JP2968901B2 - Makeup water production equipment for power plants - Google Patents

Makeup water production equipment for power plants

Info

Publication number
JP2968901B2
JP2968901B2 JP5042941A JP4294193A JP2968901B2 JP 2968901 B2 JP2968901 B2 JP 2968901B2 JP 5042941 A JP5042941 A JP 5042941A JP 4294193 A JP4294193 A JP 4294193A JP 2968901 B2 JP2968901 B2 JP 2968901B2
Authority
JP
Japan
Prior art keywords
water
ion exchange
exchange device
ultraviolet
power plants
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP5042941A
Other languages
Japanese (ja)
Other versions
JPH06254596A (en
Inventor
伸一 大橋
雄一 横溝
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.)
ORUGANO KK
Original Assignee
ORUGANO KK
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 ORUGANO KK filed Critical ORUGANO KK
Priority to JP5042941A priority Critical patent/JP2968901B2/en
Publication of JPH06254596A publication Critical patent/JPH06254596A/en
Application granted granted Critical
Publication of JP2968901B2 publication Critical patent/JP2968901B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Treatment Of Water By Ion Exchange (AREA)
  • Physical Water Treatments (AREA)
  • Removal Of Specific Substances (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は火力発電所、あるいは原
子力発電所の蒸気タービン用補給水の製造装置、更に詳
述すれば有機塩素化合物を除去した補給水を製造するた
めの装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for producing makeup water for steam turbines of thermal power plants or nuclear power plants, and more particularly to an apparatus for producing makeup water from which organochlorine compounds have been removed.

【0002】[0002]

【従来の技術】従来の蒸気タービン用補給水製造装置に
おいては、有機化合物、特に有機塩素化合物の除去は、
例えばトリハロメタン等の揮発性のものの一部が脱炭酸
塔での曝気や真空脱気塔により、またフミン酸や農薬等
の不揮発性物質の一部が凝集沈殿、濾過、活性炭吸着お
よびイオン交換の方法により除去されている。しかし、
従来の補給水製造装置はこれらの有機化合物や有機塩素
化合物を完全には除去できず、TOCとして30〜50
ppb程度が、またトリハロメタン等の有機塩素として
5〜10ppb程度が残留しており、各種の問題の原因
となっている。例えば、PWR型原子力発電所では、タ
ービンの復水中に塩素イオンが含まれていると、蒸気発
生器内のステンレス材の応力腐食割れの原因となるた
め、塩素イオンはできるだけ除去することが望ましい。
2. Description of the Related Art In a conventional make-up water production system for a steam turbine, removal of organic compounds, especially organic chlorine compounds, is carried out by the following method.
For example, some volatile substances such as trihalomethane are subjected to aeration in a decarbonation tower or vacuum deaeration tower, and some non-volatile substances such as humic acid and pesticides are aggregated and precipitated, filtered, activated carbon adsorption and ion exchange. Has been removed. But,
The conventional make-up water production apparatus cannot completely remove these organic compounds and organic chlorine compounds, and has a TOC of 30 to 50.
About ppb and about 5 to 10 ppb of organic chlorine such as trihalomethane remain, which causes various problems. For example, in a PWR-type nuclear power plant, if chlorine ions are contained in the condensed water of the turbine, it causes stress corrosion cracking of stainless steel in the steam generator. Therefore, it is desirable to remove chlorine ions as much as possible.

【0003】また、補給水中に有機塩素化合物が含まれ
ると蒸気発生器で分解されて塩素イオンを発生するた
め、上記問題を生じる。更に、有機物も分解してカルボ
ン酸等の有機酸になるため、含まれない方がよい。
[0003] Further, if an organic chlorine compound is contained in makeup water, it is decomposed by a steam generator to generate chlorine ions, thus causing the above problem. Furthermore, organic substances are also decomposed into organic acids such as carboxylic acids, so that it is better not to include them.

【0004】一方、逆浸透膜装置を用いることにより、
一般的な有機化合物は除去できるが、トリハロメタン等
の低分子有機塩素化合物は除去できない。
On the other hand, by using a reverse osmosis membrane device,
General organic compounds can be removed, but low molecular organic chlorine compounds such as trihalomethane cannot be removed.

【0005】[0005]

【発明が解決しようとする課題】本発明は上記問題を解
決するためになされたもので、その目的とする所は有機
塩素化合物の含有量の極めて低い補給水を供給すること
のできる発電所用補給水製造装置を提供することにあ
る。
SUMMARY OF THE INVENTION The present invention has been made in order to solve the above-mentioned problems, and an object of the present invention is to supply a replenishing water for a power plant capable of supplying make-up water having an extremely low content of an organic chlorine compound. It is to provide a water production device.

【0006】[0006]

【課題を解決するための手段】上記目的を達成するため
に、本発明は、紫外線酸化装置と、イオン交換装置とを
連設してなり、紫外線酸化装置に前処理水を供給してこ
れに紫外線を照射することにより前処理水中の低分子有
機塩素化合物を分解後イオン交換装置に送り、このイオ
ン交換装置で前記分解による分解生成物を除去してイオ
ン交換装置から補給水を取り出すように構成した蒸気タ
ービン用の発電所用補給水製造装置に関するもので
、また本発明は、イオン交換装置と、紫外線酸化装置
と、非再生型イオン交換装置とを順次連設してなり、前
処理水をイオン交換装置に供給して前処理水中のイオン
を除去後、紫外線酸化装置に送りここで紫外線を照射す
ることにより低分子有機塩素化合物を分解し、次いで非
再生型イオン交換装置で分解生成物を除去して非再生型
イオン交換装置から補給水を取り出すように構成した蒸
気タービン用の発電所用補給水製造装置に関するもので
ある。
In order to achieve the above object, the present invention comprises an ultraviolet oxidizer and an ion exchange device connected to each other. Low molecular content in pre-treated water by irradiating ultraviolet rays
A steam tank configured to send a chlorine compound to an ion exchange device after being decomposed, remove the decomposition products of the decomposition by the ion exchange device, and take out makeup water from the ion exchange device .
Oh those related to power plants supply water production apparatus for a turbine
In addition, the present invention comprises an ion exchanger, an ultraviolet oxidizer, and a non-regenerative ion exchanger, which are sequentially connected, and supplies pretreated water to the ion exchanger to remove ions in the pretreated water. Then, it is sent to an ultraviolet oxidizer, where it is irradiated with ultraviolet rays to decompose the low-molecular-weight organic chlorine compounds, and then the decomposition products are removed by a non-regeneration type ion exchange device, and makeup water is taken out from the non-regeneration type ion exchange device. Steam configured as
Those about the power plant makeup water production apparatus for a gas turbine.

【0007】以下、図面を参照して本発明を詳細に説明
する。
Hereinafter, the present invention will be described in detail with reference to the drawings.

【0008】図1はPWR型原子力発電プラントに組込
んだ本発明の一実施態様を示すフロー図であり、図中二
点鎖線aで囲まれた部分が本発明の一実施態様の構成を
示している。
FIG. 1 is a flow chart showing one embodiment of the present invention incorporated in a PWR type nuclear power plant. A portion surrounded by a two-dot chain line a in the drawing shows the configuration of one embodiment of the present invention. ing.

【0009】図中2は原子炉、4は蒸気発生器、6はタ
ービン、8は発電機、10は復水器、12は復水濾過装
置、14は復水脱塩装置、16は給水ポンプである。
In the drawing, reference numeral 2 denotes a nuclear reactor, 4 denotes a steam generator, 6 denotes a turbine, 8 denotes a generator, 10 denotes a condenser, 12 denotes a condensate filtration device, 14 denotes a condensate desalination device, and 16 denotes a feedwater pump. It is.

【0010】蒸気発生器4で発生した蒸気はタービン6
を動かした後、復水器10で復水になり蒸気発生器4へ
返送されるが、復水は長期間の運転で徐々に散逸し、減
少する。この復水の減少分は補給水タンク18内の補給
水で補われる。
[0010] The steam generated by the steam generator 4 is supplied to a turbine 6.
Is operated, the condensate is condensed by the condenser 10 and returned to the steam generator 4, but the condensate is gradually dissipated and reduced over a long period of operation. The reduced amount of the condensed water is supplemented by the makeup water in the makeup water tank 18.

【0011】以下、本発明の補給水の製造装置の一実施
態様を説明する。
An embodiment of the makeup water producing apparatus of the present invention will be described below.

【0012】図1中20は前処理装置で、補給水製造原
料の工業用水や井水等がこの装置に送られ、ここで凝集
沈殿装置、濾過装置、2床3塔式の純水製造装置等の組
合せによって常法により前処理される。
In FIG. 1, reference numeral 20 denotes a pretreatment device, which supplies industrial water, well water, etc., as a raw material for making-up water, to a coagulating sedimentation device, a filtration device, a two-bed, three-column type pure water production device. And the like, and is pretreated by a conventional method.

【0013】このようにして前処理がなされた前処理水
は紫外線酸化装置22に送られる。なお前処理装置の後
段に必要に応じて逆浸透膜装置を設置することもでき
る。
The pretreated water thus pretreated is sent to the ultraviolet oxidizer 22. In addition, a reverse osmosis membrane device can be installed as necessary at the subsequent stage of the pretreatment device.

【0014】前処理水はここで紫外線が照射されて、前
処理水中に含まれている有機塩素化合物を含む有機化合
物が有機酸、炭酸、塩素イオンその他に分解される。紫
外線を照射する紫外線灯としては、発生する紫外線の主
波長がそれぞれ365nm、254nm、(185nm
+254nm)の三種類の紫外線灯が製造されている
が、補給水の様な低濃度の有機物を更に分解するために
は、主波長が185nm254nmであるいわゆ
る低圧紫外線灯が適している。
The pre-treated water is irradiated with ultraviolet rays to decompose organic compounds containing organic chlorine compounds contained in the pre-treated water into organic acids, carbonic acid, chloride ions and the like. As an ultraviolet lamp for irradiating ultraviolet rays, the main wavelengths of the generated ultraviolet rays are 365 nm, 254 nm, and (185 nm , respectively).
Although three types of ultraviolet lamps ( +254 nm ) are manufactured, a so-called low-pressure ultraviolet lamp having a main wavelength of ( 185 nm + 254 nm ) is suitable for further decomposing low-concentration organic substances such as makeup water. .

【0015】上記のように紫外線照射をすることによ
り、各種の有機物は分解されるが、特にトリクロロメタ
ン、ジクロロブロモメタン等のトリハロメタン、その他
トリクロロエチレン、テトラクロロエチレン、1,1,
1−トリクロロエタン等の低分子有機塩素化合物が効率
良く分解される。一般の有機化合物は逆浸透膜装置であ
る程度除去できるが、トリハロメタン等の有機塩素化合
物は逆浸透膜装置では除去し難いものである。本発明装
置によれば、逆浸透膜装置では除去困難なトリハロメタ
ンも除去できることが特長である。
Various organic substances are decomposed by the irradiation of ultraviolet rays as described above. In particular, trihalomethanes such as trichloromethane and dichlorobromomethane, and other trichloroethylene, tetrachloroethylene, 1,1,1,2
Low molecular weight organic chlorine compounds such as 1-trichloroethane are efficiently decomposed. General organic compounds can be removed to some extent with a reverse osmosis membrane device, but organic chlorine compounds such as trihalomethane are difficult to remove with a reverse osmosis membrane device. According to the apparatus of the present invention, a feature is that trihalomethane, which is difficult to remove with a reverse osmosis membrane apparatus, can also be removed.

【0016】紫外線を照射された照射水は、次いで紫外
線酸化装置22の後段に配設されたイオン交換装置24
に送られ、ここで前記紫外線照射によって生成した照射
水中の塩素イオン、有機酸、炭酸等が除去される。
The irradiation water irradiated with the ultraviolet light is then supplied to an ion exchange device 24 disposed downstream of the ultraviolet oxidation device 22.
Where the chlorine ions, organic acids, carbonic acid, and the like in the irradiation water generated by the ultraviolet irradiation are removed.

【0017】イオン交換装置としては従来から補給水の
製造に用いられており、付帯設備として再生設備を有す
る、アニオン交換樹脂とカチオン交換樹脂との混床式イ
オン交換装置や、カチオン交換塔及びアニオン交換塔か
らなる複床式イオン交換装置(カチオン交換塔とアニオ
ン交換塔の順序に制限はない)等のいわゆる純水製造装
置を使用するか、あるいは再生設備を有しない非再生型
の混床式イオン交換装置を使用するとよいが、場合によ
ってはアニオン交換塔単独の単床式イオン交換装置を使
用することもできる。
The ion exchange apparatus has been conventionally used in the production of make-up water, and has a mixed bed type ion exchange apparatus of an anion exchange resin and a cation exchange resin, which has a regeneration facility as an incidental equipment, a cation exchange column and an anion exchange resin. Use a so-called pure water production device such as a double bed ion exchange device comprising an exchange column (the order of the cation exchange column and the anion exchange column is not limited), or use a non-regenerative mixed bed type without regeneration equipment Although an ion exchange device is preferably used, a single bed ion exchange device having an anion exchange column alone may be used in some cases.

【0018】イオン交換装置を通過し取り出される水の
有機化合物及び上記各種イオンの含有量は極めて低く、
この水は補給水として、補給水タンク18に送られ、以
後は前述のように必要に応じて復水器10に送られ、散
逸する復水の補給に利用される。
The content of the organic compounds of water and the various ions described above which are taken out through the ion exchanger is extremely low.
This water is sent to the make-up water tank 18 as make-up water, and thereafter sent to the condenser 10 as needed, as described above, to be used for making up the condensed water.

【0019】なお、上記態様においては発電プラントと
してPWR型子力発電プラントを用いて説明をしたが
これに限られず、BWR型原子力発電プラント、火力発
電プラントにも同様に用いられるものである。
[0019] In the above embodiment has been described with reference to PWR type nuclear power plant as a power plant, but not limited to, BWR nuclear power plant, and is used as well to the thermal power plant.

【0020】図2は本発明の他の実施態様を示すもの
で、図中二点鎖線aで囲まれた領域にその構成例を示し
ている。
FIG. 2 shows another embodiment of the present invention. An example of the configuration is shown in a region surrounded by a two-dot chain line a in the figure.

【0021】この態様においては、前処理装置20で前
処理された前処理水は、まずイオン交換装置26に送ら
れる。このイオン交換装置26は補給水の製造に従来か
ら用いられているものと同じでよく、アニオン交換樹脂
とカチオン交換樹脂とを適宜混合した混床式イオン交換
装置や、カチオン交換塔及びアニオン交換塔からなる複
床式イオン交換装置であって、再生設備を有するものが
使用される。
In this embodiment, the pretreated water pretreated by the pretreatment device 20 is first sent to the ion exchange device 26. The ion exchange device 26 may be the same as that conventionally used for the production of makeup water, and may be a mixed-bed ion exchange device in which an anion exchange resin and a cation exchange resin are appropriately mixed, a cation exchange column and an anion exchange column. A double-bed ion exchange apparatus having a regeneration facility is used.

【0022】上記イオン交換装置で前処理水中のイオン
を除去された脱イオン水は、次いで紫外線酸化装置22
に送られ、ここで紫外線照射され、有機塩素化合物を含
む有機化合物が分解され、塩素イオン、有機酸、炭酸等
を生成すること及び紫外線酸化装置22の構成等は前記
の実施態様と同様である。
The deionized water from which ions in the pretreatment water have been removed by the above-mentioned ion exchange device is then sent to the ultraviolet oxidizing device 22.
Is irradiated with ultraviolet rays to decompose an organic compound containing an organic chlorine compound to generate chlorine ions, organic acids, carbonic acid, etc., and the configuration of the ultraviolet oxidizing apparatus 22 is the same as that of the above-described embodiment. .

【0023】紫外線照射された照射水は、次いで非再生
型のイオン交換装置28に流入する。この交換装置28
は、塔内に、予じめ外部で再生されたカチオン交換樹脂
とアニオン交換樹脂との混合樹脂を充填した、いわゆる
カートリッジポリシャーと称されるもので、現場で再生
処理を行なわずに、カートリッジタイプで交換して使用
される非再生型のイオン交換装置である。なお、この装
置28としては照射水がその内部を通過すると照射水中
の分解生成物を除去することができるとともに、所定の
Na/Clのモル比の処理水が得られるように、アニオ
ン及びカチオンのイオン交換樹脂組成が調整されたもの
を充填したものが好ましい。その場合、Na/Clのモ
ル比は0.5±0.2の範囲に設定することが好まし
く、このようにすることにより、復水の循環経路内の腐
蝕を有効に防止できる。この効果は特にPWR発電プラ
ントにおいて著しいものである。
The irradiation water irradiated with the ultraviolet rays then flows into a non-regeneration type ion exchange device 28. This exchange device 28
Is a so-called cartridge polisher in which a mixed resin of a cation exchange resin and an anion exchange resin that has been regenerated outside in advance is filled in a tower. This is a non-regeneration type ion exchange device that is used by exchanging it. When the irradiation water passes through the inside of the apparatus 28, decomposition products in the irradiation water can be removed, and anion and cations are removed so that treated water having a predetermined Na / Cl molar ratio can be obtained. A resin filled with a resin having an adjusted ion exchange resin composition is preferable. In this case, the molar ratio of Na / Cl is preferably set in a range of 0.5 ± 0.2. By doing so, corrosion in the condensate circulation path can be effectively prevented. This effect is particularly significant in PWR power plants.

【0024】非再生型イオン交換装置28で塩素イオン
や炭酸等の分解生成物が除去され、及びNa/Clのモ
ル比が調整された処理水は、その後補給水タンク18に
送られ、以後は前述と同様に復水の補給に用いられもの
である。
The treated water from which decomposition products such as chlorine ions and carbonic acid have been removed by the non-regenerating ion exchange device 28 and the molar ratio of Na / Cl has been adjusted is then sent to the makeup water tank 18 and thereafter. It is used to supply condensate water as described above.

【0025】以下、実施例により本発明を具体的に説明
する。
Hereinafter, the present invention will be described in detail with reference to examples.

【0026】[0026]

【実施例】【Example】

実施例1 前処理装置から送られる前処理水を逆浸透膜装置で処理
して透過水を得、得られた透過水を流量80m3 /hで
紫外線酸化装置に送り、ここで0.35kWh/m3
紫外線を照射した後、再生設備を有する、すなわち再生
型の混床式イオン交換装置を通過させた。混床式イオン
交換装置は強酸性カチオン交換樹脂アンバーライト(登
録商標)200CTと強塩基性アニオン交換樹脂アンバ
ーライトIRA−900とを体積比で1:1で混合した
ものであった。イオン交換装置の出口水の含有成分の分
析を行なって表1の結果を得た(実施例1)。
Example 1 Pretreated water sent from a pretreatment device was treated with a reverse osmosis membrane device to obtain permeated water, and the obtained permeated water was sent to an ultraviolet oxidation device at a flow rate of 80 m 3 / h, where 0.35 kWh / After irradiation with ultraviolet light of m 3, the mixture was passed through a regeneration-type mixed-bed type ion exchange apparatus having regeneration equipment. The mixed bed type ion exchange apparatus was a mixture of a strongly acidic cation exchange resin Amberlite (registered trademark) 200CT and a strongly basic anion exchange resin Amberlite IRA-900 at a volume ratio of 1: 1. The components contained in the outlet water of the ion exchange device were analyzed to obtain the results shown in Table 1 (Example 1).

【0027】比較のため、紫外線酸化装置を通さない以
外は全く同様に操作した場合の分析結果を表1に示した
(比較例)。
For comparison, the results of analysis performed in exactly the same manner except that the ultraviolet light was not passed through the ultraviolet oxidation apparatus are shown in Table 1 (Comparative Example).

【0028】[0028]

【表1】 * いずれも測定下限値以下。 表1に示す様に、本発明の装置によれば補給水中の有機
物および有機塩素化合物を測定下限値以下まで低減する
ことができた。 実施例2及び3 前処理装置から送られる前処理水を流量100m3 /h
で再生型の混床式イオン交換装置に通水し、次いで得ら
れた純水を紫外線酸化装置に送り、ここで0.35kW
h/m3 の紫外線を照射した。なお、上記再生型のイオ
ン交換装置は強酸性カチオン交換樹脂アンバーライト2
00CTと強塩基性アニオン交換樹脂アンバーライトI
RA−900とを体積比で1:1で混合したものであっ
た。次いで、紫外線を照射された照射水を2分割し、そ
の一方を、イオン組成を特に調整していないH形のカチ
オン交換樹脂とOH形のアニオン交換樹脂との混合樹脂
を充填してなる通常の非再生型混床式イオン交換装置に
通水し(実施例2)、照射水の他方を、Na形樹脂の含
有率が0.1%(当量%、以下同じ)でH形樹脂の含有
率が99.9%となるようにイオン組成を調整した強酸
性カチオン交換樹脂と、OH形樹脂の含有率が96.0
%で、Cl形樹脂の含有率が4.0%となるようにイオ
ン組成を調整した強塩基性アニオン交換樹脂との混合樹
脂を充填してなるモル比調整用の非再生型混床式イオン
交換装置に通水した(実施例3)。
[Table 1] * Both are below the lower limit of measurement. As shown in Table 1, according to the apparatus of the present invention, the amount of organic substances and organic chlorine compounds in the makeup water could be reduced to below the lower limit of measurement. Examples 2 and 3 The pretreatment water sent from the pretreatment device was supplied at a flow rate of 100 m 3 / h.
, And water is passed through a regenerative mixed-bed ion exchanger, and then the obtained pure water is sent to an ultraviolet oxidizer, where it is 0.35 kW.
h / m 3 of ultraviolet light was applied. The regenerative ion exchange apparatus is a strongly acidic cation exchange resin Amberlite 2
00CT and strongly basic anion exchange resin Amberlite I
RA-900 was mixed at a volume ratio of 1: 1. Next, the irradiation water irradiated with ultraviolet rays is divided into two parts, and one of the two parts is filled with a mixed resin of an H-type cation exchange resin and an OH-type anion exchange resin whose ionic composition is not particularly adjusted. Water is passed through a non-regenerative mixed-bed ion exchange apparatus (Example 2), and the other part of the irradiated water is 0.1% (equivalent%, hereinafter the same) of the H-type resin content of the Na-type resin. Is 99.9%, and the content of the strongly acidic cation exchange resin whose ionic composition is adjusted and the OH type resin is 96.0.
% Of a non-regenerating mixed bed type ion for adjusting a molar ratio, which is filled with a mixed resin with a strongly basic anion exchange resin whose ionic composition is adjusted so that the content of Cl-type resin is 4.0%. Water was passed through the exchange device (Example 3).

【0029】なお、上記2種類の非再生型のイオン交換
装置に使用したイオン交換樹脂は、いずれの場合も前記
再生型のイオン交換装置の場合と同じアンバーライト2
00CT(強酸性カチオン交換樹脂)とアンバーライト
IRA−900(強塩基性アニオン交換樹脂)であり、
また両樹脂の混合比はいずれの場合も(カチオン交換樹
脂:アニオン交換樹脂)=9:10(体積比)であっ
た。
The ion exchange resin used in the above two types of non-regenerative ion exchangers was the same as that of the regenerative ion exchangers in both cases.
00CT (strongly acidic cation exchange resin) and Amberlite IRA-900 (strongly basic anion exchange resin)
The mixing ratio of both resins was (cation exchange resin: anion exchange resin) = 9: 10 (volume ratio) in each case.

【0030】上記2種類の非再生型混床式イオン交換装
置の出口水の水質分析結果を表2に示した。
Table 2 shows the results of water quality analysis of the outlet water of the above two types of non-regenerative mixed-bed type ion exchangers.

【0031】[0031]

【表2】 * いずれも測定下限値以下であることを示す。 表2に示す様に、実施例2および3ともに補給水中の有
機物および有機塩素化合物を測定下限値以下まで低減す
ることができた。また非再生型イオン交換装置として、
所定のNa/Clモル比の出口水(処理水)が得られる
ようにカチオン交換樹脂、及びアニオン交換樹脂のイオ
ン組成を予じめ調整した混合樹脂を充填してなる、モル
比調整用の非再生型イオン交換装置を用いた場合(実施
例3)は、有機物及び有機塩素化合物が測定下限値以下
まで低減され、かつNa/Clモル比が所定値(0.5
±0.2)に調整された補給水を得ることができた。
[Table 2] * In each case, it is below the lower limit of measurement. As shown in Table 2, both Examples 2 and 3 were able to reduce the amount of organic substances and organic chlorine compounds in the makeup water to below the lower limit of measurement. In addition, as a non-regenerative ion exchange device,
A cation exchange resin and a mixed resin in which the ionic composition of the anion exchange resin has been adjusted in advance so as to obtain outlet water (treated water) having a predetermined Na / Cl molar ratio are prepared. When a regenerative ion exchange device was used (Example 3), the amount of organic substances and organic chlorine compounds was reduced to the lower limit of measurement or lower, and the Na / Cl molar ratio was reduced to a predetermined value (0.5
Makeup water adjusted to ± 0.2) could be obtained.

【0032】[0032]

【発明の効果】本発明によれば、従来の方法では除去が
困難なトリハロメタン等の低分子有機塩素化合物が効率
良く除去でき、このため従来問題であったこれら有機塩
素化合物の分解により生成する塩素イオンが原因となる
発電プラントの復水の循環経路の腐蝕が防止できる。
According to the present invention, low-molecular-weight organic chlorine compounds such as trihalomethane, which are difficult to remove by the conventional method, can be efficiently removed. Corrosion of the circulation path of the condensate of the power plant caused by ions can be prevented.

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

【図1】本発明の一実施態様を組込んだ原子力発電プラ
ントのフロー図である。
FIG. 1 is a flow diagram of a nuclear power plant incorporating one embodiment of the present invention.

【図2】本発明の他の実施態様を示すフロー図である。FIG. 2 is a flowchart showing another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

22 紫外線酸化装置 24 イオン交換装置 26 イオン交換装置 28 非再生型イオン交換装置 Reference Signs List 22 UV oxidation device 24 Ion exchange device 26 Ion exchange device 28 Non-regenerative ion exchange device

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C02F 1/32 C02F 1/32 1/42 1/42 A 1/58 CDV 1/58 CDVA (58)調査した分野(Int.Cl.6,DB名) C02F 9/00 502 - 504 C02F 1/32 C02F 1/42 C02F 1/58 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification symbol FI C02F 1/32 C02F 1/32 1/42 1/42 A 1/58 CDV 1/58 CDVA (58) Investigated field (Int. Cl. 6 , DB name) C02F 9/00 502-504 C02F 1/32 C02F 1/42 C02F 1/58

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 紫外線酸化装置と、イオン交換装置とを
連設してなり、紫外線酸化装置に前処理水を供給してこ
れに紫外線を照射することにより前処理水中の低分子有
機塩素化合物を分解後イオン交換装置に送り、このイオ
ン交換装置で前記分解による分解生成物を除去してイオ
ン交換装置から補給水を取り出すように構成した蒸気タ
ービン用の発電所用補給水製造装置。
1. An ultraviolet oxidizing device and an ion exchange device are connected to each other, and the pretreated water is supplied to the ultraviolet oxidizing device and irradiated with ultraviolet light, whereby low-molecular-weight components in the pretreated water are provided.
A steam tank configured to send a chlorine compound to an ion exchange device after being decomposed, remove the decomposition products of the decomposition by the ion exchange device, and take out makeup water from the ion exchange device .
-A make- up water production system for power plants for bins .
【請求項2】 イオン交換装置と、紫外線酸化装置と、
非再生型イオン交換装置とを順次連設してなり、前処理
水をイオン交換装置に供給して前処理水中のイオンを除
去後、紫外線酸化装置に送りここで紫外線を照射するこ
とにより低分子有機塩素化合物を分解し、次いで非再生
型イオン交換装置で分解生成物を除去して非再生型イオ
ン交換装置から補給水を取り出すように構成した蒸気タ
ービン用の発電所用補給水製造装置。
2. An ion exchange device, an ultraviolet oxidation device,
A non-regenerating type ion exchange device is connected in series, and the pretreatment water is supplied to the ion exchange device to remove ions in the pretreatment water, and then sent to an ultraviolet oxidation device where it is irradiated with ultraviolet rays to emit low-molecular A steam tank configured to decompose an organochlorine compound , then remove decomposition products by a non-regenerative ion exchanger, and take out makeup water from the non-regenerative ion exchanger .
-A make- up water production system for power plants for bins .
JP5042941A 1993-03-03 1993-03-03 Makeup water production equipment for power plants Expired - Fee Related JP2968901B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5042941A JP2968901B2 (en) 1993-03-03 1993-03-03 Makeup water production equipment for power plants

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5042941A JP2968901B2 (en) 1993-03-03 1993-03-03 Makeup water production equipment for power plants

Publications (2)

Publication Number Publication Date
JPH06254596A JPH06254596A (en) 1994-09-13
JP2968901B2 true JP2968901B2 (en) 1999-11-02

Family

ID=12650044

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5042941A Expired - Fee Related JP2968901B2 (en) 1993-03-03 1993-03-03 Makeup water production equipment for power plants

Country Status (1)

Country Link
JP (1) JP2968901B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3922935B2 (en) * 2002-02-20 2007-05-30 オルガノ株式会社 Water treatment system
JP2009162514A (en) * 2007-12-28 2009-07-23 Japan Organo Co Ltd System for purifying system water in secondary system of nuclear power plant with pressurized water reactor
JP5097933B2 (en) * 2008-02-29 2012-12-12 独立行政法人科学技術振興機構 Method and apparatus for decomposing hardly decomposable organic substances using both ultraviolet rays and fine bubbles

Also Published As

Publication number Publication date
JPH06254596A (en) 1994-09-13

Similar Documents

Publication Publication Date Title
JPH0490885A (en) Apparatus and method for making pure water
JPH0720597B2 (en) Water treatment method and water treatment apparatus thereof
JPH1199395A (en) Treatment of organic matter containing water
JP5512357B2 (en) Pure water production method and apparatus
JPH0818040B2 (en) Purification method and device for pure water or ultrapure water
JP4635827B2 (en) Ultrapure water production method and apparatus
JP2968901B2 (en) Makeup water production equipment for power plants
JPH1199394A (en) Method for removing organic matter in water
JP3506171B2 (en) Method and apparatus for removing TOC component
JPH10309588A (en) Water treatment, water treating device and pure water producing device
JP7538361B2 (en) Method for removing trace amounts of low molecular weight organic matter from reclaimed water
JP3560631B2 (en) Water treatment equipment
JPH09122690A (en) Method for decomposing organic nitrogen and water treatment apparatus
JPH09253638A (en) Ultrapure water making apparatus
US5958247A (en) Method for disposing of a solution containing an organic acid
JP3645007B2 (en) Ultrapure water production equipment
JPH0639366A (en) Method and equipment for producing ultrapure water
JPH10277572A (en) Removal of organic matter in water
JP3313549B2 (en) Decomposition and removal method of organic matter in chloride ion-containing wastewater
JP3259557B2 (en) How to remove organic matter
JPH0889976A (en) Method for removing organic matter in water
JP3045911B2 (en) Water treatment method for nuclear power plant
JPH1128482A (en) Production of pure water
JPH05293494A (en) Apparatus for producing pure water
JPH1094785A (en) Ultrapure water producing method and device therefor

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080820

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080820

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090820

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090820

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100820

Year of fee payment: 11

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110820

Year of fee payment: 12

LAPS Cancellation because of no payment of annual fees