JP2001170404A - Magnetic separator - Google Patents
Magnetic separatorInfo
- Publication number
- JP2001170404A JP2001170404A JP35548299A JP35548299A JP2001170404A JP 2001170404 A JP2001170404 A JP 2001170404A JP 35548299 A JP35548299 A JP 35548299A JP 35548299 A JP35548299 A JP 35548299A JP 2001170404 A JP2001170404 A JP 2001170404A
- Authority
- JP
- Japan
- Prior art keywords
- magnetic
- sludge
- magnetic powder
- flocs
- tank
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は凝集沈殿装置に関す
るものであり、下水や湖沼,河川等の原水中の固形浮遊
物を磁性粉と凝集させることにより高い沈降速度で凝集
沈澱処理し、固形浮遊物を効果的に除去する沈殿処理装
置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for coagulating sedimentation, and to coagulate sedimentation at a high sedimentation rate by coagulating solid suspended matter in raw water such as sewage, lakes, rivers and the like with magnetic powder, and solid floating The present invention relates to a sedimentation treatment device for effectively removing matter.
【0002】[0002]
【従来の技術】従来の被処理水中の固形浮遊物を除去す
るた技術で主なものには、原水に凝集剤を添加して、原
水中の固形浮遊物凝集させてフロックを生成し沈降分離
する凝集沈殿処理装置がある。しかしながら、この凝集
沈殿法ではフロックの沈降速度が小さいため処理時間が
長く、大容量処理を行うためには大型のスペースが必要
となる。2. Description of the Related Art A conventional technique for removing solid suspended solids in water to be treated is mainly one in which a flocculant is added to raw water to flocculate solid suspended solids in raw water to form flocs and settle and separate. There is a coagulation and sedimentation treatment device. However, in this coagulation sedimentation method, the sedimentation speed of floc is low, so that the processing time is long, and a large space is required for performing a large-capacity processing.
【0003】そこで、フロックの沈降速度を高め、処理
時間を短縮化する方法として、原水中に砂と凝集剤と高
分子凝集補助剤を添加して凝集槽内で凝集させて、砂を
シーディングしたフロックを生成するものがある(例え
ば特開平7−302637号公報)。この方法で生成されたフロ
ックは、砂を取り込んでいるため比重が大きくなるので
沈降速度も大きくなり、処理時間も短縮化される。この
装置で生成されたフロックは凝集沈殿槽内で沈殿させて
沈殿槽下部から汚泥として引き抜かれる。[0003] As a method of increasing the sedimentation speed of flocs and shortening the treatment time, sand, a flocculant and a polymer flocculant are added to raw water and flocculated in a flocculation tank to seed the sand. There is one that generates a floc (see, for example, JP-A-7-302637). The floc generated by this method has a large specific gravity due to the incorporation of sand, so that the sedimentation speed increases and the processing time is shortened. The floc generated by this apparatus is settled in the coagulation settling tank and is pulled out as sludge from the lower part of the settling tank.
【0004】しかし、このままでは、発生する汚泥の重
量が大きくなるため、減容化する必要がある。また、砂
を供給するためコストがかかる。そこで、この汚泥から
砂をサイクロンで分離回収して再利用する方法が提案さ
れている。砂を回収した後の汚泥は系外へ排出する。回
収した砂は再び凝集槽に戻されて再利用される。[0004] However, in this case, the weight of the generated sludge increases, and it is necessary to reduce the volume. In addition, it costs much to supply sand. Therefore, a method has been proposed in which sand is separated and recovered from the sludge by a cyclone and reused. After collecting the sand, the sludge is discharged out of the system. The recovered sand is returned to the coagulation tank and reused.
【0005】[0005]
【発明が解決しようとする課題】しかしながら、上記従
来方法では、汚泥から砂を分離する手段としてサイク
ロンを使用しているが、この方法によるせん断力では、
フロック状の汚泥の中に取り込まれている砂と固形浮遊
物を分離が難しく、砂の表面に固形浮遊物や凝集剤が付
着したまま残る場合があり、凝集槽でシーディング剤と
して再利用するときに凝集性能が落ちる可能性がある。However, in the above-mentioned conventional method, a cyclone is used as a means for separating sand from sludge.
It is difficult to separate the sand and solid suspended matter taken into the floc-like sludge, and the solid suspended matter and flocculant may remain attached to the surface of the sand, and are reused as a seeding agent in the flocculation tank. Sometimes the cohesion performance may be reduced.
【0006】フロック状の汚泥の中に取り込まれてい
る砂を汚泥から分離する際、遠心力では砂だけを選択的
に分離回収することは難しく、砂を分離回収した後の汚
泥の中に砂が混入する場合があり、最終的に汚泥の重量
が増える可能性がある。When separating sand taken in floc-like sludge from sludge, it is difficult to selectively separate and collect only sand by centrifugal force. May be mixed, and the weight of sludge may eventually increase.
【0007】といった問題がある。There is such a problem.
【0008】本発明の目的は、上記従来の問題を解決
し、高速凝集沈殿処理を行う浄化装置を提供することに
ある。[0008] An object of the present invention is to solve the above-mentioned conventional problems and to provide a purification apparatus for performing high-speed coagulation sedimentation treatment.
【0009】[0009]
【課題を解決するための手段】本発明の浄化装置は、原
水に磁性粉,凝集剤、そして凝集補助剤として高分子凝
集剤を添加して凝集処理する凝集処理槽と、前記凝集槽
から流出水が導入されるスラッジブランケット型沈殿槽
と、前記スラッジブランケット下部に堆積した汚泥を引
き抜く手段と、引き抜いた汚泥を機械的分解または熱水
分解する装置と、分解した汚泥の中から磁性粉だけを選
択的に分離回収する磁気分離装置と、回収した磁性粉を
前記凝集槽に返送する手段とを有してなることを特徴と
する。According to the present invention, there is provided a purification apparatus comprising: a coagulation treatment tank for coagulating a raw water by adding a magnetic powder, a coagulant, and a polymer coagulant as a coagulation aid; A sludge blanket type sedimentation tank into which water is introduced, means for extracting sludge deposited at the lower part of the sludge blanket, a device for mechanically or hydrothermally decomposing the extracted sludge, and only magnetic powder from the decomposed sludge. It is characterized by comprising a magnetic separation device for selectively separating and collecting, and means for returning the collected magnetic powder to the flocculation tank.
【0010】本発明では、シーディング剤として磁性粉
を使用して比重の大きな磁性フロックを生成することで
沈降速度を高めて処理時間を短くし、回収した汚泥から
磁性粉の分離回収を効果的に行うことにより、磁性粉の
再利用を可能とし、効率的に高速凝集沈殿を行うことが
出来る。In the present invention, the use of magnetic powder as a seeding agent to generate magnetic flocs having a large specific gravity increases the sedimentation speed, shortens the treatment time, and effectively separates and recovers the magnetic powder from the recovered sludge. By doing so, the magnetic powder can be reused, and high-speed coagulation precipitation can be performed efficiently.
【0011】[0011]
【発明の実施の形態】以下添付図に従って本発明の磁気
分離装置の実施例について説明を行う。BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a perspective view of a magnetic separator according to an embodiment of the present invention.
【0012】図1は本発明の1実施例を示す浄化装置の
体系模式図である。FIG. 1 is a schematic system diagram of a purifying apparatus showing one embodiment of the present invention.
【0013】図1において、1は凝集剤,磁性粉,pH
調整剤を混合する急速攪拌槽である。2は急速攪拌槽1
において生成されたマイクロフロックに高分子凝集剤を
添加することにより成長させ強力なフロックにするため
の緩速攪拌槽である。急速攪拌槽の前において、pH調
整剤を添加するpH調整剤注入装置3,磁性粉を添加す
る磁性粉注入装置4,凝集剤を注入する凝集剤注入装置
5が備えられている。In FIG. 1, 1 is a flocculant, magnetic powder, pH
This is a rapid stirring tank for mixing a regulator. 2 is a rapid stirring tank 1
This is a slow stirring tank for growing a strong floc by growing a micro floc generated by adding a polymer flocculant to the micro floc. In front of the rapid stirring tank, there are provided a pH adjuster injection device 3 for adding a pH adjuster, a magnetic powder injection device for adding magnetic powder 4, and a coagulant injection device 5 for injecting a coagulant.
【0014】急速攪拌槽1と緩速攪拌槽の間には、高分
子凝集剤を添加する高分子凝集剤注入装置6が備えられ
ている。7は回転式レーキ8を備えるスラッジブランケ
ット型沈降槽である。8Aはレーキを回転させるための
駆動機構である。9は沈殿槽7の下部に沈降堆積した汚
泥を回収した後で機械的に分解する汚泥分解装置であ
る。10は分解装置9において分解された汚泥の中から
磁性粉を回収する磁気分離装置である。11は磁気分離
装置において磁場を発生させる電磁コイルであり、12
は電磁コイル11で挟まれた空間内に設置された強磁性
体を材料とする磁気フィルタである。A polymer coagulant injection device 6 for adding a polymer coagulant is provided between the rapid stirring tank 1 and the slow stirring tank. Reference numeral 7 denotes a sludge blanket settling tank provided with a rotary rake 8. 8A is a drive mechanism for rotating the rake. Reference numeral 9 denotes a sludge decomposer that mechanically decomposes sludge that has settled and deposited at the lower part of the sedimentation tank 7. Reference numeral 10 denotes a magnetic separation device that collects magnetic powder from sludge decomposed in the decomposition device 9. Numeral 11 denotes an electromagnetic coil for generating a magnetic field in the magnetic separation device.
Reference numeral denotes a magnetic filter made of a ferromagnetic material, which is provided in a space interposed between the electromagnetic coils 11.
【0015】以下に本発明の手順を説明する。The procedure of the present invention will be described below.
【0016】凝集剤,pH調整剤,磁性粉が添加された
原水は急速攪拌槽1に運ばれた後、攪拌混合される。こ
こで、原水中の固形浮遊物(以下SSと称す)は磁性粉
とともにフロックを形成する。このフロックを以下磁性
フロックと称す。このフロックは小さく、せん断力に弱
いマイクロフロックである。このマイクロ磁性フロック
を含んだ急速攪拌槽1から流出した原水に高分子凝集剤
を添加した後、緩速攪拌槽2に送りここで大きくせん断
力に強いフロックを生成する。The raw water to which the coagulant, the pH adjuster, and the magnetic powder have been added is transported to the rapid stirring tank 1 and then stirred and mixed. Here, solid suspended matter (hereinafter referred to as SS) in raw water forms flocs with magnetic powder. This floc is hereinafter referred to as a magnetic floc. This floc is small and is a micro floc that is weak against shearing force. After adding a polymer flocculant to the raw water flowing out of the rapid stirring tank 1 containing the micromagnetic flocs, the polymer flocculant is sent to the slow stirring tank 2 where a large floc resistant to shearing force is generated.
【0017】磁性粉の比重は約5g/ccであり、原水中
に含まれている、有機物,無機物の粒子の比重に比べて
大きいため、磁性フロックの比重は、磁性粉を含まない
フロックに比べて沈降速度が大きくなる。この磁性フロ
ックを含む原水を緩速攪拌槽2から沈殿槽7に送り、こ
こで沈降堆積させて回収し、上澄みとして浄化水を取り
出す。沈殿槽7の下部ではレーキ8を回転させて堆積し
た汚泥の濃縮効率を高める。堆積した濃縮汚泥を引き抜
いた後は、この汚泥を汚泥分解装置9に送る。9は30
00から10000rpm の回転数をもつ汚泥分解用のロ
ーターとステーター、およびその後段に2mm以下の隙間
をもつ磨砕処理用のローターとステーターをもつミキサ
ーである。1段目において汚泥は粉砕され、さらに2段
目において磨砕処理が加わることにより汚泥と磁性粉が
分離される。Since the specific gravity of the magnetic powder is about 5 g / cc, which is larger than the specific gravity of the organic and inorganic particles contained in the raw water, the specific gravity of the magnetic floc is larger than that of the floc containing no magnetic powder. The sedimentation velocity increases. The raw water containing the magnetic flocs is sent from the slow stirring tank 2 to the sedimentation tank 7, where it is settled and collected, and purified water is taken out as supernatant. In the lower part of the sedimentation tank 7, the rake 8 is rotated to increase the concentration efficiency of the accumulated sludge. After withdrawing the accumulated concentrated sludge, the sludge is sent to the sludge decomposing device 9. 9 is 30
This is a mixer having a rotor and a stator for rotating sludge having a rotation speed of 00 to 10000 rpm, and a rotor and a stator for grinding treatment having a clearance of 2 mm or less in the subsequent stage. In the first stage, the sludge is pulverized, and in the second stage, a grinding process is applied to separate the sludge and the magnetic powder.
【0018】9において分解した汚泥を、磁気分離装置
10に送り磁性粉の分離回収を行う。10は中空円筒の
中に電磁コイル11が入っており、中空の部分に強磁性
体で出来た磁気フィルタが備えられている。この磁気フ
ィルタの細線近傍では磁場が高勾配になるため、12の
いたるところで強力な磁気力が発生し、この中を通過す
る分解処理がなされた前記汚泥の中から磁性粉のみを選
択的に回収することが出来る。磁気分離装置から排出さ
れた汚泥はコンポストや焼却、埋め立て処分される。磁
気分離装置10で磁性粉を回収した後は、この磁性粉を
再び磁性粉注入装置に返送し再利用する。The sludge decomposed in 9 is sent to a magnetic separator 10 to separate and collect magnetic powder. Reference numeral 10 denotes a hollow cylinder in which an electromagnetic coil 11 is provided, and a magnetic filter made of a ferromagnetic material is provided in a hollow portion. Since the magnetic field has a high gradient near the fine line of the magnetic filter, a strong magnetic force is generated everywhere, and only the magnetic powder is selectively recovered from the sludge that has been subjected to the decomposition treatment passing therethrough. You can do it. Sludge discharged from the magnetic separator is composted, incinerated and landfilled. After the magnetic powder is collected by the magnetic separation device 10, the magnetic powder is returned to the magnetic powder injection device and reused.
【0019】上記実施例の説明では、汚泥分解装置とし
て機械的分解によるものとしたが、熱水分解による汚泥
分解方法でも可能である。熱水分解は温度300℃以下
の亜臨界で行う湿式酸化方法である。300℃以上に温
度を挙げる超臨界処理の場合、強磁性体である磁性粉が
酸化により磁化が小さくなるが、亜臨界では強磁性体と
して物性を示し続ける。さらにこの方法を用いれば、回
収した有機物等の汚泥の減容化を行うことが可能であ
る。また、汚泥を熱水分解すると、磁性粉と汚泥の分離
が完全になされる。In the description of the above embodiment, the sludge decomposing apparatus is mechanically decomposed, but a sludge decomposing method by hydrothermal decomposition is also possible. Hydrothermal decomposition is a wet oxidation method performed at a subcritical temperature of 300 ° C. or lower. In the case of the supercritical treatment in which the temperature is raised to 300 ° C. or more, the magnetization of the magnetic powder, which is a ferromagnetic material, decreases due to oxidation, but continues to exhibit physical properties as a ferromagnetic material in the subcritical state. Further, if this method is used, it is possible to reduce the volume of the collected sludge such as organic matter. When the sludge is hydrolyzed, the magnetic powder and the sludge are completely separated.
【0020】また上記実施例の説明では、磁気分離装置
を電磁磁石としたが、超電導磁石としてもかまわない
し、永久磁石を用いる磁気分離装置でもよい。In the above embodiment, the magnetic separation device is an electromagnetic magnet, but may be a superconducting magnet or a magnetic separation device using a permanent magnet.
【0021】図2に永久磁石を用いた磁性粉回収装置を
示す。ディスク13に永久磁石14を貼り付けた装置で
ある。図2に示すように、ディスク13を回転させなが
ら、分解汚泥をディスクの下部の磁石設置領域に接触す
るように流入させ、磁性粉をディスクに吸着させる。デ
ィスクに張り付いた磁性粉はスクレイパー15により掻
き取られ磁性粉回収槽にて回収される。FIG. 2 shows a magnetic powder recovery apparatus using a permanent magnet. This is a device in which a permanent magnet 14 is attached to a disk 13. As shown in FIG. 2, while rotating the disk 13, the decomposed sludge is caused to flow into contact with the magnet installation area below the disk, and the magnetic powder is adsorbed to the disk. The magnetic powder stuck to the disk is scraped off by the scraper 15 and collected in the magnetic powder collection tank.
【0022】また、汚泥分解装置として、熱水分解の方
法を使用する場合は必ずしも磁気分離による磁性粉回収
方法でなくともよく、比重さを利用した分級方法でもよ
い。When a method of hydrothermal decomposition is used as the sludge decomposing apparatus, a method of recovering magnetic powder by magnetic separation is not necessarily required, and a classification method utilizing specific gravity may be used.
【0023】図3に上記熱水分解と分級方式を組み合わ
せた1例を示す。沈殿槽7から回収された濃縮汚泥が熱
水処理装置17に送られる。1段目のヒータ部18では
汚泥と磁性粉の分解が行われ、2段目ヒータ部に送られ
るとき汚泥から分離された磁性粉が重力沈降により1段
目磁性粉回収槽19において回収される。さらに2段目
のヒータ部20において汚泥をさらに減容化する。2段
目の磁性粉回収槽21では1段目の磁性粉回収槽19で
回収しきれなかった磁性粉を回収する。なおこの段階で
汚泥は完全に減容化されている。FIG. 3 shows an example in which the above hydrothermal decomposition and the classification method are combined. The concentrated sludge collected from the settling tank 7 is sent to the hot water treatment device 17. The sludge and the magnetic powder are decomposed in the first-stage heater unit 18, and the magnetic powder separated from the sludge when sent to the second-stage heater unit is collected in the first-stage magnetic powder collection tank 19 by gravity sedimentation. . Further, sludge is further reduced in the second heater section 20. In the second-stage magnetic powder collection tank 21, the magnetic powder that cannot be collected in the first-stage magnetic powder collection tank 19 is collected. At this stage, the sludge has been completely reduced in volume.
【0024】また、凝集沈殿させる際、沈降方向に磁気
力がかかるように磁場を印加すれば沈降速度を更に大き
くすることが可能である。それと同時に、磁場の力によ
り凝集物であるフロックが圧密し、凝集構造の隙間の水
が抜けて含水率が低下するとともに汚泥の体積が減少す
るという利点もあることはいうまでもない。When a magnetic field is applied so that a magnetic force is applied in the sedimentation direction during coagulation and sedimentation, the sedimentation speed can be further increased. At the same time, it is needless to say that the floc, which is an aggregate, is compacted by the force of the magnetic field, water in the gaps of the aggregate structure is released, the water content is reduced, and the volume of the sludge is reduced.
【0025】沈降槽7の内部において、ラビリンス構造
をもった邪魔板などを設置することにより、フロックの
沈降面積を大きくしたり、フロックの接触頻度を高めて
フロックの成長を促進させてより沈降しやすい大きなフ
ロックを作れるような構造をもたせてもよい。By installing a baffle plate having a labyrinth structure inside the sedimentation tank 7, the sedimentation area of the floc is increased, and the frequency of the contact of the floc is increased to promote the growth of the floc to further reduce the sedimentation. A structure that can easily make a large floc may be provided.
【0026】[0026]
【発明の効果】本発明による、磁性粉をシード剤として
利用する凝集沈殿の方法を採用すると、沈降速度が速く
なることで除去速度が速くなり、磁性粉の再利用が容易
になることで連続運転の効率が向上する。According to the present invention, when the method of coagulation and sedimentation using a magnetic powder as a seed agent is adopted, the sedimentation speed is increased, the removal speed is increased, and the reuse of the magnetic powder is facilitated. Driving efficiency is improved.
【図1】本発明の実施例である浄化装置を示す体系模式
図である。FIG. 1 is a schematic system diagram showing a purification device according to an embodiment of the present invention.
【図2】磁性粉回収用磁気分離装置を示す模式された斜
視図である。FIG. 2 is a schematic perspective view showing a magnetic separation device for collecting magnetic powder.
【図3】磁性粉分離回収装置を示す構成図である。FIG. 3 is a configuration diagram showing a magnetic powder separation and recovery device.
1…急速攪拌槽、2…緩速攪拌槽、3…pH調整剤注入
装置、4…磁性粉注入装置、5…凝集剤注入装置、6…
高分子凝集剤注入装置、7…スラッジブランケット型沈
殿槽、8…レーキ、8A…レーキ駆動軸、9…汚泥分解
装置、10…磁気分離装置、11…電磁コイル、12…
磁気フィルタ、13…ディスク、14…永久磁石、15
…スクレイパー、16…磁性粉回収槽、17…熱水分解
装置、18…1段目ヒータ、19…1段目磁性粉回収
槽、20…2段目ヒータ、21…2段目磁性粉回収槽。DESCRIPTION OF SYMBOLS 1 ... Rapid stirring tank, 2 ... Slow stirring tank, 3 ... pH adjuster injection apparatus, 4 ... Magnetic powder injection apparatus, 5 ... Coagulant injection apparatus, 6 ...
Polymer coagulant injection device, 7: sludge blanket type sedimentation tank, 8: rake, 8A: rake drive shaft, 9: sludge decomposition device, 10: magnetic separation device, 11: electromagnetic coil, 12 ...
Magnetic filter, 13 ... disk, 14 ... permanent magnet, 15
... Scraper, 16 ... Magnetic powder collection tank, 17 ... Hydrolysis device, 18 ... First stage heater, 19 ... First stage magnetic powder collection tank, 20 ... Second stage heater, 21 ... Second stage magnetic powder collection tank .
───────────────────────────────────────────────────── フロントページの続き (72)発明者 磯上 尚志 茨城県土浦市神立町502番地 株式会社日 立製作所機械研究所内 (72)発明者 佐野 理志 茨城県土浦市神立町502番地 株式会社日 立製作所機械研究所内 Fターム(参考) 4D015 BA21 BB09 BB12 CA14 DA37 DB01 EA07 EA16 EA32 FA03 FA30 4D062 BA21 BB09 BB12 CA14 DA37 DB01 EA07 EA16 EA32 FA03 FA30 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Takashi Isogami 502 Kandate-cho, Tsuchiura-city, Ibaraki Pref. Machinery Research Laboratories, Hitachi, Ltd. 4D015 BA21 BB09 BB12 CA14 DA37 DB01 EA07 EA16 EA32 FA03 FA30 4D062 BA21 BB09 BB12 CA14 DA37 DB01 EA07 EA16 EA32 FA03 FA30
Claims (1)
理する凝集槽と、前記凝集槽の流出水が導入されるスラ
ッジブランケット型沈殿槽と、前記沈殿槽内のスラッジ
ブランケット下部の汚泥を引き抜いて汚泥分解装置に搬
送する手段を有してなることを特徴とする浄化装置。1. A flocculation tank for adding a flocculant and a magnetic powder to raw water to perform a flocculation treatment, a sludge blanket-type precipitation tank into which effluent of the flocculation tank is introduced, and a sludge under a sludge blanket in the precipitation tank. A purifying device, comprising means for extracting the sludge and transporting the sludge to a sludge decomposing device.
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JP35548299A JP2001170404A (en) | 1999-12-15 | 1999-12-15 | Magnetic separator |
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JP35548299A JP2001170404A (en) | 1999-12-15 | 1999-12-15 | Magnetic separator |
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JP2001170404A true JP2001170404A (en) | 2001-06-26 |
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JP35548299A Pending JP2001170404A (en) | 1999-12-15 | 1999-12-15 | Magnetic separator |
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