JP2564131B2 - Surface aeration immersion filter bed water treatment device - Google Patents

Surface aeration immersion filter bed water treatment device

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Publication number
JP2564131B2
JP2564131B2 JP62075388A JP7538887A JP2564131B2 JP 2564131 B2 JP2564131 B2 JP 2564131B2 JP 62075388 A JP62075388 A JP 62075388A JP 7538887 A JP7538887 A JP 7538887A JP 2564131 B2 JP2564131 B2 JP 2564131B2
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JP
Japan
Prior art keywords
water
filter bed
contact
plate
circulation
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 - Fee Related
Application number
JP62075388A
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Japanese (ja)
Other versions
JPS6344996A (en
Inventor
克己 飯田
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Individual
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Individual
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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

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  • Biological Treatment Of Waste Water (AREA)

Description

【発明の詳細な説明】 <産業上の利用分野> 本発明は、生物処理法の一種である固定接触法におけ
る接触酸化法に使用される表面曝気浸漬濾床水処理装置
に関する。ここで、接触酸化法とは、生物相(微生物
膜)を着床させる複数の浸漬濾床を処理槽内に配置し、
該浸漬濾床の間隙を水を表面曝気により循環流させる汚
水の生物処理法の一種である。
TECHNICAL FIELD The present invention relates to a surface aeration immersion filter bed water treatment device used for a catalytic oxidation method in a fixed contact method, which is a type of biological treatment method. Here, the catalytic oxidation method is to arrange a plurality of immersion filter beds for implanting biota (microbial membrane) in the treatment tank,
This is a kind of biological treatment method for wastewater in which water is circulated through the gap of the submerged filter bed by surface aeration.

<従来の技術> 従来、上記タイプの水処理装置としては、例えば、特
公昭58−54638号に記載されたものがある。
<Prior Art> Conventionally, as a water treatment apparatus of the above-mentioned type, for example, there is one described in Japanese Patent Publication No. 58-54638.

処理槽の上部に水車を回転可能に固定し、水車の水掻
き出し部材のすぐ下部より処理槽の幅全域にわたり、下
方が開放されている回流仕切板を設けて、水車の水掻き
出し部材のすぐ下部より、処理槽の幅全域にわたり、下
方が開放されている回流仕切板を設けて、水車の水掻き
出し部材の一部が水没する位置に水位を調節し、水車の
回転により回流仕切板の少なくとも一側に浸漬濾床が配
されている構成である。
A water turbine is rotatably fixed to the upper part of the treatment tank, and a circulation partition plate with an open lower part is provided from just below the water scraping member of the water turbine to the entire width of the treatment tank, just below the water scraping member of the water turbine. By providing a circulating partition plate whose lower part is opened over the entire width of the treatment tank, the water level is adjusted to a position where a part of the water scraping member of the water turbine is submerged, and at least one of the circulation partition plates is rotated by the rotation of the water turbine. It has a configuration in which a submerged filter bed is arranged on the side.

そして、浸漬濾床は、ラシヒリング、網状の合成樹脂
短管、小石(砕石)等の接触材を充填または形成してい
た。
Then, the immersion filter bed was filled or formed with a contact material such as Raschig rings, net-like synthetic resin short tubes, and pebbles (crushed stones).

<発明が解決しようとする課題> しかし、この水処理装置は、本発明者らが検討した結
果、下記のような問題点が発生し易いことが分かった。
<Problems to be Solved by the Invention> However, as a result of examination by the present inventors, it has been found that the water treatment device is likely to cause the following problems.

接触床の小塊物を覆うようにして微生物膜が生長肥大
し、肥大により水路が狭められ、小塊物同志の隙間にも
浮遊物質や剥離汚泥が堆積して、個々が小塊物であって
も、濾床の全体が一体化して大きな塊となり、濾床の閉
塞が起きやすい。このため、原水がそのまま浸漬濾床を
通らず、ショートパスして流出し、水流がいかない箇所
では腐食が起り、逆に水質が悪化させるおそれがある。
The microbial membrane grows and expands so as to cover the small particles in the contact bed, the water channel is narrowed due to the expansion, and floating substances and peeled sludge are accumulated in the gaps between the small particles. However, the entire filter bed is integrated into a large lump, and the filter bed is easily clogged. For this reason, the raw water does not pass through the immersion filter bed as it is, but flows out through a short path, and corrosion may occur at a place where the water flow does not occur, which may worsen the water quality.

従って、浸漬濾床の閉塞を解消しなければ充分な処理
も出来なくなるので、濾床の洗滌を、時々、行う必要が
生じる。この洗浄作業は、濾床の層が厚くなればなるほ
ど大変である。また、洗滌を行なった場合は、折角着床
した微生物膜を剥すおそれがある。そして、微生物を剥
してしまったときは、新たに微生物が付着するまでは暫
く日時がかかり、その間、生物処理効果の低下を来し、
向上して来たら、また、濾床が閉塞する。
Therefore, it is necessary to wash the filter bed from time to time because sufficient treatment cannot be performed unless the blockage of the immersion filter bed is eliminated. This cleaning operation is more difficult the thicker the bed of the filter bed. Further, when washing is performed, there is a risk that the microbial membrane that has been implanted on the corner may be peeled off. Then, when the microorganisms have been peeled off, it takes a while until a new microorganism adheres, and during that time, the biological treatment effect decreases.
When it improves, the filter bed becomes blocked again.

このように、濾床に閉塞と微生物膜の剥離が繰返し発
生し、質的及び量的に安定して、処理水を得難い。
Thus, the filter bed is repeatedly clogged and the microbial film is peeled off, which is stable in quality and quantity, making it difficult to obtain treated water.

なお、濾床としてハニカム構造のものがある。しか
し、容積当たりの接触面積を大きくしようとして、ハニ
カムの口径が小さなものを使用する場合、流れが層流に
なりやすく、ハニカムの上部と下部の入口及び出口付近
のみしか微生物が着床し難く、また、接触効率が良好
で、且つ、小さ過ぎると閉塞し易い。接触床への着床を
良くしようとして、乱流を起すために、ハニカムの口径
が大きなものを使用する場合、口径が大きくなればそれ
だけ容積当たりの接触面積が小さなる。従って、ハニカ
ム構造の濾床では、容積当たり処理能力の大きなものが
得難い。
There is a filter bed having a honeycomb structure. However, when trying to increase the contact area per volume and using a honeycomb having a small diameter, the flow is likely to be laminar, and it is difficult for the microorganisms to land only near the inlet and outlet of the upper and lower portions of the honeycomb. Further, the contact efficiency is good, and if it is too small, it tends to be blocked. When a honeycomb having a large diameter is used in order to improve the landing on the contact bed to generate turbulent flow, the larger the diameter, the smaller the contact area per volume. Therefore, it is difficult to obtain a filter bed having a honeycomb structure with a large processing capacity per volume.

本発明は、上記にかんがみて、濾床の閉塞が発生し難
く、且つ、容積当たりの接触面積も大きくすることがで
きる表面曝気浸漬濾床水処理装置を提供することを目的
とする。
In view of the above, an object of the present invention is to provide a surface aeration immersion filter bed water treatment apparatus in which clogging of the filter bed is unlikely to occur and the contact area per volume can be increased.

<課題を解決するための手段> 本発明は、上記課題を下記構成により解決するもので
ある。
<Means for Solving the Problems> The present invention solves the above problems by the following configurations.

生物処理法の一種である固定接触法における接触酸化
法に使用される表面曝気浸漬濾床水処理装置において、 処理槽の上部に水車を水平に回転可能に固定し、水車
の水の掻き出し部材のすぐ下部より処理槽の下部に向け
て、処理槽の幅全域にわたり下部が開放されている回流
仕切板を設けて、水車の水掻き出し部材の一部が水没す
る位置に水位を調節し、水車の回転により、回流仕切板
を境にして回流を発生させるように構成するとともに、 回流仕切板の少なくとも一側に複数の浸漬濾床が配さ
れ、該浸漬濾床が扁平網管を主要素とする濾床要素を複
数枚並立させて形成されていることを特徴とする。
In the surface aeration immersion filter bed water treatment device used in the catalytic oxidation method in the fixed contact method, which is a type of biological treatment method, a water wheel is fixed rotatably horizontally to the upper part of the treatment tank, and From the lower part toward the lower part of the processing tank, a circulation partition plate whose lower part is opened over the entire width of the processing tank is provided, and the water level is adjusted so that a part of the water scraping member of the water wheel is submerged. The rotating partition is configured to generate a circulating flow at the boundary, and a plurality of immersion filter beds are arranged on at least one side of the circulating partition plate, and the immersion filter bed has a flat mesh tube as a main element. It is characterized in that a plurality of floor elements are formed upright.

<実施例> A.本発明の実施例を、以下に図例に基づいて説明する。<Examples> A. Examples of the present invention will be described below with reference to the drawings.

(1)第1〜3図に本発明の一実施例を示す。(1) FIGS. 1 to 3 show an embodiment of the present invention.

処理槽1の上部に水車3を固定し、水車3の水の掻き
出し部材6のすぐ下部より処理槽1底部へ向けて、処理
槽1の略幅全域にわたり下部が開放されている回流仕切
板2が設けらている。ここで回流仕切板2の下部開放
は、通常、処理槽底部より回流仕切板のたての長さの1
〜3割程度の隙間で形成される。
A water turbine 3 is fixed to the upper part of the treatment tank 1, and a circulation partition plate 2 whose lower portion is opened over substantially the entire width of the treatment tank 1 from just below the water scraping member 6 of the water turbine 3 toward the bottom of the treatment tank 1. Is provided. Here, the lower part of the circulation partition plate 2 is usually opened from the bottom of the processing tank by 1 of the vertical length of the circulation partition plate.
It is formed with a gap of about 30%.

そして、水車3の水掻き出し部材6の一部が水没する
位置に水位を調節し、水車3の回転により、回流仕切り
板2を境にして回流を発生させるように構成されてい
る。
Then, the water level is adjusted to a position where a part of the water scraping member 6 of the water wheel 3 is submerged, and the rotation of the water wheel 3 causes a circulation to be generated with the circulation partition plate 2 as a boundary.

水車3と水槽1の側壁との隙間には逆流阻止板8が設
置されている。水車3の矢印19に示す方向の回転により
水の掻き出し部材6によって掻き出された水は、上記逆
流阻止板8の存在により、水車3と水槽1の側壁との隙
間からの逆流が阻止される。なお、水車3の下部と回流
仕切板2上端とのわずかな隙間においては、水車3の回
転により、掻き出し部材6で水が順次押し出されてくる
ため、逆流することはない。
A backflow prevention plate 8 is installed in the gap between the water wheel 3 and the side wall of the water tank 1. The water scraped out by the water scraping member 6 by the rotation of the water wheel 3 in the direction shown by the arrow 19 is prevented from flowing back from the gap between the water wheel 3 and the side wall of the water tank 1 due to the presence of the backflow blocking plate 8. . In the slight gap between the lower part of the water wheel 3 and the upper end of the circulation partition plate 2, the water is pushed out sequentially by the scraping member 6 due to the rotation of the water wheel 3, so that the water does not flow backward.

従って、水車3の掻き出された側の水位が上がり、掻
き取られた側の水位は下がり、掻き出された水は回流仕
切板2の底部開口部を通り戻ることになり、処理槽1内
に回流7が生じる。
Therefore, the water level on the scraped side of the water wheel 3 rises, the water level on the scraped side falls, and the scraped water returns through the bottom opening of the diversion partition plate 2 and the inside of the treatment tank 1 Circulation 7 is generated.

なお、図例中(特に第1図)、9は水位調整越流管、
10は処理水出口管、11は原水入口管、12は汚泥沈澱部、
13は排泥管、14は水車回転軸、15はモータである。
In the figure example (especially Fig. 1), 9 is a water level adjustment overflow pipe,
10 is a treated water outlet pipe, 11 is a raw water inlet pipe, 12 is a sludge sedimentation part,
13 is a sludge pipe, 14 is a turbine rotation shaft, and 15 is a motor.

(2)回流仕切り板2の一側に浸漬濾床4が配されてい
る。この浸漬濾床4は、扁平網管(第7図参照)を主要
素とする接触床板(板状濾床要素)4a、…を複数枚、回
流仕切板2と平行に並立させて(垂直に並べて)構成さ
れている。第4図に示す如く、回流仕切板2と直交させ
て、並立させてもよい。
(2) The immersion filter bed 4 is arranged on one side of the circulation partition plate 2. The immersion filter bed 4 comprises a plurality of contact floor plates (plate-shaped filter bed elements) 4a having flat net tubes (see FIG. 7) as main elements, arranged in parallel with the circulation partition plate 2 (aligned vertically). )It is configured. As shown in FIG. 4, the circulating partition plate 2 may be orthogonal to each other so as to stand side by side.

(3)また、浸漬濾床4を処理槽1に設置する位置は、
上記実施例に限られることがない。
(3) Further, the position where the submerged filter bed 4 is installed in the treatment tank 1 is
It is not limited to the above embodiment.

第5図は、回流仕切板2の両側を浸付濾床4としたも
のである。この装置は、比較的低濃度汚水処理に適す
る。
In FIG. 5, both sides of the circulation partition plate 2 are used as the impregnated filter bed 4. This device is suitable for treating relatively low concentration wastewater.

第6図は、二組の水車3及び回流仕切り板2を処理槽
1の両側に設置し、一対の回流仕切板2との間に浸漬濾
床4を設けたものである。この装置は、曝気された回流
7を多く必要とする高濃度汚水処理に適する。
In FIG. 6, two sets of the water turbine 3 and the circulation partition plate 2 are installed on both sides of the treatment tank 1, and the immersion filter bed 4 is provided between the pair of circulation partition plates 2. This device is suitable for high-concentration wastewater treatment requiring a large amount of aerated circulation 7.

(4)上記扁平網管5は、汚水負荷に応じて、網の素線
16の細いものから太いものまで、編目の小さいものから
粗いものまで自由に選択できる。特に樹脂網はたとえ1
ヶ所破れても伝線することはなく、土砂止めの網にも使
用される非常に強度のあるものである。また、扁平網管
5は、水流が網目を縦横無尽にどの方向にも通ることが
でき、接触効率の増大に寄与する。
(4) The flat mesh tube 5 is a mesh wire depending on the sewage load.
You can freely choose from 16 thin to thick ones, small stitches to coarse stitches. Especially if the resin net is 1
Even if it breaks in several places, it will not conduct electricity, and it is also very strong, and is used as a net for retaining sand. Further, in the flat mesh tube 5, the water flow can pass through the mesh in any direction in all directions, which contributes to an increase in contact efficiency.

そして、扁平網管5は、通常ポリエチレンやポリプロ
ピレン等のオレフィン系樹脂による押出成形される。扁
平網管5は、他の網状物(円筒網管、漁網、網シート
等)に比して、製作上、強度上、材料使用量、コスト、
接触床板4a(又は4b)への加工の面、さらには、使用時
の接触面積、微生物付着性、等、全体バランス的に優れ
ている。
The flat mesh tube 5 is usually extruded from an olefin resin such as polyethylene or polypropylene. The flat net tube 5 is superior to other net-like objects (cylindrical net tube, fishing net, net sheet, etc.) in manufacturing, strength, material usage amount, cost,
It has excellent overall balance in terms of the surface to be processed into the contact floor plate 4a (or 4b), the contact area during use, the adhesion of microorganisms, and the like.

即ち、扁平網管5は、押出成形で量産でき、網が二重
となるため、素線16が細いものでも強度があり、接触効
率及び微生物の付着性も良好で、低濃度汚水から高濃度
処理まで幅広く使える。また、それぞれ別体の複数本の
扁平網管(接触床要素)5で、接触床板4a(又は4b)を
形成するため、水流・水圧によりヒラヒラと動く。そし
て、その僅かな動きだけでも、それだけ微生物に対する
接触効率の増加が期待される。
That is, since the flat mesh tube 5 can be mass-produced by extrusion molding and the mesh is doubled, even if the wire 16 is thin, it has strength, good contact efficiency and adhesion of microorganisms, and high concentration treatment from low concentration wastewater. Can be widely used up to. In addition, since the contact floor plates 4a (or 4b) are formed by a plurality of flat mesh tubes (contact floor elements) 5 that are separate from each other, they move flutteringly due to the water flow and water pressure. Then, even a slight movement thereof is expected to increase the contact efficiency against microorganisms.

上記扁平網管5としては、仕様が、網管幅5〜20cm、
網の素線16の太さ0.5〜2mm、網管厚さ5〜15mm、編目の
大きさ3〜15mm程度のものを使用する。
As the flat mesh tube 5, the specification is a mesh tube width of 5 to 20 cm,
The net wire 16 has a thickness of 0.5 to 2 mm, a net tube thickness of 5 to 15 mm, and a stitch size of 3 to 15 mm.

(5)次に、接触床板4a(又は4b)の各種態様を説明す
る。
(5) Next, various aspects of the contact floor plate 4a (or 4b) will be described.

第8図に示すものは、接触床支持枠17に、扁平網管5
を一定間隔を空けて取り付けた接触床板4aである。
As shown in FIG. 8, a flat mesh tube 5 is attached to the contact floor support frame 17.
Is a contact floor plate 4a which is attached at regular intervals.

第9図に示すものは、接触床支持体7に、扁平網管5
を縦横チドリに取り付けた接触床板4aである。
As shown in FIG. 9, the flat bed tube 5 is provided on the contact floor support 7.
Is a contact floor plate 4a attached to vertical and horizontal plovers.

第10図に示すものは、接触床棒18a、18bに、扁平網管
5を一定間隔を空けて取り付けた懸垂接触床板4bであ
る。
What is shown in FIG. 10 is a suspended contact floor plate 4b in which flat mesh tubes 5 are attached to the contact floor bars 18a and 18b at regular intervals.

第11図に示すものは、接触床棒18a、18bに、扁平網管
5を縦横チドリに取り付けた懸垂接触床板4bである。
What is shown in FIG. 11 is a suspended contact floor plate 4b in which flat mesh tubes 5 are attached to vertical and horizontal plovers on the contact floor rods 18a and 18b.

接触床板4aの形成は、支持枠17に、扁平網管5の四端
を押え板及びビス等で固定するか、支持枠17に巻き付け
て接着するか、針金等のヒモ状物で支持枠17に編むよう
にして固定すればよい。
The contact floor plate 4a is formed by fixing the four ends of the flat mesh tube 5 to the support frame 17 with a holding plate and screws, winding the support frame 17 and adhering it, or using a string-like object such as a wire on the support frame 17. It can be fixed by knitting.

また、懸垂接触床板4bの形成は、扁平網管5の上下端
を、それぞれ上部接触床棒18a及び下部接触床棒18bに巻
き付ける如く折り返し、接触部を接着するか、針金状の
ヒモ状物で編むようにして結わえ付けるか又は押え板及
びビス等で固定すればよい。下部接触床棒18bは錘の役
目もするものである。
The suspended contact floor plate 4b is formed by folding back the upper and lower ends of the flat mesh tube 5 so as to wind around the upper contact floor bar 18a and the lower contact floor bar 18b and bonding the contact portions or knitting with a wire-like string. They may be tied together or fixed with a holding plate and screws. The lower contact floor bar 18b also serves as a weight.

そして、この懸垂接触床板4bは、第12図に示す如く、
懸垂接触床板4bの上部接触床棒18aの両端に形成された
切欠部27を、懸垂枠20に形成されたスリット21に係合さ
せることにより、懸垂枠20に多数ぶら下げて使用する。
And, this suspended contact floor plate 4b, as shown in FIG.
The notch portions 27 formed at both ends of the upper contact floor bar 18a of the suspension contact floor plate 4b are engaged with the slits 21 formed in the suspension frame 20 so as to be suspended from the suspension frame 20 for use.

なお、接触床支持枠17や懸垂枠20、接触床棒18a、18b
は、鉄やステンレス製のものが加工しやすく、強度があ
り、安価でよい。
In addition, the contact floor support frame 17, the suspension frame 20, the contact floor bars 18a, 18b
The material made of iron or stainless steel is easy to process, has strength, and is inexpensive.

(6)次に、上記接触床板4a、4bを使用しての浸漬濾床
の形成方法について説明をする。
(6) Next, a method for forming a submerged filter bed using the contact floor plates 4a and 4b will be described.

接触床板4aで浸漬濾床4を形成する場合は、接触床板
4aに一枚一枚ビス等で処理槽に固定してもよいが、第3
〜4図に示す如くスライド枠22を処理槽1に取り付け、
接触床板4aを落とし込みはめ込む方法が簡単でよい。
When forming the immersion filter bed 4 with the contact floor plate 4a, the contact floor plate
Although it may be fixed to the processing tank with screws or the like on 4a,
Attach the slide frame 22 to the processing tank 1 as shown in FIG.
The method of dropping and fitting the contact floor plate 4a is simple.

また、懸垂接触床板4bで浸漬濾床を形成する場合は、
上記のようにして多数の懸垂接触床板4bをぶら下げた第
12図に示す懸垂枠20を、第13図に示す如く、処理槽1に
取り付けられた受け支持具24にて支えればよい。
Further, when forming a submerged filter bed with the suspended contact floor plate 4b,
As described above, a number of hanging contact floor boards 4b are hung.
The suspension frame 20 shown in FIG. 12 may be supported by a receiving support 24 attached to the processing tank 1 as shown in FIG.

そして、接触床板4a又は懸垂接触床板4bのそれぞれの
間隔は30〜100mmと被処理水負荷即ち、接触面積負荷に
応じて選定する。即ち、低濃度汚水処理であれば、接触
面積負荷が小さく、接触面積が多く必要となるため、網
目の細かい扁平網管5を使用するとともに、接触床板4
a、4bの間隔を狭めて設置する。また、高濃度処理であ
れば接触面積負荷が多くとれるため、網目が粗くてもま
た接触床板4a、4bの間隔が広くてもよい。
Then, the interval between the contact floor plate 4a or the suspended contact floor plate 4b is selected to be 30 to 100 mm according to the load of the water to be treated, that is, the contact area load. That is, in the case of low-concentration wastewater treatment, the contact area load is small and a large contact area is required. Therefore, a flat mesh tube 5 with a fine mesh is used and the contact floor plate 4 is used.
Install with the space between a and 4b narrowed. In addition, since the contact area load can be increased if the treatment is performed at a high concentration, the mesh may be rough or the distance between the contact floor plates 4a and 4b may be wide.

(7)さらに、本発明に使用できる水車の各態様を第14
〜16図に示す。
(7) Furthermore, the fourteenth aspects of the water turbine that can be used in the present invention are described.
~ Figure 16 shows.

第14図は、水の掻き出し部材6が板状のものであり、
第15図は、水の掻き出し部材6が管状のものであり、第
16図は、水の掻き出し部材6が放射状に出た櫛状のもの
である。
FIG. 14 shows that the water scraping member 6 has a plate shape,
FIG. 15 shows that the water scraping member 6 has a tubular shape.
FIG. 16 shows a comb-shaped member 6 in which the water scraping member 6 is radially projected.

B.次に、上記実施例の使用態様を説明する。B. Next, the mode of use of the above embodiment will be described.

本発明は低速回転(周速30〜60m/分)の省エネ水車3
により、水車3の掻き出し部材6の全長にわたり大水量
を掻き出させて、回流仕切板2を境にして大水量の曝気
された回流7を生ぜしめ接触酸化させる。
The present invention is a low-speed rotation (peripheral speed 30 ~ 60m / min) energy-saving water turbine 3
As a result, a large amount of water is scraped out over the entire length of the scraping member 6 of the water wheel 3, and a large amount of aerated swirl 7 is generated at the boundary of the swirling partition plate 2 to cause catalytic oxidation.

前述の特公昭58−54638号公報の如く円弧面仕切り板
を有しないため、当該公報による回流に比して、小さな
動力で大きな回流量が得られる。こののため、回流水量
が数多く、浸漬濾床4のデッドスペースが相対的に小さ
くなることになり、それだけ微生物に対する接触効率が
良くなる。
Since it does not have a circular arc partition plate as in Japanese Patent Publication No. 58-54638, the large circulation flow can be obtained with a small power as compared with the circulation according to the publication. Therefore, the amount of circulating water is large, and the dead space of the submerged filter bed 4 is relatively small, and the contact efficiency with respect to the microorganisms is improved accordingly.

また、水車3の掻き出し部材6に表面積の多い有孔板
や有孔管を使用すれば回転にともなって薄い水膜が掻き
出し部材6の表面をしたたり、空気に晒されることによ
り、空気中の酸素が水中に溶解する。逆に、水中の揮発
性有機物質は晒されることにより空気中へ放射される置
換作用が働く。このように、水車による曝気は、ブロワ
ーやコンプレッサー曝気には成し得ないことが可能にな
る。
Further, if a perforated plate or a perforated pipe having a large surface area is used for the scraping member 6 of the water wheel 3, a thin water film may drip on the surface of the scraping member 6 or may be exposed to air due to the rotation. Oxygen dissolves in water. Conversely, when exposed to volatile organic substances in water, the action of displacement is emitted into the air. Thus, it becomes possible that aeration with a water turbine cannot occur with aeration with a blower or compressor.

また既設の処理槽1であれば、その槽に合致した回流
仕切板2を落とし込み固定した後、上部に水車3を設置
し、接触床板4aを落とし込むか、懸垂接触床板4bを懸垂
枠20を介してぶら下げれば、既設処理槽1の改造も簡単
にできる。特に、標準活性汚泥法の改造は、ブロワー曝
気に比して格段に省エネルギーを図れる。扁平網管5に
よる接触酸化であるため、着床した微生物(好気性)膜
の内部は曝気された回流7により好気分的消化及び嫌気
的自己消化の双方が促進され、余剰汚泥は非常に減少
し、処理水量の大幅な増大が可能となる。
In the case of the existing treatment tank 1, after dropping and fixing the circulation partition plate 2 that matches the tank, install the water turbine 3 on the upper part and drop the contact floor plate 4a, or drop the suspended contact floor plate 4b through the suspension frame 20. By hanging it up, the existing treatment tank 1 can be easily modified. In particular, the modification of the standard activated sludge method can remarkably save energy compared to blower aeration. Since it is catalytic oxidation by the flat mesh tube 5, the aerated stream 7 promotes both aerobic digestion and anaerobic autolysis, and excess sludge is greatly reduced inside the implanted microbial (aerobic) membrane. Therefore, the amount of treated water can be greatly increased.

非常に多くの浸漬濾床4における接触床板4a(4b)の
扁平網管5のなかで、微生物膜の膜厚が増大し内部に酸
素が供給されず不活性化して経時的に自然剥離が起き
る。全域にわたる良好な曝気状態の回流7により剥れた
所は、酸素が供給されすぐ新たな微生物が着床する。従
って、微生物膜の自然剥離による水質の変化はほとんど
なく、処理槽1の浸漬濾床4は、微生物環境がいつも自
然のまま一定条件にて保たれるため、いつも質的及び量
的に安定した水処理が可能となり、さらには、人為的洗
滌等の手を加える必要もない。
In the flat mesh tube 5 of the contact floor plates 4a (4b) in the very large number of the immersion filter beds 4, the film thickness of the microbial membrane increases, oxygen is not supplied to the inside, and it is inactivated to cause spontaneous peeling over time. Oxygen is supplied to the areas separated by the circulation 7 in a good aeration state over the entire area, and new microorganisms are immediately implanted. Therefore, there is almost no change in water quality due to natural exfoliation of the microbial membrane, and the immersion filter bed 4 of the treatment tank 1 is always qualitatively and quantitatively stable because the microbial environment is always kept in a natural condition under constant conditions. Water treatment is possible, and there is no need for artificial washing or the like.

なお、第17図に示すように、処理槽1を深くして、回
流仕切板2を長くすることにより、設置面積の少ない大
容量のディープシャフト方式の処理槽も製作できる。こ
れは、スペースのないところでは非常に有効である。こ
の水処理装置において、高濃度汚水を処理しようとする
際、水車の取り付け本数が設置スペースの点で制限され
曝気された回流7量が、水車3の回転数を上げても不足
すると思われるときは、図例の如く浸漬濾床4を設置し
ていない側に、散気管25で補助曝気してやるか、及び/
又は循環循環ポンプ26を設置し、水車3にて水が掻き出
されている側へ散水曝気してやればよい。なお、循環ポ
ンプ26としては、水中プロペラポンプ又はバーチカルポ
ンプ等の低揚程で大水量ポンプが省エネルギータイプで
吐出量も多いため望ましい。
As shown in FIG. 17, by deepening the processing tank 1 and lengthening the circulating partition plate 2, a large-capacity deep shaft type processing tank with a small installation area can be manufactured. This is very useful where there is no space. In this water treatment device, when trying to treat high-concentration sewage, when the number of water turbines installed is limited due to the installation space and the aerated circulation amount 7 seems to be insufficient even if the rotation speed of the water turbine 3 is increased. Does the auxiliary aeration with the air diffuser 25 on the side where the submerged filter bed 4 is not installed as shown in the figure, and /
Alternatively, the circulation circulation pump 26 may be installed, and the side where the water is being scraped by the water turbine 3 may be sprinkled and aerated. As the circulation pump 26, a large water pump with a low head such as a submersible propeller pump or a vertical pump is desirable because it is an energy-saving type and has a large discharge amount.

<発明の作用・効果> 本発明の表面曝気浸漬濾床水処理装置は、上記のよう
な構成により、濾床の閉塞が発生し難く、且つ、容積当
たりの接触面積も大きくすることができる。
<Operation and Effect of the Invention> The surface aeration-immersed filter bed water treatment apparatus of the present invention has the above-described configuration, so that clogging of the filter bed is unlikely to occur and the contact area per volume can be increased.

即ち、接触床板(濾床要素)が扁平網管を主要素とす
るため、容積当りの接触面積は非常に大きいものであ
り、小さな処理槽に浸漬濾床を設置しても接触面積が大
きいとともに、水車による回流は曝気状態が良好である
ため、他の処理槽より非常にコンパクトに設計できる。
That is, since the contact floor plate (filter bed element) has a flat mesh tube as a main element, the contact area per volume is very large, and even if the immersion filter bed is installed in a small treatment tank, the contact area is large, Since the circulation by the water turbine has a good aeration state, it can be designed much more compact than other treatment tanks.

また、濾床要素(接触床板又は懸垂接触床板)を一定
間隔を空けて処理槽の回流水路内に取り付けるため、浸
漬濾床の全体に閉塞障害は起こり得ない。さらに、水車
の掻き出し部材により押出された水は必ず脈流となり、
濾床要素は脈回流によりゆさぶられて微生物と汚水との
接触効率が高められる。
Further, since the filter bed element (contact floor plate or suspended contact floor plate) is installed in the circulating water channel of the treatment tank at regular intervals, no obstruction obstacle can occur in the entire immersed filter bed. Furthermore, the water extruded by the scraping member of the water wheel will always have a pulsating flow,
The filter bed element is shaken by the pulsating flow to enhance the contact efficiency between microorganisms and wastewater.

さらに、微生物膜が増大した場合、内部には酸素がほ
とんど供給されず微生物(好気性)は活性化されず弱る
が、通性嫌気性菌の活性化が高まり、汚泥の消化が促進
される。これにより、扁平網管の網目より大きな塊とな
って、自然剥離が起り、濾床要素間を沈降し、汚泥沈澱
部に沈澱する。このため、浸漬濾床の洗滌は必要とせ
ず、定期的に沈澱部の余剰汚泥を排泥管にて排出すれば
よい。そして、全域にわたる曝気状態が良好な回流によ
り、酸素供給が良好に行われ微生物膜が剥れた所はすぐ
新たな微生物が着床する。
Further, when the microbial membrane increases, almost no oxygen is supplied to the inside and the microorganisms (aerobic) are not activated and weakened, but the activation of facultative anaerobic bacteria is increased and the digestion of sludge is promoted. As a result, the lumps become larger than the mesh of the flat mesh tube, spontaneous peeling occurs, settles between the filter bed elements, and settles in the sludge settling section. Therefore, it is not necessary to wash the submerged filter bed, and the excess sludge in the settling section may be periodically discharged through the sludge pipe. Then, due to the good circulation of the aerated state over the entire area, oxygen is satisfactorily supplied, and new microorganisms are immediately implanted where the microbial membrane is peeled off.

微生物膜の自然剥離による水質の変化はほとんどな
く、処理槽の浸漬濾床は、微生物環境がいつも自然のま
ま一定条件にて保たれるため、いつも質的及び量的に安
定した水処理が可能となり、さらには、人為的洗滌等の
手を加える必要もない。特に、省エネのもとに曝気効果
を高め大水量の回流による微生物への接触効率も高め、
設置面積をとらない背の高い深い処理槽にも使用できる
ため、土地の少ない日本ではより有効である。
There is almost no change in water quality due to natural exfoliation of the microbial membrane, and the immersive filter bed in the treatment tank always maintains the microbial environment in a natural condition under constant conditions, so qualitatively and quantitatively stable water treatment is always possible. Moreover, there is no need to add artificial washing or the like. In particular, the aeration effect is enhanced by saving energy, and the contact efficiency with microorganisms by the circulation of a large amount of water is also enhanced.
Since it can be used for tall and deep processing tanks that do not occupy an installation area, it is more effective in Japan where there is little land.

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

第1図は本発明装置の一実施例を示す第2図のB−B線
断面図、 第2図は第1図のA−A線断面図、 第3図は第2図の平面図 第4図は第1図の実施例の変形態様における平面図 第5図の本発明装置の他の例を示す断面図、 第6図は本発明装置のさらに他の例を示す断面図、 第7図は本発明の接触床板に使用する扁平網管の斜視
図、 第8図は本発明の接触床板の一例を示す正面図、 第9図は同じく他の例を示す正面図、 第10図は本発明の垂直接触床板の一例を示す正面図、 第11図は同じく他の例を示す正面図、 第12図は接触床懸垂枠に懸垂接触床板がかけられた浸漬
濾床の斜視図、 第13図は懸垂接触床板を使用した本発明装置の一例を示
す断面図、 第14図は本発明に使用する水車の一例を示す斜視図、 第15図は同じく他の例を示す斜視図、 第16図は同じくさらに他の例を示す斜視図、 第17図は本発明の装置で回流仕切板を長くした例を示す
断面図。 1……処理槽 2……回流仕切板 3……水車 4……浸漬濾床 4a……接触床板(板状濾床要素) 4b……懸垂接触床板(板状濾床要素) 5……扁平網管 6……掻き出し部材 7……回流
1 is a sectional view taken along the line BB of FIG. 2 showing an embodiment of the device of the present invention, FIG. 2 is a sectional view taken along the line AA of FIG. 1, and FIG. 3 is a plan view of FIG. FIG. 4 is a plan view of a modification of the embodiment of FIG. 1, a sectional view showing another example of the device of the present invention shown in FIG. 5, and FIG. 6 is a sectional view showing a further example of the device of the present invention. FIG. 8 is a perspective view of a flat mesh tube used for the contact floor plate of the present invention, FIG. 8 is a front view showing an example of the contact floor plate of the present invention, FIG. 9 is a front view showing another example thereof, and FIG. A front view showing an example of the vertical contact floorboard of the invention, FIG. 11 is a front view showing another example of the same, FIG. 12 is a perspective view of a submerged filter bed in which a suspension contact floorboard is hung on a contact floor suspension frame, The figure is a cross-sectional view showing an example of the device of the present invention using a suspended contact floor plate, FIG. 14 is a perspective view showing an example of a water turbine used in the present invention, and FIG. 15 is a perspective view showing another example of the same. Figure 16 is a perspective view showing still another example also, FIG. 17 is a cross-sectional view showing an example in which a longer circumfluence partition plate in the apparatus of the present invention. 1 ... Treatment tank 2 ... Circulating partition plate 3 ... Water turbine 4 ... Immersion filter bed 4a ... Contact floor plate (plate filter bed element) 4b ... Suspended contact floor plate (plate filter bed element) 5 ... Flat Net tube 6 …… Scraping member 7 …… Circulation

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】生物処理法の一種である固定接触法におけ
る接触酸化法に使用される表面曝気浸漬濾床水処理装置
において、 処理槽(1)の上部に水車(3)を水平に回転可能に固
定し、水車(3)の水の掻き出し部材(6)のすぐ下部
より前記処理槽(1)の下部に向けて、前記処理槽
(1)の幅全域にわたり下部が開放されている回流仕切
板(2)を設けて、前記水車(3)の水掻き出し部材
(6)の一部が水没する位置に水位を調節し、前記水車
(3)の回転により、前記回流仕切板(2)を境にして
回流を発生させるように構成するとともに、 前記回流仕切板(2)の少なくとも一側に浸漬濾床
(4)が配され、該浸漬濾床(4)が扁平網管(5)を
主要素とする板状濾床要素(4a)、…を複数枚、並立さ
せて形成されていること を特徴とする表面曝気浸漬濾床水処理装置。
1. In a surface aeration submerged filter bed water treatment device used in a catalytic oxidation method in a fixed contact method, which is a kind of biological treatment method, a water turbine (3) can be horizontally rotated above a treatment tank (1). Fixed to the water tank (3), and the lower part of the water scraping member (6) of the water turbine (3) is directed toward the lower part of the processing tank (1), and the lower part is opened over the entire width of the processing tank (1). A plate (2) is provided, the water level is adjusted to a position where a part of the water scraping member (6) of the water turbine (3) is submerged, and the circulation partition plate (2) is rotated by the rotation of the water wheel (3). The dipping filter bed (4) is arranged on at least one side of the diversion partition plate (2), and the dipping filter bed (4) mainly comprises the flat mesh tube (5). A plurality of plate-shaped filter bed elements (4a), which are the base, are formed by arranging them in parallel. Surface aeration submerged biofilter water treatment device according to symptoms.
JP62075388A 1986-04-18 1987-03-27 Surface aeration immersion filter bed water treatment device Expired - Fee Related JP2564131B2 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP8973786 1986-04-18
JP61-89737 1986-04-18

Publications (2)

Publication Number Publication Date
JPS6344996A JPS6344996A (en) 1988-02-25
JP2564131B2 true JP2564131B2 (en) 1996-12-18

Family

ID=13979078

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62075388A Expired - Fee Related JP2564131B2 (en) 1986-04-18 1987-03-27 Surface aeration immersion filter bed water treatment device

Country Status (1)

Country Link
JP (1) JP2564131B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05245488A (en) * 1992-03-04 1993-09-24 Katsuragi Takao Vertical parallel type biological membrane purifying apparatus
JP4897518B2 (en) 2007-03-02 2012-03-14 株式会社ニチベイ Blind operating device

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5854638B2 (en) * 1979-08-20 1983-12-06 雅司 加藤 Catalytic oxidation water treatment equipment
JPS59179192A (en) * 1983-03-31 1984-10-11 Gokou Seisakusho:Kk Waste water treating apparatus
JPS6049995U (en) * 1983-09-14 1985-04-08 東レエンジニアリング株式会社 urban sewer

Also Published As

Publication number Publication date
JPS6344996A (en) 1988-02-25

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