JPH0710386B2 - Water purification equipment - Google Patents
Water purification equipmentInfo
- Publication number
- JPH0710386B2 JPH0710386B2 JP3497489A JP3497489A JPH0710386B2 JP H0710386 B2 JPH0710386 B2 JP H0710386B2 JP 3497489 A JP3497489 A JP 3497489A JP 3497489 A JP3497489 A JP 3497489A JP H0710386 B2 JPH0710386 B2 JP H0710386B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- jacket
- filter medium
- filter material
- filter
- 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
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- Treatment Of Water By Oxidation Or Reduction (AREA)
- Water Treatment By Sorption (AREA)
- Physical Water Treatments (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は湖沼の水質あるいは飲料用水または工場や家庭
等の排水を浄化する水質浄化装置の改良に関する。TECHNICAL FIELD The present invention relates to an improvement of a water purification apparatus for purifying water quality of lakes and marshes, drinking water, or wastewater of factories, households, and the like.
(1) 湖沼の場合 最近、例えば公園内の池等の景観を向上するため、池の
水質を浄化して、水の透明度を上げ、池に放流されてい
る鯉や金魚等を観賞しやすくすることが行われている。(1) In the case of lakes Recently, in order to improve the scenery of ponds in parks, for example, the quality of the water in the ponds is purified, the transparency of the water is increased, and the carps and goldfish released to the ponds are easier to see. Is being done.
従来、水質を浄化するには、装置の内部に例えば砂やハ
ニカム等で構成してなる濾過槽を設け浮遊物を除去する
方法、塩素や銅等の殺藻剤を利用する方法あるいは水の
内部に凝集剤を入れ、水中の浮遊物を凝集する方法がと
られている。Conventionally, in order to purify water quality, a method of removing suspended matter by providing a filter tank composed of sand or a honeycomb inside the apparatus, a method of using an algaecide such as chlorine or copper, or the inside of water A flocculant is added to the solution to flocculate suspended matter in water.
しかし、装置の内部に砂やハニカム等で構成してなる濾
過槽を設け、浮遊物を除去する方法によると、砂やハニ
カム等に浮遊物がたまり、目詰まりしやすく、浮遊物の
吸着能力が減少し、また掃除に手数を要する。However, according to the method of removing a suspended matter by providing a filter tank composed of sand or a honeycomb inside the apparatus, the suspended matter is easily accumulated in the sand or the honeycomb, and the clogging is apt to occur, and the adsorption ability of the suspended matter is high. It is reduced and cleaning is troublesome.
さらに、水の内部に塩素や銅等の殺藻剤や凝集剤を入れ
る方法によると、アオコ等の藻類を除去し、また浮遊物
を凝集することはできるが、殺藻剤や凝集剤が多い場合
は水中の鯉や金魚等が死亡したり、これらの薬剤により
水質の二次汚染が起こる欠点がある。Furthermore, according to the method of adding an algaecide such as chlorine or copper or a coagulant to the inside of water, it is possible to remove algae such as water-bloom and flocculate the suspended matter, but there are many algicides and flocculants. In this case, there are drawbacks such as death of carp and goldfish in water, and secondary pollution of water quality due to these chemicals.
(2) 工場や家庭等の下水処理の場合 工場や家庭等からの排水を処理するには一般に、下水処
理場において、排水を物理的に処理した後、塩素を入れ
殺菌し処理水を放流することが行われている。(2) In the case of sewage treatment from factories and households In order to treat wastewater from factories and households, generally, in a sewage treatment plant, after physically treating the wastewater, chlorine is added to sterilize and the treated water is discharged. Is being done.
しかし同方法によると、塩素の影響で水生植物や観賞魚
が死滅し、二次水を利用したい公園の池等では利用する
ことができず、利用範囲が限定されてしまう欠点があ
る。However, according to this method, aquatic plants and ornamental fish are killed by the influence of chlorine, and they cannot be used in ponds of parks where secondary water is desired to be used, which limits their use range.
(3) 飲料用水の場合 湖沼や貯水池の水は、沈殿・濾過後、塩素消毒して水道
水として利用されるが、最近は近隣の工場や住居からの
排水あるいは農地からの肥料を含んだ水が湖沼や貯水池
に流入し、富栄養化が進み、水中に藍藻類や緑藻類が異
常繁殖し、これらの藻類から分泌される化学物質(例え
ばボルネオール等)によって、水道水は異常なカビ臭が
発生する。(3) Water for drinking Water in lakes and reservoirs is used as tap water after being precipitated and filtered and then sterilized with chlorine. Recently, water containing fertilizer from drainage from neighboring factories and houses or fertilizer from farmland has been used. Enter into lakes and reservoirs, eutrophication progresses, cyanobacteria and green algae multiply abnormally in the water, and chemical substances (eg, borneol) secreted by these algae cause abnormal musty odor in tap water. To do.
従来これを防ぐ方法として、多量の塩素消毒や活性炭に
る吸着等による方法がとられている。Conventionally, as a method for preventing this, a method using a large amount of chlorine disinfection or adsorption on activated carbon has been used.
しかし塩素を利用すると、新たに落葉や植物の腐敗物に
含まれるフミン質と塩素が反応して発ガン物質(例えば
トリハロメタン等)が生成する欠点がある。However, the use of chlorine has a drawback that humic substances newly contained in leaf litter and plant spoilage materials react with chlorine to generate a carcinogen (eg, trihalomethane).
また活性炭は吸着性が高いが、活性炭を再利用するには
多大の設備が必要で、設備費が高くなる欠点がある。In addition, activated carbon has a high adsorptivity, but it requires a large amount of equipment to reuse the activated carbon, which has the drawback of increasing the equipment cost.
本発明は上記の諸点に鑑み発明したものであって、殺菌
ランプを収納してなるジャケットの外壁に付着した汚れ
と、濾過材に溜った浮遊物を簡単に除去することがで
き、また薬害により鯉や金魚等が死亡する恐れがなく、
且つ二次汚染が発生することがなく、さらに発ガン物質
を分解除去し、小形に構成することのできる水質浄化装
置を提供することを目的とする。The present invention has been made in view of the above points and is capable of easily removing dirt adhering to the outer wall of the jacket accommodating the sterilizing lamp and suspended matter accumulated in the filter medium, and also by chemical damage. There is no risk of carp or goldfish dying,
Moreover, it is an object of the present invention to provide a water purification apparatus that does not cause secondary pollution and that decomposes and removes carcinogens and that can be configured in a small size.
本発明は上記した課題を解決するために、次の構成とす
る。すなわち、濾材収納槽の内部に、ジャケットに収納
してなる適数の殺菌ランプを収納し、同殺菌ランプの下
側に位置して、水を浄化処理をしているときは、水中の
一部に密集する濾過材を収納する。The present invention has the following configuration in order to solve the above problems. That is, inside the filter medium storage tank, an appropriate number of sterilizing lamps housed in a jacket are stored, and when the water is located under the sterilizing lamp and the water is being purified, a part of the water is removed. Stores the filter material that is densely packed in.
また同濾過材の下側に位置して散気盤を設ける。An air diffuser is provided below the filter medium.
そして水を処理しているときは、濾過材により水中の浮
遊物を吸着し、さらに逆洗時に散気盤からのエアーによ
り、濾過材が水中に浮遊し、濾過材同志あるいは濾過材
が殺菌ランプを収納しているジャケットに接触し、ジャ
ケットに付着する汚れ、濾過材に含まれる塵埃を除去す
る。When water is being treated, the filter material absorbs suspended matter in the water, and during backwashing, the air from the air diffuser causes the filter material to float in the water, and the filter material or the filter material is a sterilization lamp. Contacting the jacket that stores the product, removes dirt and dust contained in the jacket and filter material.
また他の構造として、濾材収納槽の内部のジャケットに
収納してなる適数の殺菌ランプと、水中の一部に密集す
る濾過材の間に、オゾン供給体を配設し、同オゾンの作
用により、水中の病原菌(例えば、大腸菌)を殺菌し、
有機物を光酸化分解し、CODやBODの低減や臭気成分の低
減を図る。As another structure, an ozone supply body is provided between an appropriate number of sterilizing lamps housed in a jacket inside a filter medium storage tank and a filter medium that is densely packed in a part of water, and the ozone action is performed. Sterilize pathogens in water (eg E. coli)
Photo-oxidizes and decomposes organic substances to reduce COD and BOD and odor components.
上記した水質浄化装置によると、濾材収納槽の水を処理
しているときは、殺菌ランプからの紫外線が水中に照射
され水中の病原菌(例えば、大腸菌)を殺菌し、有機物
を光酸化分解し、CODやBODの低減や臭気成分の低減がは
かられる。According to the water purification apparatus described above, when the water in the filter medium storage tank is being treated, ultraviolet rays from the sterilization lamp are irradiated into the water to sterilize pathogenic bacteria (for example, Escherichia coli) in the water, and photooxidatively decompose organic matter, COD and BOD can be reduced and odor components can be reduced.
また濾過材により水中の浮遊物を吸着する。In addition, the filter material adsorbs suspended matter in water.
さらに逆洗時に散気盤からのエアーにより、濾過材が水
中に浮遊し、濾過材同志あるいは濾過材が殺菌ランプを
収納しているジャケットに接触し、ジャケットに付着す
る汚れ、濾過材に含まれる塵埃を除去し、外部に排出す
ることができる。Further, when backwashing, the air from the air diffuser causes the filter material to float in the water, and the filter material or the filter material comes into contact with the jacket containing the sterilization lamp and is attached to the jacket. Dust can be removed and discharged to the outside.
なお殺菌ランプから生成されたオゾンあるいはオゾナイ
ザーからのオゾンを水中に注入することによって、さら
に水中の病原菌(例えば、大腸菌)を殺菌し、有機物を
光酸化分解し、CODやBODの低減や臭気成分の低減をより
促進することができる。By injecting ozone generated from a sterilization lamp or ozone from an ozonizer into water, pathogens in the water (for example, Escherichia coli) are further sterilized, and organic matter is photooxidatively decomposed to reduce COD and BOD and reduce odorous components. The reduction can be further promoted.
さらに濾過材の前に紫外線、オゾン処理を行なうことに
よりオゾンや酸化性能力の成分酸素や酸化物を持つ水が
作られる。この水が濾過材の間をくぐる時、濾過材の間
に乱流を起こし、水中のCODやBODとの反応が促進され、
水の浄化がはかどる。Further, by carrying out an ultraviolet ray treatment and an ozone treatment before the filter medium, ozone and water having an oxygen-containing component oxygen or oxide are produced. When this water passes between the filter media, a turbulent flow occurs between the filter media, promoting the reaction with COD and BOD in the water,
Purification of water is accelerated.
以下本発明の実施例を第1図及び第5図について説明す
る。図において、1は濾材収納槽、2はジャケット3に
収納してなる適数の殺菌ランプであって、例えば65ワッ
トの殺菌ランプを12本収納して構成してある。また同ジ
ャケット3は、例えば石英ガラスで構成する。4は殺菌
ランプ2の下側に位置し、且つ網体5の上面に収納して
なる濾過材であって、例えば細い化学繊維をボール状に
束ねて、直径30mm程度に構成し、例えば40cm乃至50cm程
度の厚さで積層して構成してある。また同濾過材3は水
を浄化処理しているときは、同網体5の上面に密集して
おり、逆洗時に散気盤からのエアーを送ることにより、
濾過材同志あるいは濾過材がジャケットに接触し、ジャ
ケットに付着する汚れ、濾過材に含まれる塵埃を除去
し、外部に排出することができる。An embodiment of the present invention will be described below with reference to FIGS. In the figure, 1 is a filter medium storage tank, 2 is an appropriate number of sterilization lamps stored in a jacket 3, and for example, 12 sterilization lamps of 65 watts are stored. The jacket 3 is made of, for example, quartz glass. Reference numeral 4 denotes a filter medium located below the sterilization lamp 2 and housed on the upper surface of the net body 5. For example, thin chemical fibers are bundled into a ball shape to have a diameter of about 30 mm, for example, 40 cm to 40 cm. It is constructed by stacking with a thickness of about 50 cm. Further, the filter medium 3 is densely gathered on the upper surface of the mesh body 5 while purifying water, and by sending air from the air diffuser during backwashing,
The filter media or the filter media come into contact with the jacket, and the dirt adhering to the jacket and the dust contained in the filter media can be removed and discharged to the outside.
6は濾過材3の下側に位置して設けた散気盤であって、
逆洗時に水中にエアーを送る。7は水位センサーであっ
て、濾材収納槽1の内部の水位を検知する。8は給水パ
イプ、9は処理水注出口、10は逆洗時の汚水排出孔であ
る。11はエアーを水中に送るためのコンプレッサーであ
る。6 is an air diffuser located below the filter medium 3,
Send air into the water when backwashing. A water level sensor 7 detects the water level inside the filter medium storage tank 1. Reference numeral 8 is a water supply pipe, 9 is a treated water injection port, and 10 is a wastewater discharge hole in backwashing. 11 is a compressor for sending air into the water.
また第2図に示すように、殺菌ランプから生成されるオ
ゾンをオゾン散気盤12を通して、再度水中に注入し、水
中の病原菌(例えば、大腸菌)を殺菌し、有機物を光酸
化分解し、CODやBODの低減や臭気成分の低減をより促進
することもできる。なおオゾンはオゾナイザーから送ら
れるものを利用してもよい。Further, as shown in FIG. 2, ozone generated from the sterilization lamp is injected into the water again through the ozone diffuser 12 to sterilize pathogenic bacteria (for example, Escherichia coli) in the water, photooxidatively decompose organic matter, and COD. It is also possible to further promote reduction of BOD and BOD and reduction of odorous components. Note that ozone sent from an ozonizer may be used.
次に実施例を説明する。Next, examples will be described.
〔実験例1〕 上記した第1図の水質浄化装置を用いて、観賞魚として
鯉を飼育している50m3の池に、1日に3回転の割合で池
水を循環処理を行なった。その結果、第3図に示すよう
な経過で逆洗時に濾過材が石英ジャケッットに接触した
試験用ジャケッットが濾過材が石英ジャケットに接触し
ないようにした対照用ジャケットに比べて紫外線254の
透過率の維持率の優れることを得た。[Experimental Example 1] Using the water purification apparatus of Fig. 1 described above, the pond water was circulated at a rate of 3 times a day in a pond of 50 m 3 in which carp is raised as an ornamental fish. As a result, the filter material contacted the quartz jacket during backwashing as shown in FIG. 3, and the transmittance of the ultraviolet rays 254 was higher than that of the control jacket in which the filter material did not contact the quartz jacket. It has an excellent maintenance rate.
試験用ジャケットは、対照用ジャケットに比べ、ジャケ
ット表面の汚れが少なく、ジャケット外表面の清掃は、
年1回行なうだけでよく、対照用ジャケットの月1回に
比べ大幅に省力化された。The test jacket has less dirt on the jacket surface than the control jacket, and the outer surface of the jacket is cleaned
It only needs to be done once a year, which is significantly labor-saving compared to the monthly comparison jacket.
また逆洗時の濾過材の洗浄効率がよくなり、表1のよう
に捕捉SSの剥離は容易となり濾過材中の残留SSの減少化
に効果がある。Further, the cleaning efficiency of the filter medium at the time of backwashing is improved, the separation of the trapped SS is facilitated as shown in Table 1, and it is effective in reducing the residual SS in the filter medium.
そのために濾過圧力が増大し、第4図に示すように濾過
器の圧力損失は顕著に低下し、池のSS濃度は低下した。 As a result, the filtration pressure increased, the pressure loss of the filter decreased significantly, and the SS concentration in the pond decreased, as shown in FIG.
〔実験例2〕 上記した第2図の水質浄化装置により、観賞魚として鯉
を飼育している50m3の池に、2.8回転/日の池水の循環
処理を行った。その結果、表2に示すような経過で水質
は浄化された。[Experimental Example 2] The water purification apparatus of Fig. 2 described above was used to circulate 2.8 revolutions / day of pond water on a pond of 50 m 3 in which carp is raised as an ornamental fish. As a result, the water quality was purified as shown in Table 2.
つまり表2よりわかるように、SS(懸濁物)の量は徐々
に下がり、また透視度は徐々に上がり、当初懸濁物のた
め池内で見えなかった魚影が3日後には、はっきり見え
るようになった。 In other words, as can be seen from Table 2, the amount of SS (suspension) gradually decreased and the transparency gradually increased, and fish shadows that were not visible in the pond due to the suspension were clearly visible after 3 days. It became so.
またCOD(化学的酸素要求量)は減少し、水中の有機物
は減少したことが判る。It can also be seen that COD (chemical oxygen demand) decreased and organic matter in water decreased.
またORP(水の活性化の程度)は増大し、水の活性化が
徐々に進んでいく状態が判る。Also, it can be seen that ORP (degree of activation of water) increases and activation of water gradually progresses.
〔実験例3〕 次に水中に含まれる魚病菌の量の変化についての実験結
果を説明する。[Experimental Example 3] Next, experimental results regarding changes in the amount of fish disease bacteria contained in water will be described.
表3より明らかなように、ビブリオ菌、エロモナス菌は
日と共に減少し、4日目で0になる。 As is clear from Table 3, the vibrio bacteria and the Aeromonas bacteria decrease with the lapse of time, and become zero on the 4th day.
なお実験結果は表2に示す条件と同一である。The experimental results are the same as the conditions shown in Table 2.
〔実験例4〕 次に工場や家庭等における下水処理を処理し得た、二次
処理水を原水とした実験結果を表4に従い説明する。[Experimental Example 4] Next, an experimental result using secondary treated water as raw water, which has been treated for sewage treatment in factories, households, etc., will be described according to Table 4.
表4における処理水の値は、上記した水質浄化装置によ
り、1回通過処理した後のものである。 The values of the treated water in Table 4 are the values after one-pass treatment by the water purification device described above.
同表によると、SSの除去により、SSの成分に起因するBO
D、CODが減少し、水質が向上することが判る。According to the table, due to the removal of SS, the BO caused by the SS component
It can be seen that D and COD are reduced and water quality is improved.
またランプより発生する紫外線とオゾンにより、大腸菌
は1回通過処理後は0になり、またBOD、CODは処理と共
に減少するので、発ガン物質の源となるフミン質を中心
とする有機物が減少し、処理水の応用範囲は拡大する。Also, due to the ultraviolet rays and ozone generated from the lamp, E. coli becomes 0 after the single pass treatment, and BOD and COD decrease with the treatment, so organic substances such as humic substances which are the source of carcinogens decrease. The application range of treated water is expanded.
なお表4の実験は、前記実施例第2図に示す装置を用い
て行ったものである。The experiment of Table 4 was carried out by using the apparatus shown in FIG.
なお第5図に示すように、濾材収納槽1の上部に、処理
水注出口13を設け、濾材収納槽1内に水を逆に流しても
第1図に示す上記装置と同程度に処理効果を得ることが
できる。As shown in FIG. 5, a treated water pouring port 13 is provided in the upper part of the filter medium storage tank 1 so that even if water flows backward in the filter medium storage tank 1, the treated water is treated to the same extent as the above-mentioned device shown in FIG. The effect can be obtained.
本発明は上記したように、水を浄化処理をしているとき
は、殺菌ランプからの紫外線が水中に照射され水中の病
原菌を殺菌すると共に、発ガン物質の源となる有機物を
分解除去することができる。As described above, the present invention, when purifying water, sterilizes pathogenic bacteria in water by irradiating water with ultraviolet rays from a sterilizing lamp and decomposes and removes organic substances that are sources of carcinogens. You can
またCODやBODの低減や臭気成分の低減することができ、
さらに二次汚染の発生や恐れもない。Also, COD and BOD can be reduced and odor components can be reduced.
Furthermore, there is no risk of occurrence of secondary pollution.
また濾過材により水中の浮遊物を吸着し、水中の塵埃等
を吸着し水を効果的に浄化することができると共に紫外
線やオゾンで酸化能力の高められ活性化された水が濾過
材の間で、CODやBODなどの不純物と接触が容易となり水
質浄化が促進される効果がある。In addition, the filter material can adsorb suspended solids in the water, can adsorb dust and the like in the water to effectively purify the water, and at the same time, the water that has been activated due to its increased oxidation ability by ultraviolet rays and ozone can be activated. It has the effect of facilitating water purification by facilitating contact with impurities such as COD and BOD.
また逆洗時に散気盤からのエアーにより、濾過材が水中
に浮遊し、濾過材同志あるいは濾過材が殺菌ランプを収
納しているジャケットに接触し、ジャケットに付着する
汚れ、濾過材に含まれる塵埃を除去することができる。Also, during backwashing, air from the air diffuser causes the filter material to float in the water, and either the filter material or the filter material comes into contact with the jacket containing the sterilization lamp and is attached to the jacket. Dust can be removed.
とくにジャケットの外表面に付着した汚れが逆洗時毎に
自動的に洗浄されるので、ジャケット内の紫外線ランプ
からの紫外線透過率が回復される。それ故水中の紫外線
の照射効果が、より一層増大する。In particular, dirt adhering to the outer surface of the jacket is automatically cleaned every time backwashing is performed, so that the ultraviolet transmittance from the ultraviolet lamp in the jacket is restored. Therefore, the irradiation effect of ultraviolet rays in water is further increased.
さらにジャケット外表面の清掃メンテ作業回数も軽減さ
れ、省力化される。In addition, the number of maintenance work for cleaning the outer surface of the jacket is reduced, which saves labor.
また濾過材の洗浄度合が高いので、濾過材の濾過能力が
増大し、圧力損失も少なく濾過効率が1段と上昇する。Further, since the cleaning degree of the filtering material is high, the filtering ability of the filtering material is increased, the pressure loss is small, and the filtering efficiency is further increased.
さらに殺菌ランプと濾過材は同一の濾材収納槽に収納さ
れているので、装置を小形に構成することができ、湖沼
の水質、飲料用水、工場や家庭等の排水を浄化する装置
として利用価値が大きい。Furthermore, since the sterilization lamp and the filter medium are stored in the same filter medium storage tank, the device can be configured in a small size, and is useful as a device for purifying water quality in lakes, drinking water, and wastewater from factories and households. large.
第1図は本発明に係る水質浄化装置の側面図、第2図は
他の実施例図、第3図は紫外線透過率の変化状態を示す
図、第4図は圧力損失の変化状態を示す図、第5図は水
を逆に流したときの水質浄化装置の側面図である。 1……濾材収納槽 2……殺菌ランプ 3……濾過材 6……散気盤FIG. 1 is a side view of a water purification apparatus according to the present invention, FIG. 2 is a view of another embodiment, FIG. 3 is a view showing a change state of ultraviolet transmittance, and FIG. 4 is a change state of pressure loss. FIG. 5 and FIG. 5 are side views of the water purification device when water flows backward. 1 ... Filter material storage tank 2 ... Sterilization lamp 3 ... Filter material 6 ... Air diffuser
───────────────────────────────────────────────────── フロントページの続き (72)発明者 鈴木 信広 栃木県栃木市国府町字萱場1番地 三井三 池化工機株式会社内 (72)発明者 武田 幸雄 栃木県栃木市国府町字萱場1番地 三井三 池化工機株式会社内 審査官 富永 正史 (56)参考文献 実開 昭58−195692(JP,U) ─────────────────────────────────────────────────── ─── Continuation of front page (72) Nobuhiro Suzuki No. 1 Kayaba, Kokufu-cho, Tochigi-shi, Tochigi Mitsui Miike Chemical Machinery Co., Ltd. (72) Yukio Takeda No. 1 Kayaba, Kokufu, Tochigi-shi, Tochigi Mitsui Miike Kakoki Co., Ltd. Examiner Masafumi Tominaga (56) References
Claims (2)
てなる適数の殺菌ランプを収納し、また同殺菌ランプの
下側に位置して、水を浄化処理をしているときは、水中
の一部に密集する濾過材を収納し、また同濾過材の下側
に位置して散気盤を設け、さらに同散気盤からのエアー
により、逆洗時に濾過材が水中に浮遊し、殺菌ランプを
収納しているジャケットに接触するように構成したこと
を特徴とする水質浄化装置。1. An appropriate number of sterilizing lamps housed in a jacket are housed inside a filter medium housing tank, and when the water is located below the sterilizing lamp to purify water, The filter material that is densely packed in a part of the water is stored, and an air diffuser is installed below the filter material. Furthermore, the air from the air diffuser causes the filter material to float in the water during backwashing. A water purification device characterized in that the water purification device is configured to come into contact with a jacket containing a sterilization lamp.
なる適数の殺菌ランプと、水中の一部に密集する濾過材
の間に、オゾン供給体を配設したことを特徴とする特許
請求の範囲第1項記載の水質浄化装置。2. An ozone supplier is disposed between a suitable number of sterilizing lamps housed in a jacket inside a filter medium storage tank and a filter medium densely gathered in a part of water. The water purification apparatus according to claim 1.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3497489A JPH0710386B2 (en) | 1989-02-16 | 1989-02-16 | Water purification equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3497489A JPH0710386B2 (en) | 1989-02-16 | 1989-02-16 | Water purification equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH02214588A JPH02214588A (en) | 1990-08-27 |
JPH0710386B2 true JPH0710386B2 (en) | 1995-02-08 |
Family
ID=12429116
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3497489A Expired - Fee Related JPH0710386B2 (en) | 1989-02-16 | 1989-02-16 | Water purification equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0710386B2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
BR112018067832A2 (en) * | 2016-03-09 | 2019-01-02 | Koninklijke Philips Nv | assembly, vessel and method for controlling the operation of an anti-biofouling system |
-
1989
- 1989-02-16 JP JP3497489A patent/JPH0710386B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JPH02214588A (en) | 1990-08-27 |
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