WO2003042110A1 - Method of reusing food factory process water - Google Patents

Method of reusing food factory process water Download PDF

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Publication number
WO2003042110A1
WO2003042110A1 PCT/JP2002/010489 JP0210489W WO03042110A1 WO 2003042110 A1 WO2003042110 A1 WO 2003042110A1 JP 0210489 W JP0210489 W JP 0210489W WO 03042110 A1 WO03042110 A1 WO 03042110A1
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WIPO (PCT)
Prior art keywords
water
treatment
food factory
process water
food
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PCT/JP2002/010489
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French (fr)
Japanese (ja)
Inventor
Masahiro Kawabata
Akifumi Obu
Original Assignee
Organo Corporation
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Publication of WO2003042110A1 publication Critical patent/WO2003042110A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/002Grey water, e.g. from clothes washers, showers or dishwashers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/32Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Definitions

  • the present invention relates to a method for reusing discharge process water discharged from a manufacturing process of a food-related factory.
  • the process water used in the manufacturing process of food-related factories was all tap water ( ⁇ water), industrial water, or water with some treatment. This is because process water used once in the manufacturing process is considered to be wastewater, and recycling this wastewater back to the manufacturing process was not good for sanitation, even though there was no technical problem. is there.
  • the discharge water from the manufacturing process in conventional food-related factories is generally discharged to sewage or drainage treatment and discharged to rivers and other rivers.
  • FIG. 3 is a flowchart showing an example of a bottle washing process in a beverage manufacturing factory.
  • tap water 31 was used as the process water
  • the first pre-cleaning process 32, the second pre-cleaning process 33, the warm water cleaning process 34, and the finish cleaning process 35 were performed. It becomes.
  • the wastewater 36 to 39 discharged from each washing process 32 to 35 is discharged to sewage 40.
  • the demand for water has become tighter due to the increase in water usage in each industry and water consumption caused by climate change, and the demands of local governments and others for factories and others to reduce water usage have increased.
  • water charges and sewerage charges when draining wastewater from factories are increasing, and increasing costs at factories is becoming a problem.
  • the present invention is intended to safely collect and reuse discharged process water in food-related factories, The aim is to reduce the amount of used.
  • the present inventors have conducted intensive studies, separated the water system discharged from the manufacturing process water, collected the water while determining its origin, that is, before mixing with the discharged water from other systems, and collecting the water.
  • the present inventors have found that the above-mentioned problems can be solved by selecting system water containing as little impurities as possible as the water to be recovered and performing the recovery treatment, and have completed the present invention.
  • low-contamination discharge process water of discharge process water discharged from a manufacturing process is collected and sterilized, and the sterilized water is reused as process water. It is characterized by doing.
  • the low-contamination discharge process water is a discharge process water of TOC1Omg / 1 or less.
  • the sterilization treatment is a membrane treatment.
  • the sterilization treatment is a membrane treatment and a sterilization treatment. Further, it is preferable that the sterilization treatment is an oxidizing agent injection method.
  • the film treatment is an MF treatment.
  • FIG. 1 is a flowchart showing one embodiment of the method of the present invention.
  • FIG. 2 is a flowchart showing one embodiment of the sterilization process of the method of the present invention.
  • Figure 3 is a flow chart of the process water used in a conventional food-related factory.
  • the production process in a food factory which is the object of the present invention, is not particularly limited as long as it is a production process using process water.
  • a container production process in a beverage production plant a vegetable production process in a food production plant, etc.
  • Examples include the washing process of raw materials such as fruits, and the washing process of equipment such as piping and blending tanks.
  • the present invention is characterized by recovering relatively low-contamination water from the discharge process water discharged from the manufacturing process of a food factory, and reusing it in another process.
  • Low-contamination water is used as the discharge process water for yield collection. Is less than 10 mg / l, preferably 5 mg / l or less.
  • discharge process water with T ⁇ C exceeding 1 O mg / l is not preferable because microorganisms can easily propagate.
  • the sterilization treatment may be performed to such an extent that it can be used as process water in a process that does not require much cleanliness (a process other than the finish washing process). For example, the sterilization treatment may be performed at a cleanliness level of tap water.
  • the collected low-contamination discharge process water may be sterilized by a known method in food production.
  • the sterilization treatment may be performed by, for example, a combination of a membrane treatment, a membrane treatment, and a sterilization treatment.
  • the membrane treatment in the present invention is not particularly limited as long as it is an apertured membrane capable of removing bacteria.
  • MF microfiltration
  • UF ultrafiltration
  • R 0 reverse osmosis
  • the MF membrane has the largest aperture but has a high water flow rate, so the equipment can be reduced in size, so that the processing cost can be reduced.
  • the sterilization treatment in the present invention is not particularly limited, and examples thereof include a UV (ultraviolet) sterilization method, a hot water sterilization method, and an oxidizing agent sterilizing method using an oxidizing agent.
  • a UV (ultraviolet) sterilization method for example, sodium hypochlorite, ozone, hydrogen peroxide and the like can be mentioned.
  • the oxidizing agent sterilizing method using an oxidizing agent is preferable from the viewpoint of overall health and safety because the effect is maintained as long as the oxidizing agent remains.
  • the bottle to be washed is washed using water 1 as the process water.
  • the wastewater 10 from this washing step 5 is treated in the wastewater recovery equipment 11, and the treated water, collected water 12, is sent to the first preliminary washing step 2, the second preliminary washing step 3, and the hot water washing step 4. Supplied and used here as process water.
  • the drainage water 6, 7, 8 from the first pre-cleaning step 2, the second pre-cleaning step 3, and the hot water cleaning step 4 is discharged 9 into the sewage.
  • illustration is omitted, in the initial stage of the first pre-cleaning step 2, the second pre-cleaning step 3, and the hot water cleaning step 4, a cleaning operation is performed using hot water.
  • water 1 is used.
  • the wastewater 10 discharged from the finish cleaning process is low-pollutant wastewater.
  • the low-contamination wastewater 10 flows into the wastewater recovery facility 11 and is sterilized by membrane treatment or membrane treatment + sterilization treatment.
  • the recovered water sterilized by the wastewater recovery equipment 1 1 is reused as process water for the first pre-cleaning step 2, the second pre-cleaning step 3 and the hot water cleaning step 4, which do not require much cleanliness.
  • the wastewater 6 to 8 discharged from the first pre-cleaning step 2, the second pre-cleaning step 3 and the hot water cleaning step 4 are discharged into sewage 9.
  • FIG. 1 One embodiment of the wastewater recovery equipment 11 for sterilizing the water in the discharge process is shown in the flow diagram of FIG.
  • the discharge process water to be recovered is first stored in the recovered raw water tank 13.
  • the recovered raw water in the recovered raw water tank 13 is supplied to the heat exchanger 16 by the recovered raw water pump 14, and the recovered raw water is supplied to the recovered raw water from the sodium hypochlorite storage tank 15 at the previous stage.
  • One dose is injected. Therefore, the recovered raw water into which the sodium hypochlorite has been injected is supplied to the heat exchanger 16.
  • the recovered raw water whose temperature has been adjusted to the heat exchanger 16 is sent to the MF membrane module 18.
  • the water in the constant temperature water tank 17 is circulated to the heat exchanger 16 for adjusting the temperature of the recovered raw water.
  • heated steam can be blown into this circulation line to sterilize the system with hot water.
  • sodium hypochlorite functions as a disinfectant, and disinfects the recovered raw water.
  • the treated water filtered by the MF membrane module 18 is temporarily stored in the treated water tank 19, and the treated water in the treated water tank 19 is manufactured via the treated water pump 20. Sent to the process and reused.
  • the example shown in Fig. 2 is an example in which the injection point of sodium hypochlorite is placed first (before the heat exchanger 16). It is possible to inject the fungicide at a later stage, but the advantage of placing the injection point first is that the entire recovery system can be sterilized. On the other hand, the disadvantages are that corrosion-resistant materials must be used for the entire recovery system, and a large amount of injection is required in order to maintain the sterilization effect until the final point, compared to the latter injection. Is necessary.
  • the purpose of the heat exchanger 16 is to regulate the temperature of the drainage process water and to perform hot water sterilization that may be performed irregularly.
  • an external pressure type hollow fiber type is used as the MF membrane module 18.
  • the MF membrane module 18 For this reason, when performing regular cleaning, stop the inflow of raw water and backwash by introducing high-pressure air into the hollow fibers through the air storage tank 22 with the compressor 21 to remove the water from the membrane surface. The trapped particulate components are removed and taken out of the system as washing wastewater.
  • MF membranes such as a flat membrane type and a tubular type, but basically any type of membrane may be used to achieve the object of the present invention.
  • the discharge water in the finish cleaning process was sterilized and reused in the first pre-cleaning process, the second pre-cleaning process, and the hot water cleaning process.
  • a wastewater recovery facility 11 as shown in Fig. 2 was used, and an example in which sodium hypochlorite was added to perform MF membrane treatment, and an example in which only MF membrane treatment was performed.
  • the amount of sodium hypochlorite added was 5 mg / l.
  • the MF film used had a pore size of 0.2 ⁇ m.

Abstract

In a food-related manufacturing factory, of the discharge process water discharged from the manufacturing process, the low-polluted discharge process water is collected. The collected discharge process water is sterilized by film-treatment or disinfection, and the sterilized water is reused as process water. The discharge process water in a food-related factory can be safely collected and reused, to reduce the process water consumption.

Description

明 細 書  Specification
食品工場工程水再利用方法  Food factory process water reuse method
[技術分野] [Technical field]
本発明は、 食品関連工場の製造工程から排出される排出工程水を再利用する方 法に関する。  The present invention relates to a method for reusing discharge process water discharged from a manufacturing process of a food-related factory.
[背景技術] [Background technology]
従来から、 食品関連工場において、 野菜等の原料の洗浄工程や、 洗瓶工程など の製造工程で多量の工程水が用いられるが、 排出された工程水は再利用されるこ とはなかった。すなわち、従来は食品関連工場の製造工程で用いられる工程水は、 すべて水道水 (巿水) や工業用水またはそれらに何らかの処理を加えた水であつ た。 なぜなら製造工程で一度使用した工程水は排水と考えられ、 この排水を再利 用して製造工程に戻すことは、 技術的に問題がなくても、 衛生面での印象が悪か つたためである。  Conventionally, in food-related factories, a large amount of process water has been used in the washing process of raw materials such as vegetables and the manufacturing process such as the washing bottle process, but the discharged process water has not been reused. In other words, conventionally, the process water used in the manufacturing process of food-related factories was all tap water (巿 water), industrial water, or water with some treatment. This is because process water used once in the manufacturing process is considered to be wastewater, and recycling this wastewater back to the manufacturing process was not good for sanitation, even though there was no technical problem. is there.
従って、 従来の食品関連工場における、 製造工程から排出される排出工程水は 図 3のように、 下水放流または排水処理を行つて全量河川等に放流するのが一般 的であった。  Therefore, as shown in Fig. 3, the discharge water from the manufacturing process in conventional food-related factories is generally discharged to sewage or drainage treatment and discharged to rivers and other rivers.
図 3は、 飲料製造工場の洗瓶工程の一例を示すフロー図である。 図 3に示した ように、 洗瓶工程は、 巿水 3 1を工程水とし、 第 1予備洗浄工程 3 2、 第 2予備 洗浄工程 3 3、 温水洗浄工程 3 4、 仕上洗浄工程 3 5からなるものである。 各洗 浄工程 3 2〜3 5から排出される排水 3 6〜3 9は、 下水放流 4 0される。 近年、 各産業での水使用量の増加や気候変動に伴う渴水が原因となり、 水需要 が逼迫し、 工場等に対し、 水使用削減を求める自治体等の要求が高まっている。 また、 水道料金や、 工場から排水を流す場合の下水道使用料金が高まってきて おり、 工場におけるコスト増が問題となっている。  FIG. 3 is a flowchart showing an example of a bottle washing process in a beverage manufacturing factory. As shown in Fig. 3, in the bottle washing process, tap water 31 was used as the process water, and the first pre-cleaning process 32, the second pre-cleaning process 33, the warm water cleaning process 34, and the finish cleaning process 35 were performed. It becomes. The wastewater 36 to 39 discharged from each washing process 32 to 35 is discharged to sewage 40. In recent years, the demand for water has become tighter due to the increase in water usage in each industry and water consumption caused by climate change, and the demands of local governments and others for factories and others to reduce water usage have increased. In addition, water charges and sewerage charges when draining wastewater from factories are increasing, and increasing costs at factories is becoming a problem.
[発明の開示] [Disclosure of the Invention]
本発明は、 食品関連工場における、 排出工程水を安全に回収再利用し、 工程水 の使用量を削減することを目的とする。 The present invention is intended to safely collect and reuse discharged process water in food-related factories, The aim is to reduce the amount of used.
本発明者らは鋭意研究を重ね、 製造工程水から排出される水系統を分離しその 由来が明らかなうちに、 すなわち他の系統の排出水と混じり合う以前に回収対象 を決めて集水し、 回収対象水はなるべく不純物の混入の少ない系統水を選びだし て回収処理をすることにより、 上記課題を解決できることを見出し本発明を完成 するに至った。  The present inventors have conducted intensive studies, separated the water system discharged from the manufacturing process water, collected the water while determining its origin, that is, before mixing with the discharged water from other systems, and collecting the water. However, the present inventors have found that the above-mentioned problems can be solved by selecting system water containing as little impurities as possible as the water to be recovered and performing the recovery treatment, and have completed the present invention.
まず、 本発明は、 食品関連製造工場において、 製造工程から排出される排出ェ 程水のうち低汚染の排出工程水を回収して滅菌処理し、 該滅菌処理水を工程水と して再利用することを特徴とする。  First, in the present invention, in a food-related manufacturing plant, low-contamination discharge process water of discharge process water discharged from a manufacturing process is collected and sterilized, and the sterilized water is reused as process water. It is characterized by doing.
また、 前記低汚染の排出工程水が、 T O C 1 O m g/ 1以下の排出工程水であ ることが好適である。  Further, it is preferable that the low-contamination discharge process water is a discharge process water of TOC1Omg / 1 or less.
また、 前記滅菌処理が、 膜処理であることが好適である。  Further, it is preferable that the sterilization treatment is a membrane treatment.
また、 前記滅菌処理が、 膜処理および殺菌処理であることが好適である。 また、 前記殺菌処理が酸化剤注入法であることが好適である。  Further, it is preferable that the sterilization treatment is a membrane treatment and a sterilization treatment. Further, it is preferable that the sterilization treatment is an oxidizing agent injection method.
また、 前記膜処理が M F処理であることが好適である。  Further, it is preferable that the film treatment is an MF treatment.
[図面の簡単な説明] [Brief description of drawings]
図 1は、 本発明方法の一実施形態を示すフロー図である。  FIG. 1 is a flowchart showing one embodiment of the method of the present invention.
図 2は、 本発明方法の、 滅菌処理の一実施形態を示すフロー図である。  FIG. 2 is a flowchart showing one embodiment of the sterilization process of the method of the present invention.
図 3は、 従来の食品関連工場の工程水の処理フロ一図である。  Figure 3 is a flow chart of the process water used in a conventional food-related factory.
[発明を実施するための最良の形態] [Best Mode for Carrying Out the Invention]
本発明の対象となる、 食品工場における製造工程とは、 工程水を使用する製造 工程であれば特に限定されないが、 例えば飲料製造工場における、 容器の洗浄ェ 程や、 食品製造工場における、 野菜や果物等の原料の洗浄工程、 配管や調合タン クなどの設備洗浄工程などを挙げることができる。  The production process in a food factory, which is the object of the present invention, is not particularly limited as long as it is a production process using process water.For example, a container production process in a beverage production plant, a vegetable production process in a food production plant, etc. Examples include the washing process of raw materials such as fruits, and the washing process of equipment such as piping and blending tanks.
本発明は、 食品工場の製造工程から排出される排出工程水のうち比較的低汚染 のものを回収処理し、 再び他の工程で再利用することを特徴とするものである。 向収処理する排出工程水としては低汚染のものを用いるが、 具体的には T 0 C が l O m gZ l以下、 好ましくは 5 m g/ l以下のものである。 なお、 T〇Cが 1 O m g/ lを超える排出工程水では、微生物が繁殖しやすいため好ましくない。 滅菌処理は、清浄度をあまり求められない工程(仕上げ洗浄工程を以外の工程) の工程水として利用できる程度に行えばよく、 例えば水道水程度の清浄度で滅菌 処理すればよい。 The present invention is characterized by recovering relatively low-contamination water from the discharge process water discharged from the manufacturing process of a food factory, and reusing it in another process. Low-contamination water is used as the discharge process water for yield collection. Is less than 10 mg / l, preferably 5 mg / l or less. In addition, discharge process water with T〇C exceeding 1 O mg / l is not preferable because microorganisms can easily propagate. The sterilization treatment may be performed to such an extent that it can be used as process water in a process that does not require much cleanliness (a process other than the finish washing process). For example, the sterilization treatment may be performed at a cleanliness level of tap water.
回収された低汚染の排出工程水は、 食品製造において公知の方法により滅菌処 理すればよい。 滅菌処理としては、 例えば膜処理、 膜処理および殺菌処理の組み 合わせにより行えばよい。  The collected low-contamination discharge process water may be sterilized by a known method in food production. The sterilization treatment may be performed by, for example, a combination of a membrane treatment, a membrane treatment, and a sterilization treatment.
本発明における膜処理としては、 細菌を除去できる目開きの膜であれば特に限 定されないが、 例えば、 M F (精密ろ過) 膜処理、 U F (限外ろ過) 膜処理また は R 0 (逆浸透) 膜処理等を挙げることができる。  The membrane treatment in the present invention is not particularly limited as long as it is an apertured membrane capable of removing bacteria. For example, MF (microfiltration) membrane treatment, UF (ultrafiltration) membrane treatment or R 0 (reverse osmosis) And the like.
これらの膜のうち、 M F膜が最も目開きが大きいが通水速度が大きく取れるた め装置を小さくすることが出来るので、 処理コストを低減できる。  Of these membranes, the MF membrane has the largest aperture but has a high water flow rate, so the equipment can be reduced in size, so that the processing cost can be reduced.
本発明における殺菌処理は特に限定されないが、例えば U V (紫外線)殺菌法、 熱水殺菌法、 酸化剤による酸化剤殺菌法が挙げられる。 酸化殺菌法における酸化 剤としては、 例えば次亜塩素酸ソーダ、 オゾン、 過酸化水素等を挙げることがで きる。  The sterilization treatment in the present invention is not particularly limited, and examples thereof include a UV (ultraviolet) sterilization method, a hot water sterilization method, and an oxidizing agent sterilizing method using an oxidizing agent. As the oxidizing agent in the oxidizing sterilization method, for example, sodium hypochlorite, ozone, hydrogen peroxide and the like can be mentioned.
これらの殺菌法のうち、 酸化剤を使った酸化剤殺菌法が、 酸化剤が残留する限 りその効果が持続するため総合的な安全衛生の見地から好ましい。  Of these sterilizing methods, the oxidizing agent sterilizing method using an oxidizing agent is preferable from the viewpoint of overall health and safety because the effect is maintained as long as the oxidizing agent remains.
膜処理と殺菌処理を組み合わせることにより、 万一膜処理のトラブルで細菌類 が通過してきた場合でも、 殺菌処理を組み合わせることにより、 処理水の安全を 保つことができる。  By combining membrane treatment and sterilization treatment, the safety of treated water can be maintained by combining sterilization treatment even if bacteria pass through due to trouble in membrane treatment.
本発明の一実施形態を、 図 1のフロー図に示す。  One embodiment of the present invention is shown in the flowchart of FIG.
図 1に示したように、 仕上洗浄工程 (洗瓶工程) 5は、 巿水 1を工程水として 使用し、 洗浄対象である瓶の洗浄が行われる。 この洗浄工程 5の排水 1 0は、 排 水回収設備 1 1において処理され、 処理水である回収水 1 2が、 第 1予備洗浄ェ 程 2、 第 2予備洗浄工程 3、 温水洗浄工程 4に供給され、 ここで工程水として使 用される。 そして、 第 1予備洗浄工程 2、 第 2予備洗浄工程 3、 温水洗浄工程 4 からの排水 6、 7、 8は、 下水放流 9される。 なお、 図示は省略したが、 第 1予備洗浄工程 2、 第 2予備洗浄工程 3および温 水洗浄工程 4の初期の段階では、 巿水を用いて洗浄操作を行う。 As shown in Fig. 1, in the finish washing step (bottle washing step) 5, the bottle to be washed is washed using water 1 as the process water. The wastewater 10 from this washing step 5 is treated in the wastewater recovery equipment 11, and the treated water, collected water 12, is sent to the first preliminary washing step 2, the second preliminary washing step 3, and the hot water washing step 4. Supplied and used here as process water. Then, the drainage water 6, 7, 8 from the first pre-cleaning step 2, the second pre-cleaning step 3, and the hot water cleaning step 4 is discharged 9 into the sewage. Although illustration is omitted, in the initial stage of the first pre-cleaning step 2, the second pre-cleaning step 3, and the hot water cleaning step 4, a cleaning operation is performed using hot water.
仕上洗浄工程 5は、巿水 1を用いる。仕上洗浄工程から排出された排水 1 0は、 低汚染の排水である。 低汚染の排水 1 0は、 排水回収設備 1 1に流入し、 膜処理 または膜処理 +殺菌処理により、 滅菌処理される。 排水回収設備 1 1により滅菌 処理された回収水は、 清浄度のあまり要求されない第 1予備洗浄工程 2、 第 2予 備洗浄工程 3および温水洗浄工程 4の工程水として再利用する。 第 1予備洗浄ェ 程 2、 第 2予備洗浄工程 3および温水洗浄工程 4から排出された排水 6〜 8は、 下水放流 9される。  In the finish washing step 5, water 1 is used. The wastewater 10 discharged from the finish cleaning process is low-pollutant wastewater. The low-contamination wastewater 10 flows into the wastewater recovery facility 11 and is sterilized by membrane treatment or membrane treatment + sterilization treatment. The recovered water sterilized by the wastewater recovery equipment 1 1 is reused as process water for the first pre-cleaning step 2, the second pre-cleaning step 3 and the hot water cleaning step 4, which do not require much cleanliness. The wastewater 6 to 8 discharged from the first pre-cleaning step 2, the second pre-cleaning step 3 and the hot water cleaning step 4 are discharged into sewage 9.
排出工程水を滅菌処理するための排水回収設備 1 1の一実施形態を、 図 2のフ ロー図に示す。  One embodiment of the wastewater recovery equipment 11 for sterilizing the water in the discharge process is shown in the flow diagram of FIG.
回収対象となる排出工程水は、 まず回収原水タンク 1 3に貯留される。 回収原 水タンク 1 3内の回収原水は、 回収原水ポンプ 1 4により熱交換器 1 6に供給さ れるが、 その前段で回収原水には次亜塩素酸ソーダ貯槽 1 5より次亜塩素酸ソ一 ダが注入される。 従って、 次亜塩素酸ソ一ダが注入された回収原水が熱交換器 1 6に供給される。 熱交換器 1 6に温度調整された回収原水は、 M F膜モジュール 1 8に送られる。  The discharge process water to be recovered is first stored in the recovered raw water tank 13. The recovered raw water in the recovered raw water tank 13 is supplied to the heat exchanger 16 by the recovered raw water pump 14, and the recovered raw water is supplied to the recovered raw water from the sodium hypochlorite storage tank 15 at the previous stage. One dose is injected. Therefore, the recovered raw water into which the sodium hypochlorite has been injected is supplied to the heat exchanger 16. The recovered raw water whose temperature has been adjusted to the heat exchanger 16 is sent to the MF membrane module 18.
なお、 恒温水タンク 1 7の水は、 回収原水の温度調整のため熱交換器 1 6に循 環される。 なお、 非定常時にはこの循環ラインに加熱蒸気を吹き込み、 系内の熱 水殺菌を行うことができる。  The water in the constant temperature water tank 17 is circulated to the heat exchanger 16 for adjusting the temperature of the recovered raw water. In an unsteady state, heated steam can be blown into this circulation line to sterilize the system with hot water.
ここで、 次亜塩素酸ソーダは殺菌剤として機能し、 回収原水の殺菌処理が行わ れる。 M F膜モジュール 1 8により濾過処理された回収処理水は回収処理水タン ク 1 9に一旦貯留され、 回収処理水タンク 1 9内の回収処理水が回収処理水ボン プ 2 0を介して、 製造工程へ送られ、 再利用される。  Here, sodium hypochlorite functions as a disinfectant, and disinfects the recovered raw water. The treated water filtered by the MF membrane module 18 is temporarily stored in the treated water tank 19, and the treated water in the treated water tank 19 is manufactured via the treated water pump 20. Sent to the process and reused.
図 2に示した例は、 次亜塩素酸ソーダの注入点を最初 (熱交換器 1 6の前段) に置いた例である。 殺菌剤を後段で注入することも可能であるが、 注入点を最初 に置いた場合の利点は回収システム全体の殺菌が可能であることである。 一方、 その欠点は回収システム全体に耐腐食性の材質を使わなければいけないことと、 最終ボイントまで殺菌効果を持続させるためには後段注入に比べて多量の注入量 が必要なことである。 また、 熱交換器 1 6の意味は排水工程水の温度調整および 非定常的に行う可能性の有る熱水殺菌を実施するためのものである。 The example shown in Fig. 2 is an example in which the injection point of sodium hypochlorite is placed first (before the heat exchanger 16). It is possible to inject the fungicide at a later stage, but the advantage of placing the injection point first is that the entire recovery system can be sterilized. On the other hand, the disadvantages are that corrosion-resistant materials must be used for the entire recovery system, and a large amount of injection is required in order to maintain the sterilization effect until the final point, compared to the latter injection. Is necessary. The purpose of the heat exchanger 16 is to regulate the temperature of the drainage process water and to perform hot water sterilization that may be performed irregularly.
図 2のフローでは、 M F膜モジュール 1 8として外圧型中空糸タイプを用いて いる。 このため、 定期的な洗浄を行う時は原水の流入を止め、 中空糸の中にコン プレッサ一 2 1により、 空気貯槽 2 2を介して高圧空気を導入することにより逆 洗し、膜表面に捕捉された微粒子成分を取り除き洗浄排水として系外に取り出す。 これ以外に平膜タイプやチューブラ一タイプ等さまざまな M F膜があるが基本 的に本発明の目的を達成するためには、 どのタイプの膜でも差し支えない。  In the flow of FIG. 2, an external pressure type hollow fiber type is used as the MF membrane module 18. For this reason, when performing regular cleaning, stop the inflow of raw water and backwash by introducing high-pressure air into the hollow fibers through the air storage tank 22 with the compressor 21 to remove the water from the membrane surface. The trapped particulate components are removed and taken out of the system as washing wastewater. In addition, there are various types of MF membranes such as a flat membrane type and a tubular type, but basically any type of membrane may be used to achieve the object of the present invention.
「具体例」  "Concrete example"
図 1のフロー図に示すような、 食品製造工場において、 仕上洗浄工程の排出ェ 程水を滅菌処理し、 第 1予備洗浄工程、 第 2予備洗浄工程、 温水洗浄工程に再利 用した。 処理としては、 図 2に示すような排水回収設備 1 1を使用し、 次亜塩素 酸ソーダを添加して M F膜処理をした例と、 M F膜処理のみの例を実施した。 次 亜塩素酸ソーダの添加量は、 5 m g/ lとした。 また M F膜は孔径 0 . 2〃mの ものを使用した。  At the food manufacturing plant, as shown in the flow chart in Fig. 1, the discharge water in the finish cleaning process was sterilized and reused in the first pre-cleaning process, the second pre-cleaning process, and the hot water cleaning process. As the treatment, a wastewater recovery facility 11 as shown in Fig. 2 was used, and an example in which sodium hypochlorite was added to perform MF membrane treatment, and an example in which only MF membrane treatment was performed. The amount of sodium hypochlorite added was 5 mg / l. The MF film used had a pore size of 0.2 μm.
回収原水および滅菌処理後の処理水の水質分析を行い、その結果を表 1に示す。 「表 1」  The quality of the recovered raw water and the treated water after sterilization was analyzed, and the results are shown in Table 1. "table 1"
Figure imgf000007_0001
Figure imgf000007_0001
のように、 M F膜を利用することによって、 非常に清澄な処理水を得ること ができ、 処理水が工程水として再利用可能なことが分かる。 Use of MF membrane to obtain very clear treated water It can be seen that the treated water can be reused as process water.
なお、 表 1に示した結果で、 MF膜処理のみの例は、 2. 3個/ mlの生菌数 を示しているが、 原理的には孔径 0. 2 imの MF膜を数// mの生菌が通過する ことは考えられない。 この原因は、 サンプリングや分析操作上、 外部から混入し た菌が原因と考えられる。  In addition, in the results shown in Table 1, the case of only the MF membrane treatment shows a viable cell count of 2.3 cells / ml, but in principle, the number of MF membranes having a pore size of 0.2 im is It is unlikely that m live bacteria will pass through. This is thought to be due to bacteria contaminated from outside during sampling and analysis operations.
以上説明したように、 本発明により、 食品関連工場における、 排出工程水を安 全に回収再利用し、 工程水の使用量を削減することが可能となった。  As described above, according to the present invention, it has become possible to safely collect and reuse discharged process water in a food-related factory, thereby reducing the amount of process water used.

Claims

請 求 の 範 囲 The scope of the claims
1 . 食品関連製造工場において、 1. In a food-related manufacturing plant,
製造工程から排出される排出工程水のうち低汚染の排出工程水を回収して滅菌 処理し、 該滅菌処理水を工程水として再利用することを特徴とする食品工場工程 水再利用方法。  A method for recycling water in a food factory process, comprising collecting and sterilizing low-contamination discharge process water from discharge process water discharged from a manufacturing process, and reusing the sterilized water as process water.
2 . 請求項 1に記載の方法において、 2. The method according to claim 1, wherein
前記低汚染の排出工程水が、 T O C 1 O m g/ 1以下の排出工程水であること を特徴とする食品工場工程水再利用方法。  A method for reusing water in a food factory process, wherein the low-contamination discharge process water is a discharge process water of TOC1Omg / 1 or less.
3 . 請求項 1に記載の方法において、 3. The method according to claim 1, wherein
前記滅菌処理が、 膜処理であることを特徴とする食品工場工程水再利用方法。  The method for reusing water in a food factory process, wherein the sterilization treatment is a membrane treatment.
4 . 請求項 1に記載の方法において、 4. The method of claim 1, wherein:
前記滅菌処理が、 膜処理および殺菌処理であることを特徴とする食品工場工程 水再利用方法。  A water recycling method for a food factory process, wherein the sterilization treatment is a membrane treatment and a sterilization treatment.
5 . 請求項 4に記載の方法において、 5. The method of claim 4, wherein:
前記殺菌処理が酸化剤注入法であることを特徴とする食品工場工程水再利用方 法。  A method for reusing water in a food factory process, wherein the sterilization treatment is an oxidizing agent injection method.
6 . 請求項 4に記載の方法において、 6. The method of claim 4, wherein:
前記膜処理が M F膜処理、 U F膜処理または R 0膜処理であることを特徴とす る食品工場工程水再利用方法。 A method for reusing water in a food factory process, wherein the membrane treatment is MF membrane treatment, UF membrane treatment or RO membrane treatment.
7 . 請求項 1に記載の方法において、 7. The method of claim 1, wherein:
前記低汚染の排出工程水は、 洗瓶工程における巿水を利用して瓶の仕上げ洗浄 を行う仕上げ洗浄工程からの排水であり、 前記滅菌処理水は、 前記仕上げ洗浄に 先立って行われる瓶の予備洗浄工程に利用されることを特徴とする食品工場工程 水再利用方法。  The low-contamination discharge process water is waste water from a finish cleaning process of performing final cleaning of the bottle by using water in the bottle washing process, and the sterilized water is a waste water of the bottle performed prior to the final cleaning. A food factory process characterized by being used in a pre-cleaning process.
PCT/JP2002/010489 2001-11-14 2002-10-09 Method of reusing food factory process water WO2003042110A1 (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107427038A (en) * 2014-12-22 2017-12-01 红牛有限责任公司 Method and apparatus for being handled food and/or container by means of process liquids

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4804149B2 (en) * 2006-01-06 2011-11-02 ダイセン・メンブレン・システムズ株式会社 Filtration treatment method for washing waste water of plants containing vegetables and / or fruits
JP2007181773A (en) * 2006-01-06 2007-07-19 Daicen Membrane Systems Ltd Filtration film performance recovering method
JP2007330925A (en) * 2006-06-16 2007-12-27 Daicen Membrane Systems Ltd Leach operation method
JP2007330924A (en) * 2006-06-16 2007-12-27 Daicen Membrane Systems Ltd Leach operation method
JP5888354B2 (en) * 2014-02-19 2016-03-22 三浦工業株式会社 Water treatment method and water treatment system
JP5928504B2 (en) * 2014-02-19 2016-06-01 三浦工業株式会社 Water treatment method and water treatment system
JP7411151B2 (en) 2019-08-22 2024-01-11 株式会社K工房 Water rate management system
JP7411863B2 (en) 2019-08-28 2024-01-12 株式会社K工房 Water rate management system

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54105852A (en) * 1978-02-07 1979-08-20 Nitto Electric Ind Co Ltd Solution separating method
JP2000246206A (en) * 1999-02-26 2000-09-12 Kuraray Co Ltd Cleaning system for food conveying container and method for using wastewater from the cleaning system
JP2001191094A (en) * 2000-01-12 2001-07-17 Nagata Jozo Kikai Kk Recycling method of washing water and apparatus threfor

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS54105852A (en) * 1978-02-07 1979-08-20 Nitto Electric Ind Co Ltd Solution separating method
JP2000246206A (en) * 1999-02-26 2000-09-12 Kuraray Co Ltd Cleaning system for food conveying container and method for using wastewater from the cleaning system
JP2001191094A (en) * 2000-01-12 2001-07-17 Nagata Jozo Kikai Kk Recycling method of washing water and apparatus threfor

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107427038A (en) * 2014-12-22 2017-12-01 红牛有限责任公司 Method and apparatus for being handled food and/or container by means of process liquids

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