JPH06170127A - Method for filtering treatment of original water and its apparatus - Google Patents

Method for filtering treatment of original water and its apparatus

Info

Publication number
JPH06170127A
JPH06170127A JP4304885A JP30488592A JPH06170127A JP H06170127 A JPH06170127 A JP H06170127A JP 4304885 A JP4304885 A JP 4304885A JP 30488592 A JP30488592 A JP 30488592A JP H06170127 A JPH06170127 A JP H06170127A
Authority
JP
Japan
Prior art keywords
water
raw water
filtration
pressurized
space
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
Application number
JP4304885A
Other languages
Japanese (ja)
Inventor
Hisashi Ichihara
壽 市原
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP4304885A priority Critical patent/JPH06170127A/en
Priority to DE4335104A priority patent/DE4335104C2/en
Publication of JPH06170127A publication Critical patent/JPH06170127A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D36/00Filter circuits or combinations of filters with other separating devices
    • B01D36/04Combinations of filters with settling tanks
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/007Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with multiple filtering elements in series connection
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/02Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration
    • B01D24/10Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration the filtering material being held in a closed container
    • B01D24/12Downward filtration, the filtering material being supported by pervious surfaces
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/46Regenerating the filtering material in the filter
    • B01D24/4631Counter-current flushing, e.g. by air
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/46Regenerating the filtering material in the filter
    • B01D24/4668Regenerating the filtering material in the filter by moving the filtering element
    • B01D24/4673Regenerating the filtering material in the filter by moving the filtering element using rotary devices or vibration mechanisms, e.g. stirrers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D24/00Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
    • B01D24/48Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof integrally combined with devices for controlling the filtration
    • B01D24/4884Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof integrally combined with devices for controlling the filtration by pressure measuring

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PURPOSE:To make clogging of a filter material hardly occur and to apply directly filtering treatment without performing pretreatment even when the concn. of suspending substances in an original water is high by making the amt. of the floating substances caught by the filter material decrease remarkably. CONSTITUTION:A filtering container 2 wherein sands 3 and 4 are placed in the lower part and a space 6 is formed in the upper part is used and an original water W1 contg. suspending substance SS and a power water W4 wherein a large amt. of air is dissolved under pressure are fed in the space so as to mix both waters and majority of the suspending substance SS in the original water W1 is caught with a number of air bubbles A coming out from the power water W1. Then, the suspending substance SS with the air bubbles A is floated and separated on the uppermost part of the filtering container 2 and the original water wherein the amt. of susbending substance SS is decreased by floating and suspending is passed though the sands 3 and 4 to make the remaining suspending substance SS is the original water W1 caught by the sands 3 and 4 and the original water W1 is turned thereby into a clean treated water W2.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、原水に含まれる浮遊物
質を濾過処理により除去して清澄な処理水を得る方法及
びその装置に関し、より詳しくは、従来は適用できなか
った原水中の浮遊物質の濃度が高い場合にも適用できる
濾過処理方法及びその装置に係るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing suspended solids contained in raw water by filtration to obtain clear treated water, and an apparatus therefor. The present invention relates to a filtration treatment method and apparatus applicable even when the concentration of a substance is high.

【0002】[0002]

【従来の技術】従来の一般的な濾過処理方法は、図2に
示すような濾過処理装置50を使用して行われる。すな
わち、円筒形をなす密閉構造の濾過容器51の内部に、
濾材として上から順に、粒径0.5〜1.0mm・厚さ
600mm程度の小粒砂52、粒径2〜3mm・厚さ3
00mm程度の中粒砂53、及び粒径3〜10mm・厚
さ300mm程度の大粒砂54を積層させ、最下部に小
石70を敷く。また、濾過容器51の上部には空気抜バ
ルブ71を設ける。
2. Description of the Related Art A conventional general filtering method is carried out by using a filtering apparatus 50 as shown in FIG. In other words, inside the filtration container 51 having a cylindrical closed structure,
As a filter medium, in order from the top, a small sand 52 with a particle size of 0.5 to 1.0 mm and a thickness of about 600 mm, a particle size of 2 to 3 mm and a thickness of 3
A medium-sized sand 53 of about 00 mm and a large-sized sand 54 having a particle size of 3 to 10 mm and a thickness of about 300 mm are laminated, and a small stone 70 is laid at the bottom. Further, an air vent valve 71 is provided above the filtration container 51.

【0003】原水槽55に供給された浮遊物質SSを含
む原水W1 を、原水ポンプ56で汲み揚げて送水し、原
水注入管57、原水注入バルブ58及び注入口部材59
を経て濾過容器51の上部に注入する。なお、この送水
の途中で、凝集剤タンク60の凝集剤Fを定量ポンプ6
1で原水W1 に添加する。
Raw water W1 containing suspended solids SS supplied to a raw water tank 55 is pumped up by a raw water pump 56 and sent to a raw water injection pipe 57, a raw water injection valve 58 and an injection port member 59.
It is injected into the upper part of the filtration container 51 via. In addition, the coagulant F in the coagulant tank 60 is fed through the metering pump 6 during the water supply.
1. Add to raw water W1.

【0004】濾過容器51では、原水W1 が下向きに流
れて各砂52,53,54を通るうちに、浮遊物質SS
は、先ず小粒砂52の上面に捕捉され、さらに各砂5
2,53,54の粒子間に捕捉される。こうして得られ
た清澄な処理水W2 は、濾過容器51の下部から処理水
排出バルブ62及び処理水排出管63を経て処理水槽6
4に貯留され、該処理水槽64から放流される。
In the filter container 51, while the raw water W1 flows downward and passes through the sands 52, 53, 54, the suspended matter SS
Is first trapped on the upper surface of the small sand 52, and each sand 5
It is trapped between 2,53,54 particles. The clear treated water W2 obtained in this way passes through the treated water discharge valve 62 and the treated water discharge pipe 63 from the lower part of the filtration container 51, and is treated water tank 6
4 and is discharged from the treated water tank 64.

【0005】[0005]

【発明が解決しようとする課題】ところが、上記濾過処
理の経過に伴い、砂52,53,54による浮遊物質S
Sの捕捉量が多くなると、該砂52,53,54の目詰
まりが起こり、原水W1の流れが悪くなり、濾過容器5
1内の圧力が上昇する。そこで、濾過処理を頻繁に中断
して、次に述べる逆洗処理を短いインターバルで繰返し
行ない、浮遊物質SSを砂52〜54から分離して濾過
容器51の外に取出す必要があった。
However, along with the progress of the above-mentioned filtration treatment, the suspended solids S due to the sand 52, 53, 54
When the amount of captured S increases, the sand 52, 53, 54 is clogged, the flow of raw water W1 deteriorates, and the filtration container 5
The pressure in 1 rises. Therefore, it is necessary to frequently interrupt the filtration process and repeat the backwash process described below at short intervals to separate the suspended solids SS from the sands 52 to 54 and take them out of the filtration container 51.

【0006】すなわち、濾過容器51の上部に設けた圧
力計65の指示が所定の設定値(例えば1.0kg/cm
2 )に達すると、自動的に原水注入バルブ58及び処理
水排出バルブ62が閉じ、原水W1 の注入及び処理水W
2 の排出が停止する。続いて、処理水槽64内の逆洗水
ポンプ66が作動し、処理水W2 の一部が逆洗水W3 と
して逆洗水バルブ67を経て濾過容器51の下部に注入
され、上向きに逆流する。このため、浮遊物質SSは砂
52,53,54から剥離し、濃縮汚泥となって、濾過
容器51の上部から浮遊物質取出バルブ68及び浮遊物
質取出管69を経て取出される。従来、この逆洗処理に
は3〜5分程度の処理時間と多量の逆洗水とを必要とし
ていた。この逆洗処理後は濾過処理が再開され、以後、
このような濾過処理と逆洗処理とが頻繁に繰返される。
That is, the indication of the pressure gauge 65 provided on the upper part of the filtration container 51 indicates a predetermined set value (for example, 1.0 kg / cm).
2 ), the raw water injection valve 58 and the treated water discharge valve 62 are automatically closed to inject the raw water W1 and the treated water W.
Discharge of 2 stops. Subsequently, the backwash water pump 66 in the treated water tank 64 is operated, and a part of the treated water W2 is injected as backwash water W3 into the lower portion of the filtration container 51 through the backwash water valve 67 and flows backward upward. Therefore, the suspended solids SS are separated from the sands 52, 53, 54 and become concentrated sludge, which is taken out from the upper part of the filtration container 51 via the floating substance take-out valve 68 and the floating substance take-out pipe 69. Conventionally, this backwashing treatment required a treatment time of about 3 to 5 minutes and a large amount of backwashing water. After this backwashing process, the filtering process is restarted, and thereafter,
The filtering process and the backwashing process are frequently repeated.

【0007】なお、濾過処理中の上記目詰まりによる濾
過処理速度の低下を補うため、濾過容器51内の圧力を
0.5〜1.5kg/cm2 の範囲で適宜設定し、高圧下で
濾過処理を行っていたので、濾過容器51の耐圧性に留
意する必要があった。また、砂52,53,54による
濾過のみに負っていたため、確実な清澄化のために多量
の砂52,53,54を使用する必要があった。
In order to compensate for the decrease in the filtration processing speed due to the above clogging during the filtration processing, the pressure in the filtration container 51 is appropriately set within the range of 0.5 to 1.5 kg / cm 2 , and the filtration is performed under high pressure. Since the treatment was performed, it was necessary to pay attention to the pressure resistance of the filtration container 51. Moreover, since it was owed only to the filtration with the sands 52, 53, 54, it was necessary to use a large amount of the sands 52, 53, 54 for reliable clarification.

【0008】従来、このような濾過処理方法は、原水W
1 中の浮遊物質SSの濃度が高い場合には、直接適用で
きない方法であると考えられてきた。なぜなら、浮遊物
質SSの濃度が高いと、その濾過処理をわずか数分ない
し十数分行うだけで、砂52,53,54の目詰まりが
起こって逆洗処理が必要になり、その逆洗処理時間もか
なり長く必要なため、効率が悪いからである。また、わ
ずか数回ないし十数回の濾過処理と逆洗処理とを繰返す
うちに、逆洗処理を行っても砂52,53,54の目詰
まりが回復しなくなり、砂52,53,54の交換が必
要になるため、非常に不経済だからである。
Conventionally, such a filtration treatment method has been used in raw water W.
It has been considered that this method cannot be directly applied when the concentration of suspended solids SS in 1 is high. This is because when the concentration of the suspended solids SS is high, the backwashing process becomes necessary because the sand 52, 53, 54 is clogged only by performing the filtration process for only a few minutes to a dozen minutes. This is because it takes much time and is inefficient. In addition, the clogging of the sand 52, 53, 54 does not recover even if the backwashing process is performed while the filtration process and the backwashing process are repeated only a few times or a dozen times. It is very uneconomical because it needs to be replaced.

【0009】このため、従来の濾過処理方法は、原水W
1 中の浮遊物質SSの濃度が低い場合(例えば10mg
/l)にのみ直接適用されていた。そして、浮遊物質の
濃度が高い場合に適用するには、濾過処理の前段階処理
として別の浄化装置(例えば重力式分離装置)による浄
化処理を行って予め浮遊物質の濃度を低くした後に、前
記濾過処理を行う必要があったため、設備が大型化・複
雑化・高コスト化し、容易に導入できないという問題が
あった。
For this reason, the conventional filtration treatment method uses the raw water W
When the concentration of suspended solids in 1 is low (eg 10 mg
/ L) only was applied directly. To apply when the concentration of suspended solids is high, a purification treatment by another purification device (for example, a gravity separation device) is performed as a pre-treatment of the filtration treatment to reduce the concentration of suspended solids in advance, and then Since it was necessary to carry out a filtration process, there was a problem that the equipment became large, complicated, and expensive, and could not be easily introduced.

【0010】本発明の目的は、上記の問題を解決し、濾
材に捕捉される浮遊物質を激減させて濾材の目詰まりを
起こりにくくし、もって濾過処理速度の向上、濾材の使
用量の減少、濾材の長寿命化、逆洗処理のインターバル
の延長、逆洗処理時間の短縮、逆洗水の使用量の減少等
を図ることができ、また、原水中の浮遊物質の濃度が高
い場合にも前段階処理を行うことなく直接適用でき、さ
らに、この高濃度の原水を一つの濾過容器で処理可能に
して、設備の小型化・簡素化・低コスト化を図ることが
できる画期的な濾過処理方法及びその装置を提供するこ
とにある。但し、本発明は前段階処理を行うことを否定
・除外するものではなく、特定機能の前段階処理を加え
てもよい。
The object of the present invention is to solve the above problems and to significantly reduce the amount of suspended solids trapped in the filter medium to prevent clogging of the filter medium, thereby improving the filtration processing speed and reducing the amount of the filter medium used. It is possible to prolong the service life of filter media, extend the interval of backwashing, shorten the time of backwashing, reduce the amount of backwashing water used, and even when the concentration of suspended solids in the raw water is high. Revolutionary filtration that can be applied directly without any pre-treatment, and can treat this high-concentration raw water with one filtration container, which can achieve downsizing, simplification and cost reduction of equipment. It is to provide a processing method and an apparatus thereof. However, the present invention does not deny / exclude performing the pre-stage process, and may add the pre-stage process of the specific function.

【0011】[0011]

【課題を解決するための手段】上記目的を達成するため
に、本発明の原水の濾過処理方法においては、下部に濾
材を入れ上部に空間を形成した濾過容器を使用し、浮遊
物質を含んだ原水と加圧下で多量の気体を溶解させた加
圧水とを両水が混合するようにして前記濾過容器の空間
に注入し、該原水中の浮遊物質の大部分を加圧水から放
出された無数の気泡に捕捉させ、該浮遊物質を気泡と共
に濾過容器の最上部に浮上分離するとともに、該浮上分
離により浮遊物質の減少した原水を前記濾材に通し、該
原水中の残りの浮遊物質を濾材に捕捉させることによ
り、該原水を清澄な処理水とするという手段を採用し
た。
In order to achieve the above object, in the method for filtering raw water of the present invention, a filtration container having a filter medium in the lower part and a space in the upper part is used, and a suspended substance is contained. The raw water and the pressurized water in which a large amount of gas is dissolved under pressure are injected into the space of the filtration container so that both water are mixed, and most of the suspended substances in the raw water are innumerable bubbles released from the pressurized water. And float the floating material together with air bubbles to the uppermost part of the filter container, pass the raw water in which the floating material is reduced by the floating separation through the filter medium, and trap the remaining floating material in the raw water on the filter medium. As a result, the means for converting the raw water into clear treated water was adopted.

【0012】また、本発明の原水の濾過処理装置は、下
部に濾材を入れ上部に空間を形成した濾過容器と、加圧
下で多量の気体を溶解させた加圧水を製造する加圧水製
造装置と、浮遊物質を含んだ原水を前記濾過容器の空間
に注入する原水注入管と、前記加圧水製造装置で製造し
た加圧水を前記原水と混合するようにして前記空間に注
入する加圧水注入管とを備えるように構成した。
The apparatus for filtering raw water of the present invention comprises a filtration container having a filter medium in the lower portion and a space formed in the upper portion, a pressurized water producing apparatus for producing pressurized water in which a large amount of gas is dissolved under pressure, and a floating vessel. A raw water injection pipe for injecting raw water containing a substance into the space of the filtration container, and a pressurized water injection pipe for injecting the pressurized water produced by the pressurized water producing device into the space by mixing with the raw water. did.

【0013】本発明において、「濾材」としては、砂・
活性炭・アンスラサイト・ザクロ石等の粒状体、金属・
合成樹脂等よりなる網状体、布、又はこれらの組合わせ
等を例示できる。加圧水に溶解させる「気体」として
は、空気、窒素、二酸化炭素、又はこれらの混合気等を
例示でき、また、これらに例えばオゾンを混合して殺菌
作用や消臭作用を得ることもできる。
In the present invention, "filter material" includes sand and
Granules such as activated carbon, anthracite, garnet, metal
Examples include a mesh-like body made of synthetic resin or the like, cloth, or a combination thereof. Examples of the "gas" to be dissolved in the pressurized water include air, nitrogen, carbon dioxide, or a mixture thereof, and, for example, ozone may be mixed with these to obtain a sterilizing action or a deodorizing action.

【0014】また、原水と加圧水とを混合するようにし
て濾過容器の空間に注入するには、次の方法を例示でき
る。 原水注入管の濾過容器への接続端付近部位に加圧水
注入管を接続し、原水と加圧水とをこの原水注入管の接
続端付近部位で混合させてから濾過容器の空間に注入す
る。 濾過容器内において初めて原水と加圧水とが衝突混
合又はスワール混合するように、原水注入管と加圧水注
入管とをそれぞれ所定の位置関係で濾過容器に接続す
る。
In order to mix the raw water and the pressurized water into the space of the filtration container, the following method can be exemplified. A pressurized water injection pipe is connected to a portion near the connection end of the raw water injection pipe to the filtration container, and the raw water and the pressurized water are mixed at a region near the connection end of the raw water injection pipe and then injected into the space of the filtration container. The raw water injection pipe and the pressurized water injection pipe are respectively connected to the filtration container in a predetermined positional relationship so that the raw water and the pressurized water are collisionally mixed or swirl mixed in the filtration container for the first time.

【0015】[0015]

【作用】本発明の原水の濾過処理方法及びその装置によ
れば、原水と加圧水とが混合するようにして濾過容器の
空間に注入されたときに、それまで加圧水にかかってい
た加圧が解放されるため、加圧水に溶解していた多量の
空気は過飽和状態となり、一気に放出されて無数の気泡
となる。従って、原水中の浮遊物質の大部分が、前記無
数の気泡に付着して捕捉され、この気泡と共に濾過容器
の最上部に浮上分離するため、この浮遊物質は徐々に濃
縮して汚泥状となる。この濃縮汚泥となった浮遊物質
は、濾過容器の最上部から容易に取出すことができる。
According to the method and apparatus for filtering raw water of the present invention, when the raw water and the pressurized water are mixed and injected into the space of the filtration container, the pressure applied to the pressurized water is released. As a result, a large amount of air dissolved in the pressurized water becomes supersaturated, and is released all at once to become innumerable bubbles. Therefore, most of the suspended matter in the raw water adheres to and is trapped by the innumerable bubbles, and floats and separates at the top of the filtration container together with the bubbles, so that the suspended matter is gradually concentrated and becomes sludge-like. . The suspended matter that has become this concentrated sludge can be easily taken out from the uppermost part of the filtration container.

【0016】上記浮上分離により浮遊物質が減少した原
水及び加圧水は、下向きに流れて濾材を通る。このとき
原水中の残りの浮遊物質は濾材に捕捉されるので、濾材
を通り終った原水は清澄な処理水となる。本実施例では
上記浮上分離によって浮遊物質の大部分を除去できるの
で、濾材は目詰まりしにくい。
The raw water and the pressurized water, in which the suspended solids have been reduced by the floating separation, flow downward and pass through the filter medium. At this time, the remaining suspended solids in the raw water are captured by the filter medium, so the raw water that has passed through the filter medium becomes clear treated water. In this embodiment, most of the suspended matter can be removed by the floating separation, so that the filter medium is less likely to be clogged.

【0017】[0017]

【実施例】以下、本発明を具体化した原水の濾過処理方
法及びその装置の一実施例について、図1を参照して説
明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of a raw water filtering method and apparatus embodying the present invention will be described below with reference to FIG.

【0018】まず、本実施例の濾過処理装置1について
説明すると、2は密閉構造の濾過容器であり、上下両端
部が円錐状に窄められた円筒形をなし、その直径は60
0mm、長さは1000mmである。濾過容器2内の下
部には、濾材として上から順に、粒径0.5〜1.0m
m・厚さ200mm程度の小粒砂3、粒径2〜3mm・
厚さ100mm程度の中粒砂4、及び2mm目の金網5
が積層されている。このように本実施例では、前記従来
例に対して小粒砂3及び中粒砂4の使用量を減らすとと
もに、大粒砂の代わりに薄い金網5を使用することによ
り、小粒砂3の上面位置を低くし、濾過容器2内の上部
にできるだけ大きな空間6が形成されるようにしてあ
る。また、濾過容器2の上部には空気抜バルブ7及び圧
力計8が設けられている。
First, the filtration apparatus 1 of the present embodiment will be described. Reference numeral 2 denotes a filtration container having a closed structure, which has a cylindrical shape in which both upper and lower ends are conically closed, and its diameter is 60.
The length is 0 mm and the length is 1000 mm. In the lower part of the filter container 2, as a filter medium, the particle size is 0.5 to 1.0 m in order from the top.
m / thickness about 200 mm, small sand 3, particle size 2-3 mm
Medium-grained sand 4 with a thickness of about 100 mm and wire mesh 5 of the 2 mm
Are stacked. As described above, in this embodiment, the use amount of the small-grain sand 3 and the medium-grain sand 4 is reduced as compared with the conventional example, and the thin wire net 5 is used instead of the large-grain sand, so that the upper surface position of the small-grain sand 3 is changed. The height is made low so that the largest space 6 is formed in the upper portion of the filtration container 2. Further, an air vent valve 7 and a pressure gauge 8 are provided above the filtration container 2.

【0019】上記濾過容器2には、次のような原水注入
装置と処理水排出装置とが接続されている。10は浮遊
物質SSを含む原水W1 を一時貯留する原水槽であり、
その原水W1 は槽内の原水ポンプ11により汲み揚げら
れ、送水管12及び送水バルブ13を経て送水される。
送水管12の途中部には、凝集剤タンク14から定量ポ
ンプ15により一定量ずつ供給される凝集剤Fを原水W
1 に添加するための凝集剤管16が接続され、凝集剤F
により原水W1 中の浮遊物質SSを凝集・粗大化させて
捕捉されやすくしている。凝集剤Fとしては、ポリ塩化
アルミニウム(PAC)、その他の高分子凝集剤、カセ
イソーダ等を例示できる。
The following raw water injection device and treated water discharge device are connected to the filtration container 2. 10 is a raw water tank for temporarily storing raw water W1 containing suspended matter SS,
The raw water W1 is pumped up by a raw water pump 11 in the tank, and is sent through a water supply pipe 12 and a water supply valve 13.
In the middle of the water pipe 12, the coagulant F supplied from the coagulant tank 14 by the metering pump 15 in a constant amount is fed into the raw water W.
Flocculant tube 16 for addition to 1 is connected to flocculant F
Therefore, the suspended solids SS in the raw water W1 are aggregated and coarsened to facilitate the capture. Examples of the coagulant F include polyaluminum chloride (PAC), other polymer coagulants, caustic soda, and the like.

【0020】送水管12の先端はサイクロン式の金網濾
過器17の入口に接続され、その内部で回転流動する原
水W1が筒状金網18を外側から内側へ通過するとき
に、格別大きなごみや浮遊物質SSを捕捉し、その後こ
のごみ等を廃棄バルブ19から廃棄できるようになって
いる。金網濾過器17の出口には原水注入管20及び原
水注入バルブ21が接続され、この原水注入管20の先
端は濾過容器2の空間6に水平に配設された多数孔付管
よりなる注入口部材22に接続され、原水W1 を空間6
に拡散注入できるようになっている。この注入口部材2
2の形状は適宜変更できる。また、濾過容器2の下部に
は濾過処理された清澄な処理水W2 を排出するための処
理水排出管23及び処理水排出バルブ24が接続され、
処理水排出管23の先端には処理水槽25が設けられて
いる。
The tip of the water supply pipe 12 is connected to the inlet of a cyclone-type wire netting filter 17, and when the raw water W1 which rotates and flows therein passes through the tubular wire netting 18 from the outside to the inside, a particularly large dust or floating The substance SS can be captured, and thereafter, this dust or the like can be discarded through the discard valve 19. A raw water injection pipe 20 and a raw water injection valve 21 are connected to the outlet of the wire mesh filter 17, and the tip of the raw water injection pipe 20 is an injection port formed of a multi-hole pipe horizontally arranged in the space 6 of the filtration container 2. The raw water W1 is connected to the member 22 and the space 6
It can be diffused and injected into. This inlet member 2
The shape of 2 can be changed appropriately. Further, a treated water discharge pipe 23 and a treated water discharge valve 24 for discharging the filtered treated clear treated water W2 are connected to the lower portion of the filtration container 2,
A treated water tank 25 is provided at the tip of the treated water discharge pipe 23.

【0021】次に、上記原水注入管20には、次のよう
な加圧水製造装置が加圧水注入管を介して接続されてい
る。30は加圧水ポンプであり、その入口には、処理水
槽25内の処理水W2 の一部を供給する水供給管31及
び水供給バルブ32と、空気を供給する空気供給管33
とが接続されている。この加圧水ポンプ30では、供給
された処理水W2 と空気とを加圧することにより、処理
水W2 に多量の空気を溶解させて加圧水W4 を製造でき
るようになっている。34は加圧ポンプに並列接続され
た流量調整バルブである。35は加圧ポンプ30の出力
に接続された加圧水タンクであり、内部の加圧水W4 の
圧力は3〜6kg/cm2 の範囲で適宜設定されている。3
6,37はその圧力調整のために加圧水W4 の一部を処
理水槽25に戻す加圧調整管及び加圧調整バルブであ
る。加圧タンク35の出口には加圧水注入管38及び加
圧水注入バルブ39が接続され、加圧水注入管38の先
端は原水注入管20の注入口部材22への接続端付近部
位に接続されている。
Next, the following pressurized water producing device is connected to the raw water injection pipe 20 through the pressurized water injection pipe. Reference numeral 30 is a pressurized water pump, and at its inlet, a water supply pipe 31 and a water supply valve 32 for supplying a part of the treated water W2 in the treated water tank 25, and an air supply pipe 33 for supplying air.
And are connected. The pressurized water pump 30 pressurizes the supplied treated water W2 and air to dissolve a large amount of air in the treated water W2 to produce the pressurized water W4. Reference numeral 34 is a flow rate adjusting valve connected in parallel with the pressurizing pump. Reference numeral 35 is a pressurized water tank connected to the output of the pressure pump 30, and the pressure of the pressurized water W4 inside is appropriately set within the range of 3 to 6 kg / cm 2 . Three
Reference numerals 6 and 37 are a pressure adjusting pipe and a pressure adjusting valve for returning a part of the pressurized water W4 to the treated water tank 25 for the pressure adjustment. A pressurized water injection pipe 38 and a pressurized water injection valve 39 are connected to the outlet of the pressurized tank 35, and the tip of the pressurized water injection pipe 38 is connected to a portion of the raw water injection pipe 20 near the connection end to the injection port member 22.

【0022】次に、上記濾過容器2には、次のような逆
洗装置が接続されている。40は処理水槽25内に投入
された逆洗水ポンプであり、処理水W2 の一部を逆洗水
W3として逆洗水管41及び逆洗水バルブ42を経て濾
過容器2の下部に注入できるようになっている。43は
逆洗空気ポンプであり、外部から取入れた逆洗空気Bを
逆洗空気管44を介して、前記小粒砂3と中粒砂4との
境界部に水平に配設された散気部材45に送り、濾過容
器2内に噴出できるようになっている。46は小粒砂3
の内部に配設された回転攪拌部材であり、濾過容器2の
上部に取付けられたモータ47によりその回転軸48を
介して2〜3回/分で低速回転されるようになってい
る。
Next, the following backwashing device is connected to the filtration container 2. Reference numeral 40 denotes a backwash water pump put in the treated water tank 25 so that a part of the treated water W2 can be injected as the backwash water W3 into the lower portion of the filtration container 2 through the backwash water pipe 41 and the backwash water valve 42. It has become. Reference numeral 43 denotes a backwash air pump, which is an air diffuser horizontally arranged at the boundary between the small-grain sand 3 and the medium-grain sand 4 via the backwash air pipe 44 for the backwash air B taken from the outside. It can be sent to 45 and jetted into the filtration container 2. 46 is small sand 3
Is a rotary stirring member disposed inside of the above, and is rotated at a low speed of 2 to 3 times / minute via a rotation shaft 48 thereof by a motor 47 attached to the upper portion of the filtration container 2.

【0023】次に、上記濾過容器2には、次のような浮
遊物質取出装置が接続されている。26は濾過容器2の
最上部に接続された浮遊物質取出管であり、後述するよ
うに浮上分離して濃縮汚泥となった浮遊物質SSを浮遊
物質取出バルブ27を経て浮遊物質槽9に取出せるよう
になっている。28は濾過容器2の中程に接続された残
留浮遊物質取出管であり、後述するように逆洗処理終了
時に小粒砂3の上面に落下しようとする残留浮遊物質S
Sを残留浮遊物質取出バルブ29を経て浮遊物質槽9に
取出せるようになっている。
Next, the following floating material extraction device is connected to the filtration container 2. Reference numeral 26 is a floating substance extraction pipe connected to the uppermost part of the filtration container 2, and the floating substance SS which has been floated and separated into concentrated sludge can be taken out to the floating substance tank 9 via the floating substance extraction valve 27 as described later. It is like this. Reference numeral 28 is a residual suspended solids extraction pipe connected to the middle of the filtration container 2, and the residual suspended solids S that are about to fall on the upper surface of the small-sized sand 3 at the end of the backwashing process as described later.
S can be taken out to the floating substance tank 9 through the residual floating substance taking-out valve 29.

【0024】さて、以上のように構成された濾過処理装
置1を使用して行う本実施例の濾過処理方法は、次の通
りである。 (1)濾過処理工程 原水ポンプ11及び定量ポンプ15を作動させ、汲
み揚げた原水W1 に凝集剤Fを添加し、この原水W1 を
金網濾過器17に導く。この金網濾過器17で前述の通
りごみ等が除去された原水W1 は原水注入管20に導か
れる。
The filtration treatment method of this embodiment, which is carried out by using the filtration treatment apparatus 1 having the above-mentioned structure, is as follows. (1) Filtration Treatment Step The raw water pump 11 and the metering pump 15 are operated to add the coagulant F to the pumped raw water W1 and guide the raw water W1 to the wire mesh filter 17. The raw water W1 from which dust and the like have been removed by the wire mesh filter 17 is guided to the raw water injection pipe 20.

【0025】 一方、加圧水ポンプ30を作動させ、
前述の通り加圧下で多量の空気を溶解させた加圧水W4
を製造し、加圧水タンク35に貯留する。この加圧水W
4は加圧水注入管38に導かれる。
On the other hand, the pressurized water pump 30 is operated,
As described above, pressurized water W4 in which a large amount of air is dissolved under pressure
Is manufactured and stored in the pressurized water tank 35. This pressurized water W
4 is guided to the pressurized water injection pipe 38.

【0026】 原水W1 と加圧水W4 とは原水注入バ
ルブ21及び加圧水注入バルブ39を経て、原水注入管
20内において衝突混合する。このとき、それまで加圧
水W4にかかっていた加圧が解放されるため、加圧水W4
に溶解していた多量の空気は過飽和状態となり、一気
に放出されて無数の気泡となる。このようにして無数の
気泡を含んだ原水W1 及び加圧水W4 は、原水注入管2
0及び注入口部材22を経て、濾過容器2内の空間6に
拡散注入される。
The raw water W 1 and the pressurized water W 4 collide and mix in the raw water injection pipe 20 through the raw water injection valve 21 and the pressurized water injection valve 39. At this time, the pressure applied to the pressurized water W4 until then is released, so the pressurized water W4
A large amount of air dissolved in the air becomes supersaturated, and is released all at once to become innumerable bubbles. In this way, the raw water W1 and the pressurized water W4 containing innumerable bubbles are collected in the raw water injection pipe 2
It is diffused and injected into the space 6 in the filtration container 2 through the injection port member 0 and the injection port member 22.

【0027】 空間6に注入された原水W1 及び加圧
水W4 においては、凝集剤Fにより凝集・粗大化した浮
遊物質SSの大部分が、前記無数の気泡Aに付着して捕
捉され、この気泡Aと共に濾過容器2の最上部に浮上分
離するため、この浮遊物質SSは徐々に濃縮して汚泥状
となる。
In the raw water W 1 and the pressurized water W 4 injected into the space 6, most of the suspended matter SS aggregated and coarsened by the aggregating agent F adheres to and is captured by the innumerable bubbles A, and together with the bubbles A Since it floats and separates to the uppermost part of the filtration container 2, this suspended solid SS is gradually concentrated and becomes sludge-like.

【0028】 この濃縮汚泥となった浮遊物質SS
は、浮遊物質取出バルブ27を一定時間毎に開くことに
より、浮遊物質取出管26を経て浮遊物質槽9に取出さ
れる。
Suspended matter SS that became this concentrated sludge
Is taken out to the floating substance tank 9 through the floating substance taking-out pipe 26 by opening the floating substance taking-out valve 27 at regular intervals.

【0029】 上記浮上分離により浮遊物質SSが著
しく減少した原水W1 及び加圧水W4は、下向きに流れ
て小粒砂3及び中粒砂4を通る。このとき原水W1 中の
残りのわずかな浮遊物質SSは、先ず小粒砂3の上面に
捕捉され、さらに各砂3,4の粒子間に捕捉されるの
で、中粒砂4を通り終った原水W1 は清澄な処理水W2
となる。本実施例では上記浮上分離によって浮遊物質S
Sの大部分を除去できるので、前述の通り砂3,4の使
用量が少なくても、十分に清澄な処理水W2 を得ること
ができる。また、砂3,4もほとんど目詰まりしない。
The raw water W 1 and the pressurized water W 4 whose suspended solids SS are significantly reduced by the floating separation flow downward and pass through the small-grain sand 3 and the medium-grain sand 4. At this time, the remaining small amount of suspended solids SS in the raw water W1 is first captured on the upper surface of the small sand 3 and further between the particles of the sands 3 and 4, so that the raw water W1 which has passed through the medium sand 4 is finished. Is clear treated water W2
Becomes In this embodiment, the floating substance S is obtained by the floating separation.
Since most of S can be removed, sufficiently clear treated water W2 can be obtained even if the amounts of sands 3 and 4 used are small as described above. Also, the sands 3 and 4 are hardly clogged.

【0030】 上記処理水W2は処理水排出管を経て
処理水槽25に排出され、この処理水槽25をオーバー
フローした処理水W2は放流される。
The treated water W2 is discharged to the treated water tank 25 through the treated water discharge pipe, and the treated water W2 that overflows the treated water tank 25 is discharged.

【0031】上記の通り、本実施例では濾過処理中の砂
3,4の目詰まりが起きにくいので、濾過処理速度が高
く、濾過容器2内の圧力は0〜0.3kg/cm2 程度に設
定すれば十分である(勿論、より高くしてもよい)。こ
のため、濾過容器2の設計が容易である。
As described above, in this embodiment, the sands 3 and 4 are less likely to be clogged during the filtration process, so the filtration process speed is high and the pressure in the filtration container 2 is about 0 to 0.3 kg / cm 2 . It is enough to set (of course, it can be higher). Therefore, the design of the filter container 2 is easy.

【0032】(2)逆洗処理工程 さて、本実施例では逆洗処理を必要時にのみ行った
り、一定時間毎に行ったり、濾過容器2内の圧力上昇に
基づいて行ったりすることができるが、ここでは最後の
方法について説明する。濾過容器2の圧力計8の指示が
所定の設定値(例えば0.3kg/cm2 )に達すると、自
動的に原水注入バルブ21等が閉じて濾過処理が停止す
る。
(2) Backwashing Process In the present embodiment, the backwashing process can be performed only when necessary, at regular intervals, or based on the pressure rise in the filtration container 2. , Here, the last method is explained. When the indication of the pressure gauge 8 of the filtration container 2 reaches a predetermined set value (for example, 0.3 kg / cm 2 ), the raw water injection valve 21 and the like are automatically closed and the filtration process is stopped.

【0033】 続いて、処理水槽25内の逆洗水ポン
プ40が作動し、処理水W2 の一部が逆洗水W3 として
逆洗水管41及び逆洗水バルブ42を経て濾過容器2の
下部に注入され、上向きに逆流する。これと同時に、逆
洗空気ポンプ43が作動し、外部から取入れた逆洗空気
Bが逆洗空気管44及び散気部材45を介して濾過容器
2内に噴出される。また、モータ47が作動し、回転攪
拌部材46が2〜3回/分で低速回転する。これら逆洗
水W3 の逆流、逆洗空気Bの振動、回転攪拌部材46の
回転により、砂3,4はあらゆる方向に激しく攪拌され
るため、浮遊物質SSは砂3,4から剥離し汚泥となっ
て、浮遊物質取出管26を経て浮遊物質槽9に取出され
る。
Then, the backwash water pump 40 in the treated water tank 25 is operated, and a part of the treated water W2 is transferred to the lower portion of the filtration container 2 as the backwash water W3 through the backwash water pipe 41 and the backwash water valve 42. Injected and flows upwards. At the same time, the backwash air pump 43 is operated, and the backwash air B taken from the outside is jetted into the filtration container 2 through the backwash air pipe 44 and the air diffusing member 45. In addition, the motor 47 operates and the rotary stirring member 46 rotates at a low speed of 2 to 3 times / minute. Due to the backflow of the backwash water W3, the vibration of the backwash air B, and the rotation of the rotary stirring member 46, the sands 3 and 4 are vigorously stirred in all directions, so that the suspended solids SS are separated from the sands 3 and 4 and become sludge. Then, it is taken out to the floating substance tank 9 through the floating substance taking-out pipe 26.

【0034】 この逆洗処理終了時には、逆洗水ポン
プ40等の作動が停止し、残留浮遊物質取出バルブ29
が開くので、濾過容器2内の逆洗水W3 及びそこに浮遊
した残留浮遊物質SSは残留浮遊物質取出管28を経て
浮遊物質槽9に取出される。そして、残留浮遊物質取出
管28の内端は攪拌後に落ち着く小粒砂3の上面付近に
開口するようになっているので、小粒砂3の上面に落下
しようとする残留浮遊物質SSさえも取出すことがで
き、理想的な逆洗処理が可能になっている。
At the end of this backwashing process, the operation of the backwashing water pump 40 and the like is stopped, and the residual suspended solids extraction valve 29
Is opened, the backwash water W3 in the filter container 2 and the residual suspended matter SS suspended therein are taken out to the suspended matter tank 9 through the residual suspended matter take-out pipe 28. Since the inner end of the residual suspended solids extraction pipe 28 is opened near the upper surface of the small sand 3 which calms down after stirring, even the residual suspended solids SS that are about to fall onto the upper surface of the small sand 3 can be extracted. Yes, ideal backwashing is possible.

【0035】この逆洗処理後は前記濾過処理が再開さ
れ、以後、このような濾過処理と逆洗処理とが繰返され
る。上記の通り、本実施例ではもともと目詰まりしにく
い砂3,4を逆洗処理するので、逆洗処理のインターバ
ルの延長、逆洗処理時間の短縮、逆洗水の使用量の減少
等を図ることができる。また、濾過処理と逆洗処理とを
多数回繰返しても、砂3,4のわずかな目詰まりは容易
に回復するため、濾材の長寿命化を図ることもできる。
After the backwashing process, the filtering process is restarted, and thereafter, the filtering process and the backwashing process are repeated. As described above, in the present embodiment, since the sands 3 and 4 which are originally difficult to be clogged are backwashed, the backwashing interval is extended, the backwashing time is shortened, and the amount of backwashing water used is reduced. be able to. Further, even if the filtering process and the backwashing process are repeated many times, the slight clogging of the sands 3 and 4 can be easily recovered, so that the life of the filter medium can be extended.

【0036】次に、本発明による効果を確認するために
行った本実施例と従来例との比較試験運転について述べ
る。 [本実施例の試験運転条件] 濾過処理装置: 図1及び前記説明の通り 原水: 岐阜県可児市 可児工業団地の終末監視調整池
の池水 浮遊物質の濃度: 50mg/l 浮遊物質の成分: 固形物及び植物性プランクトン 濾過処理速度: 2.0m3 /時 濾過容器内の見掛流速 8m/時 加圧水の圧力: 4.0kg/cm2 加圧水に溶解する空気量: 0.5l/分 [従来例の試験条件] 濾過処理装置: 図2及び前記説明の通り その他: 加圧水を使用しないことを除き、上記試験条
件と同一
Next, a comparative test operation between the present embodiment and the conventional example performed to confirm the effect of the present invention will be described. [Test operation conditions of this example] Filtration treatment device: As shown in Fig. 1 and the above description Raw water: Kani City, Gifu Prefecture Kani Industrial Park Pond water of terminal monitoring and regulating pond Concentration of suspended solids: 50 mg / l Composition of suspended solids: solid Material and phytoplankton Filtration processing speed: 2.0 m 3 / hr Apparent flow velocity in the filtration container 8 m / hr Pressure of pressurized water: 4.0 kg / cm 2 Amount of air dissolved in pressurized water: 0.5 l / min [Conventional example] Test Conditions of Filtration Device: As shown in FIG. 2 and the above description Other: Same as the above test conditions except that pressurized water is not used

【0037】本実施例の試験運転においては、1時間に
1回ずつ浮遊物質取出バルブ27を開き、濃縮汚泥とな
った浮遊物質SSを約30lずつ取出した。このように
運転したところ、24時間連続して濾過処理を行っても
(逆洗処理は無し)、濾過容器2内の圧力は上昇せず、
清澄な処理水W2 を連続的に得ることができた。この2
4時間経過後に試験運転を停止し、濾過容器2から水抜
きを行って点検したところ、小粒砂3の上面にわずかに
浮遊物質SSが付着している程度で、小粒砂3も中粒砂
4も試験当初と同様に柔かく無穴であった。従って、さ
らに濾過処理を続行できる状態にあった。
In the test operation of the present example, the suspended matter extraction valve 27 was opened once an hour, and about 30 l of suspended matter SS that became concentrated sludge was taken out. When operated in this manner, the pressure in the filtration container 2 does not rise even if filtration treatment is continuously performed for 24 hours (no backwash treatment),
Clarified treated water W2 could be continuously obtained. This 2
After 4 hours, the test operation was stopped, the water was removed from the filtration container 2 and the inspection was performed. As a result, it was found that the suspended matter SS was slightly attached to the upper surface of the small sand 3, and the small sand 3 was also the medium sand 4. Was as soft and holeless as at the beginning of the test. Therefore, the filtration process could be continued.

【0038】一方、従来例の試験運転においては、濾過
処理開始後直ちに濾過容器51内の圧力が上昇し始めた
ため、20分に1回ずつ逆洗処理を繰返した。逆洗水W
3 の使用量は1回に500lであった。この濾過処理と
逆洗処理とを6時間繰返したところで、濾過漏れが起こ
り、処理水W2 に浮遊物質SSが混入し始めた。そこ
で、この時点で逆洗処理を行ったが、回復せず、濾過処
理が不可能になった。試験運転を停止し、濾過容器51
から水抜きを行って点検したところ、小粒砂52及び中
粒砂53に穴が生じており、また、小粒砂52及び中粒
砂53の内部に浮遊物質SSが入り込んで硬くなってい
た。よって、各砂を交換した。
On the other hand, in the test run of the conventional example, the pressure in the filtration container 51 began to rise immediately after the start of the filtration process, so the backwash process was repeated once every 20 minutes. Backwash water W
The amount of 3 used was 500 liters at a time. When this filtration treatment and backwashing treatment were repeated for 6 hours, filtration leakage occurred and the suspended solid SS began to be mixed into the treated water W2. Therefore, at this time point, the backwashing process was performed, but it did not recover and the filtration process became impossible. Stop the test run and filter 51
When water was drained from the container and inspected, holes were formed in the small-grain sand 52 and the medium-grain sand 53, and the suspended material SS had entered the inside of the small-grain sand 52 and the medium-grain sand 53 and became hard. Therefore, each sand was replaced.

【0039】なお、本発明は前記実施例の構成に限定さ
れるものではなく、発明の趣旨から逸脱しない範囲で適
宜変更して具体化することもできる。
The present invention is not limited to the configuration of the above-described embodiment, and can be embodied by appropriately changing it without departing from the spirit of the invention.

【0040】[0040]

【発明の効果】本発明に係る原水の濾過処理方法及びそ
の装置は、上記の通り構成されているので、濾材に捕捉
される浮遊物質を激減させて濾材の目詰まりを起こりに
くくし、もって濾過処理速度の向上、濾材の使用量の減
少、濾材の長寿命化、逆洗処理のインターバルの延長、
逆洗処理時間の短縮、逆洗水の使用量の減少等を図るこ
とができ、また、原水中の浮遊物質の濃度が高い場合に
も前段階処理を行うことなく直接適用でき、さらに、こ
の高濃度の原水を一つの濾過容器で処理可能にして、設
備の小型化・簡素化・低コスト化を図ることができると
いう優れた効果を奏する。
Since the method for filtering raw water and the apparatus therefor according to the present invention are configured as described above, the suspended matter trapped in the filter medium is drastically reduced to prevent clogging of the filter medium, thereby facilitating filtration. Improvement of processing speed, reduction of filter material usage, prolongation of filter material life, extension of backwash processing interval,
The backwashing time can be shortened, the amount of backwashing water used can be reduced, and even when the concentration of suspended solids in the raw water is high, it can be directly applied without pretreatment. It is possible to treat high-concentration raw water with a single filtration container, and it is possible to reduce the size of equipment, simplify the equipment, and reduce the cost.

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

【図1】本発明を具体化した実施例の濾過処理装置を示
す概略図である。
FIG. 1 is a schematic view showing an apparatus for filtering according to an embodiment of the present invention.

【図2】従来例の濾過処理装置を示す概略図である。FIG. 2 is a schematic view showing a conventional filtration processing apparatus.

【符号の説明】 1 濾過処理装置 2 濾過容器 3 小粒砂 4 中粒砂 5 金網 6 空間 20 原水注入管 30 加圧水ポ
ンプ 31 水供給管 32 水供給バ
ルブ 33 空気供給管 34 流量調整
バルブ 35 加圧水タンク 36 加圧調整
管 37 加圧調整バルブ 38 加圧水注
入管 39 加圧水注入バルブ W1 原水 W2 処理水 W3 逆洗水 W4 加圧水 SS 浮遊物質 A 気泡
[Explanation of Codes] 1 Filtering device 2 Filter container 3 Small-grain sand 4 Medium-grain sand 5 Wire mesh 6 Space 20 Raw water injection pipe 30 Pressurized water pump 31 Water supply pipe 32 Water supply valve 33 Air supply pipe 34 Flow rate control valve 35 Pressurized water tank 36 Pressure adjusting pipe 37 Pressure adjusting valve 38 Pressurized water injection pipe 39 Pressurized water injection valve W1 Raw water W2 Treated water W3 Backwash water W4 Pressurized water SS Suspended matter A Bubbles

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 下部に濾材を入れ上部に空間を形成した
濾過容器を使用し、浮遊物質を含んだ原水と加圧下で多
量の気体を溶解させた加圧水とを両水が混合するように
して前記濾過容器の空間に注入し、該原水中の浮遊物質
の大部分を加圧水から放出された無数の気泡に捕捉さ
せ、該浮遊物質を気泡と共に濾過容器の最上部に浮上分
離するとともに、該浮上分離により浮遊物質の減少した
原水を前記濾材に通し、該原水中の残りの浮遊物質を濾
材に捕捉させることにより、該原水を清澄な処理水とす
る原水の濾過処理方法。
1. A filter container having a filter material in the lower part and a space formed in the upper part is used so that both water mixes raw water containing suspended substances and pressurized water in which a large amount of gas is dissolved under pressure. It is injected into the space of the filtration container, most of the suspended matter in the raw water is trapped in the innumerable bubbles released from the pressurized water, and the suspended matter is floated and separated along with the bubbles on the top of the filter vessel, and the floating A method for filtering raw water in which raw water reduced in suspended matter due to separation is passed through the filter medium, and the remaining suspended matter in the raw water is captured by the filter medium to make the raw water clear treated water.
【請求項2】 下部に濾材を入れ上部に空間を形成した
濾過容器と、加圧下で多量の気体を溶解させた加圧水を
製造する加圧水製造装置と、浮遊物質を含んだ原水を前
記濾過容器の空間に注入する原水注入管と、前記加圧水
製造装置で製造した加圧水を前記原水と混合するように
して前記空間に注入する加圧水注入管とを備えた原水の
濾過処理装置。
2. A filtration container in which a filter medium is placed in the lower part to form a space in the upper part, a pressurized water production device for producing pressurized water in which a large amount of gas is dissolved under pressure, and raw water containing suspended matter is stored in the filtration container. An apparatus for filtering raw water, comprising: a raw water injection pipe for injecting into the space; and a pressurized water injection pipe for injecting into the space the pressurized water produced by the pressurized water producing device so as to mix with the raw water.
JP4304885A 1992-10-15 1992-10-15 Method for filtering treatment of original water and its apparatus Pending JPH06170127A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP4304885A JPH06170127A (en) 1992-10-15 1992-10-15 Method for filtering treatment of original water and its apparatus
DE4335104A DE4335104C2 (en) 1992-10-15 1993-10-14 Method and device for filtering spring water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4304885A JPH06170127A (en) 1992-10-15 1992-10-15 Method for filtering treatment of original water and its apparatus

Publications (1)

Publication Number Publication Date
JPH06170127A true JPH06170127A (en) 1994-06-21

Family

ID=17938454

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4304885A Pending JPH06170127A (en) 1992-10-15 1992-10-15 Method for filtering treatment of original water and its apparatus

Country Status (2)

Country Link
JP (1) JPH06170127A (en)
DE (1) DE4335104C2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006122766A (en) * 2004-10-27 2006-05-18 Hitachi Industries Co Ltd Method and apparatus for oil-water separation
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US5591347A (en) * 1995-05-26 1997-01-07 Unicel, Inc. Single cell gas flotation separator with filter media
US5516434A (en) * 1995-05-26 1996-05-14 Unicel, Inc. Single cell gas flotation separator with filter media
DE29608287U1 (en) * 1996-05-08 1997-06-12 Haupt, Steffen, 01589 Riesa Mobile oil service station
DE19810518A1 (en) * 1998-03-11 1999-09-16 Mann & Hummel Filter System for backwashing a filter
US8133396B2 (en) * 2007-01-11 2012-03-13 Smith & Loveless, Inc. Dissolved air floatation with filter system
CN112742111B (en) * 2020-12-24 2021-10-22 大庆东大盛源科技开发有限公司 Water distribution filter in oil field can dismantle high efficiency
FI20217053A1 (en) 2021-03-19 2022-09-20 Turun Seudun Vesiliike Oy Pre-filtering arrangement and method for a water pump transferring natural water

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3412217A1 (en) * 1984-04-02 1985-10-10 Ingolf 8038 Gröbenzell Kurtze Process and process arrangement for purifying untreated water by flash flotation with simultaneous filtration
DE3900731C2 (en) * 1989-01-12 1994-04-21 Mrw Gmbh Abwasserreinigungssys Waste water treatment device
FI86293C (en) * 1989-04-28 1992-08-10 Oiva Suutarinen FOERFARANDE FOER RENING AV EN VAETSKA FRAON FASTA OCH UPPLOESTA FOERORENINGAR MEDELST ETT FLOTATIONSFILTRERINGSFOERFARANDE.
DE3938607A1 (en) * 1989-11-21 1991-05-23 Didier Werke Ag METHOD AND SYSTEM FOR FILTRATION OF SUSPENSIONS, EMULSIONS AND / OR COOLING LUBRICANTS

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006122766A (en) * 2004-10-27 2006-05-18 Hitachi Industries Co Ltd Method and apparatus for oil-water separation
CN114570075A (en) * 2022-03-07 2022-06-03 昆明有色冶金设计研究院股份公司 Floating filter material filtering device
CN114570075B (en) * 2022-03-07 2023-10-17 昆明有色冶金设计研究院股份公司 Floating filter material filtering device

Also Published As

Publication number Publication date
DE4335104A1 (en) 1994-06-01
DE4335104C2 (en) 1996-12-12

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