube. The driving shaft 3 may be passed through the rotating shaft, the rotating blade 4 may be rotated by the driving shaft 3, and the rotating plate 7 may be rotated at a rotational speed different from that of the rotating blade 4 by a tubular rotating shaft.

以下、実施例及び比較例について説明する。   Hereinafter, examples and comparative examples will be described.

[実施例1]
槽体2の直径120cm、水深180cm、槽容量2mの第1図〜第3図に示す流動床式生物処理装置を用いてNO−N濃度80mg/L、PO−P濃度2mg/Lの合成排水を1kg−N/m/dの槽負荷にて供給して処理した。なお、メタノールをNの3倍量添加した。
[Example 1]
Tank body 2 having a diameter of 120 cm, depth 180cm, NO 3 -N concentration using a fluidized bed biological treatment apparatus shown in FIG. 1-FIG. 3 of the tank capacity 2m 2 80mg / L, PO 4 -P concentration 2 mg / L The synthetic waste water was supplied at a tank load of 1 kg-N / m 3 / d for treatment. Methanol was added 3 times as much as N.

担体としては密度1.01g/cmのポリオレフィン系ゲル担体(平均粒径3mm)を槽体容積の15%充填した。 As a carrier, a polyolefin gel carrier (average particle diameter: 3 mm) having a density of 1.01 g / cm 3 was filled at 15% of the tank volume.

なお、回転板7、定置板8、回転翼4の構成は次の通りである。
回転板7の長さ(半径):140mm
回転板7の上下幅:70mm
回転板7の上縁の水没深さH:20mm
回転板7の材質:SUS
定置板8の放射方向の長さ:110mm
定置板8の水没深さH:50mm
定置板8と駆動軸3との距離:30mm
定置板の下部の材質:天然ゴム(上下長さ100mm)
回転翼4の長さ:720mm
回転翼4の幅:360mm
In addition, the structure of the rotating plate 7, the stationary plate 8, and the rotary blade 4 is as follows.
Length (radius) of rotating plate 7: 140 mm
Vertical width of rotating plate 7: 70 mm
Submerged depth H 2 of the upper edge of the rotating plate 7: 20 mm
Material of rotating plate 7: SUS
Radiation length of stationary plate 8: 110 mm
Deposition depth H 1 of stationary plate 8: 50 mm
Distance between stationary plate 8 and drive shaft 3: 30 mm
Material of the lower part of the stationary plate: Natural rubber (vertical length 100mm)
Length of rotor blade 4: 720mm
Rotating blade 4 width: 360 mm

回転翼4をG値80〜150(11〜17rpm。担体の流動状態に応じて調整。)にて運転したところ、処理水のNO−N濃度は5mg/L以下であった。また、浮上した担体は殆ど認められなかった。 When the rotary blade 4 was operated at a G value of 80 to 150 (11 to 17 rpm, adjusted according to the flow state of the carrier), the NO 3 —N concentration of the treated water was 5 mg / L or less. Further, almost no surfaced carrier was observed.

[比較例1]
回転板7及び定置板8を省略したこと以外は実施例1と同様にして原水を処理したところ、処理水のNO−N濃度は10mg/Lであり、また水面表面積30%に浮上した担体が視認された。
[Comparative Example 1]
The raw water was treated in the same manner as in Example 1 except that the rotating plate 7 and the stationary plate 8 were omitted. As a result, the NO 3 —N concentration of the treated water was 10 mg / L, and the carrier floated to a surface area of 30%. Was visible.

この実施例及び比較例より明らかな通り、回転板7及び定置板8を設けた実施例によると、担体の浮上が防止されると共に、比較例に比べてN除去率が高くなる。   As is clear from this example and the comparative example, according to the example in which the rotating plate 7 and the stationary plate 8 are provided, the carrier is prevented from floating and the N removal rate is higher than that of the comparative example.

1 流動床式生物処理装置
2 槽体
3 駆動軸
4 回転翼
5 モータ
6 処理水トラフ
7 回転板
8 定置板
DESCRIPTION OF SYMBOLS 1 Fluidized bed type biological treatment apparatus 2 Tank body 3 Drive shaft 4 Rotary blade 5 Motor 6 Treated water trough 7 Rotating plate 8 Stationary plate

Claims (4)

槽内に粒状の担体が充填され、該担体を撹拌する撹拌手段と、担体に付着した気泡を放散させる気泡放散手段とを有する流動床式生物処理装置において、
該気泡放散手段は、槽内で浮上した担体を回転板と定置板とで挟むことにより気泡を放散させるように構成されていることを特徴とする流動床式生物処理装置。
In a fluidized bed biological treatment apparatus, the tank is filled with a granular carrier, and has a stirring means for stirring the carrier and a bubble diffusing means for diffusing bubbles attached to the carrier.
The fluidized bed biological treatment apparatus is characterized in that the bubble diffusing means is configured to diffuse bubbles by sandwiching a carrier floating in a tank between a rotating plate and a stationary plate.
請求項1において、該回転板は槽内の水面下で旋回するように駆動軸に取り付けられており、該定置板は、下部を水中に没するように該回転板の旋回領域に配置されており、
該回転板が旋回して該回転板の上部が該定置板の下部に当接し、この際に回転板の上部と定置板の下部との少なくとも一方が退動することにより回転板が定置板の下側を通過するように構成されていることを特徴とする流動床式生物処理装置。
2. The rotating plate according to claim 1, wherein the rotating plate is attached to the drive shaft so as to turn below the water surface in the tank, and the stationary plate is disposed in a turning region of the rotating plate so that the lower part is submerged in water. And
The rotating plate pivots so that the upper part of the rotating plate comes into contact with the lower part of the stationary plate. At this time, at least one of the upper part of the rotating plate and the lower part of the stationary plate retracts, so that the rotating plate becomes A fluidized bed biological treatment apparatus configured to pass through a lower side.
請求項2において、前記定置板の少なくとも下部が軟質材よりなり、前記回転板の上部が定置板の下部に当接したときに該定置板の下部が退動することを特徴とする流動床式生物処理装置。   The fluidized bed system according to claim 2, wherein at least a lower portion of the stationary plate is made of a soft material, and the lower portion of the stationary plate retreats when the upper portion of the rotating plate contacts the lower portion of the stationary plate. Biological treatment equipment. 請求項3において、前記回転板は、上部ほど旋回進行方向の後方となるように傾斜していることを特徴とする流動床式生物処理装置。   The fluidized bed biological treatment apparatus according to claim 3, wherein the rotating plate is inclined so that the upper part is rearward in the swivel direction.
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JP5636968B2 (en) 2014-12-10
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