JPH0760264A - Pparatus and method for purification of water - Google Patents
Pparatus and method for purification of waterInfo
- Publication number
- JPH0760264A JPH0760264A JP5212790A JP21279093A JPH0760264A JP H0760264 A JPH0760264 A JP H0760264A JP 5212790 A JP5212790 A JP 5212790A JP 21279093 A JP21279093 A JP 21279093A JP H0760264 A JPH0760264 A JP H0760264A
- Authority
- JP
- Japan
- Prior art keywords
- water
- filtered
- base material
- pool
- purifying
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Physical Water Treatments (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、プール、クーリングタ
ワー、工業用などの循環水、ビルの中水道のリサイクル
水などであって、固形物のほかに水溶性不純物を含む水
を浄化するための装置、および浄化方法に関する。とく
に、水溶性不純物による汚染度の高い、游泳用のプール
水の循環浄化に好適である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a pool, a cooling tower, circulating water for industrial use, recycled water of a building's tap water, etc., for purifying water containing water-soluble impurities in addition to solid matters. An apparatus and a purification method. In particular, it is suitable for circulation purification of pool water for swimming, which is highly contaminated by water-soluble impurities.
【0002】[0002]
【従来の技術】長年の間、水の浄化、すなわち水処理の
多くは、砂ろ過装置や沈殿装置、塩素添加などを中心に
行われてきた。最近、水質の悪化とその原因の多様化が
進み、また、水の循環使用が図られるにともなって、水
の浄化装置の開発も進められ、高分子膜を用いたろ過装
置や生物処理などが使用されるようになった。しかし、
これらの水の浄化装置は万能ではない。除去すべき水中
の物質の種類が増え、性質と形態も一様でなくなって浄
化すべき対象が複雑化してくると、ユニットプロセッス
では、最早、対応できなくなってきた。このため、最近
では、浄化する水の条件に基づき、各種の装置を適切に
組み合わせて用いることが重要になってきている。この
ように浄化すべき対象が複雑化した水の代表的な例とし
て、游泳用のプールがあげられる。従来、游泳用のプー
ルでは、プール水を循環して砂ろ過と塩素または二酸化
塩素による消毒を行い、必要に応じて塩素消毒にオゾン
や紫外線処理を併用して水を浄化していた。2. Description of the Related Art For many years, most of the purification of water, that is, water treatment has been carried out mainly by a sand filter, a sedimentation device, chlorine addition and the like. Recently, with the deterioration of water quality and the diversification of its causes, and with the recycle use of water, the development of water purification equipment has been promoted, and filtration equipment using biological membranes and biological treatment have been developed. Came to be used. But,
These water purification devices are not all-purpose. As the types of substances in the water to be removed increase, the properties and morphology become uneven, and the targets to be purified become complicated, the unit process is no longer able to handle it. For this reason, recently, it has become important to appropriately combine and use various devices based on the conditions of water to be purified. A typical example of water whose target to be purified is complicated is a swimming pool. Conventionally, in swimming pools, pool water is circulated for sand filtration and disinfection with chlorine or chlorine dioxide, and if necessary, chlorine is used together with ozone or ultraviolet treatment to purify water.
【0003】[0003]
【発明が解決しようとする課題】ところで、従来の水の
浄化方法では、前記のプール水を例にとると、次のよう
な問題があった。 (1)浄化の主体をろ過機に頼ると、水溶性の不純物が
蓄積し、過マンガン酸カリ消費量が増加する。これを押
さえるには新しい水が大量に必要になる。 (2)紫外線を照射して水の浄化の促進を図るにして
も、ランプ表面が汚れやすく、頻繁な洗浄が必要であ
る。 (3)測定の度に残留塩素量が大きく変化し、安定しな
い。 (4)pHの変動が大きく、pH調整剤を添加すると残
留塩素濃度や濁りなどが変化し制御し難い。 (5)游泳者が増えると濁りや白濁が著しく、除去し難
い。 (6)水処理によって不快な臭いを発生する。 この他にも、プール壁の汚れ、装置の腐食、換気などの
問題が発生していた。游泳用のプールに限らず、クーリ
ングタワー水、工業用水、ビルの中水道水などにおいて
も、大なり小なり同様の問題があった。本発明の水の浄
化装置および水の浄化方法は、かかる問題の解決を課題
に完成されたものである。By the way, the conventional water purification method has the following problems when the pool water is taken as an example. (1) If a filter is used as the main body of purification, water-soluble impurities accumulate and potassium permanganate consumption increases. A large amount of new water is needed to suppress this. (2) Even if ultraviolet rays are irradiated to promote the purification of water, the lamp surface is easily soiled and frequent cleaning is required. (3) The amount of residual chlorine changes greatly with each measurement and is not stable. (4) The fluctuation of pH is large, and when a pH adjusting agent is added, the residual chlorine concentration, turbidity, etc. change and it is difficult to control. (5) When the number of swimmers increases, turbidity and white turbidity are significant and it is difficult to remove. (6) An unpleasant odor is generated by water treatment. In addition to these, there were problems such as pool wall dirt, equipment corrosion, and ventilation. Not only swimming pools, but also cooling tower water, industrial water, tap water in buildings, etc., had similar problems. The water purifying apparatus and the water purifying method of the present invention have been completed to solve the above problems.
【0004】[0004]
【課題を解決するための手段】前記の課題を解決するた
め本発明は、上流側に、織物または編物の基材が起毛さ
れ、太さ0.1〜10μmの極細繊維の立毛が横たわっ
て基材の表面を覆ってなるろ過材を装着した回転ドラム
式固液分離装置が、下流側に、紫外線ランプを装着した
酸化装置が設けられていることを特徴とする、水の浄化
装置を提供する。この水の浄化装置において、酸化装置
のさらに下流側、または、回転ドラム式固液分離装置と
酸化装置との間に、中空糸膜ろ過装置を設けることによ
り、さらに十分に前記の課題を解決する水の浄化装置に
することができる。これらの水の浄化装置は、プール浄
化装置として好ましく用いることができる。In order to solve the above-mentioned problems, the present invention is based on the fact that a woven or knitted base material is napped on the upstream side and napped fibers of ultrafine fibers having a thickness of 0.1 to 10 μm lie on the upstream side. Provided is a rotary drum type solid-liquid separation device equipped with a filter material covering the surface of a material, and an oxidizing device equipped with an ultraviolet lamp on the downstream side. . In this water purification device, the above-mentioned problems can be more sufficiently solved by providing a hollow fiber membrane filtration device further downstream of the oxidation device or between the rotary drum type solid-liquid separation device and the oxidation device. It can be a water purification device. These water purification devices can be preferably used as pool purification devices.
【0005】また、本発明は、原水を、まず、織物また
は編物の基材が起毛され、太さ0.1〜10μmの極細
繊維の立毛が横たわって基材の表面を覆ってなるろ過材
を装着した回転ドラム式固液分離装置でろ過した後、ろ
過水に紫外線を照射して浄化することを特徴とする水の
浄化方法を提供する。本発明においては、原水を前記の
回転ドラム式固液分離装置でろ過して一次ろ過水とし、
一次ろ過水の一部または全量を、中空糸膜ろ過装置でろ
過して二次ろ過水にした後、一次ろ過水の残りおよび二
次ろ過水に、紫外線を照射することによって、水を高度
に浄化することができる。中空糸膜ろ過装置によるろ過
は、一次ろ過水を紫外線照射した後、得られた水の一部
または全量に対して実施してもよい。また、紫外線を照
射する水に適当な酸化剤を添加しておくと、より完全に
水を浄化することができる。上記の水の浄化方法は、プ
ールの浄化方法として好ましく用いることができる。Further, the present invention provides a filter material obtained by first fluffing raw water into a woven or knitted base material and laying naps of ultrafine fibers having a thickness of 0.1 to 10 μm to cover the surface of the base material. A method for purifying water, characterized by irradiating filtered water with ultraviolet rays to purify the filtered water after filtering with a mounted rotary drum type solid-liquid separator. In the present invention, raw water is filtered by the rotary drum type solid-liquid separator to obtain primary filtered water,
After filtering a part or all of the primary filtered water with a hollow fiber membrane filtration device to obtain secondary filtered water, the remaining primary filtered water and the secondary filtered water are irradiated with ultraviolet rays to make the water highly advanced. Can be purified. The filtration with the hollow fiber membrane filtration device may be carried out on a part or the whole amount of the obtained water after irradiating the primary filtered water with ultraviolet rays. In addition, water can be purified more completely by adding an appropriate oxidizing agent to the water to be irradiated with ultraviolet rays. The above water purification method can be preferably used as a pool purification method.
【0006】[0006]
【作用と実施態様例】本発明は、特別なろ過材を装着し
て上流側に設けた回転ドラム式固液分離装置と、紫外線
ランプを用いて下流側に設けた酸化装置とを組み合わせ
た水の浄化装置、およびこの様な装置を利用した水の浄
化方法を基礎技術とするものである。本発明について、
実施態様例を示す図面を参照しつつ説明する。図1は、
本発明を游泳用のプールに利用した実施態様例を示す概
略フローシートであり、本発明の水の浄化方法を実施す
るための装置の実施態様例でもある。OPERATION AND EXAMPLE OF THE INVENTION The present invention is a combination of a rotary drum type solid-liquid separation device equipped with a special filter material and provided on the upstream side, and an oxidizing device provided on the downstream side using an ultraviolet lamp. The purifying device and the method for purifying water using such a device are basic techniques. Regarding the present invention,
An embodiment will be described with reference to the drawings. Figure 1
It is a schematic flow sheet showing an embodiment example in which the present invention is applied to a swimming pool, and is also an embodiment example of an apparatus for carrying out the water purification method of the present invention.
【0007】上流側に設けた回転ドラム式固液分離装置
1に、特殊なろ過材が装着され、水中に含まれている生
物スライムや小さな固形分を分離する作用を有する。た
とえば、特公平4−1647号公報や特公平4−908
1号公報に記載されている濾布および装置がこれに相当
する。さらに、下流側に設ける酸化装置2に装着してあ
る紫外線ランプ10の表面の汚れを防止し、紫外線照射
の効果を持続させる大きな作用をあげることができる。The rotary drum type solid-liquid separation device 1 provided on the upstream side is equipped with a special filter material and has a function of separating biological slime and small solids contained in water. For example, Japanese Patent Publication No. 4-1647 and Japanese Patent Publication No. 4-908.
The filter cloth and device described in Japanese Patent No. 1 correspond to this. Furthermore, it is possible to prevent the surface of the ultraviolet lamp 10 mounted on the oxidation device 2 provided on the downstream side from being soiled and to exert a great effect of sustaining the effect of ultraviolet irradiation.
【0008】図1を参照して本発明に用いる回転ドラム
式固液分離装置1の一例を説明すると、まず、ろ過材を
装着して回転している円筒状のろ過ドラム4の内側に、
プール水などの原水を配管5を通して連続的に送入す
る。ついで、送入された原水は、ろ過ドラム4内の液面
とこれよりも低い受槽6のろ過液面との差圧Δpによっ
て、ろ過ドラム4を通過して受槽6に到達し、ろ過され
る。原水から分離されてろ過ドラム4の内壁に付着した
固形物は、循環ポンプ7でノズル8に送られるろ過水の
一部で逆洗され、排水配管9を径て系外に排出される。An example of the rotary drum type solid-liquid separation device 1 used in the present invention will be described with reference to FIG. 1. First, the inside of a cylindrical filtration drum 4 having a filter medium attached thereto and rotating,
Raw water such as pool water is continuously fed through the pipe 5. Then, the fed raw water passes through the filtration drum 4 and reaches the receiving tank 6 by the differential pressure Δp between the liquid surface in the filtering drum 4 and the filtered liquid surface in the receiving tank 6 lower than this, and is filtered. . The solid matter separated from the raw water and attached to the inner wall of the filtration drum 4 is backwashed with a part of the filtered water sent to the nozzle 8 by the circulation pump 7, and discharged through the drainage pipe 9 to the outside of the system.
【0009】本発明において回転ドラム式固液分離装置
1に装着されるろ過材は重要である。このろ過材は、織
物または編物からなる基材の表面に、その基材を起毛し
て形成させた太さ0.1〜10μmの極細繊維の立毛が
一方向に横たわり、この立毛がろ過層の作用を奏するの
である。横たわってとは、直立していない、あるいは寝
かせてというほどの意味である。ろ過材となる織物また
は編物は、通常、太さが0.1〜10μmのポリアミ
ド、ポリエステル、ポリオレフィン、ポリビニルアルコ
ール系、ポリフルオロエチレン、ポリアクリロニトリル
などの合成繊維の極細繊維で構成されたものを使用す
る。織成や編成の種類はとくに問わないが、織物では朱
子織物が、編物ではハーフ編のトリコット生地が起毛し
やすく好ましい。太さが0.1μm以下の極細繊維は強
度が不足し、10μm以上の繊維は起毛後、直立しやす
く、良好なろ過層を形成しにくい難点がある。起毛方法
は、従来からの公知の手段を用いればよい。このろ過材
を使用することにより、従来、砂ろ過では分離すること
のできなかった5〜10μmの微細な固形成分を、容易
に分離することができる。さらに、このろ過材の使用に
より、回転ドラム式固液分離装置1は、クーリングタワ
ーなどに付着して、従来から課題になっていた寒天様の
生物系のスライムを効率よく分離することができる。か
つ、その様なろ過物を分離しても、このろ過材は従来の
ろ布は異なりろ過物を表面から剥離しやすく、逆洗が容
易で長期にわたって目詰りしない特長がある。In the present invention, the filter material mounted on the rotary drum type solid-liquid separation device 1 is important. In this filter material, naps of ultrafine fibers having a thickness of 0.1 to 10 μm formed by raising the base are laid in one direction on the surface of the base made of a woven or knitted fabric, and the naps of the filtration layer are formed. It works. Lying means not standing upright or lying down. As the woven or knitted material to be the filtering material, usually, a fine fiber made of synthetic fiber such as polyamide, polyester, polyolefin, polyvinyl alcohol, polyfluoroethylene, polyacrylonitrile having a thickness of 0.1 to 10 μm is used. To do. The type of weaving or knitting is not particularly limited, but a satin woven fabric is preferable for the woven fabric, and a half-knit tricot fabric is preferable because it is easily raised. The ultrafine fibers having a thickness of 0.1 μm or less have insufficient strength, and the fibers having a thickness of 10 μm or more are liable to stand upright after being raised, and it is difficult to form a good filtration layer. As a raising method, a conventionally known means may be used. By using this filter material, it is possible to easily separate fine solid components of 5 to 10 μm which could not be separated by sand filtration in the past. Further, by using this filtering material, the rotary drum type solid-liquid separator 1 can be efficiently attached to a cooling tower or the like to efficiently separate agar-like biological slime, which has been a problem in the past. Moreover, even when such a filtered material is separated, this filter material is different from the conventional filter cloth in that the filtered material is easily peeled off from the surface, backwashing is easy, and clogging is not caused for a long time.
【0010】本発明において、回転ドラム式固液分離装
置1の下流に設けられる、紫外線ランプ10を装着した
酸化装置2は、回転ドラム式固液分離装置1では分離す
ることができずに水中に残存した水溶性の不純物を、分
解除去する作用および殺菌作用を有する。使用する紫外
線ランプの種類とその容量は、原水の状態によって選択
するが、波長は184.9mμまたは253.7mμが
好ましい。游泳用のプール水の浄化に使用する場合に
は、照射量として、一般的に1W/人・日程度を目途に
するとよい。酸化槽として特別なものは必要なく、たと
えば、開放系の貯槽に紫外線ランプを浸漬した装置や、
密閉系の円筒反応管に紫外線ランプを浸漬した装置など
を使用することができる。紫外線照射されて浄化した水
は、還流配管11を経てプールに還流される。游泳用プ
ールでは、プール水中の塩素濃度を規定量に維持するた
めに塩素供給装置12から塩素を供給する。In the present invention, the oxidizer 2 equipped with the ultraviolet lamp 10 which is provided downstream of the rotary drum type solid-liquid separator 1 cannot be separated by the rotary drum type solid-liquid separator 1 and is submerged in water. It has an action of decomposing and removing the remaining water-soluble impurities and a bactericidal action. The type of ultraviolet lamp used and its capacity are selected depending on the state of the raw water, but the wavelength is preferably 184.9 mμ or 253.7 mμ. When used to purify swimming pool water for swimming, the irradiation dose should generally be about 1 W / person / day. There is no need for a special oxidizing tank, for example, a device in which an ultraviolet lamp is immersed in an open storage tank,
A device in which an ultraviolet lamp is immersed in a closed cylindrical reaction tube can be used. Water purified by being irradiated with ultraviolet rays is returned to the pool via the return pipe 11. In the swimming pool, chlorine is supplied from the chlorine supply device 12 in order to maintain the chlorine concentration in the pool water at a specified amount.
【0011】浄化の対象となる原水の条件によっては、
回転ドラム式固液分離装置と酸化装置との中間に中空糸
膜ろ過装置を設け、回転ドラム式固液分離装置のろ過水
(一次ろ過水)の一部または全量をろ過して、残留する
細かい粒子をろ過分離した後、このろ過水(二次ろ過
水)と一次ろ過水の残りとを酸化装置に送入し、紫外線
照射すれば、さらに高度に浄化された水を得ることがで
きる。中空糸膜ろ過装置を酸化装置の下流側に設け、酸
化装置を出た水の一部または全量をこれでろ過してもよ
い。使用する中空糸膜としては、たとえば、特開昭61
−238834号公報に記載のポリスルホン系樹脂多孔
膜の中空糸が、機械的強度が高く、目詰まりや耐汚染性
に優れて好適であり、中空糸膜ろ過装置2としては、た
とえば特願平4−270581号願書に添付された明細
書に記載のものがコンパクトで便利である。Depending on the conditions of the raw water to be purified,
A hollow fiber membrane filtration device is installed between the rotating drum type solid-liquid separation device and the oxidation device, and some or all of the filtered water (primary filtered water) of the rotating drum type solid-liquid separation device is filtered to leave a fine residue. After the particles are separated by filtration, the filtered water (secondary filtered water) and the rest of the primary filtered water are sent to an oxidizer and irradiated with ultraviolet rays, whereby highly purified water can be obtained. A hollow fiber membrane filtering device may be provided on the downstream side of the oxidizing device, and a part or the whole amount of the water discharged from the oxidizing device may be filtered with this. The hollow fiber membrane to be used is, for example, JP-A-61 / 1986.
The hollow fiber of the polysulfone-based resin porous membrane described in JP-A-238834 is suitable because of its high mechanical strength and excellent resistance to clogging and contamination. The one described in the specification attached to the -270581 application is compact and convenient.
【0012】図1に示した実施態様例では、中空糸膜ろ
過装置3を酸化装置2の下流側に設け、酸化装置2で処
理した処理水の一部を配管13を通してポンプ14を用
い、中空糸膜ろ過装置3に送入している。中空糸膜ろ過
装置3でろ過した水は配管15を通して逆洗水槽16に
送られる。逆洗水槽16からオーバフローした水は紫外
線照射された水と混合され、還流配管11を経てプール
に循環される。17はいずれも中空糸膜ろ過装置3の逆
洗に使用する配管である。逆洗水は、排水配管18から
排出される。In the embodiment shown in FIG. 1, the hollow fiber membrane filtration device 3 is provided on the downstream side of the oxidizing device 2, and a part of the treated water treated by the oxidizing device 2 is pumped through a pipe 13 using a pump 14 It has been fed into the membrane filter 3. The water filtered by the hollow fiber membrane filtering device 3 is sent to the backwash water tank 16 through the pipe 15. The water that overflows from the backwash water tank 16 is mixed with the water that has been irradiated with ultraviolet rays, and is circulated to the pool via the reflux pipe 11. Each of 17 is a pipe used for backwashing the hollow fiber membrane filtration device 3. The backwash water is discharged from the drainage pipe 18.
【0013】また、本発明の水の浄化方法を実施するに
当って、紫外線を照射する前に原水またはろ過水に酸化
剤を添加してもよい。添加した酸化剤は、紫外線照射の
効果を大きく増大する作用がある。酸化剤としては、次
亜塩素酸ナトリウム、次亜塩素酸カルシウム、過酸化水
素、オゾン、塩素などを用いることができる。使用量
は、原水中の水溶性不純物を理論的に分解できる添加量
以上が必要である。In carrying out the method for purifying water according to the present invention, an oxidizing agent may be added to raw water or filtered water before irradiation with ultraviolet rays. The added oxidizing agent has a function of greatly increasing the effect of ultraviolet irradiation. As the oxidizing agent, sodium hypochlorite, calcium hypochlorite, hydrogen peroxide, ozone, chlorine and the like can be used. The amount used is required to be more than the amount that can theoretically decompose water-soluble impurities in raw water.
【0014】[0014]
【実施例と比較例】次に、本発明を游泳用のプール水の
浄化に利用したので、その結果を説明する。EXAMPLES AND COMPARATIVE EXAMPLES Next, the present invention was applied to the purification of pool water for swimming, and the results will be described.
【0015】実施例および比較例 本発明の水の浄化装置を温水プールに取り付けて運転
し、従来の浄化装置と比較して本発明の効果を確かめ
た。使用した温水プールの容積は275m3 であって、
従来は、1日当り900m3 のプール水を砂ろ過し、塩
素を注入して循環していた。このプールの従来の浄化装
置に並列して、本発明の水の浄化装置を取り付けた。上
流側には回転ドラム式固液分離装置(“トレローム”R
D−750−A3型:東レ(株)製)を取り付け、その
ろ過材には、太さが10μmのポリエステル繊維を48
本束ねたものを経糸とし、太さ約2.4μmのポリエス
テル極細繊維約2000本を緯糸とする織物を、起毛機
を用いて主に緯糸を起毛して製造した、2.4μmの立
毛を有し立毛数が約1000本/mmの立毛朱子織物を
装着した。さらに、その下流側に110Wの紫外線ラン
プ(ST−110NF型:セン特殊光源(株)製)を装
着した0.7×0.95×(深さ)1.3m、容量0.
78m3 の酸化槽を設けた。紫外線の照射厚さは350
mmにした。従来と同じく、本発明の浄化装置に1日当
り900m3 のプール水を循環し、塩素を注入して、本
発明の効果を確かめた。このときに測定した游泳人口と
残留塩素および過マンガン酸カリウム消費量との関係の
一例を図2に示す。図2に示した結果に加えて、本発明
を実施したときには、従来あったプール独特の臭いが消
失していた。これに対し比較例として、同じ条件下で、
従来の砂ろ過を実施し、塩素を注入して循環していた時
の状態を図3に示した。比較に用いた下向流圧力式砂ろ
過装置は、直径2.4m、高さ2.5mの密閉円筒型で
有効ろ過面積4.5m2 であった。なお、残留塩素量
は、厚生省通達(昭和53年5月25日)に準拠し、過
マンガン酸カリウム消費量(図中、KM消費量と略記)
は上水試験方法12(日本水道協会)に準拠して測定し
た。Examples and Comparative Examples The water purifying apparatus of the present invention was installed in a hot water pool and operated, and the effect of the present invention was confirmed by comparison with a conventional purifying apparatus. The volume of the warm water pool used was 275 m 3 ,
Conventionally, 900 m 3 of pool water was sand filtered per day, and chlorine was injected to circulate it. The water purification apparatus of the present invention was installed in parallel with the conventional purification apparatus for this pool. On the upstream side, a rotary drum type solid-liquid separator (“Trelom” R
D-750-A3 type: manufactured by Toray Industries, Inc. is attached, and the filter material is made of polyester fiber having a thickness of 10 μm.
A woven fabric in which the bundled warp is used as the warp, and about 2000 microfibers of polyester with a thickness of about 2.4 μm are used as the weft is manufactured by raising the weft mainly with a raising machine. A napped satin fabric having a number of naps of about 1000 / mm was attached. Further, a 110 W ultraviolet lamp (ST-110NF type: manufactured by Sen Special Light Source Co., Ltd.) was mounted on the downstream side of 0.7 x 0.95 x (depth) 1.3 m and a capacity of 0.
A 78 m 3 oxidation tank was provided. UV irradiation thickness is 350
mm. The effect of the present invention was confirmed by circulating 900 m 3 of pool water per day and injecting chlorine into the purifying apparatus of the present invention as in the conventional case. An example of the relationship between the swimming population measured at this time and the residual chlorine and potassium permanganate consumption is shown in FIG. In addition to the results shown in FIG. 2, when the present invention was carried out, the conventional peculiar odor of the pool disappeared. On the other hand, as a comparative example, under the same conditions,
FIG. 3 shows a state in which conventional sand filtration was performed and chlorine was injected to circulate. The downflow pressure type sand filter used for comparison was a closed cylindrical type having a diameter of 2.4 m and a height of 2.5 m, and an effective filtration area of 4.5 m 2 . The amount of residual chlorine is based on the notification of the Ministry of Health and Welfare (May 25, 1978), and consumption of potassium permanganate (abbreviated as KM consumption in the figure)
Was measured in accordance with water supply test method 12 (Japan Waterworks Association).
【0016】この2例の結果を比較すると、実施例で
は、残留塩素濃度が高濃度に安定しているが、比較例で
は、塩素が急激に消費され、減少している。比較例で
は、游泳者の増加によって持ち込まれる窒素化合物が蓄
積して塩素と反応し、一部は臭いの元凶であるクロラミ
ンを生成していると考えられる。実施例においては、窒
素化合物が窒素などに分解され、塩素と反応したり、吸
着されることが少ないので、残留塩素が安定し、また、
水溶性の有機物も分解されるので、過マンガン酸カリウ
ム消費量も低い値で安定するものと考えられる。Comparing the results of these two examples, in the example, the residual chlorine concentration is stable at a high concentration, but in the comparative example, chlorine is rapidly consumed and decreased. In the comparative example, it is considered that the nitrogen compounds brought in by the increase in the number of swimmers accumulate and react with chlorine, and partly produces chloramine, which is a source of odor. In the examples, the nitrogen compound is decomposed into nitrogen or the like, reacts with chlorine or is less adsorbed, so that residual chlorine is stable, and
Since the water-soluble organic matter is also decomposed, it is considered that the consumption amount of potassium permanganate is stable at a low value.
【0017】[0017]
【発明の効果】本発明の水の浄化装置および水の浄化方
法を用いることにより、紫外線照射によって、水溶性の
有機物が分解され過マンガン酸カリ消費量が低い値に押
さえられる。従って、游泳用のプールでは、大量の水を
交換する必要がなく、節水を図ることができる。一方、
紫外線照射のためのランプは、その上流に設けられた高
性能の回転ドラム式固液分離装置によって、ランプ表面
に付着しやすい生物スラムや微粒子が除去されているの
で、長時間にわたり効率よく紫外線を照射することがで
きる。水溶性有機物の含有量が大きく、塩素を注入する
必要がある游泳用のプールなどでは、水溶性有機物が低
く押さえられるので、残留塩素濃度が安定し、また、水
溶性有機物中の窒素化合物が早く分解されるので、悪臭
の原因とされているクロラミンの生成が押さえられる。
本発明に、さらに中空糸膜ろ過装置を配置すると、凝集
剤を添加しないでコロイド成分を除去することが可能に
なり、1μm以下の微粒子を除去するとともに、凝集剤
に起因する凝集物の発生がなくなるので、濁りや白濁の
発生を防止する効果がある。中空糸膜ろ過装置を酸化装
置の上流側に配置すると、紫外線ランプの汚れをさらに
減少することができる。従って、本発明の水の浄化装置
および水の浄化方法は、もっぱら循環使用する游泳用の
プール水、クーリングタワー水、工業用水などの浄化
や、ビル、マンションなどの中水道用水に利用するリサ
イクル水を浄化するのに好適である。By using the water purifying apparatus and the water purifying method of the present invention, the water-soluble organic matter is decomposed by the irradiation of ultraviolet rays and the consumption amount of potassium permanganate is suppressed to a low value. Therefore, in the swimming pool, it is not necessary to exchange a large amount of water, and water can be saved. on the other hand,
The UV irradiation lamp uses a high-performance rotary drum type solid-liquid separator installed upstream of the lamp to remove biological slums and fine particles that tend to adhere to the lamp surface. Can be irradiated. The content of water-soluble organic matter is large, and in swimming pools that require chlorine injection, the water-soluble organic matter can be kept low, so the residual chlorine concentration is stable, and the nitrogen compounds in the water-soluble organic matter are fast. As it is decomposed, the production of chloramine, which is the cause of malodor, is suppressed.
When a hollow fiber membrane filtering device is further arranged in the present invention, the colloid component can be removed without adding a coagulant, and fine particles of 1 μm or less can be removed, and a coagulant caused by the coagulant is generated. Since it disappears, it is effective in preventing the occurrence of turbidity or white turbidity. By disposing the hollow fiber membrane filtering device on the upstream side of the oxidizing device, the contamination of the ultraviolet lamp can be further reduced. Therefore, the water purifying apparatus and the water purifying method of the present invention are intended to purify pool water for swimming, cooling tower water, industrial water, etc. which are exclusively used for circulation, and recycled water used for tap water such as buildings and condominiums. It is suitable for purification.
【図1】 本発明を游泳用のプールに利用した実施態様
例を示す概略フローシート。FIG. 1 is a schematic flow sheet showing an embodiment example in which the present invention is applied to a swimming pool.
【図2】 温水プールで本発明を実施したときの水質の
変動を示すグラフ。FIG. 2 is a graph showing fluctuations in water quality when the present invention is carried out in a warm water pool.
【図3】 温水プールの従来の水質の変動を示すグラ
フ。FIG. 3 is a graph showing changes in conventional water quality of a warm water pool.
1:回転ドラム式固液分離装置 2:酸化装置 3:中空糸膜ろ過装置 4:ろ過ドラム 5:原水
配管 6:受槽 7:循環ポンプ 8:ノズル 9:排水配管 1
0:紫外線ランプ 11:還流配管 12:塩素供給装置 13:配管
14:ポンプ 15:配管 16:逆洗水槽 17:逆洗用配管
18:排水配管1: Rotating drum type solid-liquid separation device 2: Oxidation device 3: Hollow fiber membrane filtration device 4: Filtration drum 5: Raw water pipe 6: Receiving tank 7: Circulation pump 8: Nozzle 9: Drainage pipe 1
0: UV lamp 11: Reflux pipe 12: Chlorine supply device 13: Pipe 14: Pump 15: Pipe 16: Backwash water tank 17: Backwash pipe
18: Drainage pipe
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 N 7446−4D R 7446−4D 503 A 7446−4D 504 B 7446−4D E04H 4/12 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical indication C02F 9/00 N 7446-4D R 7446-4D 503 A 7446-4D 504 B 7446-4D E04H 4 / 12
Claims (9)
れ、太さ0.1〜10μmの極細繊維の立毛が横たわっ
て基材の表面を覆ってなるろ過材を装着した回転ドラム
式固液分離装置が、下流側に、紫外線ランプを装着した
酸化装置が設けられていることを特徴とする、水の浄化
装置。1. A rotary drum type in which a base material of a woven or knitted fabric is napped on the upstream side, and a napped fiber of ultrafine fibers having a thickness of 0.1 to 10 μm lies down and covers the surface of the base material. A water purification device, wherein a solid-liquid separation device is provided on the downstream side with an oxidizer equipped with an ultraviolet lamp.
置が設けられていること特徴とする、請求項1に記載の
水の浄化装置。2. The water purifying device according to claim 1, further comprising a hollow fiber membrane filtering device provided on the further downstream side of the oxidizing device.
間に中空糸膜ろ過装置が設けられていることを特徴とす
る、請求項1に記載の水の浄化装置。3. The water purification apparatus according to claim 1, further comprising a hollow fiber membrane filtration device provided between the rotary drum type solid-liquid separation device and the oxidation device.
置を用いた、プール浄化装置。4. A pool purification apparatus using the water purification apparatus according to claim 1, 2, or 3.
毛され、太さ0.1〜10μmの極細繊維の立毛が横た
わって基材の表面を覆ってなるろ過材を装着した回転ド
ラム式固液分離装置でろ過した後、ろ過水に紫外線を照
射して浄水を得ることを特徴とする、水の浄化方法。5. A rotary drum equipped with a filter medium, wherein raw water is first raised on a base material of a woven or knitted fabric, and standing fibers of ultrafine fibers having a thickness of 0.1 to 10 μm lie down to cover the surface of the base material. A method for purifying water, characterized by obtaining filtered water by irradiating filtered water with ultraviolet rays after filtering with a solid-liquid separation device.
分離装置でろ過して一次ろ過水とし、一次ろ過水の一部
または全量を、中空糸膜ろ過装置でろ過して二次ろ過水
にした後、一次ろ過水の残りおよび二次ろ過水に紫外線
を照射して浄水を得ることを特徴とする、水の浄化方
法。6. Raw water is filtered by the rotary drum type solid-liquid separator according to claim 5 to obtain primary filtered water, and a part or all of the primary filtered water is filtered by a hollow fiber membrane filtering device to obtain secondary water. A method for purifying water, which comprises obtaining purified water by irradiating the remaining primary filtered water and the secondary filtered water with ultraviolet rays after making the filtered water.
の一部または全量を、さらに中空糸膜ろ過装置でろ過し
て浄水を得ることを特徴とする、水の浄化方法。7. A method for purifying water, characterized in that a part or all of the water obtained by the method according to claim 5 is further filtered by a hollow fiber membrane filtration device to obtain purified water.
浄化する水に酸化剤を添加することを特徴とする、請求
項5、6または7に記載の水の浄化方法。8. In any step before irradiation with ultraviolet rays,
The method for purifying water according to claim 5, 6 or 7, wherein an oxidizing agent is added to the water to be purified.
化方法を用いたプール浄化方法。9. A pool purification method using the water purification method according to claim 5, 6, 7, or 8.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5212790A JPH0760264A (en) | 1993-08-27 | 1993-08-27 | Pparatus and method for purification of water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP5212790A JPH0760264A (en) | 1993-08-27 | 1993-08-27 | Pparatus and method for purification of water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0760264A true JPH0760264A (en) | 1995-03-07 |
Family
ID=16628431
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP5212790A Pending JPH0760264A (en) | 1993-08-27 | 1993-08-27 | Pparatus and method for purification of water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0760264A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2003002468A1 (en) * | 2001-06-28 | 2003-01-09 | Zenon Environmental Inc. | A process for reducing concentrations of hair, trash, or fibrous materials in a waste water |
JP2005535439A (en) * | 2002-08-08 | 2005-11-24 | アルカル フィルトレーション システムズ シー.エス. リミテッド | Method and apparatus for treating water, especially marine water |
JP2006218361A (en) * | 2005-02-09 | 2006-08-24 | Kurita Water Ind Ltd | Apparatus and method for treating water |
CN100383056C (en) * | 2004-09-09 | 2008-04-23 | 天津理工大学 | Drum photocatalysis reactor |
-
1993
- 1993-08-27 JP JP5212790A patent/JPH0760264A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2003002468A1 (en) * | 2001-06-28 | 2003-01-09 | Zenon Environmental Inc. | A process for reducing concentrations of hair, trash, or fibrous materials in a waste water |
JP2005535439A (en) * | 2002-08-08 | 2005-11-24 | アルカル フィルトレーション システムズ シー.エス. リミテッド | Method and apparatus for treating water, especially marine water |
CN100383056C (en) * | 2004-09-09 | 2008-04-23 | 天津理工大学 | Drum photocatalysis reactor |
JP2006218361A (en) * | 2005-02-09 | 2006-08-24 | Kurita Water Ind Ltd | Apparatus and method for treating water |
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