JPH0427493A - Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water - Google Patents

Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water

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Publication number
JPH0427493A
JPH0427493A JP2129026A JP12902690A JPH0427493A JP H0427493 A JPH0427493 A JP H0427493A JP 2129026 A JP2129026 A JP 2129026A JP 12902690 A JP12902690 A JP 12902690A JP H0427493 A JPH0427493 A JP H0427493A
Authority
JP
Japan
Prior art keywords
water
ozone
aeration tank
treated
tank
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
JP2129026A
Other languages
Japanese (ja)
Inventor
Shoichi Yoshinaga
吉永 正一
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 JP2129026A priority Critical patent/JPH0427493A/en
Publication of JPH0427493A publication Critical patent/JPH0427493A/en
Pending legal-status Critical Current

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  • Farming Of Fish And Shellfish (AREA)
  • Filtering Materials (AREA)
  • Physical Water Treatments (AREA)
  • Oxygen, Ozone, And Oxides In General (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PURPOSE:To allow the rapid cleaning and sterilizing treatment of polluted water and the miniaturization of the above device by feeding ozone-contg. air into a bubble generator and subjecting water to be treated to the combined effect of UV rays and ozone-contg. bubbles in an aeration tank. CONSTITUTION:A UV lamp 40 of an ultraviolet irradiation device 32 disposed in the aeration tank B is lighted and a UV lamp 52 of an ozone generator C is lighted. An air feed pump AP is simultaneously driven to feed the air into an outside cylinder 50 of the ozone generator C. The air subjected to the irradiation with the UV rays of about 185nm from the UV lamp 52 in the ozone generator C is partly ozonized is branched. This air is sent through pipings L1 to L5 disposed in the aeration tank B to a bubble generator 34 provided near the bottom of the aeration tank B and is released as the ozone-contg. bubbles into the water to be treated in the aeration tank B. Consequently, the fresh water and sea water which are the water to be treated receives the ozone-contg. bubbles and the irradiation with the UV rays of the extremely high sterilizing power in the aeration tank B and is thereby compositely treated.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は水の浄化滅菌装置及び浄化水の利用法に係り、
殊に淡水や海水を浄化滅菌して食品加工用水、養魚分用
生簀用水等として利用し得る水質のものとなし、又この
ように利用した後の廃水を処理して無公害化することに
より放流可能とする、水の浄化滅菌装置並びに斯くて処
理された浄化滅菌水を食品加工、殊に魚介類の一次加工
に用いて加工品の鮮度維持をもたらす方法に係る。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a water purification sterilization device and a method for utilizing purified water.
In particular, we purify and sterilize freshwater and seawater so that they can be used as food processing water, fish tank water, etc., and we also treat wastewater after such use to make it pollution-free and release it. The present invention relates to a water purification and sterilization device that enables water purification and sterilization, and a method for maintaining the freshness of processed products by using the thus treated purified and sterilized water in food processing, particularly in the primary processing of seafood.

(従来の技術及びその課題) 水の浄化滅菌を行う場合に、浄化対象である「水」とし
ては井戸水、湧水、河川水、湖沼水等の淡水並びに海水
がある。
(Prior art and its problems) When purifying and sterilizing water, the "water" to be purified includes freshwater such as well water, spring water, river water, lake water, etc., and seawater.

これらの淡・海水の浄化滅菌法として、淡水を大規模に
おいて処理するには都市水道等に関して実施されている
塩素処理法があり、又曝気(エアレージ冒ン)処理法や
微生物を利用する処理法があり、小規模的な処理に関し
ては場合により微生物をも利用する濾過法がある。一方
、海水を処理して魚介類の加工処理に利用しようとする
場合の浄化法としては逆滲透膜や微細孔材等を用いる濾
過法が一般に採用されており、場合により微生物膜法が
併用されている。
As methods for purifying and sterilizing freshwater and seawater, there are chlorination methods, which are used for urban water supplies, to treat freshwater on a large scale, as well as aeration methods and treatment methods that use microorganisms. For small-scale treatment, there is a filtration method that also uses microorganisms in some cases. On the other hand, when seawater is to be treated and used for processing seafood, filtration methods using reverse permeation membranes or microporous materials are generally used, and in some cases, microbial membrane methods are also used. ing.

淡・海水を処理して、殊に淡水を処理して飲料用水に利
用し得る程度まで浄化滅菌する場合は別として、−船釣
には淡水よりも海水の浄化滅菌処理の方が困難である。
Except for the treatment of freshwater and seawater, especially when freshwater is treated to purify and sterilize it to the extent that it can be used as drinking water - purification and sterilization of seawater is more difficult than freshwater for boat fishing. .

本発明は淡水の処理にも適用し得るが、海水を浄化滅菌
して魚介類の加工処理水や養魚介生簀水槽用水として用
い、又このように利用された後の廃水を処理して再び海
に放流可能になすことを主眼目にしており、従って本明
細書においては、これに関連して説明する。
The present invention can also be applied to the treatment of fresh water, but it can also be used to purify and sterilize seawater and use it as processed water for fish and shellfish or water for fish and shellfish tanks, and to treat wastewater that has been used in this way so that it can be returned to the sea. The main focus is on making it possible to discharge water into the water, and therefore, the description in this specification will be made in connection with this.

現在、魚介類の一次加工処理例えば鰺を開き処理する場
合の処理水として漁港付近では、タンクに汲み上げられ
た海水をそのまま利用しているか或は濾過器(逆滲透膜
、微細孔材、砂等を濾材とするもの)を通した後に利用
しているのが通例である。しかしながら、前者の場合に
は海洋の汚染に伴い採水場所を沖合いに求めねばならな
くなっており採水のための送水コストが高くなる点並び
に夏期等においては加工処理済み製品の保存性が著しく
低下する点に課題がある。一方、後者の濾過器を用いる
場合にも海洋汚染のためか濾材を頚繁に交換せねば口塞
りを生じるので、コスト高となるのみならずメインテナ
ンスが面倒であり、又夏期等においては上記と同様に加
工処理済み製品の保存性が著しく低下する点に課題があ
る。尚、上記の加工処理に用いられた後の廃水は網材等
を用いた簡単な濾過で粗大物を分離した後に下水道に廃
棄され、結果として海に放流されているのが実状であり
、これは海水の栄養適音化を招き海洋汚染を助長してい
る。
Currently, seawater pumped into tanks near fishing ports is used as treated water for primary processing of seafood, such as when opening and processing horse mackerel. It is customary to use it after passing it through a filter (using a filter medium). However, in the former case, due to ocean pollution, it is necessary to find a water sampling site offshore, which increases the cost of transporting water for sampling, and the shelf life of processed products decreases significantly in summer. There is a problem in doing so. On the other hand, even when using the latter type of filter, the filter medium must be replaced frequently due to ocean pollution, which causes the filter to become clogged, which not only increases costs but also makes maintenance troublesome. Similarly, there is a problem in that the shelf life of processed products is significantly reduced. In addition, the actual situation is that the wastewater used for the above processing is simply filtered using netting material to separate coarse substances, and then disposed of in the sewer system, and as a result, is discharged into the sea. This causes the seawater to become nutrient-poor and contributes to marine pollution.

尚、水の浄化滅菌は生菌の除去乃至殺菌、アンモニアや
亜硝酸の除去、脱臭・脱色、宵機性汚物の分解除去等を
対象とするものであるが、濾過を主体とする従来技術装
置の場合には、処理量が多くなると装置が著しく大型化
するのみならず、処(発明の目的) 従って、本発明の基本的な目的は採取された淡・海水、
殊に海岸付近で採取され、場合により細菌等で汚染され
ている海水を浄化滅菌して魚介類の加工処理用水や養魚
分用水として利用し、又利用後の廃水を処理して海洋汚
染を招かない水質のものとなす水の浄化滅菌装置を提供
することにある。
Note that water purification and sterilization involves the removal or sterilization of living bacteria, the removal of ammonia and nitrous acid, deodorization and decolorization, decomposition and removal of night-time waste, etc., but conventional technology equipment that mainly uses filtration In this case, when the amount of processing increases, not only does the equipment become significantly larger, but also the basic purpose of the present invention is to
In particular, seawater collected near the coast and in some cases contaminated with bacteria, etc. is purified and sterilized and used as water for processing seafood and fish cultivation, and wastewater after use is treated to prevent marine pollution. The purpose of the present invention is to provide a water purification and sterilization device that provides impermanent water quality.

本発明の附随的な、但し重要な目的はコンパクトで処理
能力が高く且つメインテナンスの容易な水の浄化滅菌装
置を提供することにある。
A secondary but important object of the present invention is to provide a water purification and sterilization system that is compact, high throughput, and easy to maintain.

尚、漁港付近にある水産加工業者、例えば魚の開き干し
製品を生産している業者は、夏期になると所謂「ネト」
を発生し易くなり、製品の日持ちが極端に低下するため
に毎年悩まされているのが実状であるが、これは加工処
理水の水質に主として起因するのではないかと推定し、
本発明者は本発明による浄化滅菌装置により処理された
水を用いて魚介類の一次加工処理を試みた処、従来通り
海水や井戸水を用いて加工処理された魚介類と比較する
場合に、その保存性が著しく向上することを見い出した
。従って、本発明の他の且つ重要な目的の一つは本発明
による浄化滅菌装置により処理された浄化滅菌水を用い
て魚介類を加工処理することにより、その鮮度維持をも
たらす方法を提供することにある。
In addition, seafood processing companies located near fishing ports, such as those that produce open-dried fish products, are exposed to so-called "neto" fish in the summer.
The reality is that we are suffering from this problem every year due to the fact that it becomes more likely to occur and the shelf life of the product is extremely reduced.We believe that this is mainly due to the quality of the processed water.
The present inventor attempted the primary processing of seafood using water treated with the purification sterilization device of the present invention, and when comparing it with seafood processed conventionally using seawater or well water, It has been found that storage stability is significantly improved. Therefore, one of the other and important objects of the present invention is to provide a method for maintaining the freshness of seafood by processing it using purified sterilized water treated by the purifying and sterilizing apparatus according to the present invention. It is in.

(課題を解決し、目的を達成する手段及び作用)本発明
者は、従来から、養魚分水槽及び該水槽における水質、
殊に海水を対象とする水質の維持改善に関するの研究開
発に従事しており、この種の水槽における水質維持には
紫外線の照射が有効であるとの確信を得て、水槽内に紫
外線ランプを設置すると共に、その底部付近には空気を
送って気泡化させ、紫外線ランプから水中に照射された
紫外線により雑菌の滅菌を行うと共に藻類の胞子等を死
滅させ且つ上記の気泡内空気をオゾン化させ、このオゾ
ンを利用して更に滅菌を行うと共に溶存酸素濃度を高め
る、養魚分用生簀水槽の水浄化装置を既に提案している
 (実開昭11t2−178888公報)。
(Means and effects for solving the problem and achieving the object) The present inventor has conventionally discovered a fish culture tank and the water quality in the tank.
In particular, I am engaged in research and development on maintaining and improving water quality in seawater, and am convinced that ultraviolet irradiation is effective in maintaining water quality in this type of aquarium, so I installed an ultraviolet lamp in the aquarium. When installed, air is sent near the bottom to form bubbles, and the ultraviolet rays irradiated into the water from the ultraviolet lamp sterilize bacteria, kill algae spores, etc., and ozone the air inside the bubbles. has already proposed a water purification device for a fish tank that utilizes this ozone to further sterilize and increase the dissolved oxygen concentration (Japanese Utility Model Publication No. 11T2-178888).

この実開昭82−1788Ei8公報に開示されている
装置は既述の通り養魚分用生簀水槽のために開発された
ものであり、好評を博しているが、魚介類の加工処理用
水等を提供するような海水の大量処理や、このような加
工処理に用いられて汚染度の著しく高くなった、所謂「
廃水」を処理して放流可能な程度迄浄化するには時間を
要するので、能力的に不十分である。
As mentioned above, the device disclosed in Japanese Utility Model Publication No. 82-1788Ei8 was developed for use in fish tank tanks, and has been well received. The so-called "seawater" that has become extremely contaminated due to the large-scale processing of seawater such as
Because it takes time to treat wastewater and purify it to the point where it can be discharged, it is insufficient in terms of capacity.

そこで、更に検討を重ね開発されたのが本発明装置であ
って、この本発明による水の浄化滅菌装置は被処理水の
導入される貯槽と、曝気槽と、上記の貯槽と曝気槽とを
接続する配管と、該配管を介して被処理水を上記の貯槽
から曝気槽に送るポンプと、オゾン発生装置とを備えて
おり、上記の曝気槽が紫外線照射装置と気泡発生器とを
具備しており、該気泡発生器には上記のオゾン発生装置
からのオゾン含有空気が送気され、斯くて上記の貯槽と
曝気槽との間を循環する被処理水が上記の曝気槽内にお
いて紫外線及びオゾン含有気泡による複合作用を受ける
ことを基本的な特徴としてい尚、利用後の廃水を処理し
て放流しようとする場合には、上記の装置構成で充分で
あるが、採取された海水を処理して魚介類の一次加工処
理用水等として利用する場合には処理対象物が食品であ
ることもあって、場合により存在する浮遊懸濁物等を除
去して水質を更に向上させることが好ましい。このため
には後処理槽を設置することができ、本発明によれば該
後処理槽は濾過処理室と貯水室とを具備し、濾過処理室
が貯槽及び曝気槽の少なくとも一方と配管で接続され且
つ下段から上段に向かって進入水の一次溜り区画と、カ
ルフラム素材充填区画とを備えており、上記の貯水室が
オーバーフロー機構を具備している。
Therefore, the device of the present invention was developed after further study, and the water purification and sterilization device of the present invention includes a storage tank into which the water to be treated is introduced, an aeration tank, and the above storage tank and aeration tank. It is equipped with connecting piping, a pump that sends the water to be treated from the storage tank to the aeration tank via the piping, and an ozone generator, and the aeration tank is equipped with an ultraviolet irradiation device and a bubble generator. Ozone-containing air from the ozone generator is supplied to the bubble generator, and the water to be treated that circulates between the storage tank and the aeration tank is exposed to ultraviolet light and ultraviolet light in the aeration tank. The basic feature is that the seawater is subjected to a complex action by ozone-containing bubbles.However, if the wastewater after use is to be treated and discharged, the above equipment configuration is sufficient; When the water is used as water for the primary processing of fish and shellfish, it is preferable to further improve the water quality by removing any suspended solids, etc., because the object to be treated is food. For this purpose, a post-treatment tank can be installed, and according to the present invention, the post-treatment tank comprises a filtration chamber and a water storage chamber, and the filtration chamber is connected to at least one of the storage tank and the aeration tank by piping. The water storage chamber is provided with a primary storage section for incoming water and a calfram material filling section from the lower stage to the upper stage, and the water storage chamber is equipped with an overflow mechanism.

本発明による水の浄化滅菌装置において、曝気槽内に配
置される紫外線照射装置は上下端が解放され、上部側面
に開口を有し且つ曝気槽内に直立状態で配置された外筒
と、この外筒内に配置されており、上端が開放され且つ
他端が閉鎖されている内筒であって紫外線透過性の素材
で構成されており、内部が液密杖態で上記の外筒に取り
付けられている内筒と、該内筒内に配置されており且つ
波長的254nmを主体とする紫外線を照射する紫外線
ランプとで構成されているのが好ましい。この場合に、
内筒を構成する紫外線透過性素材としては紫外線の透過
率が95%以上である石英が好ましいが、石英管は高価
であるので、紫外線透過ガラス例えば硬質ガラス (硼
珪酸ガラス)、オゾンレス石英、軟質ガラス(バリウム
クラウンガラス)等に代替することもできる。一方、波
長的254nmを主体とする紫外線を照射する紫外線ラ
ンプが選択されたのは低圧水銀ランプが発生する放射光
の内で波長253.7amのものが共鳴線と称され、殺
菌力が最も強いからである。尚、紫外線ランプを各々収
容している内筒を外筒内に複数本設置し、これらの紫外
線ランプの内の少なくとも一本が波長185■のオゾン
線を照射するランプであり、他が波長的254II11
1の殺菌性共鳴線を照射するランプとすることもできる
。この場合に、オゾン線照射用紫外線ランプを収容して
いる内筒の材質は透明石英であることが肝要である。
In the water purification sterilization device according to the present invention, the ultraviolet irradiation device placed in the aeration tank has an outer cylinder whose upper and lower ends are open, an opening on the upper side, and which is placed upright in the aeration tank. The inner cylinder is placed inside the outer cylinder and has an open top end and a closed end, and is made of an ultraviolet-transparent material.The inside is liquid-tight and is attached to the outer cylinder. It is preferable that the light emitting device is composed of an inner cylinder having a diameter of 254 nm, and an ultraviolet lamp disposed within the inner cylinder and emitting ultraviolet light mainly having a wavelength of 254 nm. In this case,
Quartz, which has a UV transmittance of 95% or more, is preferred as the UV-transparent material for the inner tube, but since quartz tubes are expensive, UV-transparent glass such as hard glass (borosilicate glass), ozone-free quartz, and soft It can also be replaced with glass (barium crown glass) or the like. On the other hand, an ultraviolet lamp that irradiates ultraviolet rays with a wavelength of 254 nm as a main component was selected because among the radiation emitted by a low-pressure mercury lamp, the wavelength of 253.7 am is called the resonance line, and it has the strongest sterilizing power. It is from. In addition, a plurality of inner cylinders each containing an ultraviolet lamp are installed inside the outer cylinder, and at least one of these ultraviolet lamps is a lamp that emits ozone rays with a wavelength of 185 cm, and the others are lamps that emit ozone radiation with a wavelength of 185 cm. 254II11
It can also be a lamp that emits the germicidal resonance rays of 1. In this case, it is important that the material of the inner cylinder housing the ultraviolet lamp for ozone beam irradiation be transparent quartz.

本発明による水の浄化滅菌装置において、オゾン発生装
置は空気導入孔とオゾン含有空気排出孔とを備えた外筒
と、該外筒内に配置固定されていて波長的185nmの
紫外線を照射する紫外線ランプとで構成されている。こ
の場合に、外筒を構成する耐オゾン性素材としては例え
ば塩化ビニールやステンレススチール等を例示すること
ができるが、成形性や製作コストを考慮に入れると塩化
ビニールが好ましく、又紫外線ランプは石英製内筒内に
収容されていることもできる。
In the water purification sterilization device according to the present invention, the ozone generator includes an outer cylinder provided with an air introduction hole and an ozone-containing air exhaust hole, and an ultraviolet ray that is arranged and fixed in the outer cylinder and irradiates ultraviolet rays with a wavelength of 185 nm. It consists of a lamp. In this case, examples of the ozone-resistant material constituting the outer cylinder include vinyl chloride and stainless steel, but vinyl chloride is preferable in consideration of formability and manufacturing cost, and the ultraviolet lamp is made of quartz. It can also be housed within a manufactured inner cylinder.

本発明による水の浄化滅菌装置において、後処理槽にお
けるカルシウム素材充填区画は貝殻層で形成されており
、この貝殻層が進入水の通過の向きである下段から上段
に向かって粗砕コーラル貝殻層と、カキ及びホタテの貝
殻から選ばれ粗砕された貝殻層と、コーラルサンド層と
で構成されているのが好ましい。何故ならば、上記のよ
うに構成された貝殻層を通すと、場合により存在する浮
遊懸濁物が完全に除去されるのみならず、カルシウムが
溶出してpl(7,7程度であった原水(海水)のpH
が11.0程度に上昇し、又硬直的70の原水の硬度が
75程度に上昇し、これらの点が、得られた浄化滅菌水
を魚介類の加工処理に用いた場合に、例えば魚の開き処
理に用い、次いで常法により生干し製品とした場合に酸
化の抑制、腐敗菌の発生や抑制に役立ち、その結果当該
製品の鮮度維持をもたらすものと推定されるからである
In the water purification sterilization apparatus according to the present invention, the calcium material filling section in the post-treatment tank is formed of a shell layer, and the shell layer is composed of a coarsely crushed coral shell layer from the lower layer to the upper layer, which is the direction in which the incoming water passes. , a shell layer selected from oyster and scallop shells and coarsely crushed, and a coral sand layer. This is because passing through the shell layer configured as described above not only completely removes any suspended solids that may exist, but also dissolves calcium and reduces the raw water's pl (from about 7.7 pH of (seawater)
The hardness of the raw water increases to about 11.0, and the hardness of the raw water with a hardness of 70 increases to about 75. This is because when used for processing and then made into a raw-dried product using a conventional method, it is thought to help suppress oxidation and the generation and suppression of spoilage bacteria, thereby maintaining the freshness of the product.

尚、本発明による水の浄化滅菌装置の能力は紫外線照射
装置及びオゾン発生装置の能力と、装置の全体の規模に
依存するが、貯槽の萄効内容量を150トン、曝気槽の
内容量を150 リットルとし、曝気槽内に配置される
内筒が4本とし、各内筒が約254n+++の紫外線を
照射する紫外線ランプ(石英製、25 x 500II
1m、  15W)を収容しており、又オゾン発生装置
が上記と同様の但し約185nmの紫外線を照射する紫
外線ランプを2本収容しており、オゾン発生装置の内容
積が8リツトルであって、毎分65 リットルの割合で
空気が送り込まれて0.06−0.1ppn+のオゾン
含有空気を調製し、これを5本の分岐管で曝気槽に送る
とオゾン濃度は約0.04−0.Hppmに低下し、こ
のオゾン含有空気を散気管により微細気泡として放出さ
せ、被処理水である海水を上記の貯槽と曝気槽とを介し
て毎分120リツトルの割合で循環させれば、浄化滅菌
処理は約60分間で終了する。次いで、上記のようにし
て処理された水を後処理槽に送り、濾過処理すれば所望
の浄化滅菌水が得られる。この浄化滅菌水を採取して目
視観察した処、夾雑物は何等認められず、無臭であり且
つキラキラ輝くような色調を呈していた。
The capacity of the water purification sterilization device according to the present invention depends on the capacity of the ultraviolet irradiation device and the ozone generator, as well as the overall scale of the device. The capacity is 150 liters, and there are four inner cylinders placed in the aeration tank, each of which is equipped with an ultraviolet lamp (made of quartz, 25 x 500 II) that irradiates ultraviolet light of approximately 254n++
1 m, 15 W), and the ozone generator is the same as above, except that it contains two ultraviolet lamps that emit ultraviolet light of about 185 nm, and the internal volume of the ozone generator is 8 liters. Air is pumped in at a rate of 65 liters per minute to prepare air containing ozone of 0.06-0.1 ppn+, and this is sent to the aeration tank through five branch pipes, resulting in an ozone concentration of approximately 0.04-0.1 ppn+. Hppm, this ozone-containing air is released as fine bubbles through an aeration pipe, and the seawater to be treated is circulated at a rate of 120 liters per minute through the above-mentioned storage tank and aeration tank, then purification and sterilization can be achieved. The process is completed in about 60 minutes. Next, the water treated as described above is sent to a post-treatment tank and subjected to filtration treatment to obtain the desired purified and sterilized water. When this purified sterilized water was collected and visually observed, no impurities were found, and it was odorless and had a sparkling color.

(実施例等) 次ぎに、図面を参照しつつ実施例について本発明を更に
具体的に説明し、又試験例により本発明装置の効果を例
証する。
(Examples, etc.) Next, the present invention will be described in more detail with reference to Examples with reference to the drawings, and the effects of the apparatus of the present invention will be illustrated by test examples.

第1図には本発明による水の浄化滅菌装置lOの概要が
示されている。この浄化滅菌装置lOにおいて、Aは被
処理水給水用の貯槽であり、Bは主要部を構成する曝気
槽であり、Cはオゾン発生装置であり、Dは曝気槽Bで
処理済み後の水を更に処理する後処理槽である。この図
面は各種の寸法関係を反映させて描いたものではなく、
事実、本実施例に係る実験に用いられたものは貯槽Aの
有効内容量が1.5トン、曝気槽Bの内容量が1501
Jツトルに設定されていた。尚、後処理槽Cは任意の容
量であることができる。
FIG. 1 shows an outline of a water purification and sterilization apparatus IO according to the present invention. In this purification sterilization equipment lO, A is a storage tank for supplying water to be treated, B is an aeration tank that constitutes the main part, C is an ozone generator, and D is water after being treated in the aeration tank B. This is a post-treatment tank for further processing. This drawing is not drawn to reflect various dimensional relationships,
In fact, the storage tank A used in the experiment of this example had an effective internal capacity of 1.5 tons, and the aeration tank B had an internal capacity of 1501 tons.
It was set to J-Tuttle. Note that the post-treatment tank C can have any capacity.

上記の貯槽Aは給水用開閉弁12、排水用開閉弁14、
フロートスイッチ16及びこれらを自動制御する制御装
置18とを備えている。
The above storage tank A includes a water supply on-off valve 12, a drainage on-off valve 14,
It is equipped with a float switch 16 and a control device 18 that automatically controls these.

上記の曝気槽Bは耐オゾン性の、例えば塩化ビニール製
の外套30により製作されており、中心部には直立配置
された紫外線照射装置32を有し、又底部には気泡発生
装置34を備えている。上記の紫外線照射装置は上下端
が解放され、上部側面に開口を有する外筒3Bと、この
外筒3B内に配置されており、上端が開放され且つ他端
が閉鎖されており、紫外線透過性の良好な素材で構成さ
れていて内部が液密状態で上記の外筒38に取り付けら
れている内筒38と、該内筒38内に配置されている紫
外線ランプ40とで構成されている。
The above aeration tank B is made of an ozone-resistant jacket 30 made of vinyl chloride, for example, and has an ultraviolet irradiation device 32 placed upright in the center, and a bubble generator 34 at the bottom. ing. The above-mentioned ultraviolet irradiation device has an outer cylinder 3B with open upper and lower ends and an opening on the upper side surface, and is arranged inside this outer cylinder 3B.The upper end is open and the other end is closed. The inner tube 38 is made of a good material and is attached to the outer tube 38 in a liquid-tight manner, and an ultraviolet lamp 40 is disposed inside the inner tube 38.

図示されている実施形において、外筒36は耐オゾン性
の素材、例えば塩化ビニールで製作されており、この外
筒36内には4本の内筒38が配置されている。これら
の各内筒38内には上述のように各1本の紫外線ランプ
4oが収容されている。
In the illustrated embodiment, the outer sleeve 36 is made of an ozone-resistant material, such as vinyl chloride, and has four inner sleeves 38 disposed within the outer sleeve 36 . Each of these inner cylinders 38 accommodates one ultraviolet lamp 4o, as described above.

この紫外線ランプ40は電源PSから漏電ブレーカLB
1 チョークボックス(安定器) CBを経て送られる
電力により点灯せしめられる低圧水銀灯であり、基本的
には、共鳴線乃至殺菌線と称される波長253.7nm
の紫外線を発生するものであるが、これらの内の一本又
は二本は波長185nmの所謂「オゾン線」と称される
紫外線を発生するものであることもできる。尚、共鳴線
を発生させる紫外線ランプ40を収容する内Fir 3
8の材質としては透過率が高いものであれば差し支えが
なく石英や一般的な紫外線透過ガラス例えば硬質ガラス
(硼珪酸ガラス)、オゾンレス石英、軟質ガラス(バリ
ウムクラウンガラス)等であることができるが、オゾン
線発生用紫外線ランプを収容する場合の内w38は石英
製のものであることが肝要である。
This ultraviolet lamp 40 is connected to the earth leakage breaker LB from the power supply PS.
1. Chalk box (ballast) A low-pressure mercury lamp that is lit by electricity sent through the CB, and basically uses a wavelength of 253.7 nm, which is called the resonance line or germicidal line.
One or two of these can also generate ultraviolet rays with a wavelength of 185 nm, so-called "ozone rays." Incidentally, the inner Fir 3 houses the ultraviolet lamp 40 that generates the resonance line.
There is no problem with the material 8 as long as it has a high transmittance, and examples include quartz, general ultraviolet-transmitting glass, hard glass (borosilicate glass), ozone-free quartz, soft glass (barium crown glass), etc. In the case where an ultraviolet lamp for generating ozone rays is housed, it is important that w38 be made of quartz.

図示されている実施形における内筒38は外径32n1
11.厚み 1.5IIIII+1 内径29111L
 長さ B[10mmのものであり、紫外線ランプ40
は外径2511 長さ500mm、出力15Wのもので
ある。
The inner cylinder 38 in the illustrated embodiment has an outer diameter of 32n1
11. Thickness 1.5III+1 Inner diameter 29111L
Length B [10 mm, ultraviolet lamp 40
has an outer diameter of 2511 mm, a length of 500 mm, and an output of 15 W.

既述のオゾン発生装置Cは耐オゾン材料製であって空気
導入孔とオゾン含有空気排出孔とを備えた外筒50と、
該外筒内に配置固定されていて波長約185nmの紫外
線(オゾン線)を照射する紫外線ランプ52とで構成さ
れている。外筒5oを構成する素材は上記のように耐オ
ゾン性を有していれば良く、ステンレススチール等であ
ることもできるが、コストの点から塩化ビニール製であ
り、紫外線ランプ52の保守交換の観点から分割構成さ
れているのが好ましい。図示されている実施形において
は、紫外線ランプ52が剥き出しの状態で設置されてい
るが、外f!J 50への取り付は等を考慮に入れ、既
述の紫外線照射装置32におけると同様に内筒(図示せ
ず)内に収容されていることもできる。勿論、この場合
に内筒は石英製であることが肝要である。上記のオゾン
発生装置Cの外筒50内には、電源PSに接続された送
気ポンプAPを経て空気が送られる。この送気ポンプA
P it AC100V、消費電力200 W/時、送
気量毎分130 リットル、送気圧0.5 kgf/a
m”の能力を有するものであるが、送気量毎分65 リ
ットル、送気圧0.3kgf/cm2の低圧で稼働させ
る。このオゾン発生装置Cにより調製されたオゾン含有
空気の濃度はオゾン濃度測定器54により測定され、適
宜の手段で、例えば送気ポンプAPからの送気量の調整
等によりオゾン濃度を所定のレベル(0,0G −0,
1ppm)になした上で、既述の曝気槽B内に配置され
た気泡発生器34に送られてオゾン含仔微細気泡として
曝気槽B内の被、処理水に対して放出される。
The ozone generator C described above includes an outer cylinder 50 made of an ozone-resistant material and equipped with an air introduction hole and an ozone-containing air exhaust hole;
It is comprised of an ultraviolet lamp 52 that is fixedly placed inside the outer cylinder and irradiates ultraviolet rays (ozone rays) with a wavelength of about 185 nm. The material constituting the outer cylinder 5o only needs to have ozone resistance as described above, and can be made of stainless steel, etc., but from the viewpoint of cost, it is made of vinyl chloride, and it is easy to maintain and replace the ultraviolet lamp 52. From this point of view, it is preferable to have a divided structure. In the illustrated embodiment, the ultraviolet lamp 52 is installed bare, but outside f! Taking into consideration the attachment to the J50, the ultraviolet irradiation device 32 may be housed in an inner cylinder (not shown) in the same manner as in the ultraviolet irradiation device 32 described above. Of course, in this case it is important that the inner cylinder be made of quartz. Air is sent into the outer cylinder 50 of the ozone generator C described above via an air pump AP connected to a power source PS. This air pump A
P it AC100V, power consumption 200 W/hour, air flow rate 130 liters per minute, air flow pressure 0.5 kgf/a
It has a capacity of 1.5 m", but is operated at a low pressure of 65 liters per minute and a pressure of 0.3 kgf/cm2.The concentration of the ozone-containing air prepared by this ozone generator C is measured by ozone concentration The ozone concentration is adjusted to a predetermined level (0, 0G -0,
1 ppm) and then sent to the bubble generator 34 disposed in the aeration tank B described above and released into the treated water in the aeration tank B as ozone-containing fine bubbles.

曝気槽B内において気泡発生器34は複数個の散気ノズ
ルとして構成されており、該散気ノズルの内の一つは外
筒3Bの内底部付近に配置され、他は外! 3Bの外部
に配置されている。これらの散気ノズルから被処理水中
に放出されるオゾン含有気泡は曝気槽B内の被処理水に
上昇流をもたらす。曝気槽B内において被処理水は、外
商36の内部においてはオゾンと紫外線ランプ40から
の主として波長的254nIllの殺菌性紫外線による
複合作用を受けて浄化され、又外筒36の外部において
は専らオゾンによる作用を受けて浄化されることになる
が、処理効率を向上させるためには単位時間当りにおけ
る被処理水とオゾンとの接触率を高め且つ被処理水が受
ける紫外線の受光量を高めることが重要である。このよ
うな効果をもたらすためには曝気槽B内で被処理水を循
環させることが考えられ、この水循環をもたらす手段と
して、オゾン含有気泡による被処理水の上記上昇流が利
用される。即ち外筒3Bの内部と上部排出口3(12と
を接続させ、外筒36内の被処理水の一部を一旦曝気櫂
Bの外部に導き、次いで曝気槽Bの底部付近において再
び曝気槽B内に導入させるのである。この場合に、フラ
ンジ付き套管38を外筒3Bに対して同心的に配置して
おくと、該套管のフランジ部分382が一種の邪魔板と
して作用し、従って上昇してくるオゾン含有気泡と循環
導入された被処理水との接触率が向上するので有利であ
る。
In the aeration tank B, the bubble generator 34 is configured as a plurality of aeration nozzles, one of which is arranged near the inner bottom of the outer cylinder 3B, and the others are located outside! It is located outside of 3B. The ozone-containing bubbles released into the water to be treated from these aeration nozzles cause an upward flow in the water to be treated in the aeration tank B. In the aeration tank B, the water to be treated is purified by the combined action of ozone and bactericidal ultraviolet light, mainly at a wavelength of 254nIll, from the ultraviolet lamp 40 inside the outer cylinder 36, and exclusively by ozone and the outside of the outer cylinder 36. However, in order to improve treatment efficiency, it is necessary to increase the contact rate between the water to be treated and ozone per unit time and to increase the amount of ultraviolet rays that the water to be treated receives. is important. In order to bring about such an effect, it is possible to circulate the water to be treated in the aeration tank B, and the above-mentioned upward flow of the water to be treated due to ozone-containing bubbles is used as a means for bringing about this water circulation. That is, the inside of the outer cylinder 3B and the upper discharge port 3 (12) are connected, a part of the water to be treated in the outer cylinder 36 is once led to the outside of the aeration paddle B, and then the water is returned to the aeration tank near the bottom of the aeration tank B. In this case, if the flanged sleeve 38 is arranged concentrically with respect to the outer cylinder 3B, the flange portion 382 of the sleeve acts as a kind of baffle plate, and therefore This is advantageous because the contact rate between the rising ozone-containing bubbles and the recycled water to be treated is improved.

尚、上記のフランジ付き套管3Bが配置されている場合
に、曝気槽B内における被処理水の水循環ついて述べれ
ば、被処理水は套管38と外FJ 3Bとの間を通って
下降し、底部付近で外筒36の内部に進入し、該外商3
Bの内部を上昇するオゾン含有気泡によるリフトアップ
作用により外筒36内を上昇し、この上昇流の一部は上
述のように分岐し上部排出口302を経て曝気槽Bの外
部に一旦導かれた上で下部付近から再び曝気槽B内に流
入し、オゾン含有気泡によるリフトアップ作用により曝
気槽B内を上昇し、次いで再び套管38と外II 3B
との間を通って下降するようになり、方、上部排出口3
02に向かって分岐されずに外筒36内を上昇した被処
理水は外筒36の上部側面に設けられた開口382.3
[i4を経て流出し、次いで再び套管38と外筒36と
の間を通って下降する。
Regarding the water circulation of the water to be treated in the aeration tank B when the above-mentioned flanged sleeve 3B is arranged, the water to be treated passes between the sleeve 38 and the outer FJ 3B and descends. , enters the inside of the outer cylinder 36 near the bottom, and the outer cylinder 3
The ozone-containing bubbles rising inside the aeration tank B rise inside the outer cylinder 36 due to the lift-up action, and a part of this upward flow is branched as described above and is once led to the outside of the aeration tank B via the upper discharge port 302. Then, it flows into the aeration tank B again from near the bottom, rises in the aeration tank B due to the lifting action of the ozone-containing bubbles, and then returns to the mantle 38 and the outer II 3B.
The upper discharge port 3
The water to be treated that has risen inside the outer cylinder 36 without being branched toward 02 flows through the opening 382.3 provided in the upper side of the outer cylinder 36.
[It flows out through i4, and then passes again between the cannula 38 and the outer cylinder 36 and descends.

尚、後処理槽りは濾過処理室60と、貯水室70とを具
備している。濾過処理室60は既述の貯槽A及び曝気槽
Bの少なくとも一方と配管で接続されており、貯槽A及
び曝気槽Bを経て循環され、曝気槽Bにおいて充分に処
理された後の浄化滅菌水を受け入れるようになされてお
り、下段から上段に向かって進入水の一次溜り区画62
及びカルシウム素材充填区画B4を備えている。このカ
ルシウム素材充填区画64は、図示されている実施形に
おいては、3層の貝殻層で構成されており、進入水の通
過の向きである下段から上段に向かって粗砕フーラル貝
殻層(子供の小指の指先程度の大きさ)B42と、カキ
及びホタテの貝殻、殊にホタテの粗砕貝殻層(寸法は上
記の粗砕コーラル貝殻の半分程度)644と、コーラル
サンド層64Bとで構成されている。尚、上記の各カル
シウム素材(貝殻)のカルシウム含有量は、炭酸カルシ
ウム換算で35.8〜53.1B程度であり、各カルシ
ウム素材については、図示されているように、荒目の袋
に約5−10kg程度分けて入れておくのが、交換等の
際に好都合である。上記のカルシウム素材からなる貝殻
層を担持支承するために合成樹脂製又は非腐食性の金属
製格子部材66が配設されており、該格子部材66と上
記の貝殻層との間には繊維質フィルタB8が設けられて
おり、斯くて進入水中に浮遊懸濁物が存在する場合にも
、当該浮遊物は上記の繊維質フィルタ68により捕捉さ
れ、従って貝殻層へ、延いては貯水槽70に移行しない
ようになされている。尚、繊維質フィルタ68により捕
捉された浮遊物は濾過処理室60の逆洗時に落下し、進
入水の一次溜り区画62の下部に設けられた逆洗用ドレ
ン弁の開放により糸外に排除される。尚、貯水室70に
はオーバーフロー機構702が配設されており、貯水室
内に貯えられた浄化滅菌水は開閉弁72を開放すること
により、上記のオーバーフロー機構702を経て系外に
送り出されて加工処理水等として利用される。
Note that the post-treatment tank includes a filtration chamber 60 and a water storage chamber 70. The filtration processing chamber 60 is connected by piping to at least one of the storage tank A and the aeration tank B described above, and the purified sterilized water is circulated through the storage tank A and the aeration tank B, and is sufficiently treated in the aeration tank B. The primary storage section 62 of the incoming water is formed from the lower stage to the upper stage.
and a calcium material filling section B4. In the illustrated embodiment, the calcium material-filled section 64 is composed of three shell layers, from the lower layer to the upper layer, which is the direction of passage of the incoming water, including the crushed fural shell layer (for children). The coral sand layer 64B consists of a layer 644 (about half the size of the above-mentioned crushed coral shell), and a coral sand layer 64B. There is. The calcium content of each of the above calcium materials (seashells) is approximately 35.8 to 53.1B in terms of calcium carbonate, and as shown in the figure, each calcium material is approximately It is convenient to keep 5 to 10 kg of each bag separately for replacement. A synthetic resin or non-corrosive metal lattice member 66 is disposed to support the shell layer made of the calcium material, and a fibrous material is provided between the lattice member 66 and the shell layer. A filter B8 is provided, so that even if there are suspended solids in the incoming water, they will be captured by the above-mentioned fibrous filter 68 and thus transferred to the shell layer and thus to the water tank 70. It is designed not to migrate. Incidentally, the floating matter captured by the fibrous filter 68 falls during backwashing of the filtration processing chamber 60, and is removed to the outside of the thread by opening the backwashing drain valve provided at the bottom of the primary reservoir section 62 of the incoming water. Ru. An overflow mechanism 702 is provided in the water storage chamber 70, and when the on-off valve 72 is opened, the purified sterilized water stored in the water storage chamber is sent out of the system through the overflow mechanism 702 and processed. Used as treated water, etc.

次ぎに、上記のような構成を有する、本発明による水の
浄化滅菌装置の操作態様について具体的に述べる。但し
、各種の寸法、紫外線である殺菌性共鳴線やオゾン線の
発生に用いる紫外線ランプ(低圧水銀灯)の本数や寸法
等は既述のものと同様であるので、重複部分についての
説明は省略する。
Next, the operation mode of the water purification and sterilization apparatus according to the present invention having the above-mentioned configuration will be specifically described. However, the various dimensions, the number and dimensions of the ultraviolet lamps (low-pressure mercury lamps) used to generate the germicidal resonance rays and ozone rays, which are ultraviolet rays, are the same as those already mentioned, so we will omit the explanation of the overlapping parts. .

先ず、簡便なフィルタを通して粗大浮遊懸濁物を分離す
ることにより採取した海水を給水用開閉弁12の開放に
より貯槽A内に導入する。貯槽A内の水位が一定レベル
に達すれば、フロートスイッチ16から信号が制御装置
18に送られて上記の給水用開閉弁12が閉鎖される。
First, seawater collected by separating coarse suspended solids through a simple filter is introduced into the storage tank A by opening the water supply on-off valve 12. When the water level in the storage tank A reaches a certain level, a signal is sent from the float switch 16 to the control device 18 to close the water supply on-off valve 12.

そこで、ポンプP−1が駆動され、貯槽A内の被処理水
が曝気槽Bに送られる。この場合に、貯槽A内の水位に
低下が生じるので給水用開閉弁12が再び開放され、被
処理水が補充されることになる。曝気槽Bへの給水(ま
弁V−1を醋放することにより行われる (弁V−2が
開放されるのは曝気槽の清掃時に全排水する場合である
)。被処理水の流入により曝気槽B内の水位は次第に上
昇して上部排出口302の位置に達すると、弁V−3が
開放され且つポンプP−2が稼働して曝気槽B内の被処
理水は貯槽Aに還流復帰することになり、この時点で貯
槽A及び曝気槽B内の水位は一定となり且つ被処理水の
循環が行われる (弁V−4は、弁V−2と同様に装置
の稼働中には閉鎖されていて、曝気槽の清hWIIに開
放されるか、或は開放されていて曝気槽B内における被
処理水の水循環のために使用される弁である)。
Then, the pump P-1 is driven, and the water to be treated in the storage tank A is sent to the aeration tank B. In this case, since the water level in the storage tank A decreases, the water supply on-off valve 12 is opened again, and the water to be treated is replenished. Water is supplied to aeration tank B (by opening valve V-1 (valve V-2 is opened when the aeration tank is completely drained when cleaning). Due to the inflow of water to be treated When the water level in the aeration tank B gradually rises and reaches the position of the upper discharge port 302, the valve V-3 is opened and the pump P-2 is operated, and the water to be treated in the aeration tank B is returned to the storage tank A. At this point, the water level in storage tank A and aeration tank B becomes constant, and the water to be treated is circulated. (Like valve V-2, valve V-4 is This valve is either closed and opened to the aeration tank B, or opened and used for water circulation of the water to be treated in the aeration tank B).

上記の操作で被処理水の浄化滅菌を行う準備が整った状
態となる。そこで、曝気槽B内に配置された紫外線照射
装置32における紫外線ランプ40を点灯させると共に
、オゾン発生装置Cにおける紫外線ランプ52を点灯さ
せ且つ送気ポンプAPを駆動して空気をオゾン発生装置
Cの外筒50内に送る。この場合に、曝気槽B内に配置
された紫外線照射装置32における紫外線ランプ40は
曝気槽内を移動しつつある被処理水に波長的254nm
 (好ましくは殺菌性の極めて高い共鳴線である波長2
53.7nm)の紫外線を照射して被処理水中に存在す
る大腸菌等の生菌や藻類の胞子を破壊する。一方、オゾ
ン発生装置C内で紫外線ランプ52からの波長的185
nmの紫外線照射を受けた空気は一部がオゾン化された
上で分岐され、曝気槽B内に配設された配管(L+ 、
 La 、 L3 、La 、 La )を経て曝気槽
Bの底部付近に設けられた気泡発生装置34に送られ、
オゾン含有気泡として曝気槽B中の被処理水に対して放
出される (オゾン含有空気中のオゾン濃度はオゾン発
生装置C内で0.06−0.lppm、分岐管中で0.
04−0.O8ppmとなるように設定されるべきであ
り、このように設定すれば被処理水の浄化滅菌処理に供
された後に最終的には周囲環境に放出されるオゾン濃度
は0 、O2ppm以下となって、殺菌性と清々しさを
もたらすが、これ以上の濃度で放出されると、その酸化
力がヒトの健康に害を与える可能性を宵しているからで
ある)。尚、オゾン含有空気誘導用の配管の内で配管し
3の遊端は紫外線照射装置32の外W36の内部に配置
されており、他の配管は外筒36の外部に配置されてい
る。尚、気泡発生装置34の散気ノズル部分は当然のこ
とながら耐オゾン性素材にて例えばガラスやセラミック
スを焼結して製作されており 0.1−0.8mm程度
の微細気泡としてオゾン含有空気を被処理水中に放出す
るようになされている。
With the above operations, the water to be treated is ready to be purified and sterilized. Therefore, the ultraviolet lamp 40 in the ultraviolet irradiation device 32 disposed in the aeration tank B is turned on, the ultraviolet lamp 52 in the ozone generator C is turned on, and the air supply pump AP is driven to supply air to the ozone generator C. It is sent into the outer cylinder 50. In this case, the ultraviolet lamp 40 in the ultraviolet irradiation device 32 disposed in the aeration tank B emits a wavelength of 254 nm to the water to be treated that is moving inside the aeration tank.
(Preferably wavelength 2, which is a resonance line with extremely high bactericidal properties)
53.7nm) to destroy living bacteria such as E. coli and algae spores existing in the water to be treated. On the other hand, in the ozone generator C, the wavelength 185 from the ultraviolet lamp 52 is
The air that has been irradiated with nanometer ultraviolet rays is partially ozonized and branched off into pipes (L+, L+,
La, L3, La, La) is sent to the bubble generator 34 provided near the bottom of the aeration tank B,
It is released as ozone-containing bubbles to the water to be treated in the aeration tank B.
04-0. The ozone concentration should be set to 08 ppm, and if the ozone concentration is set in this way, the ozone concentration ultimately released into the surrounding environment after the water to be treated is purified and sterilized will be 0 and 02 ppm or less. This is because, although it has bactericidal and refreshing properties, if released in higher concentrations, its oxidizing power may be harmful to human health.) Incidentally, among the piping for guiding ozone-containing air, the free end of the pipe 3 is arranged inside the outside W36 of the ultraviolet irradiation device 32, and the other pipes are arranged outside the outer cylinder 36. Incidentally, the aeration nozzle part of the bubble generator 34 is naturally made of an ozone-resistant material such as sintered glass or ceramics, and the ozone-containing air is produced as fine bubbles of about 0.1 to 0.8 mm. is released into the water being treated.

本発明による浄化滅菌装置がもたらす作用効果としては
、曝気槽B内に配置された紫外線ランプ40から照射さ
れる波長的254nmの殺菌性紫外線とオゾン含有気泡
が複合して被処理水に及ぼす作用が極めて重要であり、
従ってこれに関連して、第2図を参照しつつ説明する。
The effects brought about by the purification and sterilization apparatus according to the present invention include the combined effect of the bactericidal ultraviolet rays with a wavelength of 254 nm irradiated from the ultraviolet lamp 40 placed in the aeration tank B and ozone-containing bubbles on the water to be treated. extremely important,
Therefore, a description will be given in this regard with reference to FIG.

この第2図には、気泡発生装置34の散気ノズルから被
処理水中に放出されたオゾン含有気泡OBや紫外線ラン
プ40から照射された紫外線UVが如何なる作用を被処
理水に及ぼすかが、幾分誇張した状態で描記されている
FIG. 2 shows how the ozone-containing bubbles OB discharged into the water to be treated from the aeration nozzle of the bubble generator 34 and the ultraviolet rays UV irradiated from the ultraviolet lamp 40 have an effect on the water to be treated. It is depicted in an exaggerated manner.

上記の気泡中のオゾン (03)は、その性質上分解し
て酸素分子(02)と発生期状態の酸素(0)を生成し
、前者は被処理水中に溶は込んで酸素濃度を高め、後者
は塩素の約7倍と云う強力な酸化力を発揮して被処理水
中に場合により存在する菌体の細胞膜を破壊し、又有機
性物質、アンモニア、亜硝酸等を分解する。この場合に
、気泡OBは形状が常に動的に変化しながら上昇し且つ
本発明装置によれば、このようなオゾン含有気泡OBと
は別途に、内筒38内に収容された紫外線ランプ40か
ら強力な殺菌作用を宵する波長的254nmの紫外線U
Vが被処理水中に照射される。照射された当該紫外線U
Vは、その殺菌力を、場合により存在する菌体に及ぼし
て細胞膜を破壊すると共に、上記の形が変化しながら上
昇しつつあるオゾン含有気泡OBに衝突して反射したり
、入射して複雑に屈折したり、透過したりして当該気泡
からのオゾンの放出分解を助長するのみならず、照射さ
れた紫外線の総到達距離の延長化、即ち利用率の向上を
もたらすのである。
Due to its nature, the ozone (03) in the bubbles decomposes to produce oxygen molecules (02) and nascent oxygen (0), and the former dissolves into the water to be treated to increase the oxygen concentration. The latter exhibits a strong oxidizing power about seven times that of chlorine, destroys cell membranes of bacterial cells that may be present in the water to be treated, and also decomposes organic substances, ammonia, nitrous acid, etc. In this case, the bubbles OB rise while constantly changing their shape dynamically, and according to the device of the present invention, apart from such ozone-containing bubbles OB, the bubbles OB rise from the ultraviolet lamp 40 housed in the inner cylinder 38. UV rays with a wavelength of 254 nm have a strong bactericidal effect
V is irradiated into the water to be treated. The irradiated ultraviolet ray U
In some cases, V exerts its sterilizing power on existing bacterial cells and destroys cell membranes, and also collides with the ozone-containing bubbles OB, which is rising while changing its shape, and is reflected, or enters and causes complex damage. This not only promotes the release and decomposition of ozone from the bubbles, but also extends the total reach of the irradiated ultraviolet rays, that is, improves the utilization rate.

上記の上昇するオゾン含有気泡は、当然のことながら、
被処理水中に存在する浮遊懸濁物をリフトアップして凝
集させる作用を宵しており、従って、本発明による浄化
滅菌装置10を暫く稼働させると、曝気槽B内の上部空
間には、上記の処理により生じた汚物が泡状の、所謂「
アク」となって蓄積され初め、次いで、この汚濁泡WB
は曝気槽Bの上部に配設された案内管302を経てその
下向分岐口302Aから外部に排出される。この排出さ
れる汚物は薄茶乃至褐色を呈しており、数時間放置する
と黒褐色乃至黒色に変色して固化する物質であって分析
した処、硝酸塩の存在は認められたが、大腸菌や他の雑
菌の存在は認められなかった。尚、上記の案内管302
の上向分岐口302bからは余剰となったオゾン含有空
気が大気中に放出されるが、そのオゾン濃度は0.O2
ppm以下であって周囲環境の消毒に役だってもヒトの
健康に害を及ぼす虞はない。
The rising ozone-containing bubbles mentioned above are, of course,
It has the effect of lifting up and aggregating the floating suspended substances present in the water to be treated, and therefore, when the purification sterilization apparatus 10 according to the present invention is operated for a while, the upper space in the aeration tank B will contain the above-mentioned substances. The filth generated from the treatment is foamy, so-called
It begins to accumulate as "scum", and then this pollution foam WB
is discharged to the outside through a guide pipe 302 disposed at the upper part of the aeration tank B through its downward branch port 302A. This excreted waste has a light brown to brown color, and if left for several hours, it will change color to blackish brown or black and solidify.When analyzed, the presence of nitrates was confirmed, but it was contaminated with E. coli and other bacteria. Its existence was not recognized. In addition, the above guide tube 302
Excess ozone-containing air is released into the atmosphere from the upward branch port 302b, but the ozone concentration is 0. O2
Even if it is below ppm and useful for disinfecting the surrounding environment, there is no risk of harm to human health.

尚、汚染度が高く例えばBODが数千程度の被処理水の
場合には上記のアクの量が多く上記の下向分岐口302
Aから汚濁泡が放出され易いが、汚染度の比較的低い被
処理水の場合には、汚濁泡が案内管302を経て排出さ
れ難い場合がある。そこで、曝気槽Bの上部側面にも汚
濁泡排出用の放出管30Bを設けておくのが好ましく、
通例は汚濁泡の殆どがこの放出管306を経て排出され
る。
In addition, in the case of treated water with a high degree of contamination, for example, a BOD of several thousand, the amount of scum described above is large and the downward branch port 302 is
Although polluted foam is easily discharged from A, if the water to be treated has a relatively low degree of contamination, it may be difficult for the polluted foam to be discharged through the guide pipe 302. Therefore, it is preferable to provide a discharge pipe 30B for discharging polluted foam on the upper side of the aeration tank B.
Typically, most of the dirty foam is discharged through this discharge pipe 306.

上記のようにして、本発明による浄化滅菌装置lOを1
時間程度稼働させてゆく内に、曝気槽Bの放出管30B
や案内管302における下向分岐口302Aから外部に
排出される汚濁泡の色調が次第に淡(なり、最終的には
排出が停止するので、浄化滅菌処理の完了を確認するこ
とができる。そこて貯槽Aにおける開閉弁12が閉鎖状
態であることを確認した上で、ポンプP−1及びP−2
の運転を休止して水循環を停止させ、開閉弁14を開き
且つポンプP−3を駆動して貯槽A内の水を後処理槽り
に送った。濾過処理室60を通過し貯水室70に至った
処理済み水を採取して観察した処、浮遊懸濁物は何等認
められず、無臭であり且つキラキラ輝くような色調を呈
していた。
As described above, the purification sterilization apparatus according to the present invention is
After operating for about an hour, the discharge pipe 30B of aeration tank B
The color tone of the dirty foam discharged to the outside from the downward branch port 302A of the guide pipe 302 gradually becomes pale (and eventually the discharge stops, so it is possible to confirm the completion of the purification and sterilization process. After confirming that the on-off valve 12 in the storage tank A is in the closed state, pumps P-1 and P-2 are
operation was stopped to stop water circulation, the on-off valve 14 was opened, and the pump P-3 was driven to send water in the storage tank A to the post-treatment tank. When the treated water that had passed through the filtration chamber 60 and reached the water storage chamber 70 was sampled and observed, no suspended matter was observed, and it was odorless and had a sparkling color.

尚、被処理水のIが少ない場合には貯槽Aに送られた被
処理水を直ちに曝気槽Bに送ると共に、オゾン発生装置
C及び紫外線照射装置32を作動させ、貯槽Aを経て被
処理水を循環させることなしに、オゾン含有気泡のリフ
トアップ作用による曝気槽B内における水循環だけで処
理を行うことができ、又被処理水が魚介類の一次加工処
理、例えば魚の開き処理に使用されたような所謂「廃水
」であれば、浄化滅菌処理され貯槽A又は曝気槽Bから
送り出される処理済み水は後処理槽りに送られることな
しにその侭下)に道に放流することもできる。
In addition, when the amount of water to be treated is small, the water to be treated sent to storage tank A is immediately sent to aeration tank B, and the ozone generator C and ultraviolet irradiation device 32 are activated, and the water to be treated passes through storage tank A. The treatment can be carried out only by water circulation in the aeration tank B due to the lift-up effect of ozone-containing air bubbles, and the water to be treated can be used for primary processing of seafood, such as opening fish. In the case of so-called "waste water", the treated water that has been purified and sterilized and sent out from storage tank A or aeration tank B can be discharged into the street without being sent to a post-treatment tank.

扱1丑」 上記の結果から、本発明による水の浄化滅菌装置は所期
の作用効果を有するものであるとの確信を得たので、図
面に示されている装置を、その設計思想乃至理念から逸
脱することなしに、小型化し且つ簡易化した持ち運び可
能な改変装置を製作し、当該改変装置及び被処理水とし
ての海水(銚子港口市場前において満潮時に採取したも
の)を分析機関(社団法人、東京都食品衛生協会)に持
参して当該装置による海水の浄化効果の測定検査を委託
した。
From the above results, we are confident that the water purification and sterilization device according to the present invention has the desired effects, and therefore we have adopted the device shown in the drawings based on its design concept and philosophy. Without deviating from the above, we manufactured a compact and simplified portable modification device, and used the modification device and seawater as the water to be treated (collected at high tide in front of the Choshi Port Market) at an analytical institution (Incorporated Association). , Tokyo Food Sanitation Association) and commissioned an inspection to measure the seawater purification effect of the device.

試験方法及び結果は下記の通りであり、当該改変装置、
延いては既述の実施例による装置は優秀な浄化滅菌能力
を有するものであることが立証された。
The test method and results are as follows, and the modified device,
Furthermore, the apparatus according to the above-mentioned embodiments was proved to have excellent purification and sterilization ability.

試験l: a)試験方法 原水60 リットルを使用して装置を運転させ、一定時
間経過毎に採水して pIN、 COD (ll1g/l)、 色度(度)、 濁度(度)及び 臭気の宵無 を測定する。
Test 1: a) Test method: Operate the device using 60 liters of raw water, sample water at regular intervals, and measure pIN, COD (ll1g/l), color (degrees), turbidity (degrees), and odor. Measure the evening of the night.

b)試験結果 結果は下記の表1に示される通りであった。b) Test results The results were as shown in Table 1 below.

聚」 試験2 a)試験方法 原水GOIJットルに大腸菌を添加して細菌汚染水を調
製し、この細菌汚染水を使用して装置を運転させ、一定
時間経過毎に採水して1ml当りの生菌数及び大腸菌群
数を測定する。
Test 2 a) Test method Prepare bacteria-contaminated water by adding Escherichia coli to raw water GOIJ, operate the device using this bacteria-contaminated water, and sample water at regular intervals to determine the amount of raw material per ml. Measure the number of bacteria and coliform bacteria.

b)試験結果 結果は下記の表2に示される通りであり、細菌で強制的
に汚染させた海水を処理する場合にも、3G −80分
間程度の処理時間で生菌数が著しく減少することが判明
した。
b) Test results The results are as shown in Table 2 below, and even when treating seawater that has been forcibly contaminated with bacteria, the number of viable bacteria decreases significantly within a treatment time of about 3G - 80 minutes. There was found.

(魚の開き干し加工品の保存性試験) 試l目1」 a)試料 水揚げ直後の鰺を試料として用いた。(Storability test of open-dried fish products) Trial 1" a) Sample Mackerel immediately after landing was used as a sample.

b)試験試料及び対照試料の調製性 試料としての鰺を1群lO尾に分け、 す、但し加工処理の際の洗浄水とじて 常法によ 試験群 実施例における貯水槽からのオーバーフロー水を配管に
より作業場に導いて使用し、又対照群A: 汲み上げた井戸水を利用、 対照群B: 従来のように、タンクに汲み上げられていた海水を、そ
のまま利用 して開き処理し、次いで冷風にて乾燥させることにより
試験試料並びに対照試料人及びBを調製した。
b) Preparation of test samples and control samples Divide the mackerel as samples into 1 group of 10 tails. Control group A: Pumped well water was used; Control group B: Seawater pumped into a tank was used as it was, opened and treated, and then cooled with cold air. Test samples and control samples Man and B were prepared by drying.

C)試験方法 試験試料並びに対照試料A及びBを、それぞれ同形・同
寸法の発泡スチロール製箱内に密封し、lOoCの温度
条件下で3日間保蔵した後に開封して外観の状態や臭気
をチエツクし、次いで上記と同一の条件下に更に4日間
(計7日間)保蔵した後に再び開封して同様のチエツク
を行った。
C) Test method The test sample and control samples A and B were each sealed in a styrofoam box of the same shape and size, stored at a temperature of 100C for 3 days, and then opened to check the appearance and odor. Then, after storing for an additional 4 days (7 days in total) under the same conditions as above, the package was opened again and the same checks were performed.

d)試験結果 試験試料は3日間の保蔵後において加工処理直後のもの
と区別し得す、又7日間の保蔵後においても所謂「ネト
」の発生は認められず、臭気においても格別の変化はな
かったので、焼いて試食した処、充分に美味であった。
d) Test results The test samples can be distinguished from those immediately after processing after storage for 3 days, and no generation of so-called "neto" was observed even after storage for 7 days, and there was no particular change in odor. I didn't have any, so I baked it and tried it, and it was delicious.

一方、対照試料はA、 Ill共に3日間の保蔵でネト
の発生及び該ネトに起因する異臭の発生が確認され、そ
の度合は井戸水を加工処理水として用いいた試料の方が
強かった。尚、7日間の保蔵後においては、対照試料は
共に表面が相当程度「粘り状」を呈し、黄色乃至白っぽ
く変色していて強い異臭を発しており、調理には不適当
であって棄却処分せざるを得なかった。
On the other hand, in both control samples A and Ill, it was confirmed that after 3 days of storage, the generation of nettle and the occurrence of an off-odor caused by the netting were observed, and the degree of this was stronger in the sample in which well water was used as the processed water. After being stored for 7 days, the surfaces of both control samples exhibited a considerable degree of "stickiness," turned yellow to whitish, and emitted a strong odor, making them unsuitable for cooking and should be discarded. I had no choice.

(発明の効果) 本発明による水の浄化滅菌装置によれば、被処理水であ
る淡水や海水が曝気槽内においてオゾン含有気泡と殺菌
力の極めて高い波長的254nmを主体とする紫外線の
照射を受けることにより複合的に処理される。従って、
本発明装置の主要部を構成する曝気槽は処理効率が極め
て高いので、汚染水の急速な浄化滅菌処理を可能にする
と共に小型化を可能にする。
(Effects of the Invention) According to the water purification sterilization device of the present invention, freshwater or seawater to be treated is irradiated with ozone-containing bubbles and ultraviolet rays mainly having a wavelength of 254 nm, which has extremely high sterilizing power, in the aeration tank. It is processed in a complex manner by receiving it. Therefore,
Since the aeration tank that constitutes the main part of the apparatus of the present invention has extremely high processing efficiency, it enables rapid purification and sterilization of contaminated water and also enables miniaturization.

本発明による装置において曝気槽に送られるオゾン含有
空気を副型するオゾン発生装置は市販の低圧水銀灯を用
いて構成することができ、又曝気槽内に配置されて被処
理水やオゾン含有気泡に波長的254n++を主体とす
る上記の紫外線を照射する紫外線照射装置も市販の低圧
水銀灯を利用し、これを水に対する保護管に収容するこ
とにより構成することができるので、装置全体としての
構成や保守が容易である。
In the apparatus according to the present invention, the ozone generator that sub-types the ozone-containing air sent to the aeration tank can be constructed using a commercially available low-pressure mercury lamp. The ultraviolet irradiation device that irradiates the above-mentioned ultraviolet rays mainly with a wavelength of 254n++ can also be constructed by using a commercially available low-pressure mercury lamp and housing it in a protection tube against water, so it is easy to configure and maintain the entire device. is easy.

更に、本発明による装置にて処理された浄化滅菌水を魚
介類の一次加工処理水として、例えば生干し加工製品調
製用の洗浄用等に供すれば、当該製品の保存性を有意に
向上させることができる。
Furthermore, if the purified sterilized water treated with the apparatus according to the present invention is used as water for the primary processing of seafood, for example, for washing in the preparation of raw-dried processed products, the shelf life of the products can be significantly improved. I can do it.

尚、本発明による装置は、上記のような力a工処理に用
いられた後の水を被処理水として浄化滅菌することがで
き、従って海洋や、河川の汚染を未然に防止する公害対
策用にも適用可能である。
Furthermore, the apparatus according to the present invention can purify and sterilize the water that has been used in the above-mentioned mechanical processing as water to be treated, and therefore can be used as a pollution control device to prevent pollution of oceans and rivers. It is also applicable to

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

第1図は本発明による水の浄化滅菌装置の概要を示す図
面であって、個々の構成設備の構造を示すために縦断面
或は部分破断断面を以って表した図面、 第2図は曝気槽内で被処理水がオゾン含有気泡及び紫外
線照射により受ける複合作用を説明するための模式図で
ある。 A−−一被処理水の丘1、B−−一曝気槽、C−−−オ
ゾン発生装置、D−−一後処理槽、P−1,P−2−−
一被処理水循環用のポンプ、32−m−紫外線照射装置
、34−−一気泡発生器、40−−一紫外線ランプ、5
2−−一紫外線ランプ(オゾン発生用)、60−m−濾
過処理室、B2−−m1水室
Fig. 1 is a drawing showing an outline of the water purification sterilization apparatus according to the present invention, and is a drawing shown in longitudinal section or partially broken section to show the structure of each component equipment. FIG. 2 is a schematic diagram for explaining the combined effect that water to be treated receives in an aeration tank due to ozone-containing bubbles and ultraviolet irradiation. A--1 hill of water to be treated 1, B--1 aeration tank, C--ozone generator, D--1 post-treatment tank, P-1, P-2--
1. Pump for circulating water to be treated, 32--ultraviolet irradiation device, 34--bubble generator, 40--ultraviolet lamp, 5
2--1 ultraviolet lamp (for ozone generation), 60-m-filtration chamber, B2--m1 water chamber

Claims (7)

【特許請求の範囲】[Claims] (1)被処理水の導入される貯槽と、曝気槽と、上記の
貯槽と曝気槽とを接続する配管と、該配管を介して被処
理水を上記の貯槽から曝気槽に送るポンプと、オゾン発
生装置とを備えており、上記の曝気槽が紫外線照射装置
と気泡発生器とを具備しており、該気泡発生器には上記
のオゾン発生装置からのオゾン含有空気が送気され、斯
くて被処理水が上記の曝気槽内において紫外線及びオゾ
ン含有気泡による複合作用を受けることを特徴とする、
水の浄化滅菌装置。
(1) A storage tank into which the water to be treated is introduced, an aeration tank, piping that connects the storage tank and the aeration tank, and a pump that sends the water to be treated from the storage tank to the aeration tank via the piping; The aeration tank is equipped with an ultraviolet irradiation device and a bubble generator, and the bubble generator is supplied with ozone-containing air from the ozone generator. characterized in that the water to be treated is subjected to the combined action of ultraviolet rays and ozone-containing bubbles in the aeration tank,
Water purification sterilization equipment.
(2)後処理槽を更に備えており、該後処理槽が濾過処
理室と貯水室とを具備し、濾過処理室が貯槽及び曝気槽
の少なくとも一方と配管で接続され且つ下段から上段に
向かって進入水の一次溜り区画と、カルシウム素材充填
区画とを備えており、上記の貯水室がオーバーフロー機
構を具備していることを特徴とする、請求項(1)に記
載の水の浄化滅菌装置。
(2) The post-treatment tank further includes a filtration treatment chamber and a water storage chamber, and the filtration treatment chamber is connected to at least one of the storage tank and the aeration tank by piping, and extends from the lower stage to the upper stage. The water purification sterilization device according to claim 1, further comprising a primary storage section for incoming water and a calcium material filling section, and wherein the water storage chamber is equipped with an overflow mechanism. .
(3)曝気槽内の紫外線照射装置が上下端の解放され、
上部側面に開口を有し且つ曝気槽内に直立状態で配置さ
れた外筒と、この外筒内に配置されており、上端が開放
され且つ他端が閉鎖されている内筒であって紫外線透過
性の素材で構成されており、内部が液密状態で上記の外
筒に取り付けられている内筒と、該内筒内に配置されて
おり且つ波長約254nmを主体とする紫外線を照射す
る紫外線ランプとで構成されていることを特徴とする、
請求項(1)又は(2)に記載の水の浄化滅菌装置。
(3) The upper and lower ends of the ultraviolet irradiation device in the aeration tank are opened,
An outer cylinder that has an opening on the upper side and is placed upright in the aeration tank, and an inner cylinder that is placed inside this outer cylinder and has an open top end and a closed end that prevents ultraviolet rays from entering the tank. An inner cylinder made of a transparent material and attached to the above-mentioned outer cylinder in a liquid-tight state, and an inner cylinder that is placed inside the inner cylinder and irradiates ultraviolet rays mainly having a wavelength of about 254 nm. It is characterized by being composed of an ultraviolet lamp,
The water purification sterilization device according to claim (1) or (2).
(4)オゾン発生装置が空気導入孔とオゾン含有空気排
出孔とを備えた外筒と、該外筒内に配置固定されていて
波長約185nmの紫外線を照射する紫外線ランプとで
構成されていることを特徴とする、請求項(1)又は(
2)に記載の水の浄化滅菌装置。
(4) The ozone generator is composed of an outer cylinder equipped with an air introduction hole and an ozone-containing air exhaust hole, and an ultraviolet lamp that is placed and fixed inside the outer cylinder and emits ultraviolet light with a wavelength of about 185 nm. Claim (1) or (
2) The water purification sterilization device described in 2).
(5)後処理槽におけるカルシウム素材充填区画が貝殻
層で形成されており、この貝殻層が進入水の通過の向き
である下段から上段に向かって粗砕コーラル貝殻層と、
カキ及びホタテの貝殻から選ばれ粗砕された貝殻層と、
コーラルサンド層とで構成されていることを特徴とする
、請求項(2)に記載の水の浄化滅菌装置。
(5) The calcium material filling section in the after-treatment tank is formed of a shell layer, and this shell layer has a coarsely crushed coral shell layer from the lower layer to the upper layer, which is the direction in which the incoming water passes;
A shell layer selected from oyster and scallop shells and crushed,
The water purification sterilization device according to claim 2, characterized in that the water purification sterilization device is comprised of a coral sand layer.
(6)曝気槽内において紫外線ランプを各々収容してい
る内筒が複数本配置されており、これらの紫外線ランプ
の内の少なくとも一本が波長185nmのオゾン線を照
射するランプであり、他が波長約254nmの殺菌性共
鳴線を照射するランプであることを特徴とする、請求項
(3)に記載の水の浄化滅菌装置。
(6) A plurality of inner cylinders each containing an ultraviolet lamp are arranged in the aeration tank, and at least one of these ultraviolet lamps is a lamp that emits ozone rays with a wavelength of 185 nm, and the others are The water purification and sterilization device according to claim 3, characterized in that the lamp emits germicidal resonance radiation having a wavelength of about 254 nm.
(7)曝気槽において波長約254nm又は波長約25
4nmと約185nmの紫外線照射を受け且つオゾン含
有気泡と接触することにより充分に処理され、次いでカ
ルシウム素材の充填された濾過処理室を有する後処理槽
を通過した浄化滅菌水を魚介類の加工処理水として用い
ることを特徴とする、加工魚介類の鮮度維持法。
(7) In the aeration tank, the wavelength is approximately 254 nm or approximately 25 nm.
Purified sterilized water that has been sufficiently treated by being exposed to UV irradiation of 4 nm and about 185 nm and contacting with ozone-containing bubbles, and then passed through a post-treatment tank having a filtration chamber filled with calcium material, is used for seafood processing. A method for maintaining the freshness of processed seafood, characterized by using it as water.
JP2129026A 1990-05-21 1990-05-21 Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water Pending JPH0427493A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2129026A JPH0427493A (en) 1990-05-21 1990-05-21 Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2129026A JPH0427493A (en) 1990-05-21 1990-05-21 Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water

Publications (1)

Publication Number Publication Date
JPH0427493A true JPH0427493A (en) 1992-01-30

Family

ID=14999300

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2129026A Pending JPH0427493A (en) 1990-05-21 1990-05-21 Cleaning and sterilizing device for water and method for utilizing cleaned and sterilized water

Country Status (1)

Country Link
JP (1) JPH0427493A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05192673A (en) * 1992-01-17 1993-08-03 Takaoka Electric Mfg Co Ltd Method for decomposing ammonia with ozone
JPH11179349A (en) * 1997-12-24 1999-07-06 Masamichi Kikuchi Sterilizing method and sterilizing ice-making device for seawater
KR100834491B1 (en) * 2007-02-15 2008-06-02 한도광고산업(주) A frame for advertisement
SG169226A1 (en) * 2001-09-12 2011-03-30 Cumminscorp Ltd Water treatment apparatus
CN102596901A (en) * 2009-09-16 2012-07-18 斯塔米卡邦有限公司 Removal of urea and ammonia from exhaust gases
JP2013106565A (en) * 2011-11-21 2013-06-06 Acurusu:Kk Ozone sterilizing apparatus
JP2019122374A (en) * 2018-01-12 2019-07-25 トスレック株式会社 Purification method of shellfish and purification system of shellfish
WO2019227172A1 (en) * 2018-06-02 2019-12-05 Guthalungra Holdings LLC Nevis A waste treatment system

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05192673A (en) * 1992-01-17 1993-08-03 Takaoka Electric Mfg Co Ltd Method for decomposing ammonia with ozone
JPH11179349A (en) * 1997-12-24 1999-07-06 Masamichi Kikuchi Sterilizing method and sterilizing ice-making device for seawater
SG169226A1 (en) * 2001-09-12 2011-03-30 Cumminscorp Ltd Water treatment apparatus
KR100834491B1 (en) * 2007-02-15 2008-06-02 한도광고산업(주) A frame for advertisement
CN102596901A (en) * 2009-09-16 2012-07-18 斯塔米卡邦有限公司 Removal of urea and ammonia from exhaust gases
US9464009B2 (en) * 2009-09-16 2016-10-11 Stamicarbon B.V. Removal of urea and ammonia from exhaust gases
US9556077B2 (en) 2009-09-16 2017-01-31 Stamicarbon B.V. Removal of urea and ammonia from exhaust gases
JP2013106565A (en) * 2011-11-21 2013-06-06 Acurusu:Kk Ozone sterilizing apparatus
JP2019122374A (en) * 2018-01-12 2019-07-25 トスレック株式会社 Purification method of shellfish and purification system of shellfish
WO2019227172A1 (en) * 2018-06-02 2019-12-05 Guthalungra Holdings LLC Nevis A waste treatment system

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