JPH08304587A - Reactor purification device - Google Patents

Reactor purification device

Info

Publication number
JPH08304587A
JPH08304587A JP7115482A JP11548295A JPH08304587A JP H08304587 A JPH08304587 A JP H08304587A JP 7115482 A JP7115482 A JP 7115482A JP 11548295 A JP11548295 A JP 11548295A JP H08304587 A JPH08304587 A JP H08304587A
Authority
JP
Japan
Prior art keywords
reactor
conductivity
exchange resin
water
anion
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
JP7115482A
Other languages
Japanese (ja)
Inventor
Hiroo Igarashi
裕夫 五十嵐
Nobuyuki Ota
信之 太田
Toshihiko Fukumoto
俊彦 福本
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 Ltd
Hitachi Industry and Control Solutions Co Ltd
Original Assignee
Hitachi Engineering Co Ltd Ibaraki
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 Ibaraki, Hitachi Ltd filed Critical Hitachi Engineering Co Ltd Ibaraki
Priority to JP7115482A priority Critical patent/JPH08304587A/en
Publication of JPH08304587A publication Critical patent/JPH08304587A/en
Pending legal-status Critical Current

Links

Classifications

    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00—Energy generation of nuclear origin
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00—Energy generation of nuclear origin
    • Y02E30/30—Nuclear fission reactors

Landscapes

  • Treatment Of Water By Ion Exchange (AREA)

Abstract

(57)【要約】 【構成】給水装置1より原子炉2に持込まれる不純物
は、原子炉2内で分解又はそのまま沸騰濃縮されるので
原子炉水ろ過脱塩装置8で浄化する。原子炉内のイオン
性不純物は陽イオン種と陰イオン種に分けられるので、
その性状をサンプリング装置9の導電率計及びpH計に
より検出し、それらの比(当量)に応じた粉末又は繊維
状アニオン及びカチオン交換樹脂をプリコートタンク1
1より原子炉水ろ過脱塩装置8へプリコートし炉水を浄
化する。 【効果】原子炉浄化装置の逆洗頻度が1/2以下になる
ことにより原子炉水を浄化した比較的放射能の高い放射
性廃棄物を半減可能とした。
(57) [Summary] [Structure] Impurities brought into the reactor 2 from the water supply device 1 are decomposed in the reactor 2 or are boiled and concentrated as they are, so that they are purified by the reactor water filtration desalination device 8. Ionic impurities in the reactor can be divided into cation and anion species.
The property is detected by the conductivity meter and the pH meter of the sampling device 9, and the powder or fibrous anion and cation exchange resin according to the ratio (equivalent) thereof is added to the precoat tank 1
From 1, the reactor water filtration desalination apparatus 8 is pre-coated to purify the reactor water. [Effect] By reducing the backwashing frequency of the reactor cleaning device to 1/2 or less, it has been possible to halve the relatively high radioactive waste that has purified the reactor water.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は原子炉浄化装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a reactor cleaning device.

【0002】[0002]

【従来の技術】現在、原子炉水の浄化は原子炉ろ過脱塩
装置により給水流量に対する割合としてプラントにより
異なり1〜7%の範囲で行っている。周知のように沸騰
水型原子力プラントは、給水装置等より原子炉へ流入す
る又は炉内で発生する不純物は極一部の揮発性物質を除
き蒸気中へは移行せず炉内に蓄積することになる。金属
の腐食生成物であるクラッドは、沸騰面を持つ燃料棒上
に90%程度固着するため、原子炉水中に存在する濃度
は低いが、イオン状で原子炉水に溶解している不純物
は、燃料棒には付着しないため、原子炉水の高純度化を
達成するには、前述の給水流量比を大きい仕様とすれば
良い。しかしプラントの熱効率の面からは原子炉ろ過脱
塩装置で浄化するため、イオン交換樹脂の耐熱性上の制
約から約50℃まで炉水を冷却せねばならず得策ではな
い。一方、原子炉水ろ過脱塩装置にプリコートする陽イ
オン交換樹脂と陰イオン交換樹脂、多くの場合、粉末ま
たは繊維状であるが、これら樹脂の樹脂比は原子炉水不
純物の組成によらず1:1と一定である。実際の原子炉
水は混入する不純物によりイオン組成が多様で一率に決
定できるものではない。例えば、定期検査終了後のプラ
ント起動時にはステンレス鋼からの溶出物であるCrO
4 2- (クロム酸イオン)が支配的で、陰イオン樹脂が急
激に消費されることになる。その結果、陰イオン樹脂ブ
レークにより原子炉浄化装置出口の導電率が上昇し逆
洗,再プリコートを行うことになる。
2. Description of the Related Art At present, purification of nuclear reactor water is performed by a reactor filtration desalination apparatus within a range of 1 to 7% as a ratio to the feed water flow rate, which varies depending on the plant. As is well known, in a boiling water nuclear power plant, impurities that flow into the reactor from a water supply device or that are generated in the reactor must be accumulated in the reactor without moving to steam except for a very small amount of volatile substances. become. The clad, which is a corrosion product of metal, adheres to a fuel rod having a boiling surface by about 90%, so the concentration in the reactor water is low, but the impurities dissolved in the reactor water in the ionic form are Since it does not adhere to the fuel rods, in order to achieve high purification of the reactor water, the above-mentioned feed water flow rate ratio may be set to a large specification. However, from the viewpoint of the thermal efficiency of the plant, since it is purified by a reactor filtration desalination apparatus, the reactor water must be cooled to about 50 ° C. due to the heat resistance limitation of the ion exchange resin, which is not a good idea. On the other hand, a cation exchange resin and an anion exchange resin to be pre-coated on a reactor water filtration desalination apparatus, which are often powdery or fibrous, have a resin ratio of 1 regardless of the composition of reactor water impurities. : 1 is constant. In actual reactor water, the ionic composition varies depending on the impurities that are mixed in, and cannot be determined in a uniform manner. For example, when starting the plant after the completion of the periodic inspection, CrO, which is an eluate from stainless steel,
4 2- (Chromate ion) is predominant, and the anionic resin is consumed rapidly. As a result, the conductivity of the reactor cleaning apparatus outlet increases due to the anion resin break, and backwashing and reprecoating are performed.

【0003】また、通常運転中は復水浄化装置に使用さ
れている粒状イオン交換樹脂の逆再生によりR−H+ と
なっているべき樹脂がR−Na+ と再生剤を保持してい
る場合があり、その場合は、運転中に炉水へNa+ が定
常的に流入してくる。陽イオン交換樹脂への負荷が増加
しイオンブレークによる逆洗再プリコートとなる。この
ように現状の原子炉水ろ過脱塩装置への陽イオン/陰イ
オン交換樹脂の供給は、原子炉水のイオン組成とは無関
係に設定されているため、まだ消費していないイオン交
換樹脂も逆洗廃棄することとなり、放射性廃棄物の増加
に直結し、また運転に要する費用も増加する。
Also, during normal operation, when the resin that should be R-H + due to reverse regeneration of the granular ion exchange resin used in the condensate purification device holds R-Na + and the regenerant. In that case, Na + constantly flows into the reactor water during operation. The load on the cation exchange resin increases, and the backwash reprecoating is performed by ion break. In this way, the supply of cation / anion exchange resin to the existing reactor water filtration desalination equipment is set independently of the ionic composition of the reactor water, so that even ion exchange resin that has not yet been consumed can be used. It will be backwashed and discarded, which will directly increase the amount of radioactive waste and also increase the cost required for operation.

【0004】[0004]

【発明が解決しようとする課題】本発明の目的は、原子
炉浄化装置ろ過脱塩装置の逆洗頻度低減の具体的な手法
を確立し、原子力プラントの放射性廃棄物を低減するこ
とにある。
SUMMARY OF THE INVENTION An object of the present invention is to establish a concrete method for reducing the backwashing frequency of a reactor decontamination apparatus filter desalination apparatus, and to reduce radioactive waste in a nuclear power plant.

【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、本発明は原子炉水のイオン組成の目安となる導電率
とpHのプラントデータに基づき陽イオン導電率,陰イ
オン導電率を算出しその比に適した粉末または繊維状イ
オン交換樹脂を原子炉水ろ過脱塩装置にプリコートする
システムを提供する。
In order to achieve the above object, the present invention calculates cation conductivity and anion conductivity based on plant data of conductivity and pH, which are indicators of ionic composition of reactor water. Provided is a system for precoating a reactor water filtration desalination apparatus with a powder or fibrous ion exchange resin suitable for the ratio.

【0006】また、プリコートしたイオン交換樹脂の採
水寿命を評価することにより逆洗準備等運用管理の合理
化も図れる。
In addition, by evaluating the water collection life of the pre-coated ion exchange resin, it is possible to rationalize operational management such as backwash preparation.

【0007】[0007]

【作用】本発明によれば、原子炉水の高純度化を維持す
るために運転される原子炉浄化装置に用いられるイオン
交換樹脂が原子炉混入イオン不純物の性状、すなわち、
陽イオン種又は陰イオン種又はそれらの比率をあらかじ
め計測してプリコートされるため、イオン交換する樹脂
が最適に行われ、1プリコートあたりの採水量を多くす
ることが可能となることにより、放射性廃棄物の増加を
低減できる。
According to the present invention, the ion exchange resin used in the reactor cleaning device operated to maintain the high purity of the reactor water is characterized by the characteristics of the ionic impurities mixed in the reactor, that is,
Since cationic coating or anionic species or their ratio is pre-measured and pre-coated, the resin for ion exchange is optimally performed, and it becomes possible to increase the amount of water collected per pre-coat, which results in radioactive waste. It is possible to reduce the increase in objects.

【0008】[0008]

【実施例】本発明の実施例を図1により説明する。給水
装置1より原子炉2へ供給される給水中には、復水浄化
装置,復水貯蔵タンクなどから混入するイオン性不純物
又は復水浄化装置で使用されているイオン交換樹脂から
の劣化物等を含む。これら不純物は原子炉2内の沸騰に
より濃縮される。濃縮された原子炉水を浄化し純度を維
持するために原子炉再循環装置3より分岐した原子炉浄
化装置4がある。
EXAMPLE An example of the present invention will be described with reference to FIG. In the feed water supplied from the water supply device 1 to the reactor 2, ionic impurities mixed from the condensate purification device, the condensate storage tank, or the like, or deteriorated substances from the ion exchange resin used in the condensate purification device, etc. including. These impurities are concentrated by boiling in the reactor 2. There is a reactor cleaning device 4 branched from a reactor recirculation device 3 in order to clean concentrated reactor water and maintain its purity.

【0009】原子炉浄化装置4では、再生熱交換器5及
び非再生熱交換器6により冷却材の温度を低下した後、
ポンプ7により加圧され原子炉水ろ過脱塩装置8により
浄化された炉水は再び非再生熱交換器6で加熱された
後、給水装置1を経て原子炉へ供給するシステムとなっ
ている。本発明は原子炉水ろ過脱塩装置8の入口及び出
口水を採取するサンプリング装置9内に設けられた導電
率計及びpH計より炉水のカチオン導電率及びアニオン
導電率を計算する。カチオン導電率とは言うまでもなく
陽イオンによる導電率寄与分で、イオン種が不明の場合
は、Na+ イオンを不純物として考える。また、アニオ
ン導電率とは陰イオンによる導電率寄与分でイオン種が
不明の場合は、SO4--イオンを不純物として考える。
ここでNa+及びSO4-- をそれぞれ代表イオン種とし
て選定した理由は次の二つによる。すなわち、第1はNU
REG/CR5115“A Review of boiling water reactor chem
istry"としてFoxJ.M.等が米国のBWR原子炉一次
装置における不純物発生源を調査しており、それによる
と復水浄化装置等で用いられているイオン交換樹脂が3
0%,復水器海水リークが約20%等となっており、イ
オン交換樹脂の分解生成物としてのSO4-- 及び海水成
分のNa+ が代表的イオンであること、第2は導電率は
数1で与えられるが、
In the reactor cleaning device 4, after the temperature of the coolant is lowered by the regenerative heat exchanger 5 and the non-regenerative heat exchanger 6,
The system is such that the reactor water pressurized by the pump 7 and purified by the reactor water filtration / desalination device 8 is heated again by the non-regenerative heat exchanger 6 and then supplied to the reactor through the water supply device 1. According to the present invention, the cation conductivity and the anion conductivity of the reactor water are calculated from the conductivity meter and the pH meter provided in the sampling device 9 for sampling the inlet and outlet water of the reactor water filtration desalination device 8. Needless to say, cation conductivity is a contribution of conductivity by cations, and when the ionic species is unknown, Na + ions are considered as impurities. Further, anion conductivity is a contribution of conductivity by anions, and when the ionic species is unknown, SO 4 − ions are considered as impurities.
There are two reasons for selecting Na + and SO 4 --as the representative ion species. That is, the first is NU
REG / CR5115 “A Review of boiling water reactor chem
Fox JM et al. are investigating the source of impurities in primary reactors of BWR reactors in the United States as "istry", and it is found that the ion exchange resins used in condensate purification devices
0%, condenser seawater leakage has become about 20%, etc., SO 4 as decomposition products of ion exchange resins - and that the seawater components Na + is typical ion, Second Conductivity Is given by the number 1,

【0010】[0010]

【数1】 [Equation 1]

【0011】当量電導度は、水を構成するH+(349.
7S/cm・eq),OH-(200S/cm・eq)以外は50〜8
0S/cm・eq(at25℃)の範囲でほぼ同一なためであ
る。例えば化学便覧(丸善)では、アニオン種はCl-
:76.3,SO4-- :80.0,CrO4--:85、カ
チオン種はNa+:50.1,NH4+:73.5,Fe
3+:68.4 などである。
The equivalent electric conductivity is H + (349.
50-8 except 7S / cm ・ eq) and OH- (200S / cm ・ eq)
This is because they are almost the same in the range of 0 S / cm · eq (at 25 ° C). For example, in the Chemical Handbook (Maruzen), the anion species is Cl-
: 76.3, SO 4 -: 80.0 , CrO 4 -: 85, the cationic species Na +: 50.1, NH 4 + : 73.5, Fe
3 +: 68.4, and the like.

【0012】計算のフローを図2に示す。The calculation flow is shown in FIG.

【0013】ここで荷電平衡式とはHere, the charge balance equation

【0014】[0014]

【数2】 〔H+〕+〔A+〕=〔OH-〕+〔B-〕 …(数2) 〔A+〕〔B-〕:A,Bイオン濃度 また、水の解離式とは[Equation 2] [H +] + [A +] = [OH-] + [B-] (Equation 2) [A +] [B-]: A, B ion concentration

【0015】[0015]

【数3】 Kw=〔H+〕・〔OH-〕 …(数3) Kw:水のイオン積(10-14at25℃) これより各イオン濃度が求まれば、それに対応する粉末
又は繊維状のイオン交換樹脂を比率にして、プリコート
タンク11で混合し復水ろ過脱塩装置にプリコートす
る。当然のことながら、粉末又は繊維状のイオン交換樹
脂の貫流交換容量は事前に求めておきイオン交換樹脂量
(当量比)の決定はそのアニオン樹脂,カチオン樹脂の
比率に炉水陰イオン,陽イオンの比を掛けて行う。一般
に貫流交換容量はアニオン樹脂は新樹脂の中性塩交換容
量の90%,カチオン新樹脂の中性塩交換容量の60%
が目安であるが事前に実測する。
[Formula 3] Kw = [H +] · [OH-] (Formula 3) Kw: Ionic product of water (10 −14 at 25 ° C.) If each ion concentration is obtained from this, powder or fibrous form corresponding to it The ratio of the ion exchange resin is mixed in the precoat tank 11, and the condensate filtration desalination apparatus is precoated. As a matter of course, the flow-through exchange capacity of the powder or fibrous ion exchange resin is obtained in advance, and the ion exchange resin amount (equivalent ratio) is determined by the ratio of the anion resin and the cation resin to the anions and cations of the reactor water. Multiply by the ratio. Generally, the flow-through exchange capacity is 90% of the neutral salt exchange capacity of the new resin and 60% of the neutral salt exchange capacity of the cation new resin.
Is a guide, but it should be measured in advance.

【0016】実施例1におけるカチオン導電率,アニオ
ン導電率の求め方は、サンプリング装置9内に、カチオ
ン樹脂を入れたカラムを通過後の導電率をアニオン導電
率,アニオン樹脂をカラム通過後の導電率としても良
い。また、サンプリング装置9にイオンライン又はオフ
ラインのイオンクロマトグラフを付設し、イオン濃度の
直接定量により、プリコートするカチオン及びアニオン
樹脂の比率を決定しても良い。
The cation conductivity and the anion conductivity in Example 1 are determined by measuring the conductivity after passing through the column containing the cation resin in the sampling device 9 as the anion conductivity and the conductivity after passing through the anion resin through the column. Good as a rate. Alternatively, the sampling device 9 may be provided with an ion line or an off-line ion chromatograph, and the ratio of the cation and anion resin to be precoated may be determined by direct quantification of the ion concentration.

【0017】図3は本発明に係る実施例の一つである。
ここでは、サンプリング装置9により実測した水質に基
づいて、アニオン,カチオン樹脂量比を決定するのは図
1で説明したものと同じであるが、樹脂の供給方法にお
いて、いわゆるボディフィード法(BNES 6th Internati
onal Conference on water chemistry of Nuclear Rea
ctor Systems 1992“Performance Improvement of Prec
oat Type CondensateFilter”Maeda K.et al.)を用い
るものである。原子炉水ろ過脱塩装置8にあらかじめ通
常の半分程度の0.5kg(樹脂)/m2(ろ過面積)をプリ
コートしておき、残りをプリコートタンク11又は12
より原子炉水ろ過脱塩装置8入口に注入するものであ
る。ここでプリコートするイオン交換樹脂はあらかじめ
アニオン樹脂,カチオン樹脂を計算した比率混合しても
良いし、又はプリコートタンク11にカチオン樹脂,プ
リコートタンク12にアニオン樹脂を入れ別々にフィー
ドしても良い。
FIG. 3 shows one of the embodiments according to the present invention.
Here, the anion / cation resin amount ratio is determined based on the water quality measured by the sampling device 9 in the same manner as described in FIG. 1, but in the resin supply method, the so-called body feed method (BNES 6th Internati
onal Conference on water chemistry of Nuclear Rea
ctor Systems 1992 “Performance Improvement of Prec
oat Type CondensateFilter "Maeda K. et al.) The reactor water filtration desalination unit 8 is pre-coated with 0.5 kg (resin) / m 2 (filtration area) of about half of the normal size in advance. , The rest is precoat tank 11 or 12
It is injected into the inlet of the reactor water filtration desalination device 8 more. The ion exchange resin to be precoated here may be a mixture of anion resin and cation resin calculated in advance, or the cation resin may be put in the precoat tank 11 and the anion resin may be fed separately in the precoat tank 12.

【0018】[0018]

【発明の効果】本発明によれば、原子炉水の性状により
適切なろ過助剤(イオン交換樹脂)を提供するので、採
水寿命が従来のプリコート比アニオン:カチオン=1:
1に比べ、1:8又は8:1にも可能なので、2倍以上
延ばすことができる。これは、直接原子炉水を処理した
比較的高い放射能のイオン交換樹脂による廃棄物量を1
/2以下に低減可能となる。
According to the present invention, an appropriate filter aid (ion exchange resin) is provided according to the properties of the reactor water, so that the water sampling life is as long as the conventional precoat ratio anion: cation = 1: 1.
Since it can be 1: 8 or 8: 1 as compared with 1, it can be extended more than twice. This is the amount of waste generated by the ion exchange resin of relatively high radioactivity, which is obtained by directly treating the reactor water.
It can be reduced to / 2 or less.

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

【図1】原子力発電所純水化システムのブロック図。FIG. 1 is a block diagram of a water purification system for a nuclear power plant.

【図2】炉水導電率より不純物濃度を計算するフローチ
ャート。
FIG. 2 is a flowchart for calculating an impurity concentration from the reactor water conductivity.

【図3】本発明の一実施例でボディフィード法のブロッ
ク図。
FIG. 3 is a block diagram of a body feed method according to an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1…給水装置、2…原子炉、4…原子炉浄化装置、5…
再生熱交換器、6…非再生熱交換器、8…原子炉水ろ過
脱塩装置、9…サンプリング装置、11…プリコートタ
ンク。
1 ... Water supply device, 2 ... Reactor, 4 ... Reactor cleaning device, 5 ...
Regeneration heat exchanger, 6 ... Non-regeneration heat exchanger, 8 ... Reactor water filtration desalination apparatus, 9 ... Sampling apparatus, 11 ... Precoat tank.

───────────────────────────────────────────────────── 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 G21F 9/12 512 G21F 9/12 512G (72)発明者 福本 俊彦 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─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical display location G21F 9/12 512 G21F 9/12 512G (72) Inventor Toshihiko Fukumoto 3-chome, Hitachi-cho, Ibaraki Prefecture 2-1 Hitachi Engineering Co., Ltd.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】沸騰水型原子炉の原子炉水ろ過脱塩装置と
ろ過脱塩装置に粉末または繊維状の陽イオン交換樹脂ま
たは陰イオン交換樹脂を供給するプリコートタンクより
成る原子炉浄化装置において、原子炉水導電率及びpH
により陽イオン導電率及び陰イオン導電率を演算しその
比に比例する陽イオン交換樹脂と陰イオン交換樹脂を原
子炉水ろ過脱塩装置にプリコートすることを特徴とする
原子炉浄化装置。
1. A reactor cleaning apparatus comprising a reactor water filter desalting apparatus for a boiling water reactor and a precoat tank for supplying powdery or fibrous cation exchange resin or anion exchange resin to the filter desalination apparatus. , Reactor water conductivity and pH
An apparatus for purifying a nuclear reactor, characterized in that a cation exchange resin and an anion exchange resin, which are proportional to the ratio of cation conductivity and anion conductivity, are pre-coated on a reactor water filtration desalination apparatus.
【請求項2】請求項1において、陽イオン導電率と陰イ
オン導電率の比の算出する方法としてイオンクロマトグ
ラフによる各成分の定量値を用いる原子炉浄化装置。
2. The nuclear reactor purification device according to claim 1, wherein a quantitative value of each component by an ion chromatograph is used as a method of calculating the ratio of the cation conductivity and the anion conductivity.
【請求項3】請求項1において、粉末または繊維状の陽
イオン交換樹脂と陰イオン交換樹脂を原子炉水ろ過脱塩
装置にコーティングする方法として、原子炉水ろ過脱塩
装置入口の原子炉浄化装置配管に直接算出された比率の
前記イオン交換樹脂を注入する原子炉浄化装置。
3. The method for coating powdered or fibrous cation exchange resin and anion exchange resin on a reactor water filtration desalination apparatus according to claim 1, wherein the reactor water purification desalination apparatus inlet is cleaned. A reactor cleaning device that injects the ion-exchange resin in a calculated ratio directly into the device piping.
【請求項4】請求項1において、原子炉の陽イオン導電
率,陰イオン導電率をプロセス導電率及びpHより演算
しイオン交換樹脂の採水寿命を予測する原子炉浄化装
置。
4. The reactor cleaning apparatus according to claim 1, wherein the cation conductivity and the anion conductivity of the reactor are calculated from the process conductivity and the pH to predict the water sampling life of the ion exchange resin.
JP7115482A 1995-05-15 1995-05-15 Reactor purification device Pending JPH08304587A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7115482A JPH08304587A (en) 1995-05-15 1995-05-15 Reactor purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7115482A JPH08304587A (en) 1995-05-15 1995-05-15 Reactor purification device

Publications (1)

Publication Number Publication Date
JPH08304587A true JPH08304587A (en) 1996-11-22

Family

ID=14663618

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7115482A Pending JPH08304587A (en) 1995-05-15 1995-05-15 Reactor purification device

Country Status (1)

Country Link
JP (1) JPH08304587A (en)

Similar Documents

Publication Publication Date Title
JP2808970B2 (en) Nuclear power plant, its water quality control method and its operation method
JPH0736039B2 (en) Method for removing suspended impurities from condensate by mixed bed condensate desalination system
US4704245A (en) Method and apparatus for monitoring break of ion adsorption apparatus
JP4278211B2 (en) Pre-coating method for pre-coating filtration desalination equipment
JPH11352283A (en) Condensate processing method and condensate demineralization device
Richardson et al. Feature. Ion exchange traps chromates for reuse
JPH0640081B2 (en) Water quality monitoring method in steam power plant
JP3226971B2 (en) Water sampling and regeneration cycle controller for ion exchange equipment
JPH05288893A (en) Chromium Concentration Control Method for Boiling Water Nuclear Power Plant
Chilton Evaluation of the Low-Level Waste Treatment Plant at Oak Ridge National Laboratory, and suggested changes in the design and operation
JPH08170999A (en) Reactor water control method and reactor water control device for plant
Brooksbank et al. LOW-RADIOACTIVITY-LEVEL WASTE TREATMENT. PART II. PILOT PLANT DEMONSTRATION OF THE REMOVAL OF ACTIVITY FROM LOW-LEVEL PROCESS WASTES BY A SCAVENGING-PRECIPITATION ION-EXCHANGE PROCESS
JPS6159794B2 (en)
JPH07128488A (en) Nuclear power plant
Comley Experience with powdered resin purification at SGHWR
JP2922000B2 (en) Condensate filtration and desalination equipment
JPS60152931A (en) Sampling apparatus
JPH0531482A (en) Condensed water demineralizing method
JPS58129294A (en) Reactor water purification treatment method
Salimin et al. The Steps in Preventing, Monitoring and Removing of Fouling Scale on Operation of Evaporator
JPS62211593A (en) Washing waste water disposal plant for hollow yarn membrane type condensate filter
Scherm Treatment of Organic Chemical Manufacturing Wastewater for Reuse
Chilton et al. Decontamination of low-level liquid waste at Oak Ridge National Laboratory using a scavenging-precipitation, ion exchange process
JPS6260931B2 (en)
JPH0515875A (en) Filtering and desalting method by mixed-bed ion exchanger