JP2001340844A - Method and apparatus for sterilizing wastewater containing microorganism and/or virus - Google Patents

Method and apparatus for sterilizing wastewater containing microorganism and/or virus

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Publication number
JP2001340844A
JP2001340844A JP2000165344A JP2000165344A JP2001340844A JP 2001340844 A JP2001340844 A JP 2001340844A JP 2000165344 A JP2000165344 A JP 2000165344A JP 2000165344 A JP2000165344 A JP 2000165344A JP 2001340844 A JP2001340844 A JP 2001340844A
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Japan
Prior art keywords
wastewater
viruses
sterilization
microorganisms
heat exchanger
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.)
Granted
Application number
JP2000165344A
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Japanese (ja)
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JP3297419B2 (en
Inventor
Susumu Sato
佐藤  進
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Kajima Corp
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Kajima Corp
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Abstract

PROBLEM TO BE SOLVED: To provide a method for sterilizing wastewater containing microorganisms and/or viruses by the use of a heat exchanger in which the clogging of piping is prevented, and an apparatus for the method. SOLUTION: Wastewater A to be sterilized which is estimated to contain the microorganisms and/or viruses, the pH of which is adjusted so that the constituent proteins of the microorganisms and/or the viruses are not precipitated even after being denaturated by the sterilization, is passed through the heat exchanger 6 and kept at a necessary temperature for a necessary time to effect the sterilization. Preferably, the wastewater A is made alkaline to prevent the precipitation of the proteins even after being denaturated. More preferably, the wastewater A before the passage through the heat exchanger is heated by being heat-exchanged with the sterilized wastewater E kept at a sterilization temperature. The temperature and time for sterilization of the wastewater A are preferably adjusted so that the survival rate of the microorganism and/or the viruses after the sterilization is 1×10-6 or below.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は微生物及び/又はウ
ィルス(細菌、糸状菌、酵母、らん藻、原生動物、ウィ
ルス・ファージ、プリオン等から選択された1以上のも
のをいう。以下、同じ。)含有排水の殺菌方法及び装置
に関し、とくに微生物及び/又はウィルスの存在が懸念
される製薬施設・工場や病院等からの廃液・排水を不活
化する殺菌方法及び装置に関する。
The present invention relates to one or more microorganisms and / or viruses (bacteria, filamentous fungi, yeasts, cyanobacteria, protozoa, virus / phages, prions, etc .; the same applies hereinafter). The present invention relates to a method and apparatus for sterilizing contained wastewater, and particularly to a method and apparatus for inactivating waste liquid and wastewater from pharmaceutical facilities, factories, hospitals, and the like in which the presence of microorganisms and / or viruses is concerned.

【0002】[0002]

【従来の技術】従来、血液製剤等の製薬施設・工場や病
院からの微生物及び/又はウィルスの存在が懸念される
廃液・排水(以下、微生物及び/又はウィルス含有排水
ということがある。)に対しては、以下の措置がとられ
ている(日本感染症学会編集「病院感染対策テキスト」
改訂3版、1998年7月)。
2. Description of the Related Art Conventionally, wastewater and wastewater (hereinafter sometimes referred to as microorganism- and / or virus-containing wastewater) from microorganisms and / or viruses from pharmaceutical facilities, factories, and hospitals such as blood products are concerned. In response, the following measures have been taken (edited by the Japanese Society for Infectious Diseases, “Hospital Infection Control Text”)
3rd revised edition, July 1998).

【0003】1)排水管内の排水が逆流しないこと。必
要に応じて、排水系統を一旦大気から縁を切り、一般排
水系統に直結している水受け容器又は排水機器の中に排
水する間接排水の方法を採る。 2)排水管からの臭気、下水ガス、衛生害虫などが室内
に侵入するのを防止すること。このために必要に応じ
て、各種トラップを設置する。 3)床排水口は容易に点検できる場所に設け、トラップ
に接続すること。 4)排水管には通気機能を有する通気管を設けること。 5)排水管が詰まらないように、また詰まった場合には
対応できること。このため、必要な場所には掃除口を設
ける。 6)高度清潔区域では、排水口が汚染源とならないよう
工夫すること。
1) The drainage in the drainage pipe does not flow backward. If necessary, use an indirect drainage method in which the drainage system is once cut off from the atmosphere and drained into a water receiving container or drainage device that is directly connected to the general drainage system. 2) Prevent odor, sewage gas, sanitary insects, etc. from drainage pipes from entering the room. For this purpose, various traps are installed as needed. 3) Floor drains should be installed in a place where they can be easily inspected and connected to traps. 4) A drain pipe having a ventilation function shall be provided in the drain pipe. 5) To prevent clogging of drain pipes and to be able to cope with clogging. For this reason, a cleaning port is provided in a necessary place. 6) In highly clean areas, take measures to prevent drainage from becoming a source of pollution.

【0004】しかし、上記の排水措置では、感染が懸念
される排水が未処理のまま系外へ排出されるおそれがあ
る。また、トラップ内の汚物は不活化前であり、その汚
物を通して感染するおそれもある。
[0004] However, in the above-mentioned drainage measures, there is a possibility that wastewater which is likely to be infected is discharged out of the system without treatment. In addition, the dirt in the trap is before being inactivated, and there is a possibility that the dirt is transmitted through the dirt.

【0005】そこで、とくに感染性の微生物及び/又は
ウィルス(以下、微生物・ウィルスと表すことがあ
る。)の存在が懸念される廃液・排水に対しては、微生
物・ウィルスを不活化(以下、殺菌ということがあ
る。)するため、pH調整や凝集沈澱処理を施して沈澱部
分を脱水後に焼却処分し、液相部分は次亜塩素酸ナトリ
ウム等の消毒剤により消毒処理したのち更に過剰薬剤を
中和して系外へ排出する処理方法が採られる場合があ
る。また、排水を一旦キルタンク(バッチ式殺菌・消毒
装置、高圧蒸気投入保持装置、又は薬液(消毒剤)投入
保持装置)やオートクレーブ(高圧蒸気滅菌装置)など
に貯え、バッチ処理により蒸気又は薬液を直接投入して
熱処理又は化学処理したのち、系外へ排出する処理方法
が採用される場合もある。
[0005] Therefore, microorganisms and viruses are inactivated (hereinafter, referred to as wastewater and wastewater) in which the presence of infectious microorganisms and / or viruses (hereinafter sometimes referred to as microorganisms and viruses) is concerned. In order to perform sterilization, pH adjustment and coagulation sedimentation treatment are applied, and the precipitated part is dehydrated and incinerated. The liquid phase part is disinfected with a disinfectant such as sodium hypochlorite, and then excess drug is removed. There is a case where a treatment method of neutralizing and discharging out of the system is adopted. In addition, the wastewater is temporarily stored in a kill tank (batch-type disinfection / disinfection device, high-pressure steam charging / holding device, or chemical (disinfectant) charging / holding device) or autoclave (high-pressure steam sterilizer), and the steam or chemical solution is directly processed by batch processing. There is a case where a processing method is employed in which the heat treatment or chemical treatment is performed after the introduction, and then the treatment is discharged outside the system.

【0006】[0006]

【発明が解決しようとする課題】しかし、前記消毒剤で
殺菌する処理方法は、多量の薬品の添加が必要となり、
また焼却処分に大きなエネルギーを要するので、それら
に伴い殺菌処理のランニングコストが高騰する問題点が
ある。他方、前記キルタンクやオートクレーブに貯えて
蒸気又は薬液を直接投入して熱処理又は化学処理する方
法は、バッチ式であるため、大量の排水を処理するため
に大規模な装置が必要となるか又は並列処理するために
多数の装置が必要となり、設備コストが嵩み、装置の管
理及び制御が煩雑になる等の問題点がある。
However, the treatment method of disinfecting with the disinfectant requires the addition of a large amount of chemicals.
In addition, since a large amount of energy is required for incineration, there is a problem that the running cost of the sterilization treatment rises accordingly. On the other hand, since the method of heat treatment or chemical treatment by directly charging steam or chemical liquid stored in the kill tank or autoclave is a batch type, a large-scale apparatus is required to treat a large amount of wastewater or parallel processing is required. A large number of devices are required for processing, and the equipment costs are increased, and the management and control of the devices become complicated.

【0007】このような問題点を解決するため、熱交換
器を利用した殺菌処理が考えられる。熱交換器によれ
ば、比較的小さな装置で、排水を連続的に処理すること
が可能である。ただし、熱交換器利用の殺菌処理では、
熱処理により固化変性した微生物・ウィルス、及び排水
中の他の有機物(例えば血液製剤等の製薬施設排水中の
血漿蛋白質等)が配管内に沈澱・付着し、配管を閉塞す
るおそれがある。
In order to solve such a problem, a sterilization treatment using a heat exchanger can be considered. According to the heat exchanger, it is possible to continuously treat wastewater with a relatively small device. However, in the sterilization process using a heat exchanger,
Microorganisms and viruses solidified and denatured by the heat treatment, and other organic substances in the wastewater (for example, plasma proteins and the like in the wastewater of pharmaceutical facilities such as blood products) may precipitate and adhere to the piping, and may block the piping.

【0008】そこで本発明の目的は、配管の閉塞を生じ
させない熱交換器利用の微生物及び/又はウィルス含有
排水の殺菌方法及び装置を提供するにある。
Accordingly, an object of the present invention is to provide a method and an apparatus for disinfecting wastewater containing microorganisms and / or viruses utilizing a heat exchanger without causing clogging of piping.

【0009】[0009]

【課題を解決するための手段】図1の実施例を参照する
に、本発明の微生物及び/又はウィルス含有排水の殺菌
方法は、加熱殺菌すべき微生物及び/又はウィルス含有
排水Aを当該微生物及び/又はウィルスの構成蛋白質が
殺菌による変性後も沈澱しないpHとしたのち熱交換器6
に通し、所要殺菌温度に所要殺菌時間保持してなるもの
である。好ましくは、前記排水Aを、微生物及び/又は
ウィルスの構成蛋白質が殺菌による変性後も溶解するア
ルカリ濃度とする。
Referring to the embodiment shown in FIG. 1, the method for disinfecting wastewater containing microorganisms and / or viruses according to the present invention comprises removing the wastewater A containing microorganisms and / or viruses to be heat-sterilized with the microorganisms and / or viruses. And / or heat exchanger 6 after adjusting the pH so that the constituent proteins of the virus do not precipitate even after denaturation by sterilization.
And the required sterilization time is maintained at the required sterilization temperature. Preferably, the waste water A has an alkali concentration at which the constituent proteins of microorganisms and / or viruses are dissolved even after denaturation by sterilization.

【0010】また図1を参照するに、本発明の微生物及
び/又はウィルス含有排水の殺菌装置は、微生物及び/
又はウィルス含有排水Aを貯める原水受槽1、原水受槽
1中の排水AのpHを調整するpH調整装置3、排水Aを所
要殺菌温度に所要殺菌時間保持する熱交換装置5、及び
原水受槽1中の排水Aを熱交換装置5へ送る送水管10を
備え、pH調整装置3により前記微生物及び/又はウィル
スの構成蛋白質が殺菌による変性後も沈澱しないpHとし
た後の排水を送水管10により原水受槽1から熱交換装置
5へ送ってなるものである。好ましくは、pH調整装置3
を原水受槽1中にアルカリ剤を注入するアルカリ剤注入
装置とし、当該注入装置により原水受槽1中の排水Aを
微生物及び/又はウィルスの構成蛋白質が殺菌による変
性後も溶解するアルカリ濃度とする。
Referring to FIG. 1, the apparatus for sterilizing wastewater containing microorganisms and / or viruses according to the present invention comprises a microorganism and / or virus.
Or, a raw water receiving tank 1 for storing virus-containing wastewater A, a pH adjusting device 3 for adjusting the pH of the wastewater A in the raw water receiving tank 1, a heat exchange device 5 for maintaining the wastewater A at a required sterilizing temperature for a required sterilizing time, and the raw water receiving tank 1. A water supply pipe 10 for sending the waste water A to the heat exchange device 5 is provided. The waste water after the pH adjustment device 3 is adjusted to a pH at which the constituent proteins of the microorganisms and / or viruses do not precipitate even after denaturation by sterilization is supplied to the raw water supply pipe 10 by the water supply pipe 10. It is sent from the receiving tank 1 to the heat exchange device 5. Preferably, the pH adjusting device 3
Is an alkaline agent injection device for injecting an alkaline agent into the raw water receiving tank 1, and the injection device sets the wastewater A in the raw water receiving tank 1 to an alkali concentration at which the constituent proteins of microorganisms and / or viruses are dissolved even after denaturation by sterilization.

【0011】[0011]

【発明の実施の形態】図1は、血液製剤等の製薬施設・
工場や病院等のCIP(Cleaning in Place。生産状態のま
まで、特に装置に追加的機器を取り付けることなく又は
生産設備を分解することなく行われる自動洗浄をいう。
以下同じ。)排水、洗浄室よりの洗浄排水、床排水を含
むその他の排水などを微生物・ウィルスの含有排水Aと
して熱交換装置5により殺菌する本発明装置の実施例を
示す。排水Aを原水受槽1に一旦蓄え、pH調整装置3に
より排水Aを微生物・ウィルスの構成蛋白質が殺菌によ
る変性後も沈澱しないpHに調整する。排水A中に微生物
・ウィルスの構成蛋白質以外の蛋白質が含まれている場
合は、その蛋白質も変成後に沈澱しないpHに調整するこ
とができる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows a pharmaceutical facility for blood products and the like.
CIP (Cleaning in Place) in factories, hospitals, etc. Automatic cleaning that is performed in a production state, in particular, without attaching additional equipment to the equipment or disassembling the production equipment.
same as below. 1) An embodiment of the apparatus of the present invention for sterilizing the waste water, washing waste water from the washing room, and other waste water including floor waste water as waste water A containing microorganisms and viruses by the heat exchange device 5 will be described. The wastewater A is temporarily stored in the raw water receiving tank 1, and the pH of the wastewater A is adjusted by the pH adjusting device 3 to a pH at which the constituent proteins of microorganisms and viruses do not precipitate even after denaturation by sterilization. When wastewater A contains a protein other than the constituent proteins of microorganisms and viruses, the pH of the protein can be adjusted to a value that does not precipitate after denaturation.

【0012】図示例では、原水受槽1中にアルカリ剤を
注入するアルカリ剤注入装置をpH調整装置3とし、原水
受槽1中の排水Aを微生物及び/又はウィルスの構成蛋
白質が殺菌による変性後も溶解するアルカリ濃度に調整
している。微生物・ウィルスの構成蛋白質以外の蛋白質
を含む排水Aの場合は、その蛋白質も変成後に沈澱しな
いアルカリ濃度に調整することができる。例えば、アル
カリ剤注入により排水Aのアルカリ濃度をpH>9とし、
変性後の蛋白質を溶解可能とする。好ましくは、排水A
のアルカリ濃度をpH>11とする。ただし、排水AのpH測
定の結果、製薬施設等からの排水Aが所要のpH、例えば
前記アルカリ濃度のアルカリ性である場合は、pH調整装
置(アルカリ剤注入装置)3によるpHの調整を省略して
もよい。
In the illustrated example, a pH adjusting device 3 is used as an alkaline agent injection device for injecting an alkaline agent into the raw water receiving tank 1, and the wastewater A in the raw water receiving tank 1 is subjected to denaturation of the microorganism and / or virus constituent proteins by sterilization. Adjusted to the concentration of alkali that dissolves. In the case of waste water A containing proteins other than the constituent proteins of microorganisms and viruses, the concentration of the protein can be adjusted to an alkali concentration that does not precipitate after denaturation. For example, the alkali concentration of the wastewater A is adjusted to pH> 9 by injecting an alkali agent,
The denatured protein can be dissolved. Preferably, drainage A
Is adjusted to pH> 11. However, as a result of the pH measurement of the wastewater A, if the wastewater A from the pharmaceutical facility or the like has a required pH, for example, the alkali having the above-mentioned alkali concentration, the pH adjustment by the pH adjusting device (alkali agent injection device) 3 is omitted. You may.

【0013】排水Aのアルカリ濃度調整用のアルカリ剤
としては、例えば水酸化ナトリウム(NaOH)、水酸化カ
ルシウム(Ca(OH)2)等が使用できる。ただし、水酸化
カルシウムの場合は余剰分の析出などが懸念される。水
酸化ナトリウムは、析出のおそれがなく、また濃度・流
量の調整が容易であり簡便に使用できる。
As the alkali agent for adjusting the alkali concentration of the waste water A, for example, sodium hydroxide (NaOH), calcium hydroxide (Ca (OH) 2 ) and the like can be used. However, in the case of calcium hydroxide, there is a concern that an excessive amount of precipitation may occur. Sodium hydroxide has no risk of precipitation, and its concentration and flow rate are easily adjusted, so that it can be used easily.

【0014】以下、同図を参照して、前記アルカリ濃度
にpH調整した排水Aを殺菌する場合について本発明を説
明するが、本発明における排水AのpHはアルカリ性に限
定されず、排水A中の微生物・ウィルスの構成蛋白質が
殺菌による変性後も沈澱しないpHであれば足りる。排水
A中には微生物・ウィルスの構成蛋白質以外の有機物
(例えば血液製剤等の製薬施設排水中の血漿蛋白質等)
も含まれている場合があるが、微生物・ウィルスの構成
蛋白質が変性後も沈澱しないpHであれば、排水中の他の
有機物も変成後に沈澱しないと考えられる。
Hereinafter, the present invention will be described with reference to FIG. 1 for the case of sterilizing the wastewater A adjusted to have the above-mentioned alkaline concentration. However, the pH of the wastewater A in the present invention is not limited to alkalinity. The pH is sufficient if the constituent proteins of the microorganisms and viruses do not precipitate even after denaturation by sterilization. Organic matter other than the constituent proteins of microorganisms and viruses in wastewater A (for example, plasma proteins in wastewater from pharmaceutical facilities such as blood products)
If the pH is such that the constituent proteins of microorganisms and viruses do not precipitate even after denaturation, it is considered that other organic substances in the wastewater will not precipitate after denaturation.

【0015】前記アルカリ濃度に調整後の排水Aを、送
水管10を介して熱交換装置5へ送る。熱交換装置5は、
排水Aと蒸気Gとの熱交換により所要殺菌温度以上に昇
温する熱交換器6、及び熱交換器6から出力される高温
排水Dを前記所要殺菌温度に所要殺菌時間保持するホー
ルディングチューブ7を有する。図示例では、熱交換装
置5に熱交換器6からの出口排水温度を測定する温度セ
ンサ8、及びホールディングチューブ7内の圧力を測定
する圧力センサ9を設け、温度センサ8及び圧力センサ
9に接続した制御装置(図示せず)により、温度センサ
8の出力信号に応じた熱交換器6の温度制御、及び圧力
センサ9の出力信号に応じたホールディングチューブ7
の排水保持時間の制御を可能としている。
The wastewater A adjusted to the alkali concentration is sent to the heat exchange device 5 through the water pipe 10. The heat exchange device 5
A heat exchanger 6 that raises the temperature above the required sterilization temperature by heat exchange between the wastewater A and the steam G, and a holding tube 7 that holds the high-temperature wastewater D output from the heat exchanger 6 at the required sterilization temperature for the required sterilization time. Have. In the illustrated example, the heat exchange device 5 is provided with a temperature sensor 8 for measuring the outlet drain temperature from the heat exchanger 6 and a pressure sensor 9 for measuring the pressure in the holding tube 7, and is connected to the temperature sensor 8 and the pressure sensor 9. The control device (not shown) controls the temperature of the heat exchanger 6 according to the output signal of the temperature sensor 8 and the holding tube 7 according to the output signal of the pressure sensor 9.
Control of the drainage retention time.

【0016】一般に、初期生菌数N0に対する殺菌後の生
菌数Nの生存割合(=N/N0)が100万分の1(10-6)以
下であることをもって滅菌保証レベル(Sterility Assu
rance Level)とされる(古橋正吉著「滅菌・消毒マニ
ュアル」日本醫事新報社、1999年1月、p37。以下、6桁
殺滅という)。例えば一般細菌の6桁殺滅には、121℃
では9分間(好ましくは15分間)以上、134℃では0.45分
間(好ましくは3分間)以上の保持が必要である(前掲
「滅菌・消毒マニュアル」p49。佐々木次雄他著「日本
薬局方に準拠した滅菌法及び微生物殺滅法」日本規格協
会、1998年2月、p19)。また、B型肝炎ウィルスの6桁
殺滅には、98℃で2分間、108℃で72秒間の保持が必要
である。プリオンの6桁殺滅には、155℃で36秒間の保
持が必要である。熱交換装置5のホールディングチュー
ブ7は、微生物・ウィルスの種類に応じて、排水Aを必
要な殺菌温度に必要な殺菌時間保持するものである。好
ましくは、熱交換装置5による排水温度及びホールディ
ングチューブ7における排水保持時間を調節可能とし、
微生物・ウィルスの種類に応じて6桁殺滅を確保できる
ようにする。
In general, the sterilization assurance level (Sterility Assu) is defined as the survival rate of the viable cell count N after sterilization to the initial viable cell count N 0 (= N / N 0 ) is 1 / 100,000 (10 −6 ) or less.
rance Level) (Sterilization and Disinfection Manual, written by Masayoshi Furuhashi, Nippon Medical Science Shinposha, January 1999, p37. For example, to kill 6 orders of magnitude of general bacteria, 121 ° C
Requires at least 9 minutes (preferably 15 minutes) and at 134 ° C for at least 0.45 minutes (preferably 3 minutes) (see “Sterilization and Disinfection Manual”, p. 49; Tsugio Sasaki et al. Sterilization and Microbial Killing Methods ”, Japan Standards Association, February 1998, p19). Further, in order to kill the hepatitis B virus by 6 digits, it is necessary to hold at 98 ° C. for 2 minutes and at 108 ° C. for 72 seconds. Six-digit killing of prions requires holding at 155 ° C. for 36 seconds. The holding tube 7 of the heat exchange device 5 holds the wastewater A at a required sterilization temperature and a required sterilization time according to the type of microorganisms and viruses. Preferably, the temperature of the waste water by the heat exchange device 5 and the time for holding the waste water in the holding tube 7 can be adjusted,
Six-digit killing can be ensured according to the type of microorganisms and viruses.

【0017】本発明者は、血液製剤等の製薬施設からの
排水Aについて、135℃に90秒以上保持することによ
り、排水中に混在の危険性が否定できない細菌類のほぼ
全て、及びヒト免疫不全ウィルス(HIV)、B型肝炎ウ
ィルス(HBV)やC型肝炎ウィルス(HCV)等の肝炎ウィ
ルス、その他のウィルスを含む微生物・ウィルスを6桁
殺滅できることを実験的に確認した。
By maintaining the wastewater A from a pharmaceutical facility for blood products and the like at 135 ° C. for 90 seconds or more, the present inventor has found that almost all bacteria whose danger of contamination cannot be ruled out, It was experimentally confirmed that microorganisms and viruses including hepatitis viruses such as deficiency virus (HIV), hepatitis B virus (HBV) and hepatitis C virus (HCV), and other viruses can be killed by six orders of magnitude.

【0018】ホールディングチューブ7の殺菌処理によ
り微生物・ウィルスの構成蛋白質や排水中の他の熱固化
成分は熱変性するが、本発明では排水を蛋白質が熱変性
後も沈澱しないpHとするので、それらの変性固化した蛋
白質の熱交換器6及びホールディングチューブ7の配管
内壁への沈澱を抑制できる。また、たとえ蛋白質が沈澱
した場合でも、連続的に流入する前記pHの昇温排水Eに
よって溶解するので、配管内壁への付着の防止が期待で
きる。従って、本発明の殺菌装置はメンテナンス及び管
理が容易である。
Although the constituent proteins of microorganisms and viruses and other heat-solidified components in the wastewater are thermally denatured by the sterilization treatment of the holding tube 7, in the present invention, the wastewater is adjusted to a pH at which the protein does not precipitate even after the heat denaturation. Precipitation of the denatured and solidified protein on the inner wall of the heat exchanger 6 and the holding tube 7 can be suppressed. Further, even if the protein precipitates, it is dissolved by the temperature-raised wastewater E having the above-mentioned pH which continuously flows in, so that the adhesion to the inner wall of the pipe can be expected. Therefore, the sterilization apparatus of the present invention is easy to maintain and manage.

【0019】また、配管の閉塞を防ぐことができるの
で、連続して排出される排水の殺菌処理を長期間安定的
に継続できる。継続処理により、装置の規模を小さく抑
えることが可能となり、設備コストの低減を図ることも
期待できる。しかも熱交換装置5による殺菌効果は、排
水のpHにより影響されない。ホールディングチューブ7
を通過後の殺菌済排水Eは、適当な水温とした後、必要
に応じて薬剤の中和処理やBOD処理を施して一般の排
水と共に放流できる。
Further, since the clogging of the piping can be prevented, the sterilization of the continuously discharged wastewater can be stably continued for a long period of time. The continuous processing makes it possible to reduce the size of the apparatus, and it can be expected that equipment costs can be reduced. Moreover, the sterilizing effect of the heat exchange device 5 is not affected by the pH of the waste water. Holding tube 7
The sterilized drainage water E after passing through can be discharged together with general drainage water by subjecting it to an appropriate water temperature, subjecting it to a chemical neutralization treatment or a BOD treatment as needed.

【0020】こうして本発明の目的である「配管の閉塞
を生じさせない熱交換器利用の微生物及び/又はウィル
ス含有排水の殺菌方法及び装置」の提供が達成できる。
In this manner, the object of the present invention is to provide "a method and an apparatus for disinfecting wastewater containing microorganisms and / or viruses utilizing a heat exchanger which does not cause clogging of piping".

【0021】[0021]

【実施例】図1では、原水受槽1と熱交換装置5との間
の送水管10に、熱交換装置5へ通す前の排水Aを前記殺
菌温度に保持した後の殺菌済排水Eとの熱交換により昇
温する予熱装置15、16を設けている。ホールディングチ
ューブ7を通過後の殺菌済排水Eは高温であり、そのま
まBOD処理等を施すことは困難であり、高温のままで
の放流は避ける必要がある。図示例では、高温の排水E
で比較的低温の排水Aを昇温するので、熱交換装置5で
の昇温に必要なエネルギーを節減し、ランニングコスト
を低く押さえることができる。
FIG. 1 shows a water supply pipe 10 between a raw water receiving tank 1 and a heat exchange device 5 in which a waste water A before passing through the heat exchange device 5 and a sterilized waste water E after maintaining the above sterilization temperature. Preheating devices 15 and 16 that increase the temperature by heat exchange are provided. The sterilized wastewater E after passing through the holding tube 7 is at a high temperature, and it is difficult to perform BOD treatment or the like as it is, and it is necessary to avoid discharging at a high temperature. In the illustrated example, the high-temperature wastewater E
Since the temperature of the wastewater A at a relatively low temperature is raised, the energy required for raising the temperature in the heat exchange device 5 can be reduced, and the running cost can be kept low.

【0022】図示例では2段の予熱装置15、16を設け、
ホールディングチューブ7を通過後の排水E、F、Hの
放水管14と送水管10を予熱装置15、16に接続している。
送水管10経由で送られる原水受槽1の排水Aは予熱装置
15で昇温され、その出口昇温排水Bが予熱装置16で昇温
された後、昇温排水Cとして熱交換装置5へ送られる。
他方、放水管14経由で放水される排水Eは、予熱装置16
で排水Bとの熱交換により中温排水Fとなり、更に予熱
装置15で排水Aとの熱交換により所定排出温度まで降温
した後、系外へ処理水Hとして放流される。
In the illustrated example, two stages of preheating devices 15 and 16 are provided,
The water discharge pipes 14 and the water supply pipes 10 of the drainage waters E, F and H after passing through the holding tube 7 are connected to preheating devices 15 and 16.
Wastewater A of the raw water receiving tank 1 sent via the water pipe 10 is a preheating device
The temperature is raised at 15 and the outlet heated wastewater B is heated at the preheating device 16 and then sent to the heat exchanger 5 as the heated wastewater C.
On the other hand, the wastewater E discharged through the discharge pipe 14 is supplied to the preheating device 16.
In the preheating device 15, the temperature is reduced to a predetermined discharge temperature by heat exchange with the wastewater A, and then discharged as treated water H outside the system.

【0023】160m3の原排水Aを10時間で殺菌処理する
と仮定して図1に示す装置を試設計した。原排水Aの受
け入れ温度を20℃、熱交換装置5で135℃、90秒保持す
るとした場合、予熱装置15、16の伝熱面積を70m2、熱交
換装置5の熱交換器6の伝熱面積を20m2とすると、予熱
排水Bは62℃、予熱排水Cは110℃、高温排水Dは135
℃、中温排水Fは87℃、処理水Hは45℃となる。また、
この場合に昇温のために熱交換装置5で必要なエネルギ
ーは、4KGの蒸気圧力で800kg/時である。
The apparatus shown in FIG. 1 was designed as a trial, assuming that 160 m 3 of the raw waste water A was sterilized in 10 hours. Assuming that the receiving temperature of the raw waste water A is maintained at 20 ° C. and maintained at 135 ° C. for 90 seconds in the heat exchanger 5, the heat transfer area of the preheaters 15 and 16 is 70 m 2 , and the heat transfer of the heat exchanger 6 of the heat exchanger 5 is performed. Assuming that the area is 20 m 2 , preheating wastewater B is 62 ° C, preheating wastewater C is 110 ° C, and high-temperature wastewater D is 135 ° C.
° C, medium temperature wastewater F is 87 ° C, and treated water H is 45 ° C. Also,
In this case, the energy required in the heat exchanger 5 for raising the temperature is 800 kg / hour at a steam pressure of 4 kg.

【0024】また、比較のため、160m3の排水Aをキル
タンク(直接蒸気投入式の高圧蒸気滅菌装置)または単
一の直接熱交換器を用いて135℃、90秒保持の滅菌処理
をする場合は、必要な蒸気量は3,900kg/時となる。単
一の直接熱交換器で滅菌処理する場合は、ホールディン
グチューブ7通過後の排水Eを降温するため、別途に降
温エネルギーを加えるか又は降温する時間とスペースが
必要となる。この試設計から、図1のように予熱装置1
5、16を設けることにより、外部から供給するエネルギ
ーの節減により省エネルギーが図れることを確認でき
た。
For comparison, a case where 160 m 3 of waste water A is sterilized at 135 ° C. for 90 seconds using a kill tank (direct steam injection type high-pressure steam sterilizer) or a single direct heat exchanger is used. Means that the required steam volume is 3,900 kg / h. In the case of performing the sterilization treatment with a single direct heat exchanger, in order to lower the temperature of the wastewater E after passing through the holding tube 7, it is necessary to separately apply a cooling energy or to reduce the time and space for cooling. From this trial design, as shown in Fig. 1,
It was confirmed that energy saving can be achieved by saving energy supplied from outside by providing 5 and 16.

【0025】更に図1では、予熱装置15、16通過後の処
理水Hの放水管14と送水管10との間に弁21、22を介して
管路洗浄ユニット20を接続している。送水管10と熱交換
装置5と予熱装置15、16と放水管14とからなる管路の洗
浄時に、弁21、22の切替により、前記管路と管路洗浄ユ
ニット20とからなる閉流路を形成する。本発明は排水を
所要のpHとすることで蛋白質の沈澱・付着が抑制可能で
あるが、蛋白質以外の水中の無機物等がスケールとして
沈澱・付着する場合も考えられる。この問題解決のた
め、例えば殺菌処理の中断時に、前記管路と管路洗浄ユ
ニット20とからなる閉流路へスケール除去剤その他の洗
浄液を循環させることにより、管路内を洗浄する。
Further, in FIG. 1, a pipe cleaning unit 20 is connected between the water discharge pipe 14 and the water supply pipe 10 of the treated water H after passing through the preheating devices 15 and 16 via valves 21 and 22. At the time of cleaning the pipeline composed of the water pipe 10, the heat exchange device 5, the preheating devices 15, 16, and the water discharge pipe 14, by switching the valves 21, 22, a closed flow path composed of the pipeline and the pipeline cleaning unit 20. To form In the present invention, the precipitation and adhesion of proteins can be suppressed by adjusting the wastewater to a required pH. However, it is also conceivable that inorganic substances in water other than proteins precipitate and adhere as scale. In order to solve this problem, for example, when the sterilization process is interrupted, the inside of the pipe is cleaned by circulating a scale removing agent or other cleaning liquid through a closed flow path including the pipe and the pipe cleaning unit 20.

【0026】この場合、好ましくは送水管10と熱交換装
置5と予熱装置15、16と放水管14とからなる管路をステ
ンレス製とし、洗浄液として硝酸を用いる。硝酸は、ス
ケールを溶解すると共に、ステンレス配管に不動態皮膜
を形成し耐食性を増加することができる。不動態皮膜の
形成により、本発明装置の寿命を長く維持することが期
待できる。ただし、洗浄液は硝酸に限定されず、他の適
当な酸を利用することができる。
In this case, it is preferable that the pipeline composed of the water supply pipe 10, the heat exchange device 5, the preheating devices 15, 16 and the water discharge pipe 14 is made of stainless steel, and nitric acid is used as a cleaning liquid. Nitric acid can dissolve the scale and form a passive film on the stainless steel pipe to increase the corrosion resistance. The formation of the passivation film can be expected to maintain the life of the device of the present invention for a long time. However, the cleaning liquid is not limited to nitric acid, and other suitable acids can be used.

【0027】管路洗浄ユニット20は、前記管路のあらゆ
る部分に十分な量の適切な温度の洗浄液を行き渡らせる
ことができる従来技術のライン洗浄用CIPユニットとす
ることができる。また、熱交換装置5の出口蒸気を管路
洗浄ユニット20へ導いて再利用することにより、ユニッ
ト20以降の全てのライン(配管)及び装置を熱洗浄ない
し熱滅菌(Sterilization-in-place、SIP)することも
可能である。洗浄のみでなく蒸気を用いた簡易滅菌をす
ることにより、装置の開放点検などの頻度を減らし、メ
ンテナンスの容易化を図ることができる。
The line cleaning unit 20 can be a prior art line cleaning CIP unit capable of dispensing a sufficient amount of a suitable temperature of cleaning liquid to any portion of the line. Also, the outlet steam of the heat exchange device 5 is guided to the pipeline cleaning unit 20 for reuse, so that all the lines (piping) and the devices after the unit 20 are thermally cleaned or thermally sterilized (Sterilization-in-place, SIP). ) Is also possible. By performing simple sterilization using steam as well as cleaning, the frequency of open inspection of the apparatus can be reduced, and maintenance can be facilitated.

【0028】図1における熱交換装置5の熱交換器6、
及び予熱装置15、16として使う熱交換器に特に制限はな
いが、例えば図2に示すスパイラル式熱交換器を用いる
ことにより、スケールの付着防止が期待できる。図2に
示すスパイラル式熱交換器30は、2枚の板を中心部32か
ら渦巻き状に巻き上げて2つの流路を形成し、各流路の
一端は中央部32に設けた開口と連通し、各流路の他端は
渦巻部33の最外周部34に設けたポケット35を介して開口
と連通したものである。例えば、一方の流路に蒸気Gを
流入させ、他方の流路のポケット35から昇温排水Cを流
入させて中央部32から高温排水Dとして排出する。スパ
イラル式熱交換器30は、多管式熱交換器に比し、流路が
単一で滑らかである。このため、図3に示すように、熱
交換器30の配管36内にスケール37が付着すると付着箇所
の断面積が小さくなることによって流速が増大し、スケ
ール37を剥離させる自己浄化作用が働く。従ってスパイ
ラル式熱交換器30は、スケールが付着し難く、メンテナ
ンスが容易である。しかも化学洗浄も容易である。更に
好ましくは、ステンレス製のスパイラル式熱交換器を使
用する。
The heat exchanger 6 of the heat exchanger 5 in FIG.
Although there is no particular limitation on the heat exchangers used as the preheating devices 15 and 16, for example, the use of a spiral heat exchanger shown in FIG. 2 can prevent scale adhesion. In the spiral heat exchanger 30 shown in FIG. 2, two plates are spirally wound from a central portion 32 to form two flow paths, and one end of each flow path communicates with an opening provided in the central portion 32. The other end of each flow path communicates with the opening via a pocket 35 provided at the outermost peripheral portion 34 of the spiral part 33. For example, the steam G flows into one flow path, the heated water C flows from the pocket 35 in the other flow path, and is discharged as the high-temperature waste water D from the central part 32. The spiral heat exchanger 30 has a single flow path and is smoother than the multi-tube heat exchanger. For this reason, as shown in FIG. 3, when the scale 37 adheres to the pipe 36 of the heat exchanger 30, the cross-sectional area of the adhered portion becomes smaller, the flow velocity increases, and a self-purifying action of peeling the scale 37 works. Therefore, the scale of the spiral heat exchanger 30 does not easily adhere to the spiral heat exchanger 30, and maintenance is easy. Moreover, chemical cleaning is easy. More preferably, a spiral heat exchanger made of stainless steel is used.

【0029】[0029]

【発明の効果】以上詳細に説明した通り、本発明による
微生物及び/又はウィルス含有排水の殺菌方法及び装置
は、加熱殺菌すべき排水を当該微生物及び/又はウィル
スの構成蛋白質が殺菌による変性後も沈澱しないpHとし
たのち熱交換器に通すので、次の顕著な効果を奏する。
As described above in detail, the method and apparatus for disinfecting wastewater containing microorganisms and / or viruses according to the present invention provide the wastewater to be heat-sterilized even after the constituent proteins of the microorganisms and / or viruses have been denatured by sterilization. Since the mixture is passed through a heat exchanger after having a pH that does not precipitate, the following remarkable effects are exhibited.

【0030】(イ)配管の閉塞を避けつつ、大量の微生
物及び/又はウィルス含有排水を連続的に処理すること
が可能である。 (ロ)連続処理が可能であるため、省スペースかつコン
パクトな装置とすることができる。 (ハ)熱交換装置へ通す前の排水を、殺菌温度に保持後
の殺菌済排水と熱交換することにより、排熱の有効利用
による省エネルギーを図ることができる。 (ニ)例えば蒸気圧力を変えることで任意に殺菌温度
(不活化温度)を変更することが可能であり、将来の未
知の細菌やウィルスを含む排水の殺菌処理にも容易に対
応可能である。 (ホ)加熱処理により滅菌するので、薬液では充分に殺
菌できない細菌・ウィルスも、殺菌温度及び時間の調整
により確実に不活化することが可能である。 (ヘ)薬液による殺菌処理に比し、薬液コストが削減で
きるのでランニングコストを1/10程度に削減でき
る。また大量の薬液を使用しないので、環境を汚染する
おそれが小さい。
(A) It is possible to continuously treat a large amount of wastewater containing microorganisms and / or viruses while avoiding blockage of the piping. (B) Since continuous processing is possible, a space-saving and compact device can be provided. (C) By exchanging the wastewater before passing through the heat exchanger with the sterilized wastewater maintained at the sterilization temperature, energy can be saved by effectively using the exhaust heat. (D) It is possible to arbitrarily change the sterilization temperature (inactivation temperature) by changing the steam pressure, for example, and it is possible to easily cope with the sterilization of wastewater containing unknown bacteria and viruses in the future. (E) Since sterilization is performed by heat treatment, bacteria and viruses that cannot be sufficiently sterilized with a chemical solution can be reliably inactivated by adjusting the sterilization temperature and time. (F) Compared to the sterilization treatment using a chemical solution, the cost of the chemical solution can be reduced, so that the running cost can be reduced to about 1/10. Also, since a large amount of chemical solution is not used, there is little risk of polluting the environment.

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

【図1】は、本発明の一実施例の説明図である。FIG. 1 is an explanatory diagram of one embodiment of the present invention.

【図2】は、スパイラル式熱交換器の説明図である。FIG. 2 is an explanatory diagram of a spiral heat exchanger.

【図3】は、スパイラル式熱交換器のスケール付着箇所
の説明図である。
FIG. 3 is an explanatory diagram of a scale adhering portion of a spiral heat exchanger.

【符号の説明】[Explanation of symbols]

1…原水受槽 3…pH調整装置 5…熱交換装置 6…熱交換器 7…ホールディングチューブ 8…温度センサ 9…圧力センサ 10…送水管 11…輸液ポンプ 12…温度センサ 14…放水管 15…予熱装置 16…予熱装置 20…管路洗浄ユニット 21…弁 22…弁 30…スパイラル式熱交換器 31…カバー 32…中央部 33…渦巻部 34…最外周部 35…ポケット 36…熱交換器内配管 37…スケール A…微生物及び/又はウィルス含有排水 B…昇温排水 C…昇温排水 D…高温排水 E…殺菌済排水 F…中温排水 G…蒸気 H…処理水 DESCRIPTION OF SYMBOLS 1 ... Raw water receiving tank 3 ... pH adjuster 5 ... Heat exchanger 6 ... Heat exchanger 7 ... Holding tube 8 ... Temperature sensor 9 ... Pressure sensor 10 ... Water supply pipe 11 ... Infusion pump 12 ... Temperature sensor 14 ... Water discharge pipe 15 ... Preheating Device 16… Preheating device 20… Pipe washing unit 21… Valve 22… Valve 30… Spiral heat exchanger 31… Cover 32… Central part 33… Swirl part 34… Outermost part 35… Pocket 36… Piping in heat exchanger 37 ... Scale A ... Wastewater containing microorganisms and / or viruses B ... Heated wastewater C ... Heated wastewater D ... High temperature wastewater E ... Sterilized wastewater F ... Medium temperature wastewater G ... Steam H ... Treated water

Claims (12)

【特許請求の範囲】[Claims] 【請求項1】加熱殺菌すべき微生物及び/又はウィルス
含有排水を当該微生物及び/又はウィルスの構成蛋白質
が殺菌による変性後も沈澱しないpHとしたのち熱交換器
に通し、所要殺菌温度に所要殺菌時間保持してなる微生
物及び/又はウィルス含有排水の殺菌方法。
A wastewater containing microorganisms and / or viruses to be heat-sterilized is adjusted to a pH at which the constituent proteins of the microorganisms and / or viruses do not precipitate even after denaturation by sterilization, and then passed through a heat exchanger to obtain a required sterilization temperature. A method for disinfecting wastewater containing microorganisms and / or viruses which is maintained for a time.
【請求項2】請求項1の殺菌方法において、前記排水
を、前記微生物及び/又はウィルスの構成蛋白質が殺菌
による変性後も溶解するアルカリ濃度としてなる微生物
及び/又はウィルス含有排水の殺菌方法。
2. The method for sterilizing microorganism- and / or virus-containing wastewater according to claim 1, wherein the wastewater has an alkali concentration at which the constituent proteins of the microorganism and / or virus are dissolved even after denaturation by sterilization.
【請求項3】請求項2の殺菌方法において、前記微生物
及び/又はウィルス含有排水を水酸化ナトリウムの添加
により前記アルカリ濃度としてなる微生物及び/又はウ
ィルス含有排水の殺菌方法。
3. The method for sterilizing microorganism- and / or virus-containing wastewater according to claim 2, wherein said microorganism- and / or virus-containing wastewater is adjusted to said alkali concentration by adding sodium hydroxide.
【請求項4】請求項1から3の何れかの殺菌方法におい
て、前記排水が前記構成蛋白質以外の蛋白質を含有する
場合に、前記pH又はアルカリ濃度を、当該構成蛋白質以
外の蛋白質も変成後に沈澱しないpH又はアルカリ濃度と
してなる微生物及び/又はウィルス含有排水の殺菌方
法。
4. The sterilization method according to claim 1, wherein when the wastewater contains proteins other than the constituent proteins, the pH or alkali concentration is settled after denaturing the proteins other than the constituent proteins. A method for disinfecting wastewater containing microorganisms and / or viruses that does not have a pH or alkali concentration.
【請求項5】請求項1から4の何れかの殺菌方法におい
て、前記熱交換器へ通す前の微生物及び/又はウィルス
含有排水を、前記殺菌温度に保持した後の殺菌済排水と
の熱交換により昇温してなる微生物及び/又はウィルス
含有排水の殺菌方法。
5. The method according to claim 1, wherein the wastewater containing microorganisms and / or virus before passing through the heat exchanger is exchanged with sterilized wastewater after maintaining the sterilization temperature. A method for disinfecting wastewater containing microorganisms and / or viruses, the temperature of which is increased by the method described above.
【請求項6】請求項1から5の何れかの殺菌方法におい
て、殺菌後の微生物及び/又はウィルスの生存割合が殺
菌前の100万分の1(10-6)以下となる如く前記殺菌温
度及び殺菌時間を調節してなる微生物及び/又はウィル
ス含有排水の殺菌方法。
6. The sterilization method according to claim 1, wherein the survival rate of microorganisms and / or viruses after sterilization is not more than 1 / 100,000 (10 −6 ) before sterilization. A method for disinfecting wastewater containing microorganisms and / or viruses by adjusting the disinfection time.
【請求項7】微生物及び/又はウィルス含有排水を貯め
る原水受槽、前記原水受槽中の排水のpHを調整するpH調
整装置、前記排水を所要殺菌温度に所要殺菌時間保持す
る熱交換装置、及び前記原水受槽中の排水を前記熱交換
装置へ送る送水管を備え、前記pH調整装置により前記微
生物及び/又はウィルスの構成蛋白質が殺菌による変性
後も沈澱しないpHとした後の排水を前記送水管により前
記原水受槽から前記熱交換装置へ送ってなる微生物及び
/又はウィルス含有排水の殺菌装置。
7. A raw water receiving tank for storing wastewater containing microorganisms and / or viruses, a pH adjusting device for adjusting the pH of the wastewater in the raw water receiving tank, a heat exchange device for keeping the wastewater at a required sterilizing temperature for a required sterilizing time, and A water pipe for sending the wastewater in the raw water receiving tank to the heat exchange device, and the wastewater after setting the pH so that the constituent proteins of the microorganisms and / or viruses do not precipitate even after denaturation by sterilization by the pH adjusting device; A sterilizer for microorganism- and / or virus-containing wastewater sent from the raw water receiving tank to the heat exchanger.
【請求項8】請求項7の殺菌装置において、前記pH調整
装置を前記原水受槽中にアルカリ剤を注入するアルカリ
剤注入装置とし、当該注入装置により前記原水受槽中の
排水を前記微生物及び/又はウィルスの構成蛋白質が殺
菌による変性後も溶解するアルカリ濃度としてなる微生
物及び/又はウィルス含有排水の殺菌装置。
8. The sterilizing apparatus according to claim 7, wherein the pH adjusting device is an alkali agent injecting device for injecting an alkaline agent into the raw water receiving tank, and the wastewater in the raw water receiving tank is discharged by the injection device with the microorganism and / or the microorganism. An apparatus for disinfecting wastewater containing microorganisms and / or viruses having an alkali concentration at which a virus constituent protein is dissolved even after denaturation by sterilization.
【請求項9】請求項7又は8の殺菌装置において、前記
送水管に、前記熱交換装置へ通す前の微生物及び/又は
ウィルス含有排水を前記殺菌温度に保持した後の殺菌済
排水との熱交換により昇温する予熱装置を設けてなる微
生物及び/又はウィルス含有排水の殺菌装置。
9. The sterilizing apparatus according to claim 7, wherein the wastewater containing microorganisms and / or virus before passing through the heat exchanger is maintained at the sterilizing temperature in the water supply pipe. A sterilizing device for wastewater containing microorganisms and / or viruses, which is provided with a preheating device that raises the temperature by replacement.
【請求項10】請求項7から9の何れかの殺菌装置にお
いて、前記予熱装置通過後の殺菌済排水を排出する放水
管と前記送水管との間に弁を介して接続した管路洗浄ユ
ニットを備え、洗浄時に前記弁の切替により前記送水管
と熱交換装置と予熱装置と放水管と前記管路洗浄ユニッ
トとからなる閉流路を形成してなる微生物及び/又はウ
ィルス含有排水の殺菌装置。
10. The line cleaning unit according to claim 7, wherein a drainage pipe for discharging sterilized wastewater after passing through the preheating device and the water supply pipe are connected via a valve. An apparatus for disinfecting microorganism- and / or virus-containing wastewater which forms a closed flow path composed of the water supply pipe, the heat exchange device, the preheating device, the water discharge pipe, and the pipeline cleaning unit by switching the valve during cleaning. .
【請求項11】請求項10の殺菌装置において、前記送
水管と熱交換装置と予熱装置と放水管の管路をステンレ
ス製とし、前記管路洗浄ユニットにより前記閉流路へ酸
を供給してなる微生物及び/又はウィルス含有排水の殺
菌装置。
11. The sterilizing apparatus according to claim 10, wherein said water supply pipe, heat exchanger, preheater and water discharge pipe are made of stainless steel, and said pipe washing unit supplies acid to said closed flow path. For sterilizing wastewater containing microorganisms and / or viruses.
【請求項12】請求項7から11の何れかの殺菌装置に
おいて、前記熱交換装置及び/又は前記予熱装置をスパ
イラル式熱交換器としてなる微生物及び/又はウィルス
含有排水の殺菌装置。
12. The sterilizer for microorganism- and / or virus-containing wastewater according to claim 7, wherein the heat exchanger and / or the preheater is a spiral heat exchanger.
JP2000165344A 2000-06-02 2000-06-02 Method and apparatus for sterilizing wastewater containing microorganisms and / or viruses Expired - Lifetime JP3297419B2 (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004008174A (en) * 2002-06-11 2004-01-15 Asahi Breweries Ltd Manufacturing facilities and method for utilizing waste heat of the same
WO2009125702A1 (en) * 2008-04-09 2009-10-15 国立大学法人長崎大学 Heat sterilizing water purifier
JP5110493B1 (en) * 2011-10-11 2012-12-26 鹿島建設株式会社 Wastewater inactivation method and system
JP2014094338A (en) * 2012-11-08 2014-05-22 Miura Co Ltd Ballast water treatment apparatus
JP6761149B1 (en) * 2020-01-10 2020-09-23 鹿島建設株式会社 Decontamination system for microbial and / or virus-containing waste liquids

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004008174A (en) * 2002-06-11 2004-01-15 Asahi Breweries Ltd Manufacturing facilities and method for utilizing waste heat of the same
WO2009125702A1 (en) * 2008-04-09 2009-10-15 国立大学法人長崎大学 Heat sterilizing water purifier
JP5110493B1 (en) * 2011-10-11 2012-12-26 鹿島建設株式会社 Wastewater inactivation method and system
WO2013054390A1 (en) * 2011-10-11 2013-04-18 鹿島建設株式会社 Wastewater inactivation method and system
JP2014094338A (en) * 2012-11-08 2014-05-22 Miura Co Ltd Ballast water treatment apparatus
JP6761149B1 (en) * 2020-01-10 2020-09-23 鹿島建設株式会社 Decontamination system for microbial and / or virus-containing waste liquids
WO2021140656A1 (en) * 2020-01-10 2021-07-15 鹿島建設株式会社 Decontamination system for microbe- and/or virus-containing waste fluid

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