JPH0767522B2 - Circulating water treatment equipment - Google Patents
Circulating water treatment equipmentInfo
- Publication number
- JPH0767522B2 JPH0767522B2 JP63067561A JP6756188A JPH0767522B2 JP H0767522 B2 JPH0767522 B2 JP H0767522B2 JP 63067561 A JP63067561 A JP 63067561A JP 6756188 A JP6756188 A JP 6756188A JP H0767522 B2 JPH0767522 B2 JP H0767522B2
- Authority
- JP
- Japan
- Prior art keywords
- filter
- water
- particles
- flocs
- coagulant
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 69
- 239000002245 particle Substances 0.000 claims description 57
- 238000000034 method Methods 0.000 claims description 45
- 239000000701 coagulant Substances 0.000 claims description 26
- 239000000463 material Substances 0.000 claims description 23
- 238000011001 backwashing Methods 0.000 claims description 11
- GPRLSGONYQIRFK-UHFFFAOYSA-N hydron Chemical compound [H+] GPRLSGONYQIRFK-UHFFFAOYSA-N 0.000 claims description 11
- 239000003795 chemical substances by application Substances 0.000 claims description 9
- 238000000746 purification Methods 0.000 claims description 8
- 238000001914 filtration Methods 0.000 claims description 6
- 230000007062 hydrolysis Effects 0.000 claims description 5
- 238000006460 hydrolysis reaction Methods 0.000 claims description 5
- 238000002156 mixing Methods 0.000 claims description 5
- 229920000592 inorganic polymer Polymers 0.000 claims description 2
- 239000000356 contaminant Substances 0.000 description 11
- 244000144992 flock Species 0.000 description 10
- 239000003344 environmental pollutant Substances 0.000 description 8
- 231100000719 pollutant Toxicity 0.000 description 8
- 239000007788 liquid Substances 0.000 description 5
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 4
- 229910052782 aluminium Inorganic materials 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- 239000000853 adhesive Substances 0.000 description 3
- 230000001070 adhesive effect Effects 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 239000012141 concentrate Substances 0.000 description 3
- 239000013505 freshwater Substances 0.000 description 3
- 238000002347 injection Methods 0.000 description 3
- 239000007924 injection Substances 0.000 description 3
- 239000011236 particulate material Substances 0.000 description 3
- 239000005909 Kieselgur Substances 0.000 description 2
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical class [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 description 2
- 239000012752 auxiliary agent Substances 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000004931 aggregating effect Effects 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 1
- 239000003830 anthracite Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000003311 flocculating effect Effects 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000008236 heating water Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 238000010030 laminating Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000003607 modifier Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 230000005654 stationary process Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000011800 void material Substances 0.000 description 1
Landscapes
- Filtration Of Liquid (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Description
【発明の詳細な説明】 [産業上の利用分野] 本発明は、循環式水処理装置における過機処理方法に
かかり、特に、前記過機に比較的簡単な処理を施すこ
とにより前記過機における過材粒子間に形成される
過材空隙より小さい微粒子(濁質成分)をも捕捉でき
るようにして過能力を著しく向上させるようにしたも
のに関する。Description: TECHNICAL FIELD The present invention relates to an over-machine treatment method for a circulating water treatment apparatus, and in particular, for over-machine treatment by performing a relatively simple treatment on the over-machine. The present invention relates to a device capable of capturing even fine particles (suspended components) smaller than the voids of the excess material formed between the particles of the excess material to remarkably improve the overcapacity.
[従来の技術] 一般に、プールや浴場等においては、プール等の用水溜
の用水を浄化するために循環式水処理装置が用いられ
る。[Prior Art] Generally, in pools, baths, and the like, a circulation type water treatment device is used to purify water in a water reservoir such as a pool.
この循環式水処理装置には、通常、被処理用水中の汚染
粒子を捕捉する過機が含まれている。This circulating water treatment device usually includes an excess machine for trapping contaminant particles in the water to be treated.
この過機としては、従来から、数種の粒径のアンスラ
サイト等の石炭系過材もしくは砂等を多層に重ねて形
成し、所定範囲の大きさの汚染粒子を捕捉できるように
したいわゆる砂過機や、あるいは、これより過精度
にすぐれるケイソウ土過機等が用いられていた。Conventionally, this type of so-called sand is formed by stacking coal-based waste materials such as anthracite of several kinds of particle diameters or sands in multiple layers so that pollutant particles of a predetermined size can be captured. A diatomaceous earthmoving machine or the like which is superior in accuracy or more accurate than this was used.
しかしながら、このような過機を用いただけでは、汚
染の激しいプールや浴場等の被処理用水を十分に浄化す
ることができず、過機で過されない粒子が循環を繰
り返すことによって濃縮され、透明度の低下を来して利
用者の不評を買っており、これまで最も過精度が高い
とされている前記ケイソウ土過機を用いた場合でも利
用者密度が大きい場合には事情は同じであった。このよ
うに、プールや浴場等の現場においては、透明度の低下
という形ではっきり目視できる程コロイド物質が過機
に捕捉されずに再循環して濃縮されているのが実状であ
る。However, by simply using such an equipment, it is not possible to sufficiently purify the water to be treated such as in a pool or a bath where the pollution is severe, and the particles that are not passed by the equipment are concentrated by repeating the circulation and the transparency of The situation has been the same when the user density is high even when the diatomaceous earthmoving machine, which is said to have the highest over-accuracy so far, is used because of the drop in popularity and the user's unpopularity. As described above, in the field such as a pool or a bathhouse, the colloidal substance is recirculated and concentrated without being unnecessarily trapped so that it is clearly visible in the form of a decrease in transparency.
ところで、この過機は、過材粒子間に形成される
過材空隙より大きい汚染粒子を捕捉するものであるか
ら、該過機に使用する過材を選定して過材空隙の
極めて小さいものにすることにより極微細汚染粒子をも
捕捉させることは原理的には可能である。By the way, since this over-capture captures contaminant particles larger than the over-material voids formed between the over-material particles, the over-material used in the over-machine is selected to make the over-material void extremely small. By doing so, it is possible in principle to capture ultrafine pollutant particles.
しかしながら、実際上は、プール等で生ずる汚染粒子に
は様々の物質が様々の組成もしくは結合状態にあって、
その大きさもまちまちであり、しかも、大量に生ずるの
が普通である。したがって、汚染粒子のうちの最小の粒
子を捕捉できるような過材を用いるとたちまち目ずま
りしてしまうとともに、循環速度が遅くなるため汚染速
度に応じた浄化速度を確保できなくなって実用にならな
い。このため、単に過材粒子間の空隙の小さいものを
用いるという観点だけからは上記問題の有効な解決策は
何等導き出すことができなかった。However, in practice, pollutant particles generated in pools etc. have various substances in various compositions or binding states,
The size is also variable, and it usually occurs in large quantities. Therefore, if an excess material that can capture the smallest of the pollutant particles is used, it will instantly become clogged up, and the circulation speed will slow down, so it will not be possible to secure a purification speed according to the pollutant speed and it will not be practical. . For this reason, no effective solution to the above problem could be derived from the viewpoint of simply using particles having a small gap between the particles of the excess material.
そこで、近年にいたり、過機は従来と同じものを用
い、一方、この過機で捕捉できなかった微細汚染粒子
については、前記被処理用水に定期的に凝集剤及びアル
カリ助剤等を投入混和して凝集させ、微細粒子の凝集体
である、いわゆる、フロックを形成させてこのフロック
を前記過機によって捕捉することで除去する方法が種
々試みられている。Therefore, in recent years, the same machine as the conventional machine is used, while for the fine pollutant particles that cannot be captured by the machine, a coagulant, an alkaline auxiliary agent, etc. are periodically added to the water to be treated and mixed. Then, various methods have been tried in which a flocculation, which is an agglomerate of fine particles, is formed and the flocs are captured by the above machine to remove the flocs.
この方法の典型例として、いわゆるプレフロック法が知
られている。この方法は、前記過機に捕捉された汚染
物が一定以上滞積して入口と出口との圧力差が一定値位
以上になったとき、被処理用水の循環を一時止めて前記
過機に逆方向から水を流して前記汚染物を除去するこ
とにより過能力を再生するために行われる逆洗操作の
際に行われるもので、この逆洗操作は、具体的には、
過機に逆方向から被処理用水を流して汚染物を排出する
逆洗工程、この逆洗工程を停止させて流路を元に戻す静
止工程及び順方向から被処理用水を流して残留汚染物を
排出する洗浄工程からなるが、この洗浄工程において前
記過機の手前に設けられたフロック形成槽またはバラ
ンシングタンク内にある被処理用水にアルミニウム系凝
集剤とアルカリ助剤の投入混和を行なってフロックを形
成させ、これを前記過機に流入させることにより、該
過機の過槽表面に逆洗可能なフロックを積層させ、
しかる後、本来の循環による浄化処理を再開するように
したものである。A so-called preflock method is known as a typical example of this method. In this method, when the contaminants trapped in the excess machine accumulate for a certain amount or more and the pressure difference between the inlet and the outlet exceeds a certain value, the circulation of the water to be treated is temporarily stopped and It is performed during the backwashing operation performed to regenerate the overcapacity by flowing water from the opposite direction to remove the contaminants, and this backwashing operation is specifically
Backwashing process in which water to be treated is discharged from the opposite direction to discharge contaminants, static process in which this backwashing process is stopped and the flow path is restored to its original state, and residual contaminants are caused to flow water to be treated in the forward direction In this cleaning step, the floc forming tank or the balancing tank in front of the machine is mixed with the aluminum-based coagulant and the alkaline auxiliary agent in the water to be treated in the cleaning step. Is formed and is allowed to flow into the excess machine, thereby stacking backwashable flocs on the surface of the excess tank of the excess machine,
After that, the purification process by the original circulation is restarted.
すなわち、この方法の原理は、過機の過槽表面にフ
ロックを積層させることにより、過材粒子間の空隙を
狭めて微細汚染粒子をも捕捉できるようにするととも
に、汚染粒子が一定以上滞積したら逆洗できるようにす
ることをめざしたものである。In other words, the principle of this method is that by stacking flocs on the surface of the excess tank of the machine, it is possible to narrow the gaps between the particles of the excess material and capture even the fine contaminant particles, and the contaminant particles are accumulated for a certain amount or more. After that, the aim is to be able to backwash.
また、このほかにも、凝集剤を過機の手前から短時間
の間に大量に投入したり、あるいは、小流量のポンプで
定量の凝集剤を連続して注入したり、あるいは、30分以
上の比較的長時間に渡って定量注入したりする方法が試
みられているが、いずれも、原理的には前記プレフロッ
ク法と同じものである。In addition to this, a large amount of coagulant may be added in a short time from just before the machine, or a fixed amount of coagulant may be continuously injected with a small flow rate pump, or 30 minutes or more. Although a method of injecting a fixed amount over a relatively long time has been attempted, both methods are, in principle, the same as the pre-floc method.
[発明が解決しようとする課題] ところが、上述の従来の方法は、いずれも従来の過機
のみを用いるものに比較すると、より小さい粒子の汚染
物をより多く捕捉するという観点からは一定の効果が認
められるものの、透明度低下に対しては十分な効果を得
ることができず、場合によっては、この処理が原因でか
えって濁りを増すという事例も少なからず生じていた。[Problems to be Solved by the Invention] However, each of the above-mentioned conventional methods has a certain effect from the viewpoint of capturing a larger amount of pollutants of smaller particles, as compared with a method using only a conventional machine. Although it was observed, it was not possible to obtain a sufficient effect on the decrease in transparency, and in some cases, this treatment caused rather an increase in turbidity.
すなわち、本発明者等の知見によれば、前記プレフロッ
ク法は、原理的に過材粒子間の空隙を狭めることによ
り、より細かい汚染粒子を捕捉しようとするものであ
り、その必然的結果として、狭められた空隙よりもさら
に微細な粒子が通過してきた場合には捕捉不可能であ
り、一般に、濁りの原因の多くは、このような過では
捕捉できない極微細なコロイド状濁質成分によるもので
あるためであると理解される。That is, according to the knowledge of the present inventors, the pre-flock method is intended to trap finer contaminated particles by narrowing the voids between the particles of the over-materials in principle, and the inevitable result thereof. , When particles finer than the narrowed voids have passed, they cannot be trapped, and in general, most of the causes of turbidity are due to extremely fine colloidal turbidity components that cannot be trapped in such excess. It is understood that it is because.
また、前記プレフロック法等による処理が原因でかえっ
て濁りが増すのは、前記プレフロック法では高濃度での
加水分解であるために、また、前記定量注入法では低能
度でかつ高いpH状態での加水分解であるために、いずれ
も軟弱なフロックが形成され易く、この軟弱なフロック
が過槽中で細かく分解されて過槽を通過してプール
等に混入したり、あるいは、投入された凝集剤のうちフ
ロック形成の遅いものや余分となったものがプール等に
侵入して該プール内でフロックを形成してフロックによ
る濁りを生じさせるためであると理解される。Further, the reason why the turbidity increases due to the treatment by the prefloc method or the like is that the prefloc method is hydrolysis at a high concentration, and the quantitative injection method has low efficiency and a high pH state. Due to the hydrolysis of the above, soft flocs are likely to be formed, and the soft flocs are finely decomposed in the over tank and passed through the over tank to be mixed into the pool or the like, or the flocculated It is understood that the agent, which has a slow floc formation or an extra agent, penetrates into the pool or the like to form flocs in the pool to cause turbidity due to the flocs.
さらに、前記プレフロック法等による処理は、過材粒
子間の空隙を狭めるものであるため、この処理後は過
機の入口と出口との圧力差が大きくなり、被処理用水の
循環流量の確保に不利となるとともに、捕捉汚染粒子が
過槽表面部に集中して短時間でめずまりを起し易く、
逆洗頻度を高くする必要が生ずるという欠点もある。Further, since the treatment by the pre-flock method or the like narrows the voids between the particles of the excess material, the pressure difference between the inlet and the outlet of the excess machine becomes large after this treatment, and the circulation flow rate of the water for treatment is secured. In addition to being disadvantageous to the above, trapped pollutant particles tend to concentrate on the surface of the excess tank and easily settle in a short time,
There is also a drawback that it is necessary to increase the frequency of backwashing.
本発明の目的は、上述の欠点を除去した循環式水処理装
置における過機処理方法を提供することにある。It is an object of the present invention to provide an over-treatment method in a circulating water treatment apparatus, which eliminates the above-mentioned drawbacks.
[課題を解決するための手段] 本発明は、本発明者等がプール等の被処理用水の汚染物
の性状、該汚染物と凝集剤との反応メカニズム及び濁り
の原因等を解明する研究過程において得られた知見に基
づいてなされたものである。[Means for Solving the Problems] The present invention is a research process by which the present inventors elucidate the properties of contaminants of water to be treated such as pools, the reaction mechanism between the contaminants and a coagulant, and the cause of turbidity. It was made based on the knowledge obtained in.
すなわち、本発明者等の研究によれば、例えば、硫酸ア
ルミニウムやポリ塩化アルミニウム等のアルミニウム系
凝集剤の加水分解した水酸化物の性状は、凝集剤の内容
成分はもとより、析出時直前での混和方法、凝集剤濃
度、凝集剤周囲の水の水素イオン濃度に依存して様々な
ものとなり、例えば、これら条件の相違により、凝析し
たフロックが、Al(OH)3で示される水酸化アルミニウ
ムを主としたものとなった場合と、一般的にAl8(CH)
20 4+で示される多荷電アルミニウムポリマーを主とした
ものとなった場合とでは、フロックの平均径は当然のこ
とながら、凝集力、凝集濁質選択性、剪断応力、付着力
までも際立った差異があるという知見が得られている。That is, according to the studies by the present inventors, for example, the properties of the hydrolyzed hydroxide of an aluminum-based coagulant such as aluminum sulfate or polyaluminum chloride are not only in the content components of the coagulant but also immediately before the precipitation. Depending on the mixing method, the coagulant concentration, and the hydrogen ion concentration of the water around the coagulant, various things will occur. For example, due to the difference in these conditions, coagulated flocs are aluminum hydroxides represented by Al (OH) 3. And mainly Al 8 (CH)
In the case of a multi-charged aluminum polymer represented by 20 4+ those primarily, of course average diameter of flocs, cohesion, cohesion suspended solid selectivity, shear stress, outstanding even adhesion It has been found that there are differences.
本発明は、このような知見に基づき、前記従来のプレフ
ロック法の原理、すなわち、過槽表面にフロックを積
層させて過材粒子間の空隙を狭めるという原理と全く
異なる原理、すなわち、過材粒子自体の表面に、過
材粒子間の空隙よりも小さい粒径を有し、付着力が強
く、機械的強度にすぐれ、さらに凝集力の強いフロック
を形成し、このフロックに濁質成分を凝集させるという
新規な原理を案出し、この原理により、従来の原理では
捕捉不可能であったコロイド状濁質成分をも確実に捕捉
できるようにしたものであって、以下の構成を有する。Based on such knowledge, the present invention is based on the above-mentioned conventional pre-floc method, that is, a principle completely different from the principle of laminating flocs on the surface of a tank to narrow the gaps between particles of the material, that is, the material On the surface of the particles themselves, a particle size smaller than the voids between the particles of the oversize material is formed, forming a floc with strong adhesion, excellent mechanical strength, and strong cohesive force. The present invention has devised a new principle of making it possible to surely capture even the colloidal suspended matter component which could not be captured by the conventional principle, and has the following constitution.
用水溜の被処理水を少なくとも濾過機に流通させて浄化
した後前記用水溜に戻すようにした循環式水処理装置に
おける前記濾過機の濾過能力を向上させる濾過機処理方
法であって、 循環浄化の開始前又は濾過機の逆洗時又は循環浄化途中
における所定の時期に、前記用水溜から濾過機に用水を
導く流路を通じて該流路を流通する用水中に無機凝集剤
と水素イオン濃度調節剤とを数十秒ないし数分の間だけ
混入し、 前記混入の際に、前記無機凝集剤の混入量が5〜200mg/
lの範囲内でかつ混入された無機凝集剤の加水分解によ
って低下するpHが5以下にならないようにこれ等の混入
量を加減し、 前記流路を流通する用水中には前記濾過機の濾過材粒子
及び濾過材粒子間の間隙より大きいフロックが凝集せず
に、該用水が濾過材粒子の表面に接触したときに該濾過
材粒子表面に該濾過材粒子及び濾過材粒子間の間隙より
小さい粒径を有しかつ静電気的凝集力を有する無数の無
機ポリマーフロックが付着するようにして前記濾過機の
濾過材粒子に静電気的凝集力をもたせることにより該濾
過機の濾過能力を向上させるようにしたことを特徴とす
る循環式水処理装置における濾過機処理方法。A filter treatment method for improving the filtering ability of the filter in a circulating water treatment device, wherein the water to be treated in a water reservoir is at least passed through a filter for purification and then returned to the water reservoir. Before the start of, or at a predetermined time during the backwashing of the filter or during the circulation purification, the inorganic coagulant and the hydrogen ion concentration control in the water flowing through the channel through the channel guiding the water from the water reservoir to the filter The agent is mixed for several tens of seconds to several minutes, and the mixing amount of the inorganic coagulant is 5 to 200 mg /
Within the range of 1 and adjusting the amount of these mixed so that the pH which is lowered by the hydrolysis of the mixed inorganic coagulant does not become 5 or less, the water in the channel is filtered by the filter of the filter. A gap larger than the gap between the filter particles and the filter particles is smaller than the gap between the filter particles when the water contacts the surface of the filter particles without flocs being aggregated. In order to improve the filtering ability of the filter by imparting electrostatic cohesive force to the filter material particles of the filter so that a myriad of inorganic polymer flocs having a particle size and having electrostatic cohesive force are attached. A method for treating a filter in a circulating water treatment device, characterized in that
[作用] 前記構成によれば、前記水素イオン濃度調節剤と無機凝
集剤とを混入した被処理用水を前記過機に流通させる
ことにより、該過機の全槽にある各過材粒子自体の
表面にこれら過材粒子間の空隙よりも小さい粒径を有
し、付着力が強く、機械的強度にすぐれ、さらに凝集力
の強いフロックが形成される。[Operation] According to the above configuration, the water to be treated in which the hydrogen ion concentration modifier and the inorganic coagulant are mixed is circulated to the excess machine, whereby the excess material particles themselves in all tanks of the excess machine are On the surface, a floc having a particle size smaller than the voids between the particles of the oversize material, strong adhesion, excellent mechanical strength, and strong cohesive force is formed.
これにより、被処理用水をこの過機に流通させると、
該被処理用水中に含まれるコロイド状濁質成分が前記
過材粒子表面に形成された凝集力の強いフロックに捕捉
され、該フロックの一部となって除去される。しかも、
このフロックは付着力が強くかつ機械的強度も強いの
で、容易に離脱するようなことがない。As a result, when the water to be treated is circulated through this machine,
The colloidal turbidity component contained in the water to be treated is captured by the flocs having strong cohesive force formed on the surface of the particulate material, and is removed as a part of the flocs. Moreover,
Since this flock has a strong adhesive force and a high mechanical strength, it does not easily come off.
したがって、従来のプレフロック法等では原理的に捕捉
不可能であったコロイド状濁質成分をも確実に捕捉・除
去できる。Therefore, it is possible to reliably capture and remove the colloidal suspended matter component that could not be captured in principle by the conventional prefloc method or the like.
さらに、この方法は、過材粒子自体の表面に細かいフ
ロックを形成させるだけであり、過材粒子間の空隙は
従来のプレフロック法等に比較して著しく広く確保でき
るから、被処理用水の循環流量の確保に有利であるとと
もに、捕捉汚染粒子が過槽表面部に集中して短時間で
めずまりを起すようなこともなく、逆洗頻度も少なくて
すむ。In addition, this method only forms fine flocs on the surface of the oversize particles themselves, and the voids between the oversize particles can be remarkably wide compared to the conventional pre-floc method, etc. This is advantageous in securing a flow rate, and trapped contaminated particles do not concentrate on the surface of the excess tank to cause accumulation in a short time, and the frequency of backwashing is low.
[実施例] 第1図は本発明の実施例にかかる循環式水処理装置にお
ける過機処理方法を実施するための装置の構成を示す
ブロック図である。[Embodiment] FIG. 1 is a block diagram showing the configuration of an apparatus for carrying out an excess machine treatment method in a circulating water treatment apparatus according to an embodiment of the present invention.
以下、第1図を参照にしながら本発明の実施例にかかる
循環式水処理装置における過機処理方法を説明する。Hereinafter, with reference to FIG. 1, an over-treatment method in the circulating water treatment apparatus according to the embodiment of the present invention will be described.
図中符号1はプールその他の用水溜であり、この用水溜
1には被処理用水2が貯水されている。In the figure, reference numeral 1 is a pool or other water reservoir, and the water to be treated 2 is stored in the water reservoir 1.
前記用水溜1の下部には吸込用配管3が、上部には還水
用配管4がそれぞれ接続されている。A suction pipe 3 is connected to the lower portion of the water reservoir 1, and a return water pipe 4 is connected to the upper portion.
前記吸込用配管3は、その中間部に前記用溜1側からみ
て順に分岐手段5及び循環ポンプ6が接続され、しかる
後、多方弁7に接続され、また、前記還水用配管4は直
接前記多方弁7に接続されている。The suction pipe 3 is connected to a branching means 5 and a circulation pump 6 in the middle of the suction pipe 3 in this order, and then connected to a multi-way valve 7, and the return water pipe 4 is directly connected to the suction pipe 3. It is connected to the multi-way valve 7.
さらに、前記分岐手段5には2つの分岐ポート5a及び5b
が設けられており、これら分岐ポート5a及び5bには開閉
弁8及び9の一方の接続口がそれぞれ接続されていると
ともに、これら開閉弁8及び9の他方の接続口は給液用
配管10及び11の一端に接続されている。そして、これら
給液用配管10及び11の他端は、凝集剤12を貯液してある
凝集剤貯液用タンク13及び水素イオン濃度調節剤14を貯
液してある水素イオン濃度調節剤貯液用タンク15の下部
にそれぞれ接続されており、これら各給液用配管10及び
11の中間にはそれぞれ流量調節弁16及び17が設けられて
いる。Further, the branching means 5 has two branch ports 5a and 5b.
Is provided, and the branch ports 5a and 5b are connected to one connection ports of the on-off valves 8 and 9, respectively, and the other connection ports of the on-off valves 8 and 9 are connected to the liquid supply pipe 10 and It is connected to one end of 11. The other ends of the liquid supply pipes 10 and 11 are provided with a coagulant storage tank 13 in which a coagulant 12 is stored and a hydrogen ion concentration control agent storage in which a hydrogen ion concentration control agent 14 is stored. They are connected to the lower part of the liquid tank 15, and each of these liquid supply pipes 10 and
Flow control valves 16 and 17 are provided in the middle of 11, respectively.
また、前記多方弁7には原水管18、水管19及び排出管
20の一端がそれぞれ接続されている。前記原水管18及び
水管19は、それぞれの他端部が過機21の被処理用水
注入口21a及び過水排出口21bに接続されているととも
に、前記排出管20の他端部は図示しない外部廃液処理槽
等に接続されるようになっている。なお、前記過機21
内には種々の粒径を有する過材粒子22が多層にわけら
れて積層されている。The multi-way valve 7 has a raw water pipe 18, a water pipe 19 and a discharge pipe.
One end of each 20 is connected. The other ends of the raw water pipe 18 and the water pipe 19 are connected to the water to be treated inlet 21a and the overwater discharge port 21b of the excess machine 21, and the other end of the discharge pipe 20 is not shown outside. It is designed to be connected to a waste liquid treatment tank. In addition, the above-mentioned machine 21
Inside, the particles 22 of various particles having various particle sizes are divided into multiple layers and laminated.
上述の構成において、通常の循環による水処理を行って
いる場合、あるいは、この処理を停止して逆洗操作を行
う際の逆洗工程及び静止工程を行っている場合において
は前記開閉弁8及び9は閉じておく。In the above-mentioned configuration, when the water treatment by the normal circulation is performed, or when the backwashing step and the stationary step when the treatment is stopped and the backwashing operation is performed, the opening / closing valve 8 and Keep 9 closed.
本実施例にかかる方法は、前記静止工程の次の工程であ
る洗浄工程において実施する。The method according to the present embodiment is carried out in the cleaning process, which is a process subsequent to the stationary process.
すなわち、まず、前記多方弁7を操作して前記水管19
が前記排出管20に接続されるようにし、次に、前記開閉
弁8及び9を開き、同時に前記循環用ポンプ6を作動さ
せて前記過機21に前記凝集剤12及び水素イオン調節剤
14が混入された被処理用水を数分間流通させる。That is, first, the multi-way valve 7 is operated to operate the water pipe 19
Is connected to the discharge pipe 20, and then the opening / closing valves 8 and 9 are opened, and at the same time, the circulation pump 6 is operated so that the coagulant 12 and the hydrogen ion regulator are added to the excess machine 21.
The water to be treated mixed with 14 is circulated for several minutes.
この場合、前記流量調節弁16を調節して前記被処理用水
中の凝集剤の濃度が5〜200mg/lとなるようにする。こ
のとき、凝集剤の加水分解により水素イオン濃度が変化
するが、前記流量調節弁17を調節してこの変化速度が所
望の値となり、かつ、5pH以下にならないようにする。In this case, the flow rate control valve 16 is adjusted so that the concentration of the coagulant in the water for treatment becomes 5 to 200 mg / l. At this time, the hydrogen ion concentration changes due to the hydrolysis of the aggregating agent, but the flow rate adjusting valve 17 is adjusted so that the changing rate becomes a desired value and does not fall below 5 pH.
この操作により、前記過機21内における各過材粒子
22の表面に、有機濁質凝集力の強い多荷電アルミニウム
ポリマーのフロックや無機濁質凝集力の強い凝析水酸化
アルミニウムのフロック等の種々の性状のフロックであ
って、付着力、剪断応力(機械的強度)の極めて強い細
かいフロックが形成される。By this operation, each excess material particle in the excess machine 21
On the surface of 22, there are various properties of flocs such as those of polycharged aluminum polymer with strong organic turbidity cohesive force and flocs of coagulated aluminum hydroxide with strong inorganic turbidity cohesive force, such as adhesion force, shear stress ( Fine flock with extremely strong mechanical strength is formed.
この場合、前記実施例では、前記分岐手段5を循環ポン
プ6の直前に設けて凝集剤及び水素イオン濃度調節剤が
前記循環ポンプ6の直前において注入されるようになっ
ていることから、特に攪拌手段等を別個に設けることな
く前記注入された凝集剤等の混合が素早くかつ効果的に
行われ、所望のフロック形成が極めて良好に行われる。In this case, in the above-described embodiment, the branching means 5 is provided immediately before the circulation pump 6 so that the flocculant and the hydrogen ion concentration adjusting agent are injected immediately before the circulation pump 6. Mixing of the injected coagulant and the like can be performed quickly and effectively without separately providing a means or the like, and desired floc formation can be performed extremely well.
その際、前記過材粒子22の表面に付着せずに水管19
から排出されたフロック、あるいは、余剰となった凝集
剤等は前記排出管20を通じて外部に排出され、循環系に
は混入されないようになっている。At that time, the water pipe 19 without adhering to the surface of the particulate material 22
The flocs discharged from the device, the surplus coagulant, and the like are discharged to the outside through the discharge pipe 20 and are not mixed into the circulation system.
この操作が終了したら前記開閉弁8,9を閉じるとともに
多方弁7を操作して循環流路にし、浄化処理を再開す
る。When this operation is completed, the on-off valves 8 and 9 are closed and the multi-way valve 7 is operated to establish a circulation flow path, and the purification process is restarted.
上述の実施例によれば、以下の利点がある。According to the above-mentioned embodiment, there are the following advantages.
すなわち、被処理用水中に含まれるコロイド状濁質成分
が前記過材粒子表面に形成された凝集力の強いフロッ
クに捕捉され、該フロックの一部となって除去される。
しかも、このフロックは付着力が強くかつ機械的強度も
強いので、容易に離脱するようなことがない。That is, the colloidal turbidity component contained in the water to be treated is captured by the flocs having a strong cohesive force formed on the surface of the particulate material, and is removed as a part of the flocs.
Moreover, since this flock has a strong adhesive force and a high mechanical strength, it does not easily come off.
したがって、従来、最も過精度が高いとされていたケ
イソウ土過機を用いた場合や、あるいは、これにプレ
フロック法等を施した場合では原理的に捕捉不可能であ
ったコロイド状濁質成分をも確実に捕捉・除去でき、こ
れにより、従来の循環式水処理装置に何等大幅な変更を
加えることなく、従来不可能であったプール等の濁り除
去を確実に実現させることができる。Therefore, when using a diatomaceous earth pass machine, which was conventionally considered to have the highest over-precision, or when it was subjected to the pre-flock method, etc., it was in principle impossible to capture the colloidal suspended matter component. Can be surely captured and removed, and thereby, it is possible to surely realize the turbidity removal of the pool and the like, which has been impossible in the past, without making any significant changes to the conventional circulating water treatment device.
また、この方法は、過材粒子自体の表面に細かいフロ
ックを形成させるだけであり、過材粒子間の空隙は従
来のプレフロック法等に比較して著しく広く確保でき、
被処理用水の循環流量は従来の凝集剤等を使用しない
過機のみの場合とほぼ同等に確保できる。したがって、
汚染速度が大きい場合でもこれに十分に対応した浄化速
度を確保できる。In addition, this method only forms fine flock on the surface of the over-material particles themselves, and the voids between the over-material particles can be remarkably wider than the conventional pre-flock method, etc.,
The circulation flow rate of the water to be treated can be secured to be almost the same as in the case of the conventional machine without using the coagulant or the like. Therefore,
Even if the contamination rate is high, it is possible to ensure a purification rate that is sufficiently compatible with this.
さらに、前記従来のプレフロック法のように捕捉汚染粒
子が過槽表面部に集中して短時間でめずまりを起すよ
うなこともないから、逆洗頻度も少なくてすみ、通常の
条件では、一、二週間は逆洗を必要としない。Further, unlike the conventional pre-flock method, trapped contaminant particles do not concentrate on the surface of the excess tank to cause slumping in a short time, so that the backwashing frequency is low, and under normal conditions. No backwash for a week or two.
このようなことから、従来のプレフロック法等の凝集法
に比較して使用する凝集剤の量を十分の一程度に低減で
きるとともに、処理操作は、上述のように極めて短時間
の単一操作であるから、処理に要する時間及び手間を従
来に比較して著しく軽減できる。From this, the amount of coagulant used can be reduced to about one tenth as compared with the conventional pre-floc method and other coagulation methods, and the treatment operation is a single operation in an extremely short time as described above. Therefore, the time and labor required for the processing can be remarkably reduced as compared with the conventional case.
加えて、本方法を従来の装置を用いて実施するために必
要な改良工事費も極めて安価ですむとともに、循環式水
処理装置を新規に製作する場合においては、本方法を適
用することにより、従来、必ず必要とされていたフロッ
ク形成槽やバランシングタンクその他の設備を場合によ
っては省略することも可能となり、設備全体を小型・簡
略化した極めて合理的なものとすることも可能である。In addition, the cost of improvement work required to carry out this method using conventional equipment is extremely low, and in the case of newly manufacturing a circulating water treatment equipment, by applying this method, In some cases, it is possible to omit the flock forming tank, the balancing tank, and other equipment that were always required, and it is also possible to make the entire equipment compact and simple and extremely rational.
そして、本方法により、従来、透明度を確保するために
多量に導入しなければならなかった新鮮水の導入量を著
しく軽減できるから、この多量の新鮮水の導入自体にか
かる経費及びこの多量の新鮮水を所定の温度まで加熱す
るために必要な膨大な燃費を一挙に節減できるという著
しい利点をもたらす。Since this method can significantly reduce the amount of fresh water that has conventionally been required to be introduced in large amounts to ensure transparency, the cost of introducing the large amount of fresh water itself and the large amount of fresh water. This brings a remarkable advantage that the huge fuel consumption required for heating water to a predetermined temperature can be saved at once.
なお、本発明者等は、本実施例を様々なプールにおいて
実施し、現実のプールにおいて実際に著しい効果の得ら
れることを多数の事例によって確認しているが、以下に
その一実験例の結果を示す。In addition, the present inventors have carried out this example in various pools, and have confirmed in many cases that a remarkable effect is actually obtained in an actual pool. Indicates.
この実験例は、従来、最も過精度が高いとされている
ケイソウ土過法による場合と本法による場合とを条件
を揃えて互いの透明度(透視度=水の透視距離;単位
m)を比較したものである。In this experimental example, the transparency of each other (transparency = transparent distance of water; unit m) is compared under the conditions of the diatomaceous earth filtration method, which has been considered to have the highest accuracy, and the case of this method. It was done.
条件 用水溜……25mプール 有効容量……350m3 入泳者……560人/日 (他の入泳者条件も同一) 結果 別表に示す通りである。Condition basin …… 25m pool Effective capacity …… 350m 3 Swimmers …… 560 people / day (same conditions for other swimmers) Results As shown in the attached table.
なお、本発明は、前記実施例に限られることなく、例え
ば、凝集剤等の注入を、必ずしも前記実施例のように循
環ポンプの手前から注入しなくてもよく、循環システム
に応じてい適宜の場所を選定し、その場所から注入する
ようにしてもよい。その場合、注入後に凝集剤等が速や
かに混合されるように適宜の攪拌装置を設けることが望
ましい。Note that the present invention is not limited to the above-described embodiment, and for example, injection of a flocculant or the like does not necessarily have to be performed before the circulation pump as in the above-described embodiment, and may be appropriately selected depending on the circulation system. You may make it select a place and inject from that place. In that case, it is desirable to provide an appropriate stirring device so that the coagulant and the like can be quickly mixed after the injection.
[発明の効果] 以上詳述したように、本発明は、本発明者等の研究によ
って得られた知見に基づき、本発明者等が案出した原
理、すなわち、過材粒子自体の表面に、過材粒子間
の空隙よりも小さい粒径を有し、付着力が強く、機械的
強度にすぐれ、さらに凝集力の強いフロックを形成し、
このフロックに濁質成分を凝集させるという新規な原理
を、さらに前記知見に照らして発展させ、被処理用水の
一部に凝集剤と水素イオン濃度調節剤とを適宜混入して
過機に流通させるという極めて単純な構成により、実
際の循環式水処理装置における過機に適用できるよう
にしたもので、これにより、従来、不可能であったプー
ル等の濁りの主要な原因たるコロイド状濁質成分を確実
に除去することを可能にしたものである。[Effects of the Invention] As described in detail above, the present invention is based on the knowledge obtained by the research of the present inventors, that is, the principle devised by the present inventors, that is, on the surface of the oversize particles themselves, It has a smaller particle size than the voids between the particles, has strong adhesive force, has excellent mechanical strength, and forms flocs with strong cohesive force.
The novel principle of flocculating flocculent components in this floc is further developed in light of the above-mentioned knowledge, and a flocculant and a hydrogen ion concentration regulator are appropriately mixed in a part of the water to be treated and allowed to flow unnecessarily. With this extremely simple structure, it can be applied to the over-running of the actual circulating water treatment equipment, which allows colloidal turbidity components that are the main cause of turbidity in pools etc. It is possible to reliably remove.
第1図は本発明の実施例にかかる循環式水処理装置にお
ける過機処理方法を実施するための装置の構成を示す
ブロック図である。 1……用水溜、 2……被処理用水、 5……分岐手段、 6……循環ポンプ、 7……多方弁、 8,9……開閉弁、 12……凝集剤、 14……水素イオン濃度調節剤、 16,17……流量調節弁、 21……過機、 22……過材粒子。FIG. 1 is a block diagram showing the configuration of an apparatus for carrying out an overtreatment method in a circulating water treatment apparatus according to an embodiment of the present invention. 1 ... Water reservoir, 2 ... Water to be treated, 5 ... Branching means, 6 ... Circulation pump, 7 ... Multi-way valve, 8,9 ... Open / close valve, 12 ... Flocculant, 14 ... Hydrogen ion Concentration control agent, 16,17 …… Flow control valve, 21 …… Excessive machine, 22 …… Excess material particles.
Claims (1)
通させて浄化した後前記用水溜に戻すようにした循環式
水処理装置における前記濾過機の濾過能力を向上させる
濾過機処理方法であって、 循環浄化の開始前又は濾過機の逆洗時又は循環浄化途中
における所定の時期に、前記用水溜から濾過機に用水を
導く流路を通じて該流路を流通する用水中に無機凝集剤
と水素イオン濃度調節剤とを数十秒ないし数分の間だけ
混入し、 前記混入の際に、前記無機凝集剤の混入量が5〜200mg/
lの範囲内でかつ混入された無機凝集剤の加水分解によ
って低下するpHが5以下にならないようにこれ等の混入
量を加減し、 前記通路を流通する用水中には前記濾過機の濾過材粒子
及び濾過材粒子間の間隙より大きいフロックが凝集せず
に、該用水が濾過材粒子の表面に接触したときに該濾過
材粒子表面に該濾過材粒子及び濾過材粒子間の間隙より
小さい粒径を有しかつ静電気的凝集力を有する無数の無
機ポリマーフロックが付着するようにして前記濾過機の
濾過材粒子に静電気的凝集力をもたせることにより該濾
過機の濾過能力を向上させるようにしたことを特徴とす
る循環式水処理装置における濾過機処理方法。1. A filter treatment method for improving the filtration capacity of a filter in a circulating water treatment apparatus, wherein the water to be treated in a water reservoir is at least passed through a filter to be purified and then returned to the water reservoir. Therefore, before the start of the circulation purification or at a predetermined time during the backwashing of the filter or during the circulation purification, the inorganic coagulant is added to the water flowing through the flow channel for guiding the water from the water reservoir to the filter. And a hydrogen ion concentration adjusting agent are mixed only for several tens of seconds to several minutes, and the mixing amount of the inorganic coagulant is 5 to 200 mg /
Within the range of 1 and the pH of the mixed inorganic coagulant, which is lowered by hydrolysis of the inorganic coagulant, is not adjusted to 5 or less, and the mixing amount of these is adjusted so that the water flowing through the passage contains the filtering material of the filter. Particles smaller than the gap between the filter medium particles and the filter medium particles on the surface of the filter medium particles when the water contacts the surface of the filter medium particles without flocs larger than the gap between the particles and the filter medium particles are not aggregated. A large number of inorganic polymer flocs having a diameter and an electrostatic cohesive force are attached so that the filter material particles of the filter have an electrostatic cohesive force, thereby improving the filtering ability of the filter. A method for treating a filter in a circulating water treatment device, comprising:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63067561A JPH0767522B2 (en) | 1988-03-22 | 1988-03-22 | Circulating water treatment equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63067561A JPH0767522B2 (en) | 1988-03-22 | 1988-03-22 | Circulating water treatment equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH01242117A JPH01242117A (en) | 1989-09-27 |
| JPH0767522B2 true JPH0767522B2 (en) | 1995-07-26 |
Family
ID=13348493
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63067561A Expired - Fee Related JPH0767522B2 (en) | 1988-03-22 | 1988-03-22 | Circulating water treatment equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0767522B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CL2008003900A1 (en) * | 2008-12-24 | 2009-03-13 | Crystal Lagoons Curacao Bv | Water filtration process of a pond, without filtering the entire water, which comprises a) emitting ultrasonic waves in the pond; b) add a flocculant; c) suction the floccules with a vacuum cleaner towards an effluent collection line; d) filter said effluent and return the filtered flow to the pond. |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4918936A (en) * | 1972-06-14 | 1974-02-19 | ||
| JPS5617684A (en) * | 1979-07-23 | 1981-02-19 | Japan Organo Co Ltd | Filtering method for cooling circulation water system |
-
1988
- 1988-03-22 JP JP63067561A patent/JPH0767522B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH01242117A (en) | 1989-09-27 |
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|---|---|---|---|
| LAPS | Cancellation because of no payment of annual fees |