JP2011005375A - Solid-liquid separator - Google Patents

Solid-liquid separator Download PDF

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JP2011005375A
JP2011005375A JP2009149333A JP2009149333A JP2011005375A JP 2011005375 A JP2011005375 A JP 2011005375A JP 2009149333 A JP2009149333 A JP 2009149333A JP 2009149333 A JP2009149333 A JP 2009149333A JP 2011005375 A JP2011005375 A JP 2011005375A
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sludge
solid
rotating body
baffle
separation
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JP5619379B2 (en
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Takahiro Ito
貴浩 伊藤
Yoshiyuki Sugawara
良行 菅原
Kazuhiro Sato
一宏 佐藤
Nobuko Oshita
信子 大下
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Nishihara Environment Co Ltd
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Nishihara Environmental Technology Co Ltd
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  • Treatment Of Sludge (AREA)
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Abstract

PROBLEM TO BE SOLVED: To provide a compact and inexpensive solid-liquid separator further improving concentration performance of a concentration machine using rotary blades.SOLUTION: The solid-liquid separator includes a water tank 1, a rotary body 3 set in the water tank 1 and provided with a plurality of separation blades 5 with intervals, a driver unit 6 for rotating the rotary body 3, and flow inhibiting rods 10 set in the water tank 1. Sludge is rotated in the same direction as the rotation direction of the separation blades 5 to generate a speed difference between the sludge and flow inhibiting rods 10. Then a water channel is formed near the flow inhibiting rods 10 to promote the solid-liquid separation of raw water, further concentrating the sludge.

Description

本発明は、上水、下水、産業廃水、農業集落排水等の一次処理、または生物処理による二次処理で発生した汚泥等の固形物と分離液とが混合している原水について、汚泥と分離液とを固液分離するための固液分離装置に関するものである。   The present invention relates to raw water in which solids such as sludge generated by primary treatment such as clean water, sewage, industrial wastewater, agricultural settlement drainage, or secondary treatment by biological treatment and a separated liquid are mixed with sludge. The present invention relates to a solid-liquid separation device for solid-liquid separation from a liquid.

上記のような固液分離をする方法は、その目的に応じて、一般に、沈殿による固液分離(分離液回収)と濃縮とに大別される。
先ず、沈殿による固液分離は、汚泥等の固形物と分離液等の液体とが混合している原水について、重力によって汚泥を沈降させて原水から汚泥を分離する方法である。この沈殿による固液分離では、主に、次の重力式と機械式の2つの方法がある。
重力式は、汚泥を沈殿させるための沈殿槽、凝集沈殿槽等を用いるものである。
機械式は、膜分離、常圧(加圧)による浮上分離等の処理を行うものであるが、通常、多くのエネルギーを消費する。
The methods for solid-liquid separation as described above are generally roughly classified into solid-liquid separation by precipitation (separate recovery) and concentration according to the purpose.
First, solid-liquid separation by precipitation is a method of separating sludge from raw water by allowing the sludge to settle by gravity for raw water in which solids such as sludge and liquid such as a separation liquid are mixed. In this solid-liquid separation by precipitation, there are mainly the following two methods of gravity and mechanical.
The gravity type uses a sedimentation tank, a coagulation sedimentation tank, or the like for sedimenting sludge.
The mechanical type performs processing such as membrane separation and floating separation by normal pressure (pressurization), but usually consumes a lot of energy.

他方、濃縮による固液分離は、固形物である汚泥をさらに濃縮する方法で、上述した沈殿による固液分離と同様に、大別して以下の重力式と機械式の2つの方法がある。
重力式は一般的な方法であり、重力濃縮槽、凝集濃縮槽、または沈殿槽等を用いて実施される。これらの重力濃縮槽、凝集濃縮槽、または沈殿槽等は、汚泥を重力によって沈降させて固液分離するので、汚泥を濃縮するためのエネルギーを必要としない。
また、機械式は、遠心式、常圧浮上式、またはベルト式等があり、遠心式すなわち遠心分離法を採用する場合が比較的多い。この遠心分離法は、比重が1よりも大きな汚泥について、回転する遠心分離機によって分離するため、エネルギーを多く消費する。なお、常圧浮上式は、原水に起泡剤を添加し、微細気泡を発生させて汚泥を気泡と共に浮上させるものであって、汚泥の見かけ比重を1よりも小さくして汚泥を分離濃縮するものである。
そして本願出願人は、前述した既存固液分離技術の課題を解決する新たな固液分離装置を開発して、既に特許出願を行っている(特許文献3参照)。
On the other hand, solid-liquid separation by concentration is a method of further concentrating solid sludge, and there are roughly the following two methods of gravity and mechanical as in the case of solid-liquid separation by precipitation described above.
The gravity method is a general method, and is performed using a gravity concentration tank, a coagulation concentration tank, a precipitation tank, or the like. These gravity concentration tanks, coagulation concentration tanks, sedimentation tanks, and the like do not require energy for concentrating the sludge because the sludge is settled by gravity and solid-liquid separated.
The mechanical type includes a centrifugal type, a normal pressure levitation type, a belt type, and the like, and a centrifugal type, that is, a centrifugal separation method is relatively often employed. In this centrifugal separation method, a sludge having a specific gravity greater than 1 is separated by a rotating centrifugal separator, and therefore consumes a lot of energy. The normal pressure levitation type is a method in which a foaming agent is added to raw water, fine bubbles are generated and sludge is floated together with bubbles, and the sludge is separated and concentrated by making the apparent specific gravity of sludge smaller than 1. Is.
The applicant of the present application has developed a new solid-liquid separation device that solves the problems of the existing solid-liquid separation technology described above, and has already filed a patent application (see Patent Document 3).

特開2007-105596号公報Japanese Unexamined Patent Publication No. 2007-105596 特開2009-28665号公報JP 2009-28665 A 特開2006-263670号公報JP 2006-263670 A

上述した固液分離技術では、次のような問題があった。
(1)重力式は、維持管理が容易で実施費用が低コストである利点を有する反面、処理時の原水の性状の相違に対応して、固液分離後に得られる汚泥や分離液の性状が変動し、一定にはならない。そのため、原水によって処理性能にばらつきが生じる。
また、濃縮濃度が比較的低いため汚泥発生量が多く、汚泥処分量の増加によって処分費が高くなり、かつ、分離液水質の悪化によって水処理系に悪影響を与えるおそれがあった。
The solid-liquid separation technique described above has the following problems.
(1) The gravity type has the advantage of easy maintenance and low implementation costs, but in response to the difference in the properties of raw water during processing, the properties of sludge and separation liquid obtained after solid-liquid separation are It fluctuates and is not constant. Therefore, processing performance varies depending on the raw water.
Moreover, since the concentration of concentration is relatively low, the amount of sludge generated is large, the disposal cost increases due to an increase in the amount of sludge disposal, and the water treatment system may be adversely affected due to the deterioration of the quality of the separated liquid water.

さらに、固液分離性能や濃縮性能向上のため、沈殿池や重力濃縮槽にかき寄せ機を設置した場合、これに固液分離促進手段であるピケットフェンスを付加することがあった。図
18に示す従来装置では、駆動機101で駆動されるかき寄せ機102を設置し、このかき寄せ機102にピケットフェンス100を取り付けたものであり、ピケットフェンス100は、通常、棒状あるいはアングル状であり、かき寄せ機102と共に槽103内を移動する。この装置におけるピケットフェンス100は、ゆっくりと沈殿池や重力濃縮槽下部を移動して濃縮された汚泥中に水みち(みずみち)を形成し、水抜けを促進させ、汚泥の濃縮濃度を増加させる。しかし、ピケットフェンス100は、原水中の汚泥濃度が高くないと、かえって汚泥を拡散させてしまうおそれがある。
さらにまた、上方に溜まっていてピケットフェンス100に接触しない汚泥に対して作用せず、沈殿槽や沈殿池の汚泥が、ピケットフェンス100の位置まで降下しなければ濃縮作用を生じない。
Furthermore, in order to improve solid-liquid separation performance and concentration performance, when a scraper is installed in a sedimentation basin or gravity concentration tank, a picket fence as a solid-liquid separation promotion means may be added thereto. In the conventional apparatus shown in FIG. 18, a raking machine 102 driven by a driving machine 101 is installed, and a picket fence 100 is attached to the raking machine 102, and the picket fence 100 is usually in a rod shape or an angle shape. , Move in the tank 103 together with the scraper 102. The picket fence 100 in this device slowly moves through the sedimentation basin and the lower part of the gravity concentration tank to form a water path in the concentrated sludge, promotes drainage and increases the concentrated concentration of sludge. . However, the picket fence 100 may cause the sludge to diffuse unless the sludge concentration in the raw water is high.
Furthermore, it does not act on sludge that accumulates above and does not come into contact with the picket fence 100. If the sludge in the settling tank or sedimentation basin does not descend to the position of the picket fence 100, no concentration action occurs.

(2)一方、機械式は、性能が良好で動作が安定している反面、設備費が高くなる。また、操作が煩雑で、良好な状態を維持するには定期的なメンテナンス作業が必要であり、かつ、消耗品やエネルギーの使用量が多いため、比較的、維持管理費も高価である。そこで、沈殿槽における汚泥の沈降を促進させ、その流出を防止するために両性水溶性高分子、あるいは油中水型両性水溶性高分子エマルジョンを添加する方法等が実施されていた。 (2) On the other hand, while the mechanical type has good performance and stable operation, the equipment cost becomes high. In addition, the operation is complicated, and regular maintenance work is required to maintain a good state, and the amount of consumables and energy used is large, so the maintenance cost is relatively expensive. Therefore, a method of adding an amphoteric water-soluble polymer or a water-in-oil amphoteric water-soluble polymer emulsion or the like has been implemented in order to promote sedimentation of sludge in the sedimentation tank and prevent its outflow.

しかし、高分子やエマルジョンのような薬剤を添加すれば処理費用が上昇し、さらに汚泥や分離液が薬剤を含むため汚泥発生量が増加し、分離液処理にも悪影響を与えかねない。
上記のような事情から、取扱いが容易で、固液分離性能が良好であって、設備費や維持管理費等が安価である固液分離装置の提供が強く望まれていたところ、本願出願人は先願(特許文献3)にかかる固液分離装置を開発し、固液分離性能とくに濃縮性能を向上させたが、さらなる濃縮性能の向上、安定した固液分離および装置のコンパクト化を目指して試験研究を繰り返し、改善改良を重ねた結果、本願発明にかかる固液分離装置を得るに到った。
However, if chemicals such as polymers and emulsions are added, the processing costs increase, and sludge and separation liquid contain chemicals, and the amount of sludge generated increases, which may adversely affect the separation liquid treatment.
In view of the above circumstances, it has been strongly desired to provide a solid-liquid separation device that is easy to handle, has good solid-liquid separation performance, and has low equipment costs, maintenance costs, etc. Has developed a solid-liquid separation device according to the prior application (Patent Document 3) and improved the solid-liquid separation performance, especially the concentration performance, but with the aim of further improving the concentration performance, stable solid-liquid separation and downsizing of the device As a result of repeating the test research and repeating improvements and improvements, the solid-liquid separation device according to the present invention has been obtained.

本発明は、上記のような課題を解決するためにされたもので、従来のピケットフェンスを利用した固液分離装置に比べて汚泥の濃縮性能が向上し、かつ、コンパクトで安価な固液分離装置を提供することを目的とする。
本発明は、課題を達成するために以下のような構成とした。すなわち、水槽と、該水槽内に配設され、複数枚の分離羽根が間隔をもって設けられた回転体と、該回転体を回転させる駆動機と、前記水槽内に配設された阻流棒とからなることを特徴とする。この阻流棒は、一つまたは二つ以上設置してもよい。
The present invention has been made to solve the above-described problems, and has improved sludge concentration performance compared to a conventional solid-liquid separation device using a picket fence, and is compact and inexpensive solid-liquid separation. An object is to provide an apparatus.
The present invention has the following configuration in order to achieve the object. That is, a water tank, a rotating body disposed in the water tank, and a plurality of separation blades provided at intervals, a driving device for rotating the rotating body, and a baffle rod disposed in the water tank It is characterized by comprising. One or two or more of the baffle bars may be installed.

本発明においては、水槽(分離槽)と、この水槽内に複数の短冊状の分離羽根が間隔をもって配設される回転体と、この回転体を低速で回転させる駆動機と、回転により発生した汚泥の流れの一部を変化させる阻流棒とを設けることにより、次のような効果がある。
(1)回転体内部に汚泥中の固形物が保持され、分離液は回転体外部に排出されるので、原水の固液分離、濃縮、沈降が促進される。
(2)阻流棒の設置により、阻流棒と回転体により回転する汚泥との間に速度差が生じ、阻流棒の近傍の汚泥に水みちが形成され、原水の濃縮(固液分離)が促進されるので、効率のよい固液分離装置が提供される。
(3)水槽内部にフロックを多量に保持できるため、凝集濃縮槽の設置面積や容積が減少し、全体がコンパクト化するので設備費が削減される。また、装置構造が簡素であるので、その維持管理が容易になる。
In the present invention, a water tank (separation tank), a rotating body in which a plurality of strip-like separation blades are disposed at intervals in the water tank, a driving device that rotates the rotating body at a low speed, and rotation are generated. Providing a baffle that changes part of the sludge flow has the following effects.
(1) Solid matter in sludge is held inside the rotating body and the separated liquid is discharged to the outside of the rotating body, so that solid-liquid separation, concentration, and sedimentation of raw water are promoted.
(2) The installation of the baffle creates a speed difference between the baffle and the sludge rotating by the rotating body, forming a water channel in the sludge near the baffle, and concentrating the raw water (solid-liquid separation) ) Is promoted, an efficient solid-liquid separation device is provided.
(3) Since a large amount of floc can be held inside the water tank, the installation area and volume of the coagulation / concentration tank are reduced and the whole is made compact, so that the equipment cost is reduced. In addition, since the device structure is simple, the maintenance is easy.

(4)阻流棒による濃縮促進作用が生じるため、回転体のみ設置した場合に比べ、回転体の回転数を低くでき、装置のエネルギーの消費量が低減する。また、汚泥濃縮効率が向上するので、回転体への負荷を増加させることができる。
(5)装置の洗浄が不要なため、別途、洗浄設備を設ける必要がなくなる。
(6)糸状性細菌の増殖により糸状性バルキング状態になり沈降性が悪くなった汚泥に対しても、回転体を低速で回転させることにより、効率的な処理が可能である。
(7)機械式と比較して構造が簡単であるため、トラブルが生じにくく安定した固液分離と汚泥の濃縮が行える。
(8)凝集剤を使わずに汚水等の沈殿処理を行う場合(以下「無薬注」という)でも高濃度の濃縮液が得られるため、薬品添加に伴う添加設備や維持管理費が不要となり、汚泥発生量の増加や薬品添加の悪影響が生じることがない。
(4) Since the concentration promoting action by the baffle rod occurs, the rotational speed of the rotating body can be lowered and the energy consumption of the apparatus is reduced as compared with the case where only the rotating body is installed. Moreover, since the sludge concentration efficiency is improved, the load on the rotating body can be increased.
(5) Since it is not necessary to clean the apparatus, it is not necessary to provide a separate cleaning facility.
(6) Efficient treatment is possible by rotating the rotating body at a low speed even for sludge that has become filamentous bulking due to the growth of filamentous bacteria and has deteriorated sedimentation.
(7) Since the structure is simple compared to the mechanical type, troubles do not easily occur and stable solid-liquid separation and sludge concentration can be performed.
(8) A high-concentration concentrate can be obtained even when sewage is settled without using a flocculant (hereinafter referred to as “no chemical injection”), eliminating the need for additional equipment and maintenance costs associated with the addition of chemicals. No increase in sludge generation or adverse effects of chemical addition.

以下、本発明の実施の形態を図面に基づいて説明する。
図1は、本発明に係る固液分離装置の基本的な構造を示す概略図である。この装置は、上水、下水、産業排水、農業集落排水等の一次処理や、生物処理後の二次処理において発生した汚泥等について、固液分離をするために利用可能である。この固液分離装置は、水槽1を備え、この水槽1には、例えば下水の余剰汚泥を含んだ原水が流入管2を介して流入するようにしてある。そして、水槽1の内部には、原水の固液分離を促進するための筒状の回転体3を配置してある。水槽1は、例えば既設の汚水処理施設の最終沈殿槽とすることができるが、汚泥等の固形物と分離液を固液分離する水槽であればこれに限らない。原水は、汚泥を含んだ汚水、或いは、凝集した汚泥であるフロックを含み、フロックの凝集を促進するための薬液が注入されたものが含まれる。薬液としては、高分子凝集剤、無機凝集剤、またはそれらの混合液とすることができ、無機凝集剤としては、ポリ塩化鉄、PAC等が使用できる。
Hereinafter, embodiments of the present invention will be described with reference to the drawings.
FIG. 1 is a schematic diagram showing a basic structure of a solid-liquid separation device according to the present invention. This apparatus can be used for solid-liquid separation of sludge generated in primary treatment such as clean water, sewage, industrial wastewater, agricultural settlement wastewater, and secondary treatment after biological treatment. This solid-liquid separation device includes a water tank 1, and raw water containing, for example, excess sewage sludge flows into the water tank 1 through an inflow pipe 2. And the cylindrical rotary body 3 for accelerating | stimulating the solid-liquid separation of raw | natural water is arrange | positioned inside the water tank 1. FIG. The water tank 1 can be used as, for example, a final sedimentation tank of an existing sewage treatment facility, but is not limited to this as long as it is a liquid tank that separates solids such as sludge and separated liquid. The raw water includes sewage containing sludge or floc that is agglomerated sludge and into which a chemical solution for promoting flocculation is injected. As the chemical solution, a polymer flocculant, an inorganic flocculant, or a mixture thereof can be used. As the inorganic flocculant, polyiron chloride, PAC, or the like can be used.

水槽1の平面形状は円形、四角形、または多角形等に形成することができるが、この実施の形態1では円形である。この水槽1は、最上部に位置し、最も大径の直筒状の大径ストレート部1a、この大径ストレート部1aの下端から下方に向かって窄まる漏斗状のテーパ部1b、このテーパ部1bの下端から下方に延びる凹状の小径ストレート部1c、および、この小径ストレート部1cの下端から水平に延びる底壁1dから構成される。   The planar shape of the water tank 1 can be formed into a circular shape, a rectangular shape, a polygonal shape, or the like, but in the first embodiment, it is circular. This water tank 1 is located at the uppermost part, and has the largest straight cylindrical large-diameter straight portion 1a, a funnel-shaped tapered portion 1b that narrows downward from the lower end of the large-diameter straight portion 1a, and this tapered portion 1b. A concave small-diameter straight portion 1c extending downward from the lower end of the lower end, and a bottom wall 1d extending horizontally from the lower end of the small-diameter straight portion 1c.

前記大径ストレート部1aの全体とテーパ部1bの略上半分とによって反応部15が形成され、この反応部15には前記回転体3を配置してある。前記テーパ部1bの略下半分と小径ストレート部1cの全部とによって沈殿部16が形成され、沈降した汚泥を収容するようになっている。そして、小径ストレート部1cの下部に汚泥排出管4を接続し、大径ストレート部1aの上部には、流入管2を接続してある。なお、回転体3の上部補強帯3aは水面とほぼ一致させてある。
また、沈殿部16に沈降した汚泥は、自然流下方式で排出するか、又は、図示しない汚泥ポンプやスクリューポンプ等によって強制的に排出することができる。なお、テーパ部1bの傾斜角度は30〜70度程度に設定することが可能であるが、通常、60度程度とするのが好ましい。
A reaction portion 15 is formed by the entire large-diameter straight portion 1a and the substantially upper half of the taper portion 1b, and the rotating body 3 is disposed in the reaction portion 15. A precipitation portion 16 is formed by the substantially lower half of the taper portion 1b and the entire small-diameter straight portion 1c to accommodate the settled sludge. And the sludge discharge pipe 4 is connected to the lower part of the small diameter straight part 1c, and the inflow pipe 2 is connected to the upper part of the large diameter straight part 1a. The upper reinforcing band 3a of the rotator 3 is substantially coincident with the water surface.
Moreover, the sludge settled in the sedimentation part 16 can be discharged | emitted by a natural flow system, or can be forcedly discharged | emitted by the sludge pump, screw pump, etc. which are not shown in figure. Although the inclination angle of the taper portion 1b can be set to about 30 to 70 degrees, it is usually preferably about 60 degrees.

前記流入管2は、その大部分を占める本体2aと、この本体2aの端部において原水を鉛直下方に向けて流出する鉛直部2bを設けてあり、この鉛直部2bの下端を開口させてある。この開口部分は、水槽1内のいずれに位置させてもフロックを回転体3内に流入させることが可能であるが、これを回転体3の内部に位置させることが好ましい。本例では、前記流入管2の開口部を受け入れる漏斗状のフィードパイプ2cを回転体3内に設置し、原水を回転体3の中央に供給するようにしている
さらに、流入管2は、図示のように水槽1の上方から導くことができるが、水槽1の大径ストレート部1a、またはテーパ部1bを貫通させて導くこともできる。そして、流入管2の開口部分が、回転体3内で開口する場合、流入管2の開口部分と回転体3の分離羽根5との距離をL1とし、流入管2の開口部分と原水の水面との距離をL2とした場合、L1>L2に設定すれば、フロックを回転体3の内部に保持することがより容易になる。なお、原水は、間欠的または連続的に流入させることができる。
The inflow pipe 2 is provided with a main body 2a occupying most of the inflow pipe 2 and a vertical portion 2b through which raw water flows out vertically downward at the end of the main body 2a, and the lower end of the vertical portion 2b is opened. . Although this opening portion can be located anywhere in the water tank 1, it is possible to allow the floc to flow into the rotator 3, but it is preferable to locate this inside the rotator 3. In this example, a funnel-shaped feed pipe 2 c that receives the opening of the inflow pipe 2 is installed in the rotating body 3 to supply raw water to the center of the rotating body 3. In this way, the water tank 1 can be guided from above, but the large diameter straight part 1a or the taper part 1b of the water tank 1 can be guided therethrough. And when the opening part of the inflow pipe 2 opens in the rotary body 3, the distance of the opening part of the inflow pipe 2 and the separation blade 5 of the rotary body 3 is set to L1, and the opening part of the inflow pipe 2 and the water surface of raw | natural water Is set to L1> L2, it becomes easier to hold the floc inside the rotator 3. In addition, raw | natural water can be made to flow in intermittently or continuously.

(回転体)
分離羽根5を有する回転体3は、上部の駆動機(モータ)6によりゆっくりと低速で回転させられる。前記駆動機6は機械式でもよいが、原水を自然流下で回転体3内に流入させる自然流下のエネルギーで回転させてもよい。回転体3は、原則として、この回転体3の内外部の原水を回転させるが、フロックを外部に流出させないように構成され、軸線を鉛直方向に向けて回転体3の中心に設置された回転軸8と、この回転軸8に取り付けた上部補強帯3a、これらの内周縁に上端をそれぞれ支持された複数枚(例えば30枚)の分離羽根5、および、前記回転軸8を回転駆動する前記駆動機6、図示しない減速機等の駆動手段によって構成してある。
(Rotating body)
The rotating body 3 having the separation blade 5 is slowly rotated at a low speed by an upper driving machine (motor) 6. The drive unit 6 may be a mechanical type, but may be rotated by natural flow energy that flows raw water into the rotator 3 under natural flow. The rotating body 3 is configured to rotate the raw water inside and outside the rotating body 3 in principle, but is configured so as not to let the floc flow outside, and is installed at the center of the rotating body 3 with the axis line in the vertical direction. The shaft 8, the upper reinforcing band 3 a attached to the rotating shaft 8, a plurality of (for example, 30) separating blades 5 each supported at the upper edge by the inner peripheral edge thereof, and the rotating shaft 8 being driven to rotate It is comprised by drive means, such as the drive device 6 and the reducer which is not shown in figure.

図2は、回転体3内における分離羽根5の設置状態を示す図である。図示されるように、複数の分離羽根5が所定間隔をおいて同一円周上に隣接配置され、隣接する分離羽根5、5同士の間の上記隙間は鉛直方向に細長いスリット7となっている。しかし、分離羽根5やスリット7の形状は、回転体3の大きさ、材質等によりそれぞれ異なるものとしてもよい。前記回転体3の材質は特に限定されないが、前記分離羽根5は、例えば、鋼、ステンレス鋼、プラスチック、塩化ビニール等により形成することができる。   FIG. 2 is a diagram illustrating an installation state of the separation blade 5 in the rotating body 3. As shown in the drawing, a plurality of separation blades 5 are arranged adjacent to each other on the same circumference at a predetermined interval, and the gap between adjacent separation blades 5, 5 is a slit 7 that is elongated in the vertical direction. . However, the shapes of the separation blade 5 and the slit 7 may be different depending on the size, material, and the like of the rotating body 3. Although the material of the said rotary body 3 is not specifically limited, The said isolation | separation blade | wing 5 can be formed with steel, stainless steel, a plastic, a vinyl chloride etc., for example.

前記分離羽根5の各々は、図1に示すように短冊状とされ、一方、その水平断面形状は、図2に示すように「く」の字状としてある。これらの分離羽根5は、それぞれ所定幅を有する一方の第1短辺5aと他方の第2短辺5bとが屈曲部5cにおいて折曲げられ、図示例では、これらの短辺同士の交差角度は、鈍角、例えば150度(接線に対して30度)としてある。   Each of the separation blades 5 has a strip shape as shown in FIG. 1, while its horizontal cross-sectional shape is a "<" shape as shown in FIG. Each of the separation blades 5 has one first short side 5a and another second short side 5b each having a predetermined width folded at a bent portion 5c. In the illustrated example, the intersection angle between these short sides is The obtuse angle is, for example, 150 degrees (30 degrees with respect to the tangent line).

なお、第2短辺5bは、円形の回転体3内でその接線方向に沿って配置され、結果として、第1短辺5aは回転体の内部方向に向けられている。そして、互いに隣接する分離羽根5のうち、一方の分離羽根5の第1短辺5aの端部と、他方の分離羽根5の屈曲部5cとの間隔Sを同一長さにすると共に、一方の分離羽根の第1短辺5aの端部と、他方の分離羽根の第2短辺5bの端部との間隔、すなわちスリット7の幅が同じになるように配置してある。   In addition, the 2nd short side 5b is arrange | positioned along the tangent direction within the circular rotary body 3, As a result, the 1st short side 5a is orient | assigned to the internal direction of the rotary body. And among the separation blades 5 adjacent to each other, the distance S between the end portion of the first short side 5a of one separation blade 5 and the bent portion 5c of the other separation blade 5 is made the same length, The distance between the end of the first short side 5a of the separation blade and the end of the second short side 5b of the other separation blade, that is, the width of the slit 7 is arranged to be the same.

この例では、これらの間隔S、およびスリット7は、全ての分離羽根5、5同士で一致させてあるが、これらは必ずしも等間隔で設けられる必要はない。これらは、ランダムの長さの間隔S、またはスリット7であっても、また、1つ置き、2つ置きに同一の間隔または長さとなるようにしてもよい。
なお、上部補強帯3aに対する分離羽根5の連結位置を調整可能とすれば、スリット7の幅を回転体3の回転数に応じて水面の上方から調整することが可能となる。
In this example, the interval S and the slit 7 are made to coincide with each other in all the separation blades 5 and 5, but they do not necessarily have to be provided at equal intervals. These may be random length intervals S or slits 7 and may be the same interval or length every other one.
If the connection position of the separating blade 5 with respect to the upper reinforcing band 3a can be adjusted, the width of the slit 7 can be adjusted from above the water surface according to the number of rotations of the rotating body 3.

また、固液分離により得られた分離液が、分離液管17に流出する際、フロックが伴わないようにするために、回転体3の回転速度が処理水の流出速度よりも速くなるように制御し、フロックを可能な限り分離羽根5の内面に接触させて回転体3の中心部に押し戻すことが必要になる。そして、回転体3の外側における水槽1の水平断面面積、つまり水槽流出部19の面積は、回転体3の外側における処理水の上昇速度によって決定される。したがって、処理水の上昇速度V3が、処理水の分離羽根からの流出速度V2よりも小さく(V3<V2)なるように制御する必要がある。   In addition, when the separation liquid obtained by the solid-liquid separation flows out to the separation liquid pipe 17, the rotation speed of the rotating body 3 is set to be higher than the outflow speed of the treated water in order to prevent flocs from being accompanied. It is necessary to control and push the floc back to the center of the rotating body 3 as much as possible by contacting the inner surface of the separation blade 5. And the horizontal cross-sectional area of the water tank 1 in the outer side of the rotary body 3, ie, the area of the water tank outflow part 19, is determined by the rising speed of the treated water in the outer side of the rotary body 3. Therefore, it is necessary to control the rising speed V3 of the treated water to be smaller than the outflow speed V2 from the treated water separation blade (V3 <V2).

さらに、回転体3の回転数は、水槽1の直径、回転体3の直径、汚泥の粘性等の関係、これらのバランスを考慮して決定する必要があり、回転体3の周辺速度は毎分1〜10m程度とするのが好ましい。すなわち、回転体の回転数は60回転/分以下とするのが好ましく、1〜10回転/分程度の低速度とするのが好適である。
前記回転体3によれば、スリット7を介して汚泥中の分離液が流出し、フロック等の固形物は回転体3内に保持されるので、汚泥の固液分離、濃縮、沈降が効率的に行われる。
Further, the rotational speed of the rotating body 3 needs to be determined in consideration of the relationship between the diameter of the water tank 1, the diameter of the rotating body 3, the viscosity of sludge, etc., and the balance between them. It is preferably about 1 to 10 m. That is, the rotational speed of the rotating body is preferably 60 revolutions / minute or less, and is preferably a low speed of about 1 to 10 revolutions / minute.
According to the rotating body 3, the separated liquid in the sludge flows out through the slits 7, and solids such as floc are held in the rotating body 3, so that sludge solid-liquid separation, concentration, and sedimentation are efficient. To be done.

(阻流棒)
また、図1及び図2に示す装置では、2本の阻流棒10、10が、水槽1の内部に固定されたサポート18の先端において、垂直方向に向けて設置されている。すなわち、水槽1の内部に、2本の阻流棒10、10を固定した例が示されている。この例のように、阻流棒10、10を回転体3内部に停止状態で設ける場合は、回転体3の回転に伴って移動する汚泥と阻流棒10との間に速度差が生じるため、汚泥が阻流棒10に衝突し汚泥の濃縮化が進行しやすくなる。
(Barrier)
Further, in the apparatus shown in FIGS. 1 and 2, the two baffle rods 10 and 10 are installed in the vertical direction at the tip of the support 18 fixed inside the water tank 1. That is, an example in which two baffle rods 10 and 10 are fixed inside the water tank 1 is shown. When the baffle rods 10 and 10 are provided in a stopped state inside the rotating body 3 as in this example, a speed difference is generated between the sludge moving along with the rotation of the rotating body 3 and the baffle rod 10. Then, the sludge collides with the baffle rod 10 and the sludge is easily concentrated.

前記阻流棒10の作用は次のようなものである。
先ず、固形物と分離液等の液体とが混合されている原水は、ポンプ等により回転体3の中心部に設けられた流入管2に送られ、フィードパイプ2cを介して水槽1の中心部へ投入される。漏斗状のフィードパイプ2cは、原水の流速を低減し水流を安定させるために設けられる。この回転体3は、周速で1分間に1〜2mの低速で回転し、この回転体3の内部に原水が投入される。
次に、図2に示すように、固液分離装置に原水が流入し始めた初期段階では、阻流棒10を内部に設けた回転体3の内部では、汚泥が緩やかに回転し始め、徐々に周辺部に分散してゆき、汚泥が分離羽根5と接する。分離羽根5は「く」の字状に折れ曲がり、原水中の汚泥をその内部に保持しやすい形状となっている。したがって、汚泥が回転体3の内部に集まり濃縮されて、水槽1の前記沈殿部16に沈降する。
The action of the baffle 10 is as follows.
First, raw water in which a solid and a liquid such as a separation liquid are mixed is sent to an inflow pipe 2 provided in the central portion of the rotating body 3 by a pump or the like, and the central portion of the water tank 1 through a feed pipe 2c. It is thrown into. The funnel-shaped feed pipe 2c is provided to reduce the flow rate of the raw water and stabilize the water flow. The rotating body 3 rotates at a peripheral speed at a low speed of 1 to 2 m per minute, and raw water is poured into the rotating body 3.
Next, as shown in FIG. 2, in the initial stage when raw water begins to flow into the solid-liquid separator, the sludge begins to rotate slowly inside the rotating body 3 provided with the baffle 10 inside, and gradually. The sludge is dispersed in the periphery and the sludge comes into contact with the separation blade 5. The separation blade 5 is bent in a “<” shape and has a shape that can easily hold sludge in the raw water. Therefore, sludge is collected inside the rotating body 3 and concentrated, and settles in the settling portion 16 of the water tank 1.

図3は、原水の流入が進み、回転体の分離羽根5内部に汚泥Xが保持された状態を示す。この汚泥の回転と分散、分離羽根5の形状により、汚泥Xは回転体3内部で濃縮されてゆく。原水中の汚泥Xは、分離羽根5と同方向に緩やかに回転するが、阻流棒10は、移動せず固定されているため、図4に示すように、移動する汚泥Xの層と接触する。その結果、阻流棒10は、汚泥粒子の凝集作用を促進し、汚泥フロックを大きくすることで沈降性を良好にする。   FIG. 3 shows a state where the inflow of raw water has progressed and the sludge X is held inside the separating blade 5 of the rotating body. Due to the rotation and dispersion of the sludge and the shape of the separation blade 5, the sludge X is concentrated inside the rotating body 3. The sludge X in the raw water rotates gently in the same direction as the separation blade 5, but the baffle 10 is fixed without moving, so that it contacts the moving sludge X layer as shown in FIG. 4. To do. As a result, the baffle rod 10 promotes the aggregating action of sludge particles and makes the sludge flocs larger to improve the sedimentation property.

また、図5に示すように、物理的に汚泥層をかき分けて、水みちYをつくることにより、この水みちYに周囲の汚泥中の水が集まり固液分離が促進し、かつ、汚泥の圧密工程への移行を早めることで、濃縮汚泥の高濃度化を可能にする。濃縮汚泥は水槽1の下部に沈降し、圧密されて更に濃縮される。分離液は分離羽根5の間(スリット7)を通過して、オーバーフローにより処理水管17から系外へ排出される。
前記阻流棒10は単純な構造であるが、以上のような作用に基づいて、固液分離において大きな効果を奏するものである。
In addition, as shown in FIG. 5, by physically dividing the sludge layer and creating a water channel Y, the water in the surrounding sludge gathers in the water channel Y, and solid-liquid separation is promoted. By accelerating the transition to the consolidation process, it is possible to increase the concentration of concentrated sludge. The concentrated sludge settles in the lower part of the water tank 1, is consolidated and further concentrated. The separation liquid passes between the separation blades 5 (slit 7) and is discharged out of the system from the treated water pipe 17 due to overflow.
Although the baffle rod 10 has a simple structure, it has a great effect in solid-liquid separation based on the above-described action.

以下、阻流棒についてさらに詳しく説明する。
通常、阻流棒は、固液分離装置内に複数設置することが望ましい。その効果的な設置数は、装置規模によって異なるが、一般に阻流棒の設置間隔は100〜400mm程度が適切であるので、これに基づいて設置数を決定することができる。例えば、図6に示すように、分離羽根5の内側で、その回転軸8の周囲に設置することができる。図6(a)では、回転軸8を中心に、阻流棒10が点対称に2本設けられている。図6(b)では、阻流棒10が、回転軸8の周囲に3本が設けられ、図6(c)では、4本が設けられている。図6(d)では、4本が回転軸8を中心に、左右非対称に偏って設けられている。
Hereinafter, the blocking rod will be described in more detail.
Usually, it is desirable to install a plurality of baffle rods in the solid-liquid separator. The effective number of installations varies depending on the scale of the apparatus, but generally, the installation interval of the baffle rods is appropriately about 100 to 400 mm, and the number of installations can be determined based on this. For example, as shown in FIG. 6, it can be installed around the rotary shaft 8 inside the separation blade 5. In FIG. 6A, two baffle rods 10 are provided point-symmetrically around the rotation shaft 8. In FIG. 6B, three baffle rods 10 are provided around the rotation shaft 8, and in FIG. 6C, four baffle rods are provided. In FIG. 6 (d), four are provided in a bilaterally asymmetric manner around the rotation shaft 8.

また、図7(a)に示すように、阻流棒10は、分離羽根5の回転軸8を中心として、同心円上に設けるか、または異なる半径位置に設けることができる。
さらに、図7(b)に示すように、分離羽根5の外側のみに設けるか、あるいは、図7(c)に示すように、分離羽根5の内側及び外側の両方に設けることが可能である。
上記のように、阻流棒10は、回転体3の内部で、同心円上に設けても、または同心円上ではない位置に設けてもよい。また、これらの阻流棒10は、回転体3内に設置するのが好適であるが、回転体3の外に設置することも可能であり、さらに回転体3の内部と外部の両方に設置してもよい。上記のように、阻流棒10の設置位置は、水槽内において特に限定されるものではない。
Further, as shown in FIG. 7A, the baffle rod 10 can be provided on a concentric circle around the rotation shaft 8 of the separation blade 5 or at a different radial position.
Furthermore, as shown in FIG. 7 (b), it can be provided only on the outside of the separation blade 5, or as shown in FIG. 7 (c), it can be provided both on the inside and outside of the separation blade 5. .
As described above, the baffle rod 10 may be provided on the concentric circle inside the rotating body 3 or may be provided at a position not on the concentric circle. These baffles 10 are preferably installed in the rotating body 3, but can also be installed outside the rotating body 3, and further installed both inside and outside the rotating body 3. May be. As described above, the installation position of the baffle 10 is not particularly limited in the water tank.

阻流棒10の形状は、通常、棒状で断面形状が円であり、直径が50〜100mm程度ものが好適である。しかし、それは楕円棒、四角棒、三角棒、菱形棒、穴の空いた丸棒等でもよく、上述した汚泥の水みちYを形成できれば何れの形状でもよい。阻流棒10の径は、全体が均一でも異なってもよく、また、断面形状は、一部で異なっていてもよい。さらに、断面形状は、角形状、またはパイプ状であってもよい。全体形状は棒状でなくてもよく、ワイヤーやチェーン状、曲線部を有する形状、傾斜部を有する形状であってもよい。なお、前記直径は、水槽や回転体の大きさや形状、数によって上記の範囲外であってもよい。すなわち、全体として長尺状であれば所期の効果が期待できる。
なお、前記阻流棒10は、上記のような停止状態で設置される場合に限られず、可動状態としてもよい。
The shape of the baffle rod 10 is preferably a rod shape with a circular cross-sectional shape and a diameter of about 50 to 100 mm. However, it may be an elliptical bar, a square bar, a triangular bar, a rhombus bar, a round bar with holes, or the like, and may have any shape as long as the sludge water channel Y can be formed. The diameter of the baffle 10 may be uniform or different as a whole, and the cross-sectional shape may be partially different. Further, the cross-sectional shape may be a square shape or a pipe shape. The overall shape may not be a rod shape, but may be a wire or chain shape, a shape having a curved portion, or a shape having an inclined portion. The diameter may be outside the above range depending on the size, shape, and number of water tanks and rotating bodies. That is, the desired effect can be expected if it is long as a whole.
The baffle rod 10 is not limited to being installed in the stopped state as described above, and may be in a movable state.

次に、回転体3に対する阻流棒10の設置について、変形態様を図8に示す。
図8(a)(b)は、阻流棒10の下端を水槽1の底部に固定したものが示されている。また、図8(c)(d)は、阻流棒10の上端を、水槽1の上部に設けた支持体52に固定し、回転体3内に吊下げた状態としたものを示す。上記した図8(a)(b)(c)及び(d)に示す装置では、阻流棒10が回転体3の内部で固定され、設置される。また、阻流棒10の固定位置は、回転体3の側面、底部等であってもよいが、図8(c)(d)のように、阻流棒10を吊り下げた構造では、阻流棒10の取り外しや設置位置の変更が容易で、汚泥の状態に合った適切な設置が可能となる。
Next, a modification aspect is shown in FIG. 8 about installation of the baffle 10 with respect to the rotary body 3. FIG.
8A and 8B show the baffle rod 10 fixed to the bottom of the water tank 1 at the lower end. 8C and 8D show a state in which the upper end of the baffle rod 10 is fixed to a support body 52 provided on the upper part of the water tank 1 and is suspended in the rotating body 3. In the apparatus shown in FIGS. 8A, 8B, 8C, and 8D, the baffle rod 10 is fixed and installed inside the rotating body 3. FIG. In addition, the fixing position of the baffle rod 10 may be the side surface, the bottom portion or the like of the rotator 3. However, in the structure in which the baffle rod 10 is suspended as shown in FIGS. The removal of the flow stick 10 and the change of the installation position are easy, and appropriate installation suitable for the state of sludge becomes possible.

(その他の実施態様)
以下、阻流棒を備えた固液分離装置のその他の実施態様を説明する。なお、上述した固液分離装置と同一の符号を付した部分は、同一の部材を示すので説明を省略する。
図9には、重力濃縮槽50において、左右3本ずつの阻流棒10が、左右内側に固定されたサポート18の先端に、垂直方向に沿って設置された例を示す。これは阻流棒10を固定設置した例である。水槽1の底部には、回転可能な汚泥かき寄せ機51が設けられている。
阻流棒10を備えた上記のような装置は、無薬注での濃縮以外に、凝集剤を使用した凝集濃縮や通常の沈澱池等、あらゆる固液分離に使用することが可能である。
(Other embodiments)
Hereinafter, other embodiments of the solid-liquid separator provided with the baffle will be described. In addition, since the part which attached | subjected the code | symbol same as the solid-liquid separator mentioned above shows the same member, description is abbreviate | omitted.
FIG. 9 shows an example in which three left and right baffle bars 10 are installed along the vertical direction at the tip of a support 18 fixed to the left and right inner sides in the gravity concentration tank 50. This is an example in which the baffle 10 is fixedly installed. A rotatable sludge scraper 51 is provided at the bottom of the water tank 1.
The above-described apparatus provided with the baffle 10 can be used for any solid-liquid separation, such as agglomeration concentration using a flocculant or a normal sedimentation basin, in addition to concentration without chemical injection.

図10には、阻流棒10を、水槽1の上部に設けた支持体52に固定し、回転体3内に吊下げた状態とした例の詳細が示されている。ここでは、モータである駆動機6を上面に設けた支持体52の底部に、左右2本ずつの阻流棒10が、垂直に吊下げ状態に保持されている。また、水槽1の底部に回転可能に設けたかき寄せ機51には、垂直に上方に起立した状態の複数のピケットフェンス53が取り付けられている。ピケットフェンス53は、主に沈殿池や重力濃縮槽で使用されるものであり、かき寄せ機51、分離羽根5と共に回転する。   FIG. 10 shows details of an example in which the baffle rod 10 is fixed to a support body 52 provided at the upper part of the water tank 1 and is suspended in the rotating body 3. Here, two left and right baffle rods 10 are held vertically suspended at the bottom of a support 52 provided with a driving device 6 as a motor on the upper surface. In addition, a plurality of picket fences 53 that are erected vertically upward are attached to a raking machine 51 that is rotatably provided at the bottom of the water tank 1. The picket fence 53 is mainly used in a sedimentation basin or a gravity concentration tank, and rotates together with the scraper 51 and the separation blade 5.

一方、前記阻流棒10は、上記のようなピケットフェンス53と形状が類似している。しかし、両者間の大きな違いは、阻流棒10が水槽50内で停止し、回転体3と共に回転している汚泥との間に水みちYを形成するのに対し、ピケットフェンス53は汚泥かき寄せ機51、分離羽根5と共に回転し、ほぼ静置している汚泥との間で水みちを形成する点である。   On the other hand, the baffle 10 is similar in shape to the picket fence 53 as described above. However, the major difference between the two is that the baffle 10 stops in the water tank 50 and forms a water channel Y with the sludge rotating together with the rotating body 3, whereas the picket fence 53 scrapes the sludge. It is a point which rotates with the machine 51 and the separation blade 5 and forms a water channel with the sludge which is almost stationary.

次に、図10に示すような、複数の短冊状の分離羽根が所定間隔をもって配設されて成る回転体3と、この回転体3を低速で回転させる駆動機6とを備えた水槽50において、ピケットフェンス53を設置した装置における阻流棒の作用効果を説明する。
回転体3の分離羽根は、前述したように汚泥を内部に保持しやすい形状となっている。この回転体3が緩やかに回転すると、その内部の汚泥や水も分離羽根5(図2、図3)よりもやや遅い速度で均一に回転する。ピケットフェンス53は汚泥かき寄せ機51に設置されているが、駆動機6が一台なので、回転体3はかき寄せ機51と一体であり、回転体3とピケットフェンス53は同速で回転することになる。
Next, in a water tank 50 including a rotating body 3 in which a plurality of strip-shaped separation blades are arranged at a predetermined interval as shown in FIG. 10 and a drive unit 6 that rotates the rotating body 3 at a low speed. The function and effect of the baffle rod in the apparatus provided with the picket fence 53 will be described.
As described above, the separation blades of the rotating body 3 have a shape that can easily hold sludge inside. When the rotator 3 rotates gently, sludge and water inside the rotator 3 rotate uniformly at a slightly lower speed than the separating blade 5 (FIGS. 2 and 3). Although the picket fence 53 is installed in the sludge scraper 51, since the drive unit 6 is one, the rotating body 3 is integrated with the scraper 51, and the rotating body 3 and the picket fence 53 rotate at the same speed. Become.

回転体3内にピケットフェンス53を設置すると、汚泥や水も回転するため、これらとピケットフェンス53との速度差が少なくなり、内部で供回りする現象が見られる。この現象は、濃度が高い場合や分離羽根直径が小さい場合に顕著である。ピケットフェンス53は、本来、汚泥の中に水みちを作り、汚泥中からの水抜けを促進し濃縮濃度を増加させるものであるが、この装置では、ピケットフェンス本来の効果が生じにくい。
このような場合、阻流棒10を設置すれば、汚泥中に水みちが形成されやすくなり、汚泥の濃縮が促進され、効率的な固液分離が実施できる。
When the picket fence 53 is installed in the rotating body 3, sludge and water also rotate, so that the speed difference between them and the picket fence 53 is reduced, and a phenomenon in which the picket fence 53 is circulated inside is observed. This phenomenon is remarkable when the concentration is high or the separation blade diameter is small. The picket fence 53 originally creates a water channel in the sludge and promotes water drainage from the sludge to increase the concentration concentration. However, with this apparatus, the original effect of the picket fence is unlikely to occur.
In such a case, if the baffle 10 is installed, a water channel is easily formed in the sludge, the concentration of the sludge is promoted, and efficient solid-liquid separation can be performed.

図11は、阻流棒10の上端を、水槽50の上部に設けた支持体52に固定し、回転体3内に吊下げた状態とした装置が示されているが、ここではピケットフェンスは設けられていない。
なお、図10及び図11に示す装置では、阻流棒10は、固定されて移動しないものであるが、これらを回転体3と異なる速度で回転させるように設置してもよい。
図12には、阻流棒10を、かき寄せ機51を回転駆動する駆動機6とは別の駆動モータ9を用い、回転可能とした装置が示されている。この装置では、回転体3とかき寄せ機51、及び阻流棒10がそれぞれ独立して回転し、水槽50内に原水を供給する流入管2も、水槽1を貫通するように底部側に設けられ、水槽1内で原水を上方に向けて噴出させるものとなっている。
FIG. 11 shows a device in which the upper end of the baffle rod 10 is fixed to a support body 52 provided at the upper part of the water tank 50 and is suspended in the rotating body 3. Not provided.
10 and 11, the baffle rod 10 is fixed and does not move. However, the baffle rod 10 may be installed so as to rotate at a speed different from that of the rotating body 3.
FIG. 12 shows a device in which the baffle rod 10 can be rotated by using a drive motor 9 different from the drive machine 6 that rotationally drives the scraper 51. In this apparatus, the rotating body 3, the scraper 51, and the baffle rod 10 rotate independently, and the inflow pipe 2 that supplies raw water into the water tank 50 is also provided on the bottom side so as to penetrate the water tank 1. The raw water is jetted upward in the water tank 1.

次に、図13及び図14は、阻流棒を矩形の比較的大型の沈殿池において固定するように設置した固液分離装置の側面図である。図13に示す装置では、矩形沈殿池55の前段に設けた回転体3の内部に、沈殿池スラブ57から吊下げるようにして阻流棒10を固定している。駆動機6を上面に支持する支持体52の底部に、左右2本ずつの阻流棒10が、垂直に吊下げ状態で回転体3の内部まで達するように保持されている。
一方、図14に示す装置では、矩形沈殿池の前段に設けた回転体3の内部まで、沈殿池の側面に設けた支持部18に固定した阻流棒が挿入されるように設置している。
Next, FIG.13 and FIG.14 is a side view of the solid-liquid separation apparatus installed so that a baffle rod may be fixed in a rectangular comparatively large sedimentation basin. In the apparatus shown in FIG. 13, the baffle rod 10 is fixed inside the rotating body 3 provided in the front stage of the rectangular sedimentation basin 55 so as to be suspended from the sedimentation basin slab 57. On the bottom of the support body 52 that supports the drive unit 6 on the upper surface, two left and right baffle bars 10 are held so as to reach the inside of the rotating body 3 while being suspended vertically.
On the other hand, in the apparatus shown in FIG. 14, it installs so that the baffle rod fixed to the support part 18 provided in the side surface of a sedimentation basin may be inserted to the inside of the rotary body 3 provided in the front | former stage of the rectangular sedimentation basin. .

上記の図13、図14に示す装置では、共に、沈殿池の後段に、公知のリンクベルト式汚泥かき寄せ機54が設置されている。このような四角形、台形をなす大規模な水槽においても、前記阻流棒10の設置は有効である。
図15及び図16は、矩形沈殿池55に三台の回転体3を配置した構造の装置を示すものであり、図15はその平面図、図16はその側面図、図17は断面図である。このような構造の装置では、各々の回転体3の内部に阻流棒10が到達するようにこれを設置するため、沈殿池の側面における、各々の回転体3の位置に対応する三カ所に支持部56を設け、それぞれに阻流棒10を取り付けている。その結果、阻流棒10が下方から垂直に伸びて、各々の回転体3内に到達した状態となっている。しかし、阻流棒の設置方法はこれに限られず、底面等に固定してもよい。図17には、矩形沈殿池に複数の回転体を設け、矩形の水槽55の側面に支持部18を設け、この支持部18に阻流棒10を取付けて、阻流棒が回転体3へ挿入されるように設置した装置が示されている。この水槽55の底部には、かき寄せ機51が設置されている。この装置では、水槽55の設置面に載置された保持部59により、回転体3を吊下げ状態で保持している。
In the apparatus shown in FIG. 13 and FIG. 14, a known link belt type sludge squeezer 54 is installed downstream of the settling basin. The installation of the baffle rod 10 is also effective in a large-scale water tank having such a quadrilateral and trapezoidal shape.
15 and 16 show an apparatus having a structure in which three rotary bodies 3 are arranged in a rectangular sedimentation basin 55. FIG. 15 is a plan view thereof, FIG. 16 is a side view thereof, and FIG. is there. In the apparatus having such a structure, since the baffle rod 10 is installed so as to reach the inside of each rotating body 3, three sides corresponding to the position of each rotating body 3 on the side surface of the settling basin are provided. Support portions 56 are provided, and the baffle rod 10 is attached to each. As a result, the baffle rod 10 extends vertically from below and reaches each rotary body 3. However, the installation method of the baffle rod is not limited to this, and may be fixed to the bottom surface or the like. In FIG. 17, a plurality of rotating bodies are provided in a rectangular sedimentation basin, a support portion 18 is provided on a side surface of the rectangular water tank 55, and the baffle rod 10 is attached to the support portion 18. The device installed to be inserted is shown. At the bottom of the water tank 55, a scraper 51 is installed. In this apparatus, the rotating body 3 is held in a suspended state by the holding portion 59 placed on the installation surface of the water tank 55.

流入管2から供給される原水は、前記流入管2から分岐した分岐管58を介して、各々の回転体3内に流入する。
また、この装置では、矩形沈殿池55の後段(斜面部分)に汚泥かき寄せ機51が設置される。なお、複数の回転体3が設けられ、前記後段にも回転体3が存在する関係上、これらの下方に収納できるタイプのものとして、往復動式の汚泥かき寄せ機51が設置されている。しかし、複数の前記回転体3の下方に設置できるものであれば、かき寄せ機の形式、構造は問わない。例えば、フライトによる汚泥かき寄せ機構と往復動機構を組み合わせたカスケード式の汚泥かき寄せ機であってもよい。
上記のような大規模な水槽においても、前記阻流棒10の設置は有効である。
さらに別の例として、分離羽根5と異なる速度で回転駆動されるかき寄せ機やスカムスキマが設けられる場合、これらに阻流棒を取り付けるようにしてもよい。
The raw water supplied from the inflow pipe 2 flows into the respective rotators 3 via the branch pipes 58 branched from the inflow pipe 2.
Moreover, in this apparatus, the sludge scraper 51 is installed in the back | latter stage (slope part) of the rectangular sedimentation basin 55. FIG. In addition, the reciprocating-type sludge scraper 51 is installed as a thing of the type which can be accommodated in the downward direction on the relationship that the some rotary body 3 is provided and the rotary body 3 exists also in the said back | latter stage. However, the type and structure of the raking machine are not limited as long as they can be installed below the plurality of rotating bodies 3. For example, a cascade-type sludge squeezer combining a sludge squeezing mechanism and a reciprocating mechanism by flight may be used.
Even in a large-scale water tank as described above, the installation of the baffle rod 10 is effective.
As another example, when a scraper or a scum clearance that is rotationally driven at a speed different from that of the separation blade 5 is provided, a baffle may be attached to these.

上記の実施の形態において説明した固液分離装置は、次のような利点がある。
回転体3による汚泥の濃縮作用について、阻流棒10による濃縮促進作用が相乗的に加えられ、効率のよい汚泥濃縮が実現される。
分離羽根5の内部にフロックを多量に保持でき、従来の凝集濃縮槽と比べ設置面積や容積が減少して、全体がコンパクト化するので設備費が削減できる。また、構造が簡素であるので交換部品が少なく、維持管理が容易になる。処理対象なる汚泥は、例えば、下水、産業排水等から発生する余剰汚泥等であり、濃縮濃度として1.5%〜4.0%が得られ、SS(浮遊物質:suspended solidsの略)回収率も95%以上であり良好である。
また、回転体3の回転数を60回転/分以下とすることで、エネルギーの消費量が低減し、かつ、騒音や振動の対策が不要となる。また、汚泥濃縮効率が向上するので、水槽の負荷も向上する。
The solid-liquid separator described in the above embodiment has the following advantages.
About the concentration action of the sludge by the rotary body 3, the concentration promotion action by the baffle rod 10 is added synergistically, and efficient sludge concentration is implement | achieved.
A large amount of floc can be held inside the separation blade 5, and the installation area and volume are reduced as compared with the conventional coagulation concentration tank, and the whole is made compact, so that the equipment cost can be reduced. Further, since the structure is simple, there are few replacement parts, and maintenance management becomes easy. The sludge to be treated is, for example, surplus sludge generated from sewage, industrial wastewater, etc., and a concentrated concentration of 1.5% to 4.0% is obtained, and SS (suspended solids) recovery rate Is 95% or more.
Further, by setting the rotational speed of the rotating body 3 to 60 revolutions / minute or less, energy consumption is reduced, and measures for noise and vibration are not required. Moreover, since the sludge concentration efficiency is improved, the load on the water tank is also improved.

従来の機械式の常圧浮上濃縮法と比べると、薬注率を低下させても同等のSS回収率(98%以上)が得られる。濃縮性能例としては、原水のSS濃度が0.6%である場合に、排出汚泥のSS濃度は2%以上となる。回転体3を低速で回転させることで、糸状性細菌を絡める効果がある。
装置が機械式と比較して簡単であるため、装置トラブルが起きにくく、常に安定した分離液と汚泥の濃縮が行える。
無薬注で高濃度の濃縮液が得られるため、薬品添加に伴う添加設備や維持管理費が不要となり、汚泥発生量の増加や薬品添加の悪影響にさらされることがない。
Compared with the conventional mechanical atmospheric pressure flotation concentration method, the same SS recovery rate (98% or more) can be obtained even if the drug injection rate is lowered. As an example of the concentration performance, when the SS concentration of the raw water is 0.6%, the SS concentration of the discharged sludge is 2% or more. By rotating the rotating body 3 at a low speed, there is an effect of entanglement of filamentous bacteria.
Since the device is simpler than the mechanical type, troubles in the device are unlikely to occur, and stable separation liquid and sludge can always be concentrated.
Since a concentrated solution with a high concentration can be obtained without chemicals, no additional equipment and maintenance costs associated with the addition of chemicals are required, and there is no increase in sludge generation or adverse effects of chemical additions.

前記阻流棒10を設置した効果は以下の通りである。
糸状性バルキングを起こし沈降性が悪くなった汚泥等に対して、阻流棒を設置すれば、回転体3のみの場合と比較し、さらに沈降性が改善されることが判明した。
水槽1にピケットフェンスを設けた汚泥かき寄せ機を設置しても、回転体3内の汚泥が供回りをするため、水みちを形成することができないが、阻流棒10を設置した場合は、回転体3と阻流棒10の間で回転速度差が生じるので、濃縮された汚泥のさらなる濃縮が可能となる。
阻流棒10は、ピケットフェンスよりも少ない設置本数であっても汚泥濃縮効果が高いことが判明した。また、ピケットフェンスは汚泥界面が維持できる水槽1の下部に設置されるが、阻流棒10は、水槽上部に設置が可能であるため、分離羽根により汚泥界面を高く維持できることから、水槽1内の全体に濃縮効果を及ぼすことができ、長時間濃縮することが可能となる。
The effect of installing the baffle 10 is as follows.
It has been found that if a baffle rod is installed against sludge or the like that has deteriorated in sedimentation due to filamentous bulking, the sedimentation is further improved as compared with the case of the rotating body 3 alone.
Even if a sludge scraper equipped with a picket fence is installed in the aquarium 1, the sludge in the rotating body 3 is circulating, so a water channel cannot be formed, but when a baffle 10 is installed, Since a rotational speed difference is generated between the rotating body 3 and the baffle rod 10, the concentrated sludge can be further concentrated.
It has been found that the baffle rod 10 has a high sludge concentration effect even if the number of the baffle rods 10 is smaller than that of the picket fence. In addition, the picket fence is installed in the lower part of the water tank 1 where the sludge interface can be maintained. However, since the baffle rod 10 can be installed in the upper part of the water tank, the sludge interface can be maintained high by the separating blade. It is possible to exert a concentration effect on the whole, and it is possible to concentrate for a long time.

以下、汚泥濃縮について阻流棒を適用した実施例について説明する。
農業集落排水処理施設の余剰汚泥を対象に、回転体直径1000mm、水槽直径1200mm、水槽容積1.8m3の装置を使用して処理量0.3m3/h、回転体回転数0.5/min.の条件で性能を調査した。
流入汚泥濃度はTS 0.6%程度、VTS 80%程度である。
調査は、直径10mmのステンレス製丸棒を阻流棒として、以下の条件で装置内部に設置し性能を比較した。「阻流棒無し」を基準に、回転体と同速度で回転する「吊り下げタイプ」と槽内に固定する「側面固定タイプ」について実施し、これらを比較した。
Hereinafter, the Example which applied the baffle for sludge concentration is described.
For surplus sludge from agricultural settlement wastewater treatment facilities, using a device with a rotating body diameter of 1000 mm, a water tank diameter of 1200 mm, and a water tank volume of 1.8 m 3 , a treatment volume of 0.3 m 3 / h and a rotating body rotation speed of 0.5 / min. The performance was investigated.
The inflow sludge concentration is about 0.6% TS and about 80% VTS.
In the investigation, a stainless steel round bar with a diameter of 10 mm was used as a baffle bar, and the performance was compared by installing it inside the device under the following conditions. Based on "no baffle", the "suspended type" rotating at the same speed as the rotating body and the "side fixed type" fixed in the tank were compared and compared.

Figure 2011005375
濃縮性能は、阻流棒の設置により、若干SS回収率が悪くなるが、濃縮濃度は高濃度となり、性能が向上する。阻流棒の設置方法は、回転体と速度差がある方が高濃度となる傾向を示す。
このことから、回転体内部に阻流棒を設置することで濃縮性能が向上し、特に、回転体との回転速度差が大きい場合に効果が大きくなることが認められる。
Figure 2011005375
As for the concentration performance, the SS recovery rate is slightly deteriorated by the installation of the baffle rod, but the concentration concentration becomes high and the performance is improved. As for the installation method of the baffle rod, there is a tendency that the concentration is higher when there is a speed difference from the rotating body.
From this fact, it is recognized that the concentration performance is improved by installing the baffle rod inside the rotating body, and the effect is enhanced particularly when the rotational speed difference from the rotating body is large.

本発明に係る固液分離装置の基本的な構造を示す概略図である。It is the schematic which shows the basic structure of the solid-liquid separator which concerns on this invention. 回転体内における分離羽根の構造を示す図である。It is a figure which shows the structure of the separation blade in a rotary body. 回転体の分離羽根の内部に汚泥が保持された状態を示す図である。It is a figure which shows the state by which the sludge was hold | maintained inside the separation blade of a rotary body. 阻流棒が移動する汚泥の層と接触し、汚泥に速度差を生じさせる状態を示す図である。It is a figure which shows the state which a baffle stick contacts with the layer of the sludge which moves, and produces a speed difference in sludge. 阻流棒によって汚泥に水みちが形成される状態を示す図である。It is a figure which shows the state in which a water path is formed in sludge by a baffle stick. 阻流棒の設置数の例を示す図である。(a)は、回転軸を中心に阻流棒を2本設けた状態を示し、(b)は、回転軸の周囲に3本を設けた状態を示す。(c)は、回転軸の周囲に4本を設けた状態を示し、(d)では、回転軸を中心に、4本を左右非対称に偏って設けた状態を示す。It is a figure which shows the example of the number of installation of a baffle rod. (A) shows a state where two baffle bars are provided around the rotation axis, and (b) shows a state where three baffle bars are provided around the rotation axis. (C) shows a state in which four are provided around the rotating shaft, and (d) shows a state in which four are provided in a bilaterally asymmetric manner around the rotating shaft. 阻流棒の設置位置の例を示す図である。(a)は、阻流棒を、回転軸を中心として設けた状態を示し、(b)は、分離羽根の外側に設けた状態を示し、また、(c)は、分離羽根の内側及び外側の両方に設けた状態を示す。It is a figure which shows the example of the installation position of a baffle. (A) shows the state which provided the baffle rod centering on the rotating shaft, (b) shows the state provided in the outer side of the separation blade, and (c) shows the inner side and the outer side of the separation blade. The state provided in both is shown. 回転体に対する阻流棒の設置の変形態様を示す図であり、(a)は、阻琉棒を回転体の底部に設置した装置の概略を示す底面図、(b)は、その側面図である。(c)は、阻流棒を回転体の上部に別途に設けた支持体から吊下げて設置した装置の概略を示す底面図、(d)は、その側面図である。It is a figure which shows the deformation | transformation aspect of installation of the blocking bar with respect to a rotary body, (a) is a bottom view which shows the outline of the apparatus which installed the blocking bar in the bottom part of a rotary body, (b) is the side view. is there. (C) is the bottom view which shows the outline of the apparatus which suspended and installed the baffle from the support body separately provided in the upper part of the rotary body, (d) is the side view. 阻流棒の下端を、水槽の側面に設けた支持体に固定した装置を示す図である。It is a figure which shows the apparatus which fixed the lower end of the baffle rod to the support body provided in the side surface of the water tank. 阻流棒の上端を、水槽の上部に設けた支持体に固定し、回転体内に吊下げるとともに、ピケットフェンスを設けた装置を示す図である。It is a figure which shows the apparatus which fixed the upper end of the baffle rod to the support body provided in the upper part of the water tank, suspended in the rotary body, and provided the picket fence. 阻流棒の上端を、水槽の上部に設けた支持体に固定し、回転体内に吊下げた装置を示す図である。It is a figure which shows the apparatus which fixed the upper end of the baffle rod to the support body provided in the upper part of the water tank, and was suspended in the rotary body. 阻流棒を、回転体を回転駆動する駆動機とは別の駆動体で回転可能とした装置を示す図である。It is a figure which shows the apparatus which enabled the baffle rod to rotate with the drive body different from the drive machine which rotationally drives a rotary body. 阻流棒を矩形の沈殿池において設置した固液分離装置を示す側面図である。It is a side view which shows the solid-liquid separator which installed the baffle rod in the rectangular sedimentation basin. 阻流棒を矩形の沈殿池において設置した固液分離装置の別の例を示す側面図である。It is a side view which shows another example of the solid-liquid separator which installed the baffle rod in the rectangular sedimentation basin. 矩形沈殿池に三台の回転体を配置した構造の装置の平面図であるIt is a top view of the apparatus of the structure which has arrange | positioned the three rotary bodies to the rectangular sedimentation basin. 図15に示す装置の側面図である。It is a side view of the apparatus shown in FIG. 図15に示す装置の断面図である。It is sectional drawing of the apparatus shown in FIG. 従来の固液分離装置の例を示す図である。It is a figure which shows the example of the conventional solid-liquid separator.

1、50、55 水槽
1a大径ストレート部
1b テーパ部1b
1c 小径ストレート部
1d 底壁
2 流入管
2a 本体
2b 鉛直部
3 回転体
3a 上部補強帯
3b 下部補強帯
4 汚泥排出管
5 分離羽根
5a 第1短辺
5b 第2短辺
5c 屈曲部
6 駆動機(モータ)
7 スリット
8 回転軸
9 駆動モータ
10 阻流棒
15 反応部
16 沈殿部
17 分離液管
18 サポート
19 水槽流出部
51 かき寄せ機
52 支持体
53 ピケットフェンス
56 支持部
57 沈殿池スラブ
58 分岐管
59 保持部
1, 50, 55 Water tank 1a Large diameter straight portion 1b Tapered portion 1b
1c Small-diameter straight part 1d Bottom wall 2 Inflow pipe 2a Main body 2b Vertical part 3 Rotating body 3a Upper reinforcement band 3b Lower reinforcement band 4 Sludge discharge pipe 5 Separation blade 5a First short side 5b Second short side 5c Bending part 6 Driving machine ( motor)
7 Slit 8 Rotating shaft 9 Drive motor 10 Baffle 15 Reaction section 16 Sedimentation section 17 Separation liquid pipe 18 Support 19 Water tank outflow section 51 Scraper 52 Support 53 Picket fence 56 Support section 57 Sedimentation basin slab 58 Branch pipe 59 Holding section

Claims (2)

水槽と、
該水槽内に配設され、
複数枚の分離羽根が間隔をもって設けられた回転体と、
該回転体を回転させる駆動機と、
前記水槽内に配設された阻流棒と
からなることを特徴とする固液分離装置。
A tank,
Disposed in the aquarium,
A rotating body having a plurality of separation blades provided at intervals;
A drive for rotating the rotating body;
A solid-liquid separator comprising a baffle disposed in the water tank.
前記阻流棒は、一つまたは二つ以上設けられていることを特徴とする請求項1に記載の固液分離装置。 The solid-liquid separator according to claim 1, wherein one or two or more baffle rods are provided.
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