JPH0629683U - Solid-liquid separation device - Google Patents

Solid-liquid separation device

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Publication number
JPH0629683U
JPH0629683U JP7001992U JP7001992U JPH0629683U JP H0629683 U JPH0629683 U JP H0629683U JP 7001992 U JP7001992 U JP 7001992U JP 7001992 U JP7001992 U JP 7001992U JP H0629683 U JPH0629683 U JP H0629683U
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Prior art keywords
tank
raw water
long fiber
separation device
water
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JP7001992U
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Japanese (ja)
Inventor
健 村上
信行 星
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オルガノ株式会社
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Priority to JP7001992U priority Critical patent/JPH0629683U/en
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Abstract

(57)【要約】 【目的】 従来装置では不可欠であった逆洗排水受槽を
不要として設置面積が少なくて済み、且つ原水の懸濁固
形分の負荷の均一化を図った固液分離装置を提供する。 【構成】 浮上分離装置4の後段に長繊維束7を充填し
た長繊維濾過装置6を付設する。当該長繊維濾過装置6
の逆洗時に生ずる逆洗排水を浮上分離装置4の前段に設
置した原水槽1に戻すための戻し管9を配設する。
(57) [Summary] [Purpose] A solid-liquid separation device that does not require a backwash drainage receiving tank, which was indispensable in conventional equipment, and requires a small installation area, and that has a uniform load of suspended solids of raw water. provide. [Structure] A long fiber filtering device 6 filled with a long fiber bundle 7 is attached to a stage subsequent to the floating separation device 4. The long fiber filtration device 6
A return pipe 9 is provided for returning the backwash drainage generated during the backwash to the raw water tank 1 installed in the preceding stage of the flotation separator 4.

Description

【考案の詳細な説明】[Detailed description of the device]

【0001】[0001]

【産業上の利用分野】[Industrial applications]

本考案は上水や工業用水、河川水、湖沼水、各種工程中間水、各種回収水、各 種産業排水等の原水中に存在する懸濁物質を分離除去する固液分離装置の改良に 関するものである。 The present invention relates to improvement of a solid-liquid separation device for separating and removing suspended substances existing in raw water such as tap water, industrial water, river water, lake water, various process intermediate water, various recovered water, and various industrial wastewater. It is a thing.

【0002】[0002]

【従来の技術】[Prior art]

上水や工業用水、河川水、各種産業排水等の原水中に含まれる懸濁物質を原水 から分離除去する固液分離装置として、従来は凝集沈澱槽の後段に砂濾過器を付 設した構造のものが一般的に用いられている。 図2はこのような従来の一般的な固液分離装置の概略を示すもので、図中21 は処理対象の原水を一時貯溜しておく原水槽、22は原水槽21から送られてく る原水中に硫酸アルミニウムやポリ塩化アルミニウムのような凝集剤を添加して 原水中の固形分を粗大化するための凝集反応槽、23は当該凝集反応槽22から 送られてくる原水中の懸濁固形分を沈降分離させる凝集沈澱槽、24は凝集沈澱 槽23からキャリーオーバーされた固形分を濾過分離するため凝集沈澱槽23の 後段に付設した砂濾過器である。 25は砂濾過器24の逆洗時に大量に生ずる逆洗排水を貯溜する逆洗排水受槽 である。なお、当該逆洗排水受槽25は設置スペースに余裕がない場合には、前 記沈澱槽23において分離される懸濁固形分(汚泥)の汚泥濃縮槽26内に逆洗 排水を排出するようにして、逆洗排水受槽25を設置しない場合もある。 As a solid-liquid separation device that separates and removes suspended solids contained in raw water such as tap water, industrial water, river water, and various industrial wastewater, a structure with a sand filter attached to the latter stage of the coagulating sedimentation tank has been used in the past. Are commonly used. FIG. 2 shows an outline of such a conventional general solid-liquid separator. In the figure, 21 is a raw water tank for temporarily storing raw water to be treated, and 22 is a raw water sent from the raw water tank 21. A flocculation reaction tank for adding a flocculant such as aluminum sulfate or polyaluminum chloride to the water to coarsen the solid content in the raw water, and 23 is a suspended solid in the raw water sent from the flocculation reaction tank 22. A coagulation-sedimentation tank for separating and separating the components, and 24 is a sand filter attached to the subsequent stage of the coagulation-sedimentation tank 23 for separating the carry-over solids from the coagulation-sedimentation tank 23 by filtration. Reference numeral 25 denotes a backwash drainage storage tank for storing a large amount of backwash drainage generated when the sand filter 24 is backwashed. If the backwash drainage receiving tank 25 does not have enough space for installation, the backwash drainage should be discharged into the sludge thickening tank 26 of the suspended solids (sludge) separated in the settling tank 23. In some cases, the backwash drainage tank 25 may not be installed.

【0003】[0003]

【考案が解決しようとする課題】[Problems to be solved by the device]

前記したように従来の固液分離装置は、凝集沈澱槽の後段に砂濾過器を付設し た構造のものが一般的であった。しかしながら、この従来装置によった場合は原 水中の懸濁固形分を沈降分離させる凝集沈澱槽の占有する面積の割合が非常に大 きいという難点がある。 このため、この凝集沈澱槽を敷地面積を余り必要とせず、しかも分離固形分の 濃度が凝集沈澱の場合に較べ高濃度となり汚泥濃縮槽を削除することも可能とな る浮上分離装置に代替させることが考えられるが、浮上分離装置に代替させた場 合には次に述べるような欠点がある。 すなわち、当該浮上分離装置からキャリーオーバーしてきた固形分を濾過するの が砂濾過器であると、当該砂濾過器の逆洗時に大量の排水が生じ、逆洗排水受槽 、あるいは削除可能であった汚泥濃縮槽等の逆洗排水を受容できるだけの容積を もった槽を設置する必要がある。また、仮に砂濾過器の逆洗排水を浮上分離装置 の前段に位置する原水槽に戻すようにすると、逆洗時に生ずる排水が大量である ため、原水槽を無為に大型化しなければならないと共に、浮上分離装置に流入す る水中に含まれる懸濁固形分の濃度変動が著しく大となり、浮上分離装置におけ る固形分の浮上分離に悪影響を与えることに繋がる。 As described above, the conventional solid-liquid separation device generally has a structure in which a sand filter is attached to the subsequent stage of the coagulation sedimentation tank. However, this conventional apparatus has a drawback that the proportion of the area occupied by the coagulation sedimentation tank for sedimenting and separating the suspended solids in the raw water is very large. For this reason, this flocculation sedimentation tank can be replaced with a flotation separation device that does not require much site area, and the concentration of separated solids is higher than in the case of coagulation sedimentation, and the sludge concentration tank can be deleted. However, if the flotation device is replaced, it has the following drawbacks. That is, if the sand filter filters the solid content carried over from the flotation device, a large amount of wastewater is generated during backwashing of the sand filter, and it was possible to remove the backwash drainage tank or remove it. It is necessary to install a tank such as a sludge thickening tank with a volume that can receive backwash wastewater. Also, if the backwash wastewater from the sand filter is returned to the raw water tank located in the previous stage of the flotation separator, the amount of wastewater generated during backwashing will be large, and the raw water tank must be enlarged in size. Fluctuations in the concentration of suspended solids contained in water flowing into the flotation device become significantly large, which adversely affects the flotation separation of solids in the flotation device.

【0004】 そこで本考案は、前記した凝集沈澱槽の後段に砂濾過器を付設した従来の固液 分離装置の不具合点を解決し、沈澱槽に代えて設置スペースを余り必要としない 浮上分離装置にすると共に、従来の砂濾過器に代えて逆洗時に大量の排水が生じ ない長繊維束を充填してなる長繊維濾過装置を採用し、逆洗排水を浮上分離装置 の前段に戻しても原水の固形分負荷にそれほど変動を来さないようになした固液 分離装置を提供することを目的とするものである。Therefore, the present invention solves the problems of the conventional solid-liquid separator having a sand filter attached to the latter stage of the coagulating sedimentation tank, and does not require much installation space in place of the sedimentation tank. In addition, instead of the conventional sand filter, a long-fiber filter that is filled with a long-fiber bundle that does not generate a large amount of drainage during backwashing is used, and the backwash drainage can be returned to the front stage of the flotation separator. It is an object of the present invention to provide a solid-liquid separation device in which the solid content load of raw water does not fluctuate so much.

【0005】[0005]

【課題を解決するための手段】[Means for Solving the Problems]

前記目的を達成するための本考案の構成を詳述すれば、浮上分離装置の後段に 長繊維束を充填してなる長繊維濾過装置を付設し、当該長繊維濾過装置の逆洗時 に生ずる逆洗排水を浮上分離装置の前段に設置した原水槽に戻すための戻し管を 配設してなることを特徴とする固液分離装置であり、本考案装置によれば、従来 不可欠であった逆洗排水受槽及び場合によっては汚泥濃縮槽が不要となり、大幅 な敷地面積の削減が可能になると共に、浮上分離装置に対する固形分負荷の均一 化を図ることができるものである。 To describe the structure of the present invention for achieving the above-mentioned purpose in detail, a long-fiber filtering device filled with a long-fiber bundle is attached after the flotation / separation device, and occurs when the long-fiber filtering device is backwashed. This is a solid-liquid separation device characterized by being provided with a return pipe for returning the backwash drainage to the raw water tank installed in the preceding stage of the flotation separation device, and according to the device of the present invention, it was conventionally indispensable. It eliminates the need for a backwash drainage tank and, in some cases, a sludge thickening tank, and can greatly reduce the site area and also make the solid content load on the flotation separator uniform.

【0006】[0006]

【実施例】 以下、本考案固液分離装置の具体的構成を図示の実施例に基づき詳細に説明す る。 図1は本考案装置のフローの一例を示す概略図であり、図中1は処理対象の原 水を一時貯溜しておく原水槽、2は原水槽1から送られてくる原水中に硫酸アル ミニウムやポリ塩化アルミニウムのような凝集剤を添加して原水中の固形分を粗 大化するための凝集反応槽、3は当該凝集反応槽2から送られる懸濁固形分を含 んだ原水中に含気加圧水を注入させる加圧水槽である。[Embodiment] Hereinafter, a specific configuration of the solid-liquid separation device of the present invention will be described in detail with reference to the illustrated embodiment. FIG. 1 is a schematic diagram showing an example of the flow of the device of the present invention. In the figure, 1 is a raw water tank for temporarily storing raw water to be treated, and 2 is raw water sent from the raw water tank 1. A flocculation reaction tank for adding a flocculant such as minium or polyaluminum chloride to coarsen the solid content in the raw water, and 3 is the raw water containing the suspended solid content sent from the flocculation reaction tank 2. It is a pressurized water tank for injecting aerated pressurized water into.

【0007】 4は浮上分離装置であり、前記凝集反応槽2から浮上分離装置4に原水を送る 原水供給管5の管路途中で、前記加圧水槽3によって空気を加圧下で多量に溶解 させた加圧水が原水中に混合されるので、浮上分離装置4内において加圧水から 発生する気泡が原水中の懸濁固形分に付着して、当該固形分を原水より浮上分離 させるものである。なお、浮上分離装置4における浮上槽の水面に浮上した浮上 懸濁固形分(スカム)は、図示しない迴転掻取機等によって掻き取り、掻き取っ た懸濁固形分を浮上槽の水面の一部に設けた図示しない排出溝内に落とし込み、 これを排出手段13を通じて外部に排出処理する。Reference numeral 4 denotes a flotation separator, which feeds raw water from the flocculation reaction tank 2 to the flotation separator 4 midway in the raw water supply pipe 5, in which a large amount of air is dissolved under pressure by the pressurized water tank 3. Since the pressurized water is mixed with the raw water, the bubbles generated from the pressurized water in the flotation device 4 adhere to the suspended solids in the raw water, and the solids are floated and separated from the raw water. The floating suspended solids (scum) that have floated to the surface of the flotation tank in the flotation device 4 are scraped off by a not-shown scraping scraper, etc. It is dropped into a discharge groove (not shown) provided in the section, and is discharged to the outside through discharge means 13.

【0008】 6は前記浮上分離装置4の後段に付設した長繊維濾過装置である。当該長繊維 濾過装置6内には、たとえばアクリル繊維やポリエステル繊維、ポリアミド繊維 等の非撚単繊維の集合体である長さ0.4〜3.0mの長繊維束7を、その下端 を支持板14に固定すると共に上端を自由端とした状態で比較的密に直立状に充 填してあり、前記浮上分離装置4から流出する上澄水を下降流で通水することに よって上澄水に混じってキャリーオーバーしてくる懸濁固形分を捕捉し、濾過水 を下端に連通させた排出管8より取り出すものである。Reference numeral 6 denotes a long fiber filtration device attached to the latter stage of the floating separation device 4. A long fiber bundle 7 having a length of 0.4 to 3.0 m, which is an aggregate of non-twisted single fibers such as acrylic fibers, polyester fibers, and polyamide fibers, is supported in the long fiber filtering device 6 at its lower end. It is fixed to the plate 14 and is relatively densely filled in an upright state with the upper end being a free end. By passing the supernatant water flowing out from the floating separation device 4 in a downward flow, The suspended solids that are mixed and carry over are captured, and the filtered water is taken out through the discharge pipe 8 which is connected to the lower end.

【0009】 本考案はこのように、浮上分離装置4と長繊維濾過装置6を結合させると共に 、長繊維濾過装置6の逆洗時に生ずる逆洗排水を前記浮上分離装置4の前段に設 置した原水槽1に戻す戻し管9を配設したことを特徴とするものである。 すなわち、長繊維濾過装置6内に充填してある長繊維束7が懸濁固形分を捕捉 することによって当該濾過装置6内の圧力損失が増加した場合には、長繊維濾過 装置6の下方部より、たとえば圧縮空気を吹き込んで長繊維束7を攪拌揺動させ 、次いで逆洗水を上昇流にて送り込んで懸濁固形分を洗い出すが、長繊維濾過装 置の場合には長繊維束7の下端が支持板13に固定されているために高流速の圧 縮空気や逆洗水を流入させることができ、よって従来の砂濾過器に較べて短時間 で、かつ効率的に懸濁固形分を除去することが可能であり、一回の逆洗排水量は 従来の砂濾過器の場合と較べると1/4程度と少量で済む。したがって、長繊維 濾過装置6の逆洗時に生ずる逆洗排水を戻し管9を通じて浮上分離装置4の前段 にある原水槽1等に戻すとしても、無為に原水槽1の容量を大型化する必要がな く、また浮上分離装置の固形分負荷に大きな変動を与えることもないので、何ら 支障なく逆洗排水を浮上分離装置4の前段に戻すことが可能となるものである。In this way, according to the present invention, the flotation separation device 4 and the long fiber filtration device 6 are combined, and the backwash drainage generated when the long fiber filtration device 6 is backwashed is installed in the preceding stage of the flotation separation device 4. A return pipe 9 for returning to the raw water tank 1 is provided. In other words, when the long fiber bundle 7 filled in the long fiber filtering device 6 captures suspended solids and the pressure loss in the filtering device 6 increases, the lower part of the long fiber filtering device 6 is reduced. For example, compressed air is blown into the long fiber bundle 7 to agitate and oscillate, and then backwash water is sent in ascending flow to wash out suspended solids. In the case of a long fiber filtration device, the long fiber bundle 7 is used. Since the lower end of the filter is fixed to the support plate 13, high-velocity compressed air or backwash water can be flowed in, so that compared to the conventional sand filter, the suspended solids can be efficiently suspended. It is possible to remove the amount of water, and the amount of backwashing water discharged once can be reduced to about 1/4 as compared with the conventional sand filter. Therefore, even if the backwash drainage generated during backwashing of the long fiber filtration device 6 is returned to the raw water tank 1 or the like in the preceding stage of the flotation separation device 4 through the return pipe 9, it is necessary to enlarge the capacity of the raw water tank 1 without necessity. In addition, since the solid content load of the flotation separator is not greatly changed, it is possible to return the backwash drainage to the front stage of the flotation separator 4 without any trouble.

【0010】 その他、図中の10は原水槽1と凝集反応槽2を連通する配管、11は浮上分 離装置4によって懸濁固形分の除去された除濁水の一部(20〜30%)を加圧 水槽3へ供給するための供給管、12は長繊維濾過装置6の下端に連通させた排 出管8より分岐させた濾過水送り管であり、図示しない逆洗用水槽に濾過水を送 るためのものである。なお、排出管8を介して濾過水は図示しない処理水槽に送 られる。In addition, in the figure, 10 is a pipe that connects the raw water tank 1 and the flocculation reaction tank 2 to each other, and 11 is a part (20 to 30%) of the suspended water from which suspended solids have been removed by the flotation / separation device 4. Is a supply pipe for supplying water to the pressurized water tank 3, and reference numeral 12 is a filtered water feed pipe branched from a discharge pipe 8 communicating with the lower end of the long fiber filtration device 6. Is for sending. The filtered water is sent to a treated water tank (not shown) through the discharge pipe 8.

【0011】 次に、図2に示す従来型の固液分離装置と、図1に示す本考案に係る固液分離 装置との比較例を示す。 固形分濃度50mg/lの原水を、流量84.2m3 /hで、従来装置により固 液分離する場合において、凝集沈澱槽を通水LV(線速度)0.6m/h、砂濾 過器を通水LV7m/hとすると、必要となる設置面積は凝集沈澱槽が141m 2 (13.4mφ)、砂濾過器が12.3m2 (2.8mφ×2基)となった。 なお、砂濾過器のSS(懸濁固形分)捕捉量は3kgSS/m2 であり、逆洗は LV36m/h、10分間通水で行った。一回の逆洗排水量は88.7m3 であ り、また固形分濃度は416mg/lであった。処理水の水質は凝集沈澱槽の処 理水で固形分濃度21mg/l程度であり、砂濾過処理水で固形分濃度3mg/ l程度であった。凝集沈澱槽より排出される汚泥(分離固形分)は0.8%程度 の濃度であった。 更に、その他の付帯設備として図2中の原水槽が200m3 、凝集反応槽が2 1.3m3 、汚泥濃縮槽が10m3 、逆洗排水受槽が100m3 必要となる。Next, a comparative example of the conventional solid-liquid separation device shown in FIG. 2 and the solid-liquid separation device according to the present invention shown in FIG. 1 will be described. Raw water with a solid content concentration of 50 mg / l, a flow rate of 84.2 m3In the case of solid-liquid separation with a conventional device at a water flow rate of / m / h, if the coagulation sedimentation tank water flow LV (linear velocity) is 0.6 m / h and the sand filter water flow LV is 7 m / h, the required installation area is Coagulation sedimentation tank 141m 2 (13.4 mφ), sand filter is 12.3 m2(2.8 mφ x 2 units). The amount of SS (suspended solids) captured by the sand filter is 3 kgSS / m.2The backwash was carried out by passing water for 10 minutes at LV 36 m / h. The amount of backwash drainage once is 88.7m3And the solid content concentration was 416 mg / l. The water quality of the treated water was about 21 mg / l in the treated water in the coagulation-sedimentation tank, and about 3 mg / l in the solid content in the treated water after sand filtration. The sludge (separated solids) discharged from the coagulating sedimentation tank had a concentration of about 0.8%. In addition, as other auxiliary equipment, the raw water tank in Figure 2 is 200m3, Agglomeration reaction tank 2 1.3m3, Sludge thickening tank 10m3, Backwash drainage tank is 100m3Will be needed.

【0012】 これに対し、上記と同様の原水を、本考案装置により固液分離する場合は、浮 上分離装置の通水LVを4m/h以上、長繊維濾過装置の通水LVを40m/h 程度とすることができ、所要設置面積が浮上分離装置で28.3m2 (6mφ) 、長繊維濾過装置で2.3m2 (1.2mφ×2基)となり、上記従来型固液分 離装置の場合と較べて大幅な設置面積の削減が可能となった。 長繊維濾過装置のSS捕捉量は3.2kgSS/m2 であり、逆洗はLV100 m/h、5分間通水で行った。この場合の一回の逆洗排水量は22.6m3 、固 形分濃度320mg/lであり、浮上分離装置前段の原水槽(200m3 )に戻 し管を介して戻しても、浮上分離装置に対する固形分負荷変動は最大で流入原水 の1.5倍程度に抑えられ、処理水質は浮上分離処理水で固形分濃度19mg/ l程度、長繊維濾過処理水で3mg/l程度と、従来型装置による処理水質と同 等であった。分離固形分濃度は大半の浮上操作によって排出されるもの(スカム )が3.2%程度、一部底泥として排出されるものが0.9%程度であった。 このため、その他の付帯設備として加圧水槽1.35m3 が増えるものの、従来 型装置と較べて、原水槽及び凝集反応槽の大きさを増すことなく、逆洗排水受槽 、汚泥濃縮槽を削除することが可能であり、このように全体としてみても大幅な 設置面積の削減が可能となった。On the other hand, when solid-liquid separation of the same raw water as described above is performed by the device of the present invention, the water flow LV of the flotation separator is 4 m / h or more, and the water flow LV of the long fiber filtration device is 40 m / h. The required installation area is 28.3 m 2 (6 mφ) for the flotation separator and 2.3 m 2 (1.2 mφ × 2 units) for the long fiber filtration device. Compared to the case of the device, the installation area can be reduced significantly. The SS capture amount of the long fiber filtration device was 3.2 kg SS / m 2 , and the backwash was performed by passing water through the LV 100 m / h for 5 minutes. In this case, the amount of backwash drainage per wash was 22.6 m 3 , and the solid content concentration was 320 mg / l. Even if it was returned to the raw water tank (200 m 3 ) in the previous stage of the flotation separator, it was returned to the flotation separator. The fluctuation of the solid content load against water is suppressed to a maximum of about 1.5 times that of the inflowing raw water. The quality of treated water by the equipment was the same. The concentration of separated solids was about 3.2% in most of the floating operations (scum) and about 0.9% in some of the bottom sludge. Therefore, although 1.35 m 3 of pressurized water tank will be added as other auxiliary equipment, the backwash drainage tank and sludge thickening tank will be deleted without increasing the sizes of the raw water tank and the coagulation reaction tank compared to the conventional equipment. This makes it possible to reduce the installation area drastically as a whole.

【0013】 また、前記と同様の原水の処理に、浮上分離装置の後段に砂濾過器を付設して 図1の場合と同様に戻し管を介し砂濾過器逆洗排水を原水槽に戻すようにして逆 洗排水受槽の削除を狙ったが、逆洗排水受容のために原水槽の大きさを200m 3 から300m3 に大型化する必要性が生じ、またこのように原水槽を大型化し ても浮上分離装置に対する固形分負荷の変動が最大で流入原水の3倍強の値を示 すものとなり、そのため、良好な浮上分離処理が行えなかった。なお、この場合 の他の操作条件は上記各操作条件に準じた。In addition, for the same treatment of raw water as described above, a sand filter is attached to the rear stage of the flotation device to return the sand filter backwash drainage to the raw water tank through the return pipe as in the case of FIG. The aim was to remove the backwash drainage receiving tank, but the size of the raw water tank was set to 200 m in order to receive the backwashing drainage. 3 From 300m3It is necessary to increase the size of the raw water tank, and even if the raw water tank is increased in size in this way, the fluctuation of the solid content load on the flotation separator is the maximum and shows a value that is more than three times the inflowing raw water. Floating separation processing could not be performed. The other operating conditions in this case were in accordance with the above operating conditions.

【0014】[0014]

【考案の効果】[Effect of device]

以上のように、本考案固液分離装置は浮上分離装置の後段に長繊維束を充填し てなる長繊維濾過装置を付設すると共に、当該長繊維濾過装置の逆洗時に生ずる 逆洗排水を浮上分離装置の前段に設置した原水槽に戻すための戻し管を配設して なるもので、従来不可欠であった逆洗排水受槽が不要となり、浮上分離装置及び 長繊維濾過装置自体が大きな設備面積を要しないことと相俟って大幅な敷地面積 の削減が可能になる。また、長繊維濾過装置の逆洗時に生ずる逆洗排水の量が従 来の砂濾過器の場合と較べて格段に少ないので、逆洗排水を原水槽に戻した場合 にも浮上分離装置に対する固形分負荷はそれ程増大せず、したがって浮上分離処 理を何ら支障なく行うことができる。 As described above, the solid-liquid separation device of the present invention is provided with a long fiber filtering device, which is filled with long fiber bundles, at the latter stage of the flotation device, and the backwash drainage generated during backwashing of the long fiber filtering device is floated. Since a return pipe for returning to the raw water tank installed in the previous stage of the separation device is installed, the backwash drainage receiving tank, which was indispensable in the past, is not required, and the flotation separation device and the long fiber filtration device itself have a large equipment area. Combined with the fact that it does not require, it is possible to significantly reduce the site area. In addition, since the amount of backwash wastewater generated during backwashing of the long fiber filter is significantly smaller than that of the conventional sand filter, even when the backwash wastewater is returned to the raw water tank, the solid content for the flotation separator is reduced. The partial load does not increase so much, and therefore the levitation separation process can be performed without any problems.

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

【図1】本考案に係る固液分離装置のフローの一例を示
す概略図である。
FIG. 1 is a schematic diagram showing an example of a flow of a solid-liquid separation device according to the present invention.

【図2】従来型固液分離装置のフローの一例を示す概略
図である。
FIG. 2 is a schematic diagram showing an example of a flow of a conventional solid-liquid separation device.

【符号の説明】[Explanation of symbols]

1:原水槽 2:凝集反応槽 3:加圧水槽 4:浮上分離装
置 5:原水供給管 6:長繊維濾過
装置 7:長繊維束 8:排出管 9:戻し管
1: Raw water tank 2: Coagulation reaction tank 3: Pressurized water tank 4: Floating separation device 5: Raw water supply pipe 6: Long fiber filtration device 7: Long fiber bundle 8: Discharge pipe 9: Return pipe

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 B01D 29/62 36/00 6953−4D C02F 9/00 Z 7446−4D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Internal reference number FI Technical display location B01D 29/62 36/00 6953-4D C02F 9/00 Z 7446-4D

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 【請求項1】 浮上分離装置の後段に長繊維束を充填し
てなる長繊維濾過装置を付設し、当該長繊維濾過装置の
逆洗時に生ずる逆洗排水を浮上分離装置の前段に設置し
た原水槽に戻すための戻し管を配設してなることを特徴
とする固液分離装置。
1. A raw fiber in which a long fiber filtration device filled with a long fiber bundle is attached to a stage subsequent to the flotation device, and backwash drainage generated during backwashing of the long fiber filtration device is placed in a stage preceding the flotation device. A solid-liquid separation device comprising a return pipe for returning to the water tank.
JP7001992U 1992-09-14 1992-09-14 Solid-liquid separation device Pending JPH0629683U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7001992U JPH0629683U (en) 1992-09-14 1992-09-14 Solid-liquid separation device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7001992U JPH0629683U (en) 1992-09-14 1992-09-14 Solid-liquid separation device

Publications (1)

Publication Number Publication Date
JPH0629683U true JPH0629683U (en) 1994-04-19

Family

ID=13419483

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7001992U Pending JPH0629683U (en) 1992-09-14 1992-09-14 Solid-liquid separation device

Country Status (1)

Country Link
JP (1) JPH0629683U (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56152780A (en) * 1980-04-30 1981-11-26 Sanken Setsubi Kogyo Kk Device for waste water treatment
JPH02227189A (en) * 1989-03-01 1990-09-10 Japan Organo Co Ltd Biological treatment apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56152780A (en) * 1980-04-30 1981-11-26 Sanken Setsubi Kogyo Kk Device for waste water treatment
JPH02227189A (en) * 1989-03-01 1990-09-10 Japan Organo Co Ltd Biological treatment apparatus

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