JPH0994572A - Method for treating organic matter-containing water and apparatus therefor - Google Patents

Method for treating organic matter-containing water and apparatus therefor

Info

Publication number
JPH0994572A
JPH0994572A JP7252806A JP25280695A JPH0994572A JP H0994572 A JPH0994572 A JP H0994572A JP 7252806 A JP7252806 A JP 7252806A JP 25280695 A JP25280695 A JP 25280695A JP H0994572 A JPH0994572 A JP H0994572A
Authority
JP
Japan
Prior art keywords
containing water
organic matter
ultraviolet
conductivity
irradiation
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
JP7252806A
Other languages
Japanese (ja)
Inventor
Yusaku Nishimura
勇作 西村
Tsutomu Yamanobe
勉 山野邉
Naoshi Usui
直志 碓井
Yamato Asakura
大和 朝倉
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.)
Hitachi Engineering Co Ltd
Hitachi Engineering and Services Co Ltd
Hitachi Ltd
Original Assignee
Hitachi Engineering Co Ltd
Hitachi Engineering and Services Co Ltd
Hitachi Ltd
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 Hitachi Engineering Co Ltd, Hitachi Engineering and Services Co Ltd, Hitachi Ltd filed Critical Hitachi Engineering Co Ltd
Priority to JP7252806A priority Critical patent/JPH0994572A/en
Publication of JPH0994572A publication Critical patent/JPH0994572A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • Y02E30/30Nuclear fission reactors

Landscapes

  • Investigating Or Analyzing Materials By The Use Of Electric Means (AREA)
  • Treatment Of Water By Ion Exchange (AREA)
  • Physical Water Treatments (AREA)

Abstract

PROBLEM TO BE SOLVED: To effectively treat org. matter without requiring large energy by setting the ultraviolet irradiation treatment condition to org. matter-containing water on the basis of the change in the conductivity of treated water caused by an ionic intermediate product formed from org. matter by the irradiation with ultraviolet rays. SOLUTION: Org. matter-containing water enters an ultraviolet irradiation apparatus 2 by a liquid supply pump 1 to be irradiated with ultraviolet rays while flows through the passage thereof and org. matter is decomposed to an ionic intermediate product and this product enters an ion exchange resin tower 4 to be subjected to ion exchange treatment and removed. Herein, the change in the conductivity of treated water by the irradiation with ultraviolet rays is measured by a conductivity meter 3 and, by an ultraviolet irradiation condition control unit 5 receiving the signal of the conductivity meter 3, the liquid supply amt. of the liquid supply pump 1 or the powder of an ultraviolet lamp is controlled so that the conductivity of ultraviolet treated water shows the max. value. Since the irradiation with ultraviolet rays is performed under a condition more forming the ionic intermediate product, the org. matter can be removed in the stage of the intermediate product without being finally decomposed to carbon dioxide and water and can be efficiently treated.

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、有機物含有水の処
理方法及び装置に係わり、特に原子力発電プラントにお
ける復水脱塩器や濾過脱塩器から溶出する有機物を含有
する水の処理方法及び装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for treating organic matter-containing water, and more particularly, a method and apparatus for treating water containing organic matter eluted from a condensate desalination unit or a filter desalting unit in a nuclear power plant. Regarding

【0002】[0002]

【従来の技術】発電プラントは高温高圧の蒸気条件で操
作される。一方、発電プラントの系統機器及び配管等は
大部分が鉄鋼材で構成されており、その構成材料を防食
するために復水は不純物を除去した高純度水が使用され
る。特に沸騰水型原子力発電プラントでは復水中に含ま
れる不純物は原子炉内に持込まれ炉内構造材の腐食を促
進するため、復水系に脱塩装置を設け不純物の徹底した
除去を行っている。脱塩装置としては粉末イオン交換樹
脂を用いる濾過脱塩器や粒状イオン交換樹脂を用いる脱
塩器が設けられている。他の従来例として特開平4−3
34588号公報又は特開平6−138289号公報が
挙げられ、これらには紫外線を照射して復水中の有機物
を分解することが開示されている。
Power plants are operated in high temperature, high pressure steam conditions. On the other hand, most of the system equipment and pipes of the power plant are made of steel, and high-purity water from which impurities have been removed is used as condensate to prevent corrosion of the constituent materials. In particular, in boiling water nuclear power plants, impurities contained in condensate are brought into the reactor and promote corrosion of the structural materials inside the reactor. Therefore, a desalting device is installed in the condensate system to thoroughly remove impurities. As the desalting device, a filter desalting device using a powder ion exchange resin and a desalting device using a granular ion exchange resin are provided. As another conventional example, Japanese Patent Laid-Open No. 4-3
No. 34588 or Japanese Patent Application Laid-Open No. 6-138289 is disclosed, which discloses irradiating ultraviolet rays to decompose organic substances in the condensate.

【0003】[0003]

【発明が解決しようとする課題】イオン交換樹脂を用い
る脱塩器はイオン性不純物の除去能は優れているが、非
イオン性不純物、例えばアルコール等の有機物の除去能
はない。又、脱塩器に用いられているイオン交換樹脂は
スチレンとジビニルベンゼンの共重合体を樹脂母体とし
ているため、イオン交換樹脂自身からの有機物の溶出は
避けられない。溶出有機物として陽イオン交換樹脂から
はポリスチレンスルホン酸、陰イオン交換樹脂からはト
リメチルアミン、メタノール、ポリスチレン4級アンモ
ニウムなどが知られている。このため復水中の非イオン
性有機物や脱塩器自体から溶出する有機物は原子炉内に
持込まれ分解され硫酸イオンや硝酸イオンを生成すると
いう問題があった。また、特開平4−334588号公
報等の紫外線を照射して復水中の有機物を分解する方法
は、その紫外線照射により有機物を最終的な炭酸ガスと
水にまで完全に分解させるため、その分解に大きなエネ
ルギーが必要となり経済的でない問題があった。
A desalting device using an ion exchange resin has excellent ability to remove ionic impurities, but does not have ability to remove nonionic impurities such as organic substances such as alcohol. Further, since the ion exchange resin used in the desalting device uses a copolymer of styrene and divinylbenzene as a resin matrix, elution of organic substances from the ion exchange resin itself cannot be avoided. As leaching organic substances, polystyrene sulfonic acid is known as a cation exchange resin, and trimethylamine, methanol, polystyrene quaternary ammonium as an anion exchange resin are known. Therefore, there is a problem that nonionic organic substances in the condensate or organic substances eluted from the desalting device itself are brought into the reactor and decomposed to generate sulfate ions and nitrate ions. Further, in the method of irradiating ultraviolet rays such as JP-A-4-334588 to decompose organic matter in the condensate, the organic matter is completely decomposed into final carbon dioxide gas and water by the ultraviolet ray irradiation. There was a problem that it required large amount of energy and was not economical.

【0004】本発明の目的は、原子力発電プラント等の
復水浄化における上記の問題点を解決し、効果的で且つ
有機物分解に大きなエネルギーを必要としない経済的な
有機物含有水の処理方法及び装置を提供することにあ
る。
An object of the present invention is to solve the above-mentioned problems in condensate purification of a nuclear power plant and the like, and to provide an effective method and apparatus for treating water containing organic matter, which is effective and does not require large energy for decomposing organic matter. To provide.

【0005】[0005]

【課題を解決するための手段】上記目的を達成するため
本発明は、有機物含有水に対する紫外線照射処理条件
を、その処理水中の有機物が紫外線照射により生成する
イオン性中間生成物に基づく該処理水の導電率変化に基
づき設定することを特徴とする有機物含有水の処理方法
である。
In order to achieve the above object, the present invention provides the conditions for ultraviolet irradiation treatment of organic matter-containing water such that the organic matter in the treated water is an ionic intermediate product produced by ultraviolet irradiation. The method for treating organic matter-containing water is characterized in that it is set on the basis of the change in conductivity.

【0006】また他の発明は、前記発明において、有機
物含有水の紫外線照射処理条件は、紫外線の照射時間を
変えて前記導電率が大きくなる方向に設定することを特
徴とするものである。
Another aspect of the present invention is characterized in that, in the above-mentioned invention, the ultraviolet irradiation treatment condition of the organic matter-containing water is set so that the conductivity increases by changing the irradiation time of ultraviolet rays.

【0007】また他の発明は、前記発明において、有機
物含有水の紫外線照射処理条件は、紫外線ランプ電力を
変えて前記導電率が大きくなる方向に設定することを特
徴とするものである。
Another aspect of the present invention is characterized in that, in the above invention, the ultraviolet irradiation treatment condition of the organic matter-containing water is set so that the electric conductivity increases by changing the electric power of the ultraviolet lamp.

【0008】また他の発明は、前記いずれかの発明にお
いて、イオン性中間生成物が生成している状態の処理水
をイオン交換処理することを特徴とする有機物含有水の
処理方法である。
Another aspect of the present invention is the method for treating organic matter-containing water according to any one of the above aspects, characterized in that the treated water in a state where an ionic intermediate product is produced is subjected to an ion exchange treatment.

【0009】また他の発明は、前記いずれかの発明にお
いて、有機物含有水が粒状の陽イオン交換樹脂と陰イオ
ン交換樹脂を混合充てんした脱塩器から溶出する有機物
含有水であることを特徴とする有機物含有水の処理方法
である。
According to another invention, in any one of the above inventions, the organic substance-containing water is an organic substance-containing water that is eluted from a desalting device that is mixed and filled with a granular cation exchange resin and an anion exchange resin. It is a method of treating organic matter-containing water.

【0010】また他の発明は、前記いずれかの発明にお
いて、有機物含有水が粉末の陽イオン交換樹脂と陰イオ
ン交換樹脂をプリコートした濾過脱塩器から溶出する有
機物含有水であることを特徴とするものである。
According to another invention, in any one of the above inventions, the organic matter-containing water is an organic matter-containing water that is eluted from a filter desalting device precoated with powdered cation exchange resin and anion exchange resin. To do.

【0011】また他の発明は、処理水である有機物含有
水を送る送液手段と、この送液手段から送られた処理水
に紫外線を照射する紫外線照射手段と、この紫外線照射
手段を通過した処理水が送られるイオン交換手段と、前
記紫外線照射手段とイオン交換手段との間に設けられて
紫外線照射処理された処理水の導電率を検出する導電率
検出手段と、この導電率検出手段の検出信号を受けてそ
の導電率が大きくなる方向に前記処理水に対する紫外線
照射処理条件を設定する紫外線照射条件制御手段とを備
えたことを特徴とする有機物含有水の処理装置である。
According to another aspect of the invention, a liquid feeding means for feeding organic matter-containing water as treated water, an ultraviolet ray irradiating means for irradiating the treated water fed from the liquid feeding means with ultraviolet rays, and the ultraviolet ray irradiating means are passed through. Ion exchange means to which the treated water is sent, conductivity detection means provided between the ultraviolet irradiation means and the ion exchange means for detecting the conductivity of the treated water subjected to the ultraviolet irradiation treatment, and the conductivity detection means An apparatus for treating organic matter-containing water, comprising: an ultraviolet ray irradiation condition control unit for setting an ultraviolet ray irradiation treatment condition for the treated water in a direction in which the conductivity thereof increases in response to a detection signal.

【0012】また他の発明は、前記装置の発明におい
て、導電率検出手段の検出信号は紫外線照射手段に送ら
れて紫外線ランプ電力が変更制御されるものである。
According to another aspect of the invention, in the above invention, the detection signal of the conductivity detecting means is sent to the ultraviolet irradiating means to change and control the ultraviolet lamp power.

【0013】また他の発明は、前記装置の発明におい
て、導電率検出手段の検出信号は送液手段に送られて紫
外線の照射時間が変更制御されるものである。
According to another invention, in the above invention, the detection signal of the conductivity detecting means is sent to the liquid feeding means and the irradiation time of the ultraviolet rays is changed and controlled.

【0014】本発明は、発電プラントの復水等の有機物
含有水を紫外線照射した後、イオン交換処理するに際
し、紫外線照射により前記有機物をイオン性中間生成物
に分解し、このイオン性中間生成物の生成に基づいて処
理水の導電率が変化するが、その導電率変化に基づいて
最適の紫外線照射条件を設定するものである。これによ
り有機物分解に大きなエネルギーを必要とせずに効率よ
く有機物含有水を処理することができる。
According to the present invention, when organic matter-containing water such as condensate of a power plant is irradiated with ultraviolet rays and then subjected to an ion exchange treatment, the organic matter is decomposed into an ionic intermediate product by the irradiation of ultraviolet rays, and the ionic intermediate product is decomposed. Although the conductivity of the treated water changes based on the generation of the, the optimum ultraviolet irradiation conditions are set based on the change in the conductivity. As a result, the organic substance-containing water can be efficiently treated without requiring a large amount of energy for decomposing the organic substance.

【0015】本発明者等は発電プラントの性能向上及び
構成機器の腐食防止のために発電プラントの復水の浄化
方法について種々検討した。復水中に含まれる腐食性成
分の一種であるナトリウムイオンや塩素イオンは、陽イ
オン交換樹脂と陰イオン交換樹脂を混合充てんした脱塩
器で除去される。しかし、前記したように復水中の有機
物や脱塩器のイオン交換樹脂から溶出する有機物は除去
できない。ここで脱塩器のイオン交換樹脂から溶出する
有機物量は通常の流水状態では脱塩器内での復水の滞留
時間が非常に短いため少量でありほとんど問題とはなら
ない。しかし、復水脱塩器の逆洗、再生や復水濾過脱塩
器のプリコート時は復水系からアウトサービスされ、こ
れらの操作終了後、次の通水時まで待機している。この
ような状態は時間が長いため脱塩器内のイオン交換樹脂
から溶出する有機物は高濃度となり、インサービス時復
水に多量の有機物が持込まれる。これらはいずれも原子
炉内に持込まれ分解され不純物イオンを生成する。これ
を防ぐため現状ではやむなく脱塩器のインサービス前に
ボトムドレン水を系外に排出している。しかし、この有
機物を含むボトムドレン水は回収され補給水として復水
に戻される。このため脱塩器等のボトムドレン水中の有
機物は分解除去されないかぎり最終的には復水に入って
しまう。このような事を防止するためにはボトムドレン
水中等の有機物の分解除去が必要である。
The present inventors have conducted various studies on a method for purifying condensate of a power plant in order to improve the performance of the power plant and prevent corrosion of constituent equipment. Sodium ions and chlorine ions, which are one of the corrosive components contained in the condensate, are removed by a desalting device in which a cation exchange resin and an anion exchange resin are mixed and filled. However, as described above, the organic matter in the condensate and the organic matter eluted from the ion exchange resin of the desalting device cannot be removed. Here, the amount of organic substances eluted from the ion-exchange resin of the desalting device is small in a normal running water state because the residence time of the condensate water in the desalting device is very short, and there is almost no problem. However, when the condensate demineralizer is backwashed, regenerated and the condensate filtration desalinator is pre-coated, it is out of service from the condensate system, and after these operations are completed, it waits until the next water flow. Since such a state takes a long time, the organic matter eluted from the ion-exchange resin in the desalting device has a high concentration, and a large amount of organic matter is brought into the condensate during in-service. All of these are brought into the reactor and decomposed to produce impurity ions. In order to prevent this, at present, bottom drain water is unavoidably discharged to the outside of the system before in-service of the desalinizer. However, the bottom drain water containing this organic matter is recovered and returned to the condensate as makeup water. Therefore, organic matter in the bottom drain water of the desalting device or the like will eventually enter condensate unless it is decomposed and removed. In order to prevent such a situation, it is necessary to decompose and remove organic substances such as bottom drain water.

【0016】有機物の分解除去法としては酸化剤等の薬
剤の添加を必要としない紫外線照射処理が好ましい。こ
の方法は主波長が185nm及び254nmである低圧
水銀ランプを用い紫外線を照射し有機物を酸化分解する
ものである。特に185nmの光は水分子を分解して強
力な酸化力をもつヒドロキシラジカルを生成するととも
に水中の溶存有機物の化学結合を解離する。これらの作
用により有機物は最終的には炭酸ガスと水に分解され
る。しかし、有機物を炭酸ガスと水にまで完全に分解す
るには大きなエネルギーを必要する。ここで有機物は紫
外線照射されると酸化分解の程度により各種の中間生成
物を経て最終的に炭酸ガスと水に分解される。
As a method for decomposing and removing organic substances, ultraviolet irradiation treatment which does not require addition of a chemical agent such as an oxidizing agent is preferable. In this method, a low-pressure mercury lamp having main wavelengths of 185 nm and 254 nm is used to irradiate ultraviolet rays to oxidize and decompose organic substances. In particular, the light of 185 nm decomposes water molecules to generate hydroxy radicals having a strong oxidizing power, and dissociates chemical bonds of dissolved organic substances in water. By these actions, the organic matter is finally decomposed into carbon dioxide gas and water. However, a large amount of energy is required to completely decompose organic matter into carbon dioxide and water. Here, the organic matter is decomposed into carbon dioxide gas and water through various intermediate products depending on the degree of oxidative decomposition when it is irradiated with ultraviolet rays.

【0017】ところで、前記中間生成物は主にギ酸、酢
酸等の有機酸等のイオン性物質であり、これはイオン交
換樹脂で除去可能である。我々の検討結果によれば有機
物含有水の紫外線照射をイオン性中間生成物をより多く
生成する条件で行い、続いてイオン交換処理を行えば、
有機物を最終的な炭酸ガスと水にまで分解せずに中間生
成物の段階で除去でき、有機物含有水の処理が効率よく
行えることが分った。有機物の紫外線照射による中間生
成物の種類、量は有機物濃度、紫外線照射時間、紫外線
照射量等に依存するものである。このような方法により
有機物含有水の処理を効率よく行うには紫外線照射処理
水の導電率が最大となるよう有機物含有水の紫外線照射
を行えばよい。
By the way, the intermediate product is mainly an ionic substance such as an organic acid such as formic acid or acetic acid, which can be removed by an ion exchange resin. According to our study results, if ultraviolet irradiation of organic matter-containing water is performed under the condition that more ionic intermediate products are produced, and then ion exchange treatment is performed,
It was found that the organic matter can be removed at the intermediate product stage without being decomposed into the final carbon dioxide gas and water, and the treatment of the organic matter-containing water can be performed efficiently. The type and amount of the intermediate product produced by the irradiation of the organic substance with ultraviolet light depends on the concentration of the organic substance, the ultraviolet irradiation time, the ultraviolet irradiation amount, and the like. In order to efficiently treat the organic matter-containing water by such a method, the organic matter-containing water may be irradiated with ultraviolet rays so that the conductivity of the ultraviolet ray-treated water becomes maximum.

【0018】また有機物含有水の紫外線照射処理条件
は、紫外線の照射時間を変えて前記導電率が大きくなる
方向に設定することは送液ポンプなどの送液量を変える
ことにより簡単に行える。又は紫外線ランプ電力を変え
て紫外線照射量を前記導電率が大きくなる方向に設定す
ることも簡単に行える。
Further, the ultraviolet irradiation treatment condition of the organic substance-containing water can be easily set by changing the irradiation time of the ultraviolet light so as to increase the conductivity by changing the liquid feed amount of the liquid feed pump or the like. Alternatively, it is possible to easily set the ultraviolet irradiation amount in the direction in which the conductivity increases by changing the power of the ultraviolet lamp.

【0019】また本発明に係る有機物含有水の処理装置
によれば、構造簡単にして前記処理方法に係る発明を実
施できる。特に、導電率検出手段の検出信号が紫外線照
射手段に送られて紫外線ランプ電力が変更制御されるも
のや、導電率検出手段の検出信号が送液手段に送られて
紫外線の照射時間が変更制御されるものが構造的に簡単
である。
Further, according to the treatment apparatus for organic substance-containing water according to the present invention, the invention relating to the treatment method can be carried out with a simple structure. Particularly, the detection signal of the conductivity detection means is sent to the ultraviolet irradiation means to change and control the ultraviolet lamp power, and the detection signal of the conductivity detection means is sent to the liquid feeding means to change and control the irradiation time of ultraviolet rays. What is done is structurally simple.

【0020】[0020]

【発明の実施の形態】BEST MODE FOR CARRYING OUT THE INVENTION

〔具体例1〕次に本発明を図1に基づいて具体的に説明
する。図1は本発明による有機物含有水の処理装置の構
成図である。本有機物含有水の処理装置は送液ポンプ
1、紫外線照射装置2、導電率計3、イオン交換樹脂塔
4、紫外線照射条件制御装置5により構成される。紫外
線照射装置2は図2に示すように紫外線ランプ6と有機
物含有水の流路7とにより構成される。紫外線ランプ6
は主波長が185nm及び254nmである低圧水銀ラ
ンプが好ましい。イオン交換樹脂塔4は本実施例では陽
イオン交換樹脂と陰イオン交換樹脂を混合充てんしたも
のである。又、紫外線照射条件制御装置5は紫外線照射
装置2を通過した紫外線照射処理水の導電率を導電率計
3で測定し、その導電率が最大となるように送液ポンプ
1の送液量や紫外線照射装置2の紫外線ランプ電力等を
制御するものである。送液ポンプ1の送液量を変えるこ
とは、紫外線の照射時間を変えることに相当する。前記
送液量と紫外線ランプ電力の両方を制御してもよいが、
いずれか一方だけの制御で通常はよい。
Specific Example 1 Next, the present invention will be specifically described with reference to FIG. FIG. 1 is a block diagram of an apparatus for treating organic matter-containing water according to the present invention. This organic substance-containing water treatment device is composed of a liquid feed pump 1, an ultraviolet irradiation device 2, a conductivity meter 3, an ion exchange resin tower 4, and an ultraviolet irradiation condition control device 5. As shown in FIG. 2, the ultraviolet irradiation device 2 is composed of an ultraviolet lamp 6 and an organic substance-containing water flow path 7. UV lamp 6
Is preferably a low-pressure mercury lamp with dominant wavelengths of 185 nm and 254 nm. In this embodiment, the ion exchange resin tower 4 is a mixture of a cation exchange resin and an anion exchange resin. Further, the ultraviolet irradiation condition control device 5 measures the conductivity of the ultraviolet irradiation treated water that has passed through the ultraviolet irradiation device 2 with the conductivity meter 3, and adjusts the liquid feed amount of the liquid feed pump 1 so as to maximize the conductivity. It controls the electric power of the ultraviolet lamp of the ultraviolet irradiation device 2. Changing the amount of liquid sent by the liquid sending pump 1 corresponds to changing the irradiation time of ultraviolet rays. Although it is possible to control both the liquid delivery amount and the ultraviolet lamp power,
It is usually good to control only one of them.

【0021】図1における工程を説明する。有機物含有
水は送液ポンプ1により紫外線照射装置2に入り、有機
物含有水が流路7を流れる間に紫外線照射され、有機物
はイオン性中間生成物に分解される。次にイオン交換樹
脂塔4に入りイオン交換処理されて除去される。ここ
で、紫外線照射による処理水の導電率の変化を導電率計
3で測定し、その信号を受ける紫外線照射条件制御装置
5により送液ポンプの送液量や紫外線ランプ電力を制御
し、紫外線処理水の導電率が最大値を示すようにしてあ
る。この処理方法をフローチャートで表すと図3の如く
なる。
The steps in FIG. 1 will be described. The organic substance-containing water enters the ultraviolet ray irradiation device 2 by the liquid feed pump 1, is irradiated with ultraviolet rays while the organic substance-containing water flows through the flow path 7, and the organic substance is decomposed into an ionic intermediate product. Next, it enters the ion-exchange resin tower 4 and is ion-exchanged and removed. Here, a change in conductivity of treated water due to ultraviolet irradiation is measured by a conductivity meter 3, and an ultraviolet irradiation condition control device 5 which receives the signal controls the liquid feed amount of a liquid feed pump and the ultraviolet lamp power to perform the ultraviolet treatment. The conductivity of water shows the maximum value. A flowchart of this processing method is as shown in FIG.

【0022】次に、図1の有機物含有水の処理装置によ
る処理例を示す。有機物含有水は陽イオン交換樹脂と陰
イオン交換樹脂の混合状態から溶出した有機物を含むも
のである。この処理水の有機物濃度(TOC:Total
Organic Carbon)は1200μg/l、導電率は3.5
μS/cmであった。送液ポンプ1の流量を変えること
により紫外線照射装置2での照射時間を変化させ処理し
た。続いてイオン交換樹脂塔4によりイオン交換処理を
行った。紫外線照射処理後の導電率とTOCを図4に示
す。照射時間の増加に伴い導電率は大きくなり照射時間
3分附近で最大となり、以後は低下しやがて一定とな
る。これは紫外線照射により先ずイオン性の中間物が生
成し、続いてこれらが酸化分解され炭酸ガスと水を生成
するためと考えられる。TOCは照射時間の増加に伴い
低下し、照射時間6分以降で100μg/l以下になっ
ており、有機物が炭酸ガスと水に完全に分解しているこ
とが分る。一方、この時の紫外線照射処理の後段に設置
したイオン交換樹脂塔4によるイオン交換処理水の水質
は紫外線照射により導電率が最大となる照射時間3分以
上ではTOC 100μg/l以下、導電率0.1μS/
cm以下であり、有機物、イオンとも十分除去されてい
た。
Next, an example of treatment by the treatment apparatus for organic substance-containing water of FIG. 1 will be shown. The organic substance-containing water contains organic substances eluted from the mixed state of the cation exchange resin and the anion exchange resin. Organic matter concentration of this treated water (TOC: Total
Organic Carbon) is 1200 μg / l, conductivity is 3.5
μS / cm. By changing the flow rate of the liquid feed pump 1, the irradiation time in the ultraviolet irradiation device 2 was changed and processing was performed. Subsequently, an ion exchange treatment was performed by the ion exchange resin tower 4. FIG. 4 shows the conductivity and TOC after the ultraviolet irradiation treatment. As the irradiation time increases, the conductivity increases, reaches a maximum near the irradiation time of 3 minutes, and thereafter decreases and becomes constant. This is considered to be because ionic intermediates are first generated by the irradiation of ultraviolet rays, and then these are oxidatively decomposed to generate carbon dioxide gas and water. The TOC decreases as the irradiation time increases, and becomes 100 μg / l or less after the irradiation time of 6 minutes, showing that the organic substances are completely decomposed into carbon dioxide gas and water. On the other hand, at this time, the water quality of the ion-exchange treated water by the ion-exchange resin tower 4 installed in the latter stage of the ultraviolet irradiation treatment is TOC 100 μg / l or less and conductivity 0 or less at the irradiation time of 3 minutes or longer at which the conductivity is maximized by the ultraviolet irradiation. .1 μS /
cm or less, and both organic substances and ions were sufficiently removed.

【0023】〔具体例2〕図5は原子力発電プラントの
系統及び脱塩器から溶出する有機物の処理系統図であ
る。図5において、8は脱塩器10のボトムドレン水回
収タンク、9は本発明に係る有機物含有水の処理装置を
示す。脱塩器10には粒状の陽イオン交換樹脂と陰イオ
ン交換樹脂が混合充てんされている。また濾過脱塩器1
1は粉末の陽イオン交換樹脂と陰イオン交換樹脂をプリ
コートしたものである。脱塩器10や濾過脱塩器11の
ボトムドレン水は回収され、有機物含有水の処理装置9
により処理された後、プラントの補給水等として再使用
される。
[Specific Example 2] FIG. 5 is a system diagram of a system of a nuclear power plant and a treatment system of organic substances eluted from a desalination unit. In FIG. 5, 8 indicates a bottom drain water recovery tank of the desalting device 10, and 9 indicates a treatment device for organic substance-containing water according to the present invention. The desalinizer 10 is mixed and filled with granular cation exchange resin and anion exchange resin. In addition, filter desalting machine 1
1 is pre-coated with powdered cation exchange resin and anion exchange resin. The bottom drain water of the desalting device 10 and the filter desalting device 11 is recovered, and the organic substance-containing water treatment device 9
After being treated by, it is reused as make-up water for the plant.

【0024】[0024]

【発明の効果】本発明によれば、有機物含有水の紫外線
照射をイオン性中間生成物をより多く生成する条件で行
い、続いてイオン交換処理するので、有機物を最終的な
炭酸ガスと水にまで分解せずに中間生成物の段階で除去
でき、有機物含有水の処理が効率よく行えると共に有機
物分解に大きなエネルギーを必要としない。これによ
り、原子力発電プラントにおける復水中の有機物が低減
し原子炉内への持込みを防止でき炉内構造物等の腐食が
低減し、発電プラントの性能を向上させ、かつ機器の長
寿命化が図れるという効果が得られる。
EFFECTS OF THE INVENTION According to the present invention, the irradiation of the organic matter-containing water with ultraviolet rays is performed under the condition that more ionic intermediate products are produced, and then the ion exchange treatment is performed, so that the organic matter is finally converted into carbon dioxide gas and water. It can be removed at the stage of an intermediate product without decomposition, and the organic substance-containing water can be efficiently treated, and a large amount of energy is not required to decompose the organic substance. As a result, the organic matter in the condensate of the nuclear power plant is reduced, it is possible to prevent it from being brought into the reactor, the corrosion of reactor internals, etc. is reduced, the performance of the power plant is improved, and the life of the equipment is extended. The effect is obtained.

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

【図1】本発明の有機物含有水の処理装置の構成図であ
る。
FIG. 1 is a block diagram of an apparatus for treating organic matter-containing water according to the present invention.

【図2】紫外線照射装置の縦断面図である。FIG. 2 is a vertical sectional view of an ultraviolet irradiation device.

【図3】本発明の処理方法のフローチャート図である。FIG. 3 is a flowchart of a processing method of the present invention.

【図4】本発明の有機物含有水の処理方法による有機物
含有水の紫外線照射処理例であり、紫外線照射時間に対
する導電率とTOCとの関係を示す図である。
FIG. 4 is an example of ultraviolet irradiation treatment of organic matter-containing water by the method for treating organic matter-containing water according to the present invention, showing the relationship between conductivity and TOC with respect to ultraviolet ray irradiation time.

【図5】本有機物含有水の処理装置を備えた原子力発電
プラントの復水系を示す構成図である。
FIG. 5 is a configuration diagram showing a condensate system of a nuclear power plant equipped with the present organic matter-containing water treatment apparatus.

【符号の説明】[Explanation of symbols]

1 送液ポンプ 2 紫外線照射装置 3 導電率計 4 イオン交換樹脂塔 5 紫外線照射条件制御装置 1 Liquid Delivery Pump 2 Ultraviolet Irradiation Device 3 Conductivity Meter 4 Ion Exchange Resin Tower 5 Ultraviolet Irradiation Condition Control Device

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 G21D 1/00 GDB G21F 9/12 512C G21F 9/12 512 G21C 19/30 GDBC G21D 1/00 GDBW (72)発明者 山野邉 勉 茨城県日立市幸町三丁目2番2号 株式会 社日立エンジニアリングサービス内 (72)発明者 碓井 直志 茨城県日立市幸町三丁目2番1号 日立エ ンジニアリング株式会社内 (72)発明者 朝倉 大和 茨城県日立市幸町三丁目1番1号 株式会 社日立製作所日立工場内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location G21D 1/00 GDB G21F 9/12 512C G21F 9/12 512 G21C 19/30 GDBC G21D 1/00 GDBW (72) Inventor Tsutomu Yamano 3-2-2 Sachimachi, Hitachi City, Ibaraki Prefecture Hitachi Engineering Service (72) Inventor Naoshi Usui 3-2-1 Sachimachi, Hitachi City, Ibaraki Hitachi Engineering Co., Ltd. Incorporated (72) Inventor Yamato Asakura 3-1-1, Saiwaicho, Hitachi-shi, Ibaraki Hitachi Ltd. Hitachi factory

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 有機物含有水に紫外線を照射して処理す
る有機物含有水の処理方法において、有機物含有水に対
する紫外線照射処理条件を処理水中の有機物が紫外線照
射により生成するイオン性中間生成物に基づく該処理水
の導電率変化に基づき設定することを特徴とする有機物
含有水の処理方法。
1. A method for treating organic matter-containing water, comprising irradiating an organic matter-containing water with ultraviolet rays to treat the organic matter-containing water with ultraviolet rays, wherein the organic matter in the treated water is based on an ionic intermediate product produced by ultraviolet ray irradiation. A method for treating organic matter-containing water, which is set based on a change in conductivity of the treated water.
【請求項2】 請求項1において、有機物含有水の紫外
線照射処理条件は、紫外線の照射時間を変えて前記導電
率が大きくなる方向に設定することを特徴とする有機物
含有水の処理方法。
2. The method for treating organic matter-containing water according to claim 1, wherein the conditions for irradiating the organic matter-containing water with ultraviolet rays are set so that the conductivity increases by changing the irradiation time of ultraviolet rays.
【請求項3】 請求項1において、有機物含有水の紫外
線照射処理条件は、紫外線ランプ電力を変えて前記導電
率が大きくなる方向に設定することを特徴とする有機物
含有水の処理方法。
3. The method for treating organic matter-containing water according to claim 1, wherein the ultraviolet ray irradiation treatment condition for the organic matter-containing water is set in such a direction that the electric conductivity is increased by changing the electric power of the ultraviolet lamp.
【請求項4】 請求項1乃至3のいずれかにおいて、イ
オン性中間生成物が生成している状態の処理水をイオン
交換処理することを特徴とする有機物含有水の処理方
法。
4. The method for treating organic matter-containing water according to claim 1, wherein the treated water in a state where the ionic intermediate product is produced is subjected to an ion exchange treatment.
【請求項5】 請求項1乃至4のいずれかにおいて、有
機物含有水が粒状の陽イオン交換樹脂と陰イオン交換樹
脂を混合充てんした脱塩器から溶出する有機物含有水で
あることを特徴とする有機物含有水の処理方法。
5. The organic substance-containing water according to claim 1, wherein the organic substance-containing water is an organic substance-containing water that is eluted from a desalting device that is mixed and filled with a granular cation exchange resin and an anion exchange resin. A method for treating organic matter-containing water.
【請求項6】 請求項1乃至4のいずれかにおいて、有
機物含有水が粉末の陽イオン交換樹脂と陰イオン交換樹
脂をプリコートした濾過脱塩器から溶出する有機物含有
水であることを特徴とする有機物含有水の処理方法。
6. The organic matter-containing water according to any one of claims 1 to 4, wherein the organic matter-containing water is an organic matter-containing water that is eluted from a filter desalting device precoated with powdered cation exchange resin and anion exchange resin. A method for treating organic matter-containing water.
【請求項7】 処理水である有機物含有水を送る送液手
段と、この送液手段から送られた処理水に紫外線を照射
する紫外線照射手段と、この紫外線照射手段を通過した
処理水が送られるイオン交換手段と、前記紫外線照射手
段とイオン交換手段との間に設けられて紫外線照射処理
された処理水の導電率を検出する導電率検出手段と、こ
の導電率検出手段の検出信号を受けてその導電率が大き
くなる方向に前記処理水に対する紫外線照射処理条件を
設定する紫外線照射条件制御手段とを備えたことを特徴
とする有機物含有水の処理装置。
7. A liquid feed means for feeding organic matter-containing water which is treated water, an ultraviolet ray irradiating means for irradiating the treated water fed from this liquid feed means with ultraviolet rays, and a treated water which has passed through this ultraviolet ray irradiating means is fed. An ion exchange means, a conductivity detection means provided between the ultraviolet irradiation means and the ion exchange means for detecting the conductivity of the treated water subjected to the ultraviolet irradiation treatment, and a detection signal of the conductivity detection means. And an ultraviolet irradiation condition control means for setting ultraviolet irradiation processing conditions for the treated water in a direction in which the conductivity increases.
【請求項8】 請求項7において、導電率検出手段の検
出信号は紫外線照射手段に送られて紫外線ランプ電力が
変更制御されるものであることを特徴とする有機物含有
水の処理装置。
8. A treatment apparatus for organic substance-containing water according to claim 7, wherein the detection signal of the conductivity detecting means is sent to the ultraviolet irradiating means to change and control the power of the ultraviolet lamp.
【請求項9】 請求項7において、導電率検出手段の検
出信号は送液手段に送られて紫外線の照射時間が変更制
御されるものであることを特徴とする有機物含有水の処
理装置。
9. The apparatus for treating organic matter-containing water according to claim 7, wherein the detection signal of the conductivity detecting means is sent to the liquid feeding means and the irradiation time of the ultraviolet rays is changed and controlled.
JP7252806A 1995-09-29 1995-09-29 Method for treating organic matter-containing water and apparatus therefor Pending JPH0994572A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7252806A JPH0994572A (en) 1995-09-29 1995-09-29 Method for treating organic matter-containing water and apparatus therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7252806A JPH0994572A (en) 1995-09-29 1995-09-29 Method for treating organic matter-containing water and apparatus therefor

Publications (1)

Publication Number Publication Date
JPH0994572A true JPH0994572A (en) 1997-04-08

Family

ID=17242486

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7252806A Pending JPH0994572A (en) 1995-09-29 1995-09-29 Method for treating organic matter-containing water and apparatus therefor

Country Status (1)

Country Link
JP (1) JPH0994572A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001153828A (en) * 1999-11-26 2001-06-08 Dkk Toa Corp Method and device for measuring organic carbon content
KR20020046974A (en) * 2000-12-13 2002-06-21 주식회사 노무라코리아 Apparatus and method for detecting impurities
JP2004521318A (en) * 2000-10-16 2004-07-15 シーヴァーズ インスツルメンツ,インク. Pulse flow total organic carbon analyzer

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001153828A (en) * 1999-11-26 2001-06-08 Dkk Toa Corp Method and device for measuring organic carbon content
JP2004521318A (en) * 2000-10-16 2004-07-15 シーヴァーズ インスツルメンツ,インク. Pulse flow total organic carbon analyzer
KR20020046974A (en) * 2000-12-13 2002-06-21 주식회사 노무라코리아 Apparatus and method for detecting impurities
JP2002214221A (en) * 2000-12-13 2002-07-31 Samsung Electronics Co Ltd Impurities detector and impurities detection method

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