JP2005111424A - Method and apparatus for removing substance to be removed from fluid and sludge separation and recovery apparatus - Google Patents

Method and apparatus for removing substance to be removed from fluid and sludge separation and recovery apparatus Download PDF

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JP2005111424A
JP2005111424A JP2003351476A JP2003351476A JP2005111424A JP 2005111424 A JP2005111424 A JP 2005111424A JP 2003351476 A JP2003351476 A JP 2003351476A JP 2003351476 A JP2003351476 A JP 2003351476A JP 2005111424 A JP2005111424 A JP 2005111424A
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flocculant
substance
magnetic
fluid
tank
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Susumu Harada
進 原田
Seiji Nomura
聖次 野村
Hisashi Isokami
尚志 磯上
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Hitachi Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method and an apparatus for removing substances to be removed from fluid and a sludge separation and recovery device which can recover recyclable materials from sludge and reduce the operation costs of the apparatus. <P>SOLUTION: A magnetic material and a coagulant are continuously supplied to raw water 1 to be stirred, thereby generating magnetic flocs 10. The magnetic flocs 10 are collected in a sludge recovery tank 11 by a magnetic separation and purification device having a mesh 6' having an aperture through which the magnetic flocs 10 cannot pass, a magnetic field generation means 8 for magnetically attracting the magnetic flocs 10, and a scraper 9 for recovering the flocs. In a sludge decomposition tank 12, hydrochloric acid 13 is added to the magnetic flocs 10 to be stirred, thereby decomposing the magnetic flocs. The treated liquid containing the decomposed magnetic flocs is subjected to gravity separation in a sedimentation tank 14, and the treated liquid containing magnetic powder and the coagulant is recycled. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は汚泥の分解を行い水質浄化を行う流体内からの被除去物除去処理方法及び装置と汚泥分離回収装置に関するものである。   The present invention relates to a method and apparatus for removing an object to be removed from a fluid that decomposes sludge and purifies water, and a sludge separation and recovery apparatus.

水質浄化を目的として、細めの金網や高分子繊維で編んだ網を分離膜として使用し、汚濁粒子を有する原水に凝集剤と磁性粉を添加して磁性フロックを生成し、磁性フロックを膜で分離し、膜で捕集した磁性フロックを磁場発生手段で磁気分離,除去して高濃度汚泥を回収する磁気分離浄化装置がある。このような分離浄化装置はステンレス鋼の細線やポリエステル繊維等の網で構成され、たとえば数十ミクロンメートルの目開きの開口部を有した膜分離部を有する。開口部よりも小さい微細な汚濁物質を分離するため、予め原水に、例えば、凝集剤の硫酸バン土やポリ塩化アルミニウムや塩化鉄と磁性粉を加えて攪拌し、原水中の微細な固形浮遊物や藻類,微生物を凝集剤によって数百ミクロンメートル程度の大きさに結合させた磁性フロックを形成させる。この磁性フロックは数十ミクロンメートルの目開きを有した開口部を通過できず高い除去率で捕集分離され、膜を通過した処理水はさらに浄化される。   For the purpose of water purification, a thin wire net or a net woven with polymer fibers is used as a separation membrane. A flocculant and magnetic powder are added to raw water with contaminated particles to generate magnetic floc, and the magnetic floc is formed with a membrane. There is a magnetic separation and purification device that collects high-concentration sludge by magnetic separation and removal of magnetic flocs separated and collected by a membrane by a magnetic field generating means. Such a separation and purification device is made of a mesh made of stainless steel fine wires or polyester fibers, and has a membrane separation part having an opening with an opening of several tens of micrometers, for example. In order to separate fine pollutants smaller than the opening, for example, flocculant vanous sulfate, polyaluminum chloride, iron chloride, and magnetic powder are added to the raw water and stirred, and fine solid suspension in the raw water A magnetic floc is formed by binding algae, algae, and microorganisms to a size of about several hundred micrometers using a flocculant. This magnetic floc cannot pass through an opening having an opening of several tens of micrometers, and is collected and separated at a high removal rate. The treated water that has passed through the membrane is further purified.

従来は膜上に捕集された磁性フロックは、洗浄水で膜から洗い流された後、水面近傍に停留し、水面近傍に静止配置された磁石の磁気力で分離され、汚泥移送手段で汚泥回収槽に蓄えられる。汚泥は最終的には、トラックで処分場や焼却場に運搬したり、コンポスト化される。   Conventionally, the magnetic flocs collected on the membrane are washed away from the membrane with washing water, then stopped near the water surface, separated by the magnetic force of a magnet placed stationary near the water surface, and sludge collected by the sludge transfer means Stored in the tank. The sludge is eventually transported to a disposal site or incinerator by truck or composted.

特開2002−273261号公報JP 2002-273261 A

上記従来技術は、磁性フロック等の汚泥(凝集剤によって凝集された凝集物質)をそのまま廃棄しており、資源の再利用に関して配慮されていなかった。   In the above-described prior art, sludge such as magnetic floc (aggregated material aggregated by a coagulant) is discarded as it is, and no consideration is given to the reuse of resources.

本発明の目的は、汚泥から再利用できるものを回収し、装置の運転コストを低減することのできる流体内からの被除去物除去処理方法及び装置と汚泥分離回収装置を提供することにある。   An object of the present invention is to provide a method and apparatus for removing an object to be removed from a fluid and a sludge separation and recovery apparatus that can recover what can be reused from sludge and reduce the operating cost of the apparatus.

上記目的は、被除去物が含まれた被処理流体に複数の材料から成る凝集剤を供給し、凝集剤によって被除去物を所定の大きさに凝集させて凝集物質を形成させ、被処理流体から凝集物質を分離回収し、該回収された凝集物質に分解剤を加えて被除去物と凝集剤とをそれぞれに分離し、該分離された被除去物および凝集剤をそれぞれに回収し、回収された凝集剤を複数の材料が混ざったまま新たな被除去物が含まれる被処理流体に供給することにより、達成される。   The purpose is to supply a flocculant made of a plurality of materials to a fluid to be treated containing the material to be removed, and to agglomerate the material to be removed to a predetermined size by the flocculant to form an aggregated material. The agglomerated material is separated and recovered from the product, a decomposing agent is added to the collected agglomerated material to separate the object to be removed and the flocculant, and the separated object to be removed and the flocculant are recovered and recovered respectively. This is achieved by supplying the obtained flocculant to a fluid to be treated containing a new material to be removed while a plurality of materials are mixed.

さらに、凝集剤に高分子剤を用いて凝集物質の大きさを大きくし、凝集物質を分離し易くして回収し、回収された凝集物質に塩酸を添加して高分子剤による結合を分解し、分解された凝集物質から凝集剤を分離して被処理流体に供給することにより、凝集剤を再利用する。   In addition, a polymer agent is used as a flocculant to increase the size of the agglomerated material, so that the agglomerated material can be easily separated and recovered, and hydrochloric acid is added to the recovered agglomerated material to break down the bond due to the polymer agent. The flocculant is reused by separating the flocculant from the decomposed flocculant and supplying it to the fluid to be treated.

本発明によれば、汚泥を分解して凝集剤を回収して再利用するので、装置の運転コストを低減できるという効果がある。   According to the present invention, since sludge is decomposed and the flocculant is recovered and reused, there is an effect that the operating cost of the apparatus can be reduced.

また、凝集剤に高分子剤を用いて凝集物質の大きさを大きくし、凝集物質を分離し易くして回収し、回収された凝集物質に所定濃度の塩酸を添加することにより、高分子剤による結合を効率良く解くことができ、分解された凝集物質から凝集剤を効率良く分離回収して、被処理流体に供給し凝集剤を再利用できる。   In addition, the polymer agent is increased by using a polymer agent as the aggregating agent, collecting the agglomerated material so that it can be easily separated, and adding a predetermined concentration of hydrochloric acid to the recovered agglomerated material. Thus, the coagulant can be efficiently released, and the coagulant can be efficiently separated and recovered from the decomposed aggregated material, supplied to the fluid to be treated, and the coagulant can be reused.

被処理流体に凝集剤を添加して被除去物を大きくし(凝集物質にし)、被処理流体から被除去物を濾過分離して取り除き、汚泥である取り除かれた被除去物(凝集物質)に分解剤を添加して分解し過ぎることなく元の被除去物と凝集剤とに分解し、分解された凝集剤をそのまま新たな被処理流体に供給する。   The flocculant is added to the fluid to be treated to enlarge the material to be removed (to make the agglomerated material), and the material to be removed is filtered and removed from the fluid to be treated to remove the material to be removed (aggregated material) that is sludge. The decomposition agent is added to decompose the material to be removed and the flocculant without excessive decomposition, and the decomposed flocculant is supplied as it is to a new fluid to be treated.

本発明の一実施例を図1により説明する。図1は磁気分離浄化装置と汚泥回収装置を組合せた汚泥分離回収装置のフローを示したものである。油等の汚濁粒子を有する原水1は凝集剤(例えば、硫酸バン土,ポリ塩化アルミニウムや塩化鉄)及び磁性粉が予め適量混入(図示していない)されており、比較的回転数が高い(翼の周速が1m/s〜2m/s程度)攪拌槽3に導入され、数百ミクロンメートル程度の磁性マイクロフロックを形成しながら、次に比較的回転数が低い(翼の周速が0.5m/s 〜1m/s程度)攪拌槽4に流入し、高分子凝集剤2を加えることで磁性マイクロフロックは数ミリメートル程度の大きさの磁性フロックを形成する(磁性フロックの形成過程を図8に示す)。このように生成した磁性フロックと前処理水は次の槽5に導入される。槽5では回転ドラム6の外周面に、例えば、ステンレス鋼の細線やポリエステル繊維等で数ミクロンメートルから数十ミクロンメートルの目開きを有した膜となる網6′が設けられている。   An embodiment of the present invention will be described with reference to FIG. FIG. 1 shows a flow of a sludge separation / recovery device combining a magnetic separation / purification device and a sludge recovery device. The raw water 1 having contaminated particles such as oil is preliminarily mixed (not shown) with a coagulant (for example, vanous sulfate, polyaluminum chloride or iron chloride) and magnetic powder, and has a relatively high rotational speed ( The blade was introduced into the agitation tank 3 with a peripheral speed of about 1 m / s to 2 m / s), and then formed with a magnetic micro floc of about several hundred micrometers, while the rotation speed was relatively low (the peripheral speed of the blade was 0). Flowing into the stirring tank 4 and adding the polymer flocculant 2, the magnetic micro flocs form magnetic flocs of the order of several millimeters (the process of forming the magnetic flocs is illustrated). 8). The magnetic floc and pretreatment water generated in this way are introduced into the next tank 5. In the tank 5, a net 6 ′ is formed on the outer peripheral surface of the rotating drum 6. The net 6 ′ is a film having openings of several micrometers to several tens of micrometers, for example, made of stainless steel fine wires or polyester fibers.

槽5に流入した前処理水は、網6′を通過し回転ドラム6内に流入する。このとき前処理水中の磁性フロックは網6′に捕集され、濾過されて磁性フロックが取り除かれた前処理水は回転ドラム6内の排出用の開口部から排出され浄化水17として系外に放流される。   The pretreated water flowing into the tank 5 passes through the net 6 ′ and flows into the rotating drum 6. At this time, the magnetic flocs in the pretreated water are collected by the net 6 ′, and the pretreated water from which the magnetic flocs have been removed by filtration are discharged from the discharge opening in the rotary drum 6 and removed as purified water 17 from the system. It is released.

一方、網6′に付着した磁性フロックは、回転ドラム6内部に設けられたノズルより洗浄水(図示していない)を噴出して網6′から洗い流された後、水面近傍に停留し、水面近傍に配置された回転体7に内蔵された磁場発生手段8、例えば、超伝導磁石や永久磁石により回転体7の表面に吸着されて、回転体7の回転によりカキ取り板9の方向に移動し、カキ取り板9によって回転体7の表面からはく離され、汚泥回収槽11に自然落下して蓄えられる。   On the other hand, the magnetic flocs adhering to the net 6 ′ are washed away from the net 6 ′ by ejecting washing water (not shown) from a nozzle provided inside the rotary drum 6, and then staying near the water surface. The magnetic field generating means 8 built in the rotating body 7 arranged in the vicinity, for example, is attracted to the surface of the rotating body 7 by a superconducting magnet or a permanent magnet, and moves in the direction of the oyster removing plate 9 by the rotation of the rotating body 7. Then, it is peeled off from the surface of the rotating body 7 by the oyster removing plate 9 and naturally falls in the sludge collecting tank 11 and stored.

汚泥回収槽11内にある程度蓄えられた磁性フロック10は、次の汚泥分解槽12に移送され、攪拌しながら適量の塩酸13を加えることにより、高分子凝集剤を分解して、例えば、油,処理水を含んだ凝集剤及び磁性粉に分解される(磁性フロックの分解過程を図9に示す)。加える塩酸のpHは磁性フロック10の状態にもよるが、2から4の範囲であることが望ましい。適量の塩酸を加えることにより、高分子凝集剤の結合が壊れ、マイクロフロックの状態になる。マイクロフロックは、油や塩化鉄の有する電荷によってくっついているだけなので、撹拌によりこれを切り離すことができ、それぞれをバラバラにすることができる。余り塩酸の濃度が濃いと高分子凝集剤以外に磁性粉が溶解するので不適当である。適当な滞留時間で分解された磁性フロックは沈殿槽14にさらに移送される。   The magnetic floc 10 stored to some extent in the sludge recovery tank 11 is transferred to the next sludge decomposition tank 12 and decomposes the polymer flocculant by adding an appropriate amount of hydrochloric acid 13 with stirring, for example, oil, It is decomposed into a flocculant and magnetic powder containing treated water (decomposition process of magnetic floc is shown in FIG. 9). The pH of the hydrochloric acid to be added depends on the state of the magnetic floc 10 but is preferably in the range of 2 to 4. By adding an appropriate amount of hydrochloric acid, the binding of the polymer flocculant is broken and a micro floc state is obtained. Since the micro floc is only stuck by the electric charge of oil or iron chloride, it can be separated by stirring and can be separated. If the concentration of hydrochloric acid is too high, the magnetic powder dissolves in addition to the polymer flocculant, which is inappropriate. The magnetic floc decomposed with an appropriate residence time is further transferred to the settling tank 14.

更に、沈殿槽14において、適当な滞留時間を設けることによって沈殿槽14の上方に比重の軽い油が浮上し、その下部には処理水を含んだ凝集剤と比重の大きい磁性粉とに分離される。処理水を含んだ凝集剤と磁性粉の混合物16は原水1に戻され、再利用される。なお、翼20の形状は一般的なパドル翼,タービン翼等を用いることができる。また、21は混合物16のpHを調整するためのpH調整剤、例えば、苛性ソーダであり、22は混合物16のpH値を検出してpH調整剤21の量を調整する調整手段である。   Furthermore, in the settling tank 14, by providing an appropriate residence time, oil having a low specific gravity floats above the settling tank 14, and in the lower part thereof is separated into a flocculant containing treated water and a magnetic powder having a high specific gravity. The The mixture 16 of the flocculant and the magnetic powder containing the treated water is returned to the raw water 1 and reused. As the shape of the blade 20, a general paddle blade, a turbine blade, or the like can be used. Reference numeral 21 denotes a pH adjusting agent for adjusting the pH of the mixture 16, for example, caustic soda, and 22 denotes an adjusting means for detecting the pH value of the mixture 16 and adjusting the amount of the pH adjusting agent 21.

原水が原油を含んだ海水等の場合には、汚泥粒子である油15は回収され、海水を含んだ凝集剤と磁性粉の混合物16がそのまま原水1に戻され、再利用される。これにより、油田の随伴水処理に適用することにより、海水の浄化,油の回収,凝集剤および磁性粉の消費軽減を図ることができる。   When the raw water is seawater or the like containing crude oil, the oil 15 that is sludge particles is recovered, and the mixture 16 of the flocculant and magnetic powder containing seawater is returned to the raw water 1 and reused. Thereby, by applying it to the accompanying water treatment of the oil field, it is possible to purify seawater, recover oil, reduce consumption of coagulant and magnetic powder.

以上、本実施例によれば、磁性フロックを塩酸で分解して、沈降分離することができ、凝集剤と磁性粉を回収して再利用することができるので、装置の運転コストを低減できる効果がある。さらに、原水が有価価値のある原油を含む場合には原油の回収量を増加できる効果がある。   As described above, according to this embodiment, the magnetic floc can be decomposed with hydrochloric acid and separated by sedimentation, and the flocculant and the magnetic powder can be recovered and reused, so that the operating cost of the apparatus can be reduced. There is. Furthermore, when the raw water contains valuable crude oil, the amount of recovered crude oil can be increased.

また、本実施例によれば、汚泥回収槽11,汚泥分解槽12,沈殿槽14を重力方向に配置して組み合わせているので、処理水は重力方向に流れ動力の消費をほとんど必要とせず、凝集剤と磁性粉の回収を実現することができる。   In addition, according to the present embodiment, the sludge recovery tank 11, the sludge decomposition tank 12, and the settling tank 14 are arranged and combined in the direction of gravity, so that the treated water flows in the direction of gravity and requires little power consumption. Recovery of the flocculant and magnetic powder can be realized.

なお、本実施例は、油を含有する処理水の場合を例に説明したが、被除去物が油以外のものにも適用可能である。   In addition, although the present Example demonstrated the case of the treated water containing oil as an example, to-be-removed thing is applicable also to things other than oil.

図2は本発明の他の実施例を示す。沈殿槽14には、例えば、差圧式の液面計32が設けられており、設定値よりも液面が高い場合には、信号33により適当な制御器(図示していない)を介してポンプ30の出口に設けられた自動弁31を開いて液面を一定に保つ構造となっている。液面が設定値よりも低い場合には、この逆の動作を行う。   FIG. 2 shows another embodiment of the present invention. The sedimentation tank 14 is provided with, for example, a differential pressure type liquid level gauge 32. When the liquid level is higher than the set value, the signal 33 is pumped via an appropriate controller (not shown). The automatic valve 31 provided at the outlet of 30 is opened to keep the liquid level constant. When the liquid level is lower than the set value, the reverse operation is performed.

本実施例によれば、沈殿槽14の液面を一定に保つことができるので、塩酸により分解された磁性フロック40の処理量が変動した場合でも、沈殿槽14の沈降分離の状態を乱すことなく、凝集剤と磁性粉を回収して再利用することができるので、装置の運転コストを低減できる効果がある。   According to the present embodiment, since the liquid level of the precipitation tank 14 can be kept constant, even if the processing amount of the magnetic floc 40 decomposed by hydrochloric acid fluctuates, the state of sedimentation separation in the precipitation tank 14 is disturbed. Since the flocculant and the magnetic powder can be recovered and reused, the operation cost of the apparatus can be reduced.

図3は本発明の他の実施例を示す。沈殿槽14の上部には2組の多孔板42及び43が設けられ、下部には攪拌翼41が槽底と近接して配置されている。塩酸により分解された磁性フロック40は沈殿槽14の上部に流下し、第1の多孔板42によりその垂直方向の速度成分の運動エネルギを減少させられる。さらにその垂直方向の運動エネルギは第2の多孔板43により減少する。これにより、比重分離されている油と処理水を含む凝集剤及び磁性粉の分離状態に余り影響を与えることがない。一方、沈殿槽下部では攪拌翼41が低速で回転、すなわち、比重分離された油の層を乱すことのない速度で回転しており、凝集剤と磁性粉が良好に混合されている。なお、本実施例では運動エネルギを減じる手段として多孔板を示したが、適当な金網等を用いても良い。   FIG. 3 shows another embodiment of the present invention. Two sets of perforated plates 42 and 43 are provided in the upper part of the sedimentation tank 14, and a stirring blade 41 is disposed in the lower part in the vicinity of the tank bottom. The magnetic floc 40 decomposed by hydrochloric acid flows down to the upper part of the settling tank 14, and the first perforated plate 42 reduces the kinetic energy of the velocity component in the vertical direction. Further, the vertical kinetic energy is reduced by the second perforated plate 43. Thereby, the separation state of the flocculant and the magnetic powder containing the oil and the treated water separated by specific gravity is not so much affected. On the other hand, in the lower part of the precipitation tank, the stirring blade 41 rotates at a low speed, that is, rotates at a speed that does not disturb the oil layer separated by specific gravity, and the flocculant and the magnetic powder are well mixed. In the present embodiment, a perforated plate is shown as a means for reducing kinetic energy, but an appropriate wire mesh or the like may be used.

本実施例によれば、より均一な濃度の凝集剤と磁性粉を回収して再利用できるので、磁気分離浄化装置の性能を安定化できる効果があり、また装置の運転コストを低減できる効果がある。また、攪拌翼41によって凝集剤と磁性粉を含んだ処理水が撹拌されるので、凝集剤や磁性粉による供給ラインの目詰まり発生の可能性を防ぐことができる。   According to the present embodiment, the flocculant and magnetic powder having a more uniform concentration can be recovered and reused, so that the performance of the magnetic separation and purification device can be stabilized, and the operation cost of the device can be reduced. is there. Moreover, since the treated water containing the flocculant and the magnetic powder is stirred by the stirring blade 41, it is possible to prevent the supply line from being clogged with the flocculant and the magnetic powder.

図4は本発明の他の実施例を示す。沈殿槽14の上部には邪魔板50ないし54が槽の垂直方向に対して千鳥状に4枚配列されている。塩酸により分解された磁性フロック40は沈殿槽14の上部に流下し、第1の邪魔板50によりその垂直方向の速度成分の運動エネルギを減じて、第1の邪魔板50に沿った水平方向の流れに転換される。次に沈殿槽の内壁で流れは反転し、第2の邪魔板51に沿う流れを生じる。このような流れを発生しながら第3の邪魔板52及び第4の邪魔板53を通って沈殿槽14内を流下する。これにより、沈殿槽14の垂直方向の流れが減少し、比重分離されている油と処理水を含む凝集剤及び磁性粉の分離状態に余り影響を与えることがない。   FIG. 4 shows another embodiment of the present invention. Four baffle plates 50 to 54 are arranged in a staggered pattern in the upper part of the settling tank 14 in the vertical direction of the tank. The magnetic floc 40 decomposed by hydrochloric acid flows down to the upper part of the settling tank 14, reduces the kinetic energy of the velocity component in the vertical direction by the first baffle plate 50, and moves in the horizontal direction along the first baffle plate 50. Converted to flow. Next, the flow is reversed at the inner wall of the settling tank, and a flow along the second baffle plate 51 is generated. The inside of the sedimentation tank 14 flows down through the third baffle plate 52 and the fourth baffle plate 53 while generating such a flow. Thereby, the flow of the vertical direction of the sedimentation tank 14 reduces, and it does not have much influence on the separation state of the flocculant and the magnetic powder containing the oil and the treated water separated by specific gravity.

本実施例によれば、沈殿槽14の沈降分離の状態を乱すことなく、凝集剤と磁性粉を回収して再利用することができるので、装置の運転コストを低減できる効果がある。   According to this embodiment, the flocculant and the magnetic powder can be recovered and reused without disturbing the state of sedimentation separation in the sedimentation tank 14, so that the operation cost of the apparatus can be reduced.

図5は本発明の他の実施例を示す。本図において、図1と同符号は同一部材を示し説明を省略する。本図が図1と異なる点は、槽3,槽4および槽5を独立の層にした点である。油田から排出される油含有廃液は原水槽100に入れられ、pH調整剤61を添加されて最適なpH値に調整される。この場合は、槽3内に塩化鉄(塩化第二鉄)が供給され酸性になるのを防ぎ、ほぼ中性になるように前もって調整している。なお、ここではpH調整剤61を原水槽100に供給するようにしているが、槽3内又は槽3に入る前に調整するようにしても良い。ここで、62は磁性粉であり、63は凝集剤である塩化第二鉄である。70は沈殿槽14の上部に浮いた油を回収する油回収器である。64は塩酸13の添加によって酸性の度合いが強くなった磁性粉を含む凝集剤溶液、この場合、塩化鉄水溶液のpH値を所定の値に調整するpH調整剤、この場合、苛性ソーダである。   FIG. 5 shows another embodiment of the present invention. In this figure, the same reference numerals as those in FIG. This figure is different from FIG. 1 in that the tank 3, the tank 4, and the tank 5 are made into independent layers. The oil-containing waste liquid discharged from the oil field is put into the raw water tank 100, and the pH adjuster 61 is added to adjust the pH value to an optimum value. In this case, iron chloride (ferric chloride) is supplied into the tank 3 to prevent acidity, and the tank 3 is adjusted in advance so as to be almost neutral. Here, the pH adjusting agent 61 is supplied to the raw water tank 100, but may be adjusted in the tank 3 or before entering the tank 3. Here, 62 is magnetic powder, and 63 is ferric chloride which is a flocculant. Reference numeral 70 denotes an oil recovery device that recovers oil floating on the upper portion of the settling tank 14. Reference numeral 64 denotes a flocculant solution containing magnetic powder whose acidity is increased by addition of hydrochloric acid 13, in this case, a pH adjuster for adjusting the pH value of the aqueous iron chloride solution to a predetermined value, in this case, caustic soda.

本実施例によれば、槽3,4,5をそれぞれに独立させているので、処理に最適な条件に設定し易い。   According to the present embodiment, since the tanks 3, 4, and 5 are independent of each other, it is easy to set conditions optimal for processing.

図6は本発明の他の実施例を示す。本図において、図1及び図5と同符号は同一部材を示し説明を省略する。本図が図5と異なる点は、磁性粉62を供給しない点であり、槽4内では磁性粉を有さない凝集物質であるフロックが形成され、槽5a内に供給される。槽5a内では、例えば、螺旋状の網を回転させて槽5a内に溜まったフロックをフロック回収機7aによって、処理水中からすくい上げて汚泥回収槽11に溜めるようになっている。沈殿槽14からは凝集剤である塩化鉄の水溶液を回収し、再利用する。   FIG. 6 shows another embodiment of the present invention. In this figure, the same reference numerals as those in FIGS. 1 and 5 denote the same members, and a description thereof will be omitted. This figure is different from FIG. 5 in that the magnetic powder 62 is not supplied. In the tank 4, flocs that are aggregated substances having no magnetic powder are formed and supplied to the tank 5 a. In the tank 5a, for example, the floc accumulated in the tank 5a by rotating a spiral net is scooped up from the treated water by the flock recovery machine 7a and stored in the sludge recovery tank 11. An aqueous solution of iron chloride as a flocculant is recovered from the settling tank 14 and reused.

本実施例によれば、磁性粉を用いずに油を回収し、凝集剤を再利用することができる。   According to this embodiment, oil can be recovered without using magnetic powder, and the flocculant can be reused.

図7は本発明の他の実施例を示す。本図において、図1及び図5と同符号は同一部材を示し説明を省略する。本図が図5と異なる点は、槽5を複数、この場合、2つ設けて2台の濾過機で磁性フロックを有する処理水を分離処理する点にある。   FIG. 7 shows another embodiment of the present invention. In this figure, the same reference numerals as those in FIGS. 1 and 5 denote the same members, and a description thereof will be omitted. This figure is different from FIG. 5 in that a plurality of tanks 5, in this case two, are provided and the treated water having magnetic flocs is separated by two filters.

本実施例によれば、分離装置の大型化を防ぎ、処理能力に合わせて汚泥分離回収装置を構成することができる。   According to the present embodiment, the separation apparatus can be prevented from being enlarged, and the sludge separation and recovery apparatus can be configured in accordance with the processing capacity.

河川や湖の水質浄化,油田の随伴水処理,タンカーのバラスト処理等液体中の不要物の除去に好適であり、さらに不要物の除去に用いる凝集剤等の回収・再利用に適用できる。   It is suitable for removing unnecessary substances in liquids such as water purification of rivers and lakes, associated water treatment of oil fields, ballast treatment of tankers, and can be applied to the recovery and reuse of flocculants used for removing unnecessary substances.

本発明の一実施例である汚泥分離回収装置を示す概略図である。It is the schematic which shows the sludge separation-and-recovery apparatus which is one Example of this invention. 図1の沈殿槽の他の実施を示す構成図である。It is a block diagram which shows other implementation of the sedimentation tank of FIG. 図1の沈殿槽の他の実施を示す構成図である。It is a block diagram which shows other implementation of the sedimentation tank of FIG. 図1の沈殿槽の他の実施を示す構成図である。It is a block diagram which shows other implementation of the sedimentation tank of FIG. 本発明の他の実施例である汚泥分離回収装置を示す概略図である。It is the schematic which shows the sludge separation-and-recovery apparatus which is the other Example of this invention. 本発明の他の実施例である汚泥分離回収装置を示す概略図である。It is the schematic which shows the sludge separation-and-recovery apparatus which is the other Example of this invention. 本発明の他の実施例である汚泥分離回収装置を示す概略図である。It is the schematic which shows the sludge separation-and-recovery apparatus which is the other Example of this invention. 磁性フロックの形成過程を示す図である。It is a figure which shows the formation process of a magnetic floc. 磁性フロックの分解過程を示す図である。It is a figure which shows the decomposition | disassembly process of a magnetic floc.

符号の説明Explanation of symbols

1…原水、2…高分子凝集剤、6…回転ドラム、6′…網、7…回転体、8…磁場発生手段、9…カキ取り板、10…磁性フロック、11…汚泥回収槽、12…汚泥分解槽、
13…塩酸、14…沈殿槽、20…翼、32…液面計、41…攪拌翼、42…第1の多孔板、50…第1の邪魔板。
DESCRIPTION OF SYMBOLS 1 ... Raw water, 2 ... Polymer flocculant, 6 ... Rotary drum, 6 '... Net, 7 ... Rotating body, 8 ... Magnetic field generating means, 9 ... Oyster removing plate, 10 ... Magnetic flock, 11 ... Sludge collection tank, 12 ... sludge decomposition tank,
DESCRIPTION OF SYMBOLS 13 ... Hydrochloric acid, 14 ... Precipitation tank, 20 ... Wing | blade, 32 ... Level gauge, 41 ... Stirring blade, 42 ... 1st perforated plate, 50 ... 1st baffle plate.

Claims (12)

被除去物が含まれた被処理流体に複数の材料から成る凝集剤を供給し、前記凝集剤によって前記被除去物を所定の大きさに凝集させて凝集物質を形成させ、前記被処理流体から前記凝集物質を分離回収し、該回収された前記凝集物質に分解剤を加えて前記被除去物と前記凝集剤とをそれぞれに分離し、該分離された前記被除去物および前記凝集剤をそれぞれに回収し、前記回収された凝集剤を複数の材料が混ざったまま新たな被除去物が含まれる被処理流体に供給することを特徴とする流体内からの被除去物除去処理方法。   A flocculant made of a plurality of materials is supplied to a fluid to be treated containing the material to be removed, and the material to be removed is agglomerated to a predetermined size by the flocculant to form an agglomerated material. The aggregated material is separated and recovered, a decomposition agent is added to the recovered aggregated material to separate the object to be removed and the flocculant, and the separated object to be removed and the flocculant are separated from each other. And removing the recovered flocculant into a fluid to be treated containing a new material to be removed while mixing a plurality of materials. 被除去物が含まれた被処理流体に磁性体と凝集剤を供給し、前記凝集剤によって前記被除去物とともに前記磁性体を凝集させて凝集物質を形成させ、前記被処理流体から前記凝集物質を分離回収し、該回収された前記凝集物質に分解剤を加えて前記被除去物と前記磁性体と前記凝集剤に分離し、該分離された前記被除去物を回収し、前記分離された前記磁性体および前記凝集剤を一緒にして新たな被除去物が含まれる被処理流体に供給することを特徴とする流体内からの被除去物除去処理方法。   A magnetic substance and an aggregating agent are supplied to a fluid to be treated containing a substance to be removed, and the agglomerated substance is formed by aggregating the magnetic substance together with the substance to be removed by the aggregating agent. Separating and recovering, adding a decomposing agent to the recovered aggregated material to separate the object to be removed, the magnetic body and the flocculant, and recovering the separated object to be removed and separating A method for removing an object to be removed from a fluid, wherein the magnetic substance and the flocculant are combined and supplied to a treatment fluid containing a new object to be removed. 請求項1ないし2記載の流体内からの被除去物除去処理方法において、前記凝集剤に高分子剤を含み、前記分解剤に塩酸を用いる流体内からの被除去物除去処理方法。   3. The method for removing an object to be removed from a fluid according to claim 1, wherein the flocculant contains a polymer agent and hydrochloric acid is used as the decomposing agent. 被除去物が含まれた被処理流体に凝集剤を供給する手段と、前記供給された凝集剤によって前記被除去物を所定の大きさに凝集させて凝集物質を形成する凝集物質形成槽と、前記凝集物質を含んだ前記被処理流体から前記凝集物質を分離回収する分離手段と、該分離回収された前記凝集物質に分解剤を供給する手段と、該分解剤が加えられ前記被除去物と前記凝集剤とをそれぞれに分離する分離槽と、該分離された前記被除去物および前記凝集剤をそれぞれに回収する回収手段と、前記回収された凝集剤を新たな被除去物が含まれる被処理流体に供給する供給手段とから成ることを特徴とする流体内からの被除去物除去処理装置。   Means for supplying a flocculant to the fluid to be treated containing the object to be removed, and an agglomerated substance forming tank for aggregating the object to be removed to a predetermined size by the supplied flocculant to form an agglomerated substance, Separating means for separating and collecting the aggregated substance from the fluid to be treated containing the aggregated substance, means for supplying a decomposing agent to the separated and collected aggregated substance, A separation tank that separates the flocculant from each other, a collection unit that collects the separated object to be removed and the flocculant, respectively, and a collected object that contains the collected flocculant as a new object to be removed. An apparatus for removing an object to be removed from a fluid, comprising supply means for supplying the treatment fluid. 被除去物が含まれた被処理流体に磁性体と凝集剤を供給する手段と、前記供給された凝集剤によって前記被除去物とともに前記磁性体を凝集させて凝集物質を形成する凝集物質形成槽と、前記凝集物質を含んだ前記被処理流体から前記凝集物質を分離回収する分離手段と、該分離回収された前記凝集物質に分解剤を供給する手段と、該分解剤が加えられ前記凝集物質を前記被除去物と前記磁性体と前記凝集剤に分離する分離槽と、該分離された前記被除去物と前記磁性体と前記凝集剤を回収する回収手段と、前記回収された磁性体および凝集剤を一緒にして新たな被除去物が含まれる被処理流体に供給する供給手段とから成ることを特徴とする流体内からの被除去物除去処理装置。   Means for supplying a magnetic substance and a flocculant to a fluid to be treated containing a substance to be removed, and an agglomerated substance forming tank for aggregating the magnetic substance together with the substance to be removed by the supplied flocculant to form an agglomerated substance Separating means for separating and collecting the aggregated substance from the fluid to be treated containing the aggregated substance, means for supplying a decomposition agent to the separated and collected aggregated substance, and adding the decomposition agent to the aggregated substance A separation tank for separating the object to be removed, the magnetic body, and the flocculant, a recovery means for recovering the separated object to be removed, the magnetic body, and the flocculant, the recovered magnetic body, and An apparatus for removing an object to be removed from a fluid, comprising supply means for supplying a flocculant together to a fluid to be treated containing a new object to be removed. 被除去物を含む被処理流体に、磁性体と凝集剤を連続的に供給し、攪拌することにより被除去物を前記磁性体と凝集剤により凝集させ凝集物質を形成させる凝集物生成手段と、前記凝集物質が通過できない目開きを有し前記凝集物質を含む被処理流体を濾過する濾過手段と、前記濾過手段で捕集された前記凝集物質を磁気吸引させる磁場発生手段と、前記磁気吸引された凝集物質を回収する汚泥回収手段と、前記汚泥回収手段に前記凝集物質をカキ取るカキ取り手段を設けた磁気分離浄化装置において、前記カキ取り手段によってカキ取られた凝集物質を貯え該凝集物質に塩酸を加えて攪拌する槽と、該槽内で前記塩酸により分解された前記凝集物質を磁性体と凝集剤及び被除去物に分離する沈殿槽と、該沈殿槽により分離された磁性体および凝集剤を一緒に回収して前記被処理流体に添加する供給手段とを設けてことを特徴とする汚泥分離回収装置。   Agglomerate generating means for continuously supplying a magnetic substance and an aggregating agent to a fluid to be treated containing the object to be removed, and aggregating the object to be removed with the magnetic substance and the aggregating agent to form an aggregated substance by stirring; Filtration means for filtering the fluid to be treated having an opening through which the aggregated substance cannot pass, magnetic field generating means for magnetically attracting the aggregated substance collected by the filtration means, and the magnetically attracted In a magnetic separation and purification apparatus provided with a sludge collecting means for collecting the agglomerated material and a oyster removing means for removing the agglomerated material in the sludge collecting means, the agglomerated material stored by the oyster removing means A tank in which hydrochloric acid is added and stirred, a settling tank for separating the agglomerated material decomposed by the hydrochloric acid in the tank into a magnetic substance, a coagulant and a material to be removed, and a magnetic substance separated by the settling tank. Yo Sludge separation and recovery apparatus characterized by and a flocculant is recovered together provided a supply means for adding to the treated fluid. 請求項6記載の汚泥分離回収装置において、前記沈殿槽に液面計を設けて、液面を一定に制御する汚泥分離回収装置。   The sludge separation and recovery apparatus according to claim 6, wherein a liquid level gauge is provided in the settling tank to control the liquid level to be constant. 請求項6記載の汚泥分離回収装置において、前記沈殿槽の上部に少なくとも1つの多孔板を設けた汚泥分離回収装置。   7. The sludge separation and recovery apparatus according to claim 6, wherein at least one perforated plate is provided above the settling tank. 請求項6記載の汚泥分離回収装置において、前記沈殿槽の上部に少なくとも1つの邪魔板を設けた汚泥分離回収装置。   The sludge separation and recovery apparatus according to claim 6, wherein at least one baffle plate is provided on the upper part of the settling tank. 請求項8ないし9記載の汚泥分離回収装置において、前記沈殿槽の下部に攪拌翼を具備した汚泥分離回収装置。   10. The sludge separation and recovery device according to claim 8, wherein a sludge separation and recovery device comprises a stirring blade at a lower portion of the settling tank. 請求項6記載の汚泥分離回収装置において、前記沈殿槽により分離された磁性体および凝集剤のpHを測定しpH調整を行う汚泥分離回収装置。   The sludge separation and recovery apparatus according to claim 6, wherein the sludge separation and recovery apparatus performs pH adjustment by measuring the pH of the magnetic substance and the flocculant separated by the settling tank. 請求項6記載の汚泥分離回収装置において、前記凝集剤に高分子剤を含み、前記分解剤に塩酸を用いる汚泥分離回収装置。
The sludge separation and recovery apparatus according to claim 6, wherein the flocculant contains a polymer agent and hydrochloric acid is used as the decomposition agent.
JP2003351476A 2003-10-10 2003-10-10 Method and apparatus for removing substance to be removed from fluid and sludge separation and recovery apparatus Pending JP2005111424A (en)

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CN113348152A (en) * 2018-08-17 2021-09-03 莫尼耶技术有限公司 Method for extracting water from sludge by magnetic treatment
CN114534322A (en) * 2022-04-25 2022-05-27 山东省核工业二七三地质大队 Mineral processing thickener
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WO2009019971A1 (en) * 2007-08-09 2009-02-12 Sumitomo Electric Industries, Ltd. Water treatment apparatus and water treatment method
JP2011016117A (en) * 2009-07-10 2011-01-27 Hitachi Plant Technologies Ltd Ballast water treatment method and apparatus
JP2011125811A (en) * 2009-12-18 2011-06-30 Hitachi Plant Technologies Ltd Waste water treatment apparatus
JP2011143330A (en) * 2010-01-12 2011-07-28 Hitachi Plant Technologies Ltd Method and apparatus for treating wastewater
US8597520B2 (en) 2010-01-12 2013-12-03 Hitachi Plant Technologies, Ltd. Wastewater treatment method and wastewater treatment apparatus
JP2012040536A (en) * 2010-08-23 2012-03-01 Hitachi Plant Technologies Ltd Flocculation-magnetic separation system
CN105854408A (en) * 2016-05-25 2016-08-17 安徽普氏生态环境工程有限公司 Pretreatment device before magnetic separation film
CN106673293B (en) * 2017-03-29 2023-09-08 张家富 Device and method for treating black and odorous water body
CN106673293A (en) * 2017-03-29 2017-05-17 张家富 Device for managing black and odorous water body and method for managing black and odorous water body
CN107867741A (en) * 2017-09-15 2018-04-03 北京航天斯达科技有限公司 A kind of novel high speed is sirred and separated mechanism
CN113348152A (en) * 2018-08-17 2021-09-03 莫尼耶技术有限公司 Method for extracting water from sludge by magnetic treatment
US11760676B2 (en) 2018-08-17 2023-09-19 Meunier Technologies Inc. Method of extracting water from sludge using magnetic treatment
CN112246011A (en) * 2020-10-21 2021-01-22 王燕飞 Glass processing cutting fluid circulating and filtering equipment
CN114534322A (en) * 2022-04-25 2022-05-27 山东省核工业二七三地质大队 Mineral processing thickener
CN117046187A (en) * 2023-09-18 2023-11-14 广州旭璟科技有限公司 Black liquor and fiber separation equipment and method in lignin preparation process by organic solvent method
CN117046187B (en) * 2023-09-18 2024-06-11 广州旭璟科技有限公司 Black liquor and fiber separation equipment and method in lignin preparation process by organic solvent method

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