JPH05100081A - Suppressing/reducing method for all organic carbon of feed/condense water - Google Patents

Suppressing/reducing method for all organic carbon of feed/condense water

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Publication number
JPH05100081A
JPH05100081A JP3260106A JP26010691A JPH05100081A JP H05100081 A JPH05100081 A JP H05100081A JP 3260106 A JP3260106 A JP 3260106A JP 26010691 A JP26010691 A JP 26010691A JP H05100081 A JPH05100081 A JP H05100081A
Authority
JP
Japan
Prior art keywords
condensate
reactor
water
toc
condenser
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
JP3260106A
Other languages
Japanese (ja)
Inventor
Katsuharu Maeda
克治 前田
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.)
Toshiba Corp
Original Assignee
Toshiba Corp
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 Toshiba Corp filed Critical Toshiba Corp
Priority to JP3260106A priority Critical patent/JPH05100081A/en
Publication of JPH05100081A publication Critical patent/JPH05100081A/en
Pending legal-status Critical Current

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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

  • Treatment Of Water By Ion Exchange (AREA)

Abstract

(57)【要約】 【目的】原子炉起動前の全有機炭素濃度を低減・抑制す
ることにより、原子炉起動時の原子炉持ち込みTOCを
減らし、原子炉水の水質悪化を抑制・緩和する。 【構成】タービン6からの蒸気を凝縮する復水器7と、
この復水器7に連設した復水フィルタ9と復水脱塩塔10
とを有する復水浄化ライン5およびこの復水浄化ライン
5に接続した給水ライン17とを備え、前記復水フィルタ
9のみで原子炉1の起動前の復水浄化を行う。また、前
記復水脱塩塔10のインサービスを原子炉1の起動直前の
復水器7の真空度上昇後行う。
(57) [Abstract] [Purpose] To reduce or suppress the total organic carbon concentration before the reactor is started to reduce the TOC brought into the reactor at the time of reactor startup, and to suppress or mitigate the deterioration of the water quality of the reactor water. [Constitution] A condenser 7 for condensing steam from a turbine 6,
Condensate filter 9 and condensate demineralization tower 10 connected to this condenser 7
And a water supply line 17 connected to the condensate purification line 5, and the condensate filter 9 alone purifies the condensate before starting the reactor 1. Further, the in-service of the condensate demineralization tower 10 is performed after the vacuum degree of the condenser 7 is raised immediately before the reactor 1 is started.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は沸騰水型原子力発電プラ
ントにおける原子炉起動前の給復水の全有機炭素抑制・
低減方法に関する。
FIELD OF THE INVENTION The present invention relates to the control of total organic carbon in feed / condensate water before starting a reactor in a boiling water nuclear power plant.
Regarding a reduction method.

【0002】[0002]

【従来の技術】原子力発電プラントにおいては原子炉一
次系構造材,燃料等に及ぼす水質環境を高純度に維持す
るために原子炉起動前に給復水の全有機物(以下、TO
Cと記す)を低減・抑制する必要がある。
2. Description of the Related Art In a nuclear power plant, in order to maintain a high-purity water quality environment affecting primary reactor structural materials, fuels, etc., all organic matter (hereinafter referred to as TO
It is necessary to reduce / suppress C).

【0003】また、原子炉起動時に原子炉水導電率が過
渡的に上昇し、水質が悪化する場合がある。これは起動
前の給復水に含まれているTOC成分が原子炉起動に伴
う給水により原子炉内に持ち込まれ熱分解,放射線分解
し、イオン不純物を生成するためである。原子炉起動前
にはあらかじめ給復水系の再循環浄化運転を実施する
が、この目的は従来給復水中の腐食生成物,いわゆるク
ラッドの除去が主であり、同時に給復水のイオン不純物
の除去するものである。
In addition, when the reactor is started, the water conductivity of the reactor may transiently rise and the water quality may deteriorate. This is because the TOC component contained in the condensate water before start-up is brought into the reactor by the water supply accompanying the start-up of the reactor and is thermally decomposed and radiolyzed to generate ionic impurities. Before the reactor is started up, the recirculation purification operation of the feed / condensation system is carried out in advance. The main purpose of this is to remove the corrosion products, so-called clad, in the conventional feed / condensate, and at the same time remove the ionic impurities in the feed / condensate. To do.

【0004】従って、原子炉起動前の給復水再循環浄化
運転時には原子炉の手前から復水器に戻る給水再循環ラ
インを利用し、復水脱塩塔等の復水浄化系をインサービ
スし、循環浄化を約1ヶ月近く行う場合がある。原子炉
起動前の給復水浄化運転時に復水脱塩塔をインサービス
し、運転することによって復水脱塩塔樹脂から溶出した
TOC成分が給復水中に蓄積することとなる。TOCは
一般に導電率監視では検出され難く、復水脱塩塔樹脂か
ら溶出したTOCは復水脱塩塔それ自身では除去され難
く、従って給復水浄化運転期間が長くなるにつれて給復
水中のTOC量は一層増加することとなる。
Therefore, during the supply / condensate recirculation purification operation before the reactor is started, the condensate purification system such as the condensate demineralization tower is in-service by using the feedwater recirculation line returning from the front of the reactor to the condenser. However, circulation purification may be performed for about one month. By in-service and operating the condensate demineralization tower during the supply / condensate purification operation before the reactor is started, the TOC component eluted from the condensate demineralizer resin will be accumulated in the condensate water. TOC is generally difficult to detect by conductivity monitoring, and TOC eluted from the condensate demineralization tower resin is difficult to remove by the condensate demineralization tower itself. The amount will increase further.

【0005】[0005]

【発明が解決しようとする課題】従来、原子炉起動前の
給復水中のTOCを低減・抑制するために復水脱塩塔イ
ンサービス前に塔内に溶出して溜っているTOCを給復
水系外に除去する、いわゆるボトムドレンを実施してい
る場合がある。
Conventionally, in order to reduce / suppress TOC in feed / condensation water before reactor startup, the TOC that has been eluted and accumulated in the tower before the condensate demineralization tower in-service is restored. In some cases, so-called bottom drain is implemented to remove it outside the water system.

【0006】しかしながら、長時間にわたる起動前の給
復水系再循環浄化運転によって給復水のTOC濃度が上
昇し、これが原子炉起動に伴う給水開始によって原子炉
に持ち込まれ熱分解または放射線分解することによって
イオン不純物を生成し、原子炉水質を悪化させる課題が
ある。
However, the TOC concentration of the feed / condensate in the feed / condensate system is increased by the recirculation / purification operation of the feed / condensate system before starting for a long time, and the TOC concentration is brought into the reactor by the start of the feed water accompanying the start-up of the reactor and is pyrolyzed or radioactively decomposed. However, there is a problem that ionic impurities are generated by this and the water quality of the reactor is deteriorated.

【0007】本発明は上記課題を解決するためになされ
たもので、原子炉起動前の給復水のTOC低減・抑制方
法を提供することにある。
The present invention has been made to solve the above problems, and an object of the present invention is to provide a TOC reduction / suppression method for feed / condensation water before the reactor is started.

【0008】[0008]

【課題を解決するための手段】本発明はタービンからの
蒸気を凝縮する復水器と、この復水器に連設した復水フ
ィルタと復水脱塩塔とを有する復水浄化ラインおよび前
記復水脱塩塔を通過した復水を原子炉へ給水する給水ラ
インとを備えた沸騰水型原子力発電プラントの給復水の
全有機炭素抑制・低減方法において、前記復水フィルタ
のみで原子炉起動前の復水浄化を行うとともに、前記復
水脱塩塔のインサービスを前記原子炉起動直前の復水器
の真空度上昇後行うことを特徴とする。
The present invention is directed to a condensate purification line having a condenser for condensing steam from a turbine, a condensate filter connected to the condenser, and a condensate demineralization tower, and the above-mentioned condensate purification line. In a method for suppressing / reducing total organic carbon of feedwater / condensation water of a boiling water nuclear power plant equipped with a feedwater line for feeding condensed water having passed through a condensate demineralization tower to a reactor, the reactor is provided with only the condensate filter. Condensate purification before start-up is performed, and in-service of the condensate demineralization tower is performed after the degree of vacuum of the condenser is increased immediately before the reactor is started up.

【0009】[0009]

【作用】原子炉起動前の給復水中のTOC濃度を低減・
抑制するためには復水脱塩塔のインサービス期間を極力
短くするとともに、インサービスは給復水の溶存酸素濃
度が低くなり、復水脱塩塔からのTOC溶出が抑制出来
る復水器の真空度上昇後とすることが効果的である。
[Operation] Reduction of TOC concentration in the water supply / condensation water before reactor startup
In order to suppress it, the in-service period of the condensate demineralization tower should be shortened as much as possible, and the dissolved oxygen concentration of the condensate water in the condensate water should be low, and the in-service condenser should be able to suppress TOC elution from the condensate desalination tower. It is effective to make it after the degree of vacuum is increased.

【0010】また、給復水系に原子炉起動前に存在する
TOCを除去するためには起動前浄化時に照射燃料から
放出されるγ−線によってその分解を促進することが効
果的なTOC分解・除去方法の一つと言える。
Further, in order to remove TOC existing in the feed / condensation system before the reactor is started, it is effective to promote the decomposition by the γ-rays emitted from the irradiated fuel at the time of pre-start purification. It can be said to be one of the removal methods.

【0011】すなわち、原子炉起動前の給復水再循環浄
化時に復水脱塩塔内のイオン交換樹脂から溶出するTO
Cにより給復水TOC濃度が上昇することを避けるため
には、復水浄化系に復水フィルタと復水脱塩塔を備える
プラントにおいては復水浄化系フィルタのみで起動前給
復水浄化を行う。復水脱塩塔のインサービスは原子炉起
動前の復水器真空度上昇後とするとともに、万一復水脱
塩塔インサービスに伴いTOCが給復水系に混入した場
合、その除去を効率的に行うために、復水脱塩塔インサ
ービス直前に復水浄化系フィルタを逆洗・再生しインサ
ービスすることが有効である。
That is, the TO that is eluted from the ion exchange resin in the condensate demineralization tower at the time of cleansing the condensate recirculation before starting the reactor
In order to avoid an increase in the TOC concentration of the condensate water due to C, in a plant equipped with a condensate filter and a condensate demineralization tower in the condensate purification system, the condensate purification system filter alone should be used to purify the condensate before startup. To do. The in-service of the condensate demineralization tower will be performed after the condenser vacuum level is raised before the reactor is started, and if TOC is mixed into the feed / condensate system due to the in-service of the condensate demineralization tower, the removal will be efficient. In order to do so, it is effective to backwash and regenerate the condensate purification system filter immediately before in-service of the condensate demineralization tower.

【0012】一方、復水浄化系が復水脱塩塔単独のプラ
ントの場合、原子炉起動前の給復水浄化運転の為に復水
脱塩塔をインサービスせざるを得ないが、この場合復水
脱塩塔をバイパスして給復水系再循環運転を行い、給復
水配管内面に付着するクラッドを十分剥離させておき、
クラッド除去の為の復水脱塩塔インサービス期間を極力
短くするとともにインサービス時期を復水器真空度上昇
後となるようにすることが有効である。
On the other hand, in the case where the condensate purification system is a plant having only a condensate demineralization tower, the condensate demineralization tower must be in-service for the supply / condensate purification operation before the reactor is started. In this case, bypass the condensate demineralization tower and perform a feed / condensate system recirculation operation to sufficiently remove the clad that adheres to the inner surface of the feed / condensate piping.
It is effective to shorten the in-service period of the condensate demineralization tower for removing the clad as much as possible and to make the in-service period after the condenser vacuum degree is raised.

【0013】また、給復水再循環時に給復水に存在する
TOCをあらかじめ分解除去しておくことは原子炉起動
時の炉水水質悪化抑制上極めて有効である。TOCは熱
放射線,紫外線等で分解し、炭酸ガスになるが、同時に
TOCに含まれていた窒素,イオウ化合物はアンモニ
ア、硝酸,亜硝酸,硫酸等のイオンとなる。これらのイ
オン不純物は一般に低温条件下で存在する場合には、原
子炉一次系材料であるステンレス鋼に対する腐食寄与は
少ないと言われており、燃料等に対しても、その影響は
高温条件下よりは十分に少ないと言える。
Further, it is very effective to decompose and remove the TOC existing in the condensate water at the time of recirculation of the condensate water in advance in order to suppress deterioration of the water quality of the reactor water at the time of starting the reactor. TOC is decomposed by heat radiation, ultraviolet rays and the like to become carbon dioxide gas, but at the same time, nitrogen and sulfur compounds contained in TOC become ions such as ammonia, nitric acid, nitrous acid and sulfuric acid. When these ionic impurities are present under low temperature conditions, it is generally said that they contribute little to the corrosion of stainless steel, which is the primary material for nuclear reactors. Can be said to be small enough.

【0014】従って、起動前後に給復水TOCを分解除
去する方法の一つとして、給復水の一部を連続して照射
済みの燃料が存在する原子炉,或るいは燃料プールに移
送し、照射済みの燃料から出るγ線により分解除去する
ことが有効である。また、粉末状イオン交換樹脂を使用
する復水フィルタを備えたプラントにおいては、復水脱
塩塔の「採水」による給復水のTOC濃度上昇を緩和す
るためには、復水脱塩塔「採水」前に復水フィルタを逆
洗・再生したうえでインサービスしておくことが、TO
Cの除去上効果的となる。
Therefore, as one of the methods for decomposing and removing the condensate water TOC before and after the start-up, a part of the condensate water is continuously transferred to a reactor or a fuel pool in which irradiated fuel exists. , It is effective to decompose and remove by γ-ray emitted from the irradiated fuel. In a plant equipped with a condensate filter using powdered ion-exchange resin, in order to mitigate the TOC concentration increase in the condensate in the condensate in the condensate demineralization tower, the Before injecting water, it is necessary to backwash and regenerate the condensate filter before in-service.
It is effective in removing C.

【0015】[0015]

【実施例】図1から図5を参照しながら本発明に係る給
復水のTOC抑制・低減方法の一実施例を説明する。図
1は本実施例方法を説明するための沸騰水型原子力発電
所に適用する給復水系と原子炉再循環系を示す系統図で
ある。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the method for suppressing / reducing TOC of supplied / condensed water according to the present invention will be described with reference to FIGS. FIG. 1 is a system diagram showing a feed / condensation system and a reactor recirculation system applied to a boiling water nuclear power plant for explaining the method of the present embodiment.

【0016】図1中、符号1は沸騰水型原子炉を示して
おり、この原子炉1には再循環ポンプ2を有する原子炉
再循環系20を備え、この再循環ポンプ2の吸込側から分
岐し原子炉冷却材浄化系3が接続されている。この原子
炉冷却材浄化系3の出口側は給水ライン17に接続され、
給水ライン17は原子炉1に接続している。原子炉冷却材
浄化系3の出口側から分岐して復水器ブローダウンライ
ン4が接続しており、給水ライン17の入口側に浄化ライ
ン5が接続している。復水器ブローダウンライン4およ
び浄化ライン5はタービン6に接続している。
In FIG. 1, reference numeral 1 denotes a boiling water reactor, which is provided with a reactor recirculation system 20 having a recirculation pump 2 and which is connected to the suction side of the recirculation pump 2. It is branched and the reactor coolant purification system 3 is connected. The outlet side of this reactor coolant purification system 3 is connected to a water supply line 17,
The water supply line 17 is connected to the reactor 1. The condenser blowdown line 4 is branched from the outlet side of the reactor coolant purification system 3, and the purification line 5 is connected to the inlet side of the water supply line 17. The condenser blowdown line 4 and the purification line 5 are connected to the turbine 6.

【0017】タービン6には復水器7が、復水器7には
復水ポンプ8が接続している。復水ポンプ8の吐出側に
は復水フィルタ9および復水脱塩塔10が順次接続し、復
水脱塩塔10の出口側は浄化ライン5に接続している。復
水フィルタ9および復水脱塩塔10にはそれぞれバイパス
ライン11,12が設けられている。浄化ライン5から分岐
してスピルオーバーライン13の一端が接続され、このス
ピルオーバーライン13の他端はCRD冷却水ライン16に
接続している。
A condenser 7 is connected to the turbine 6, and a condenser pump 8 is connected to the condenser 7. A condensate filter 9 and a condensate demineralizer 10 are sequentially connected to the discharge side of the condensate pump 8, and an outlet side of the condensate demineralizer 10 is connected to the purification line 5. The condensate filter 9 and the condensate demineralization tower 10 are provided with bypass lines 11 and 12, respectively. One end of the spillover line 13 is branched from the purification line 5, and the other end of the spillover line 13 is connected to the CRD cooling water line 16.

【0018】CRD冷却水ライン16の一端は原子炉1の
底部に接続しており、その他端は燃料貯蔵プール14に接
続している。この燃料貯蔵プール14は燃料プール浄化系
15に接続され、この燃料プール浄化系15の出口側ライン
18は復水器ブローダウンライン4に接続している。燃料
プール浄化系15の出口側ライン18から分岐して戻りライ
ン19の一端が接続され、戻りライン19の他端は燃料貯蔵
プール14に接続している。
One end of the CRD cooling water line 16 is connected to the bottom of the nuclear reactor 1, and the other end is connected to the fuel storage pool 14. This fuel storage pool 14 is a fuel pool purification system.
The outlet side line of this fuel pool purification system 15 connected to 15.
18 is connected to the condenser blowdown line 4. One end of a return line 19 is branched from the outlet side line 18 of the fuel pool purification system 15, and the other end of the return line 19 is connected to the fuel storage pool 14.

【0019】復水脱塩塔10に使用しているイオン交換樹
脂は表1に示すように酸化劣化、ホフマン(Hofmann )
分解,アミン離脱反応等によりTOCを溶出する。
As shown in Table 1, the ion exchange resin used in the condensate demineralization tower 10 undergoes oxidative deterioration and Hofmann
TOC is eluted by decomposition, amine elimination reaction, etc.

【0020】[0020]

【表1】 [Table 1]

【0021】一方、イオン交換樹脂からのTOC溶出速
度は、図2に示すように、使用年数が長くなるに従って
増加する。図3に示すように空気飽和水においては、窒
素(N2 )ガスをバブリングし溶液中の溶存酸素を低減
させた条件に比べてイオン交換樹脂からのTOC溶出が
多くなる傾向が見られる。このことは、低溶存酸素条件
下では酸化劣化により、イオン交換樹脂からTOCが溶
出することが抑制出来ることを示している。従って復水
脱塩塔10の「採水」は給復水系のTOC濃度上昇抑制の
為には復水器7の真空度上昇後とすることが有効と言え
る。
On the other hand, the TOC elution rate from the ion exchange resin increases as the years of use increase, as shown in FIG. As shown in FIG. 3, in the air-saturated water, the TOC elution from the ion-exchange resin tends to increase as compared with the condition where the nitrogen (N 2 ) gas is bubbled to reduce the dissolved oxygen in the solution. This indicates that under low dissolved oxygen conditions, TOC can be suppressed from being eluted from the ion exchange resin due to oxidative deterioration. Therefore, it can be said that the “water sampling” of the condensate demineralization tower 10 is effective after the degree of vacuum of the condenser 7 is increased in order to suppress the increase in the TOC concentration of the water supply / condensation system.

【0022】又、図4に示すように、イオン交換樹脂か
らのTOC溶出は、通水流速に対して明らかな依存性が
認められ、通水流速が低いほど、TOCの溶出が少なく
なる傾向がある。従ってプラント起動前の給復水系浄化
運転時のように、 100%定格流量より低い流量で系統水
を通水する場合、常に全部の復水脱塩塔10を採水するこ
とにより、各復水脱塩塔毎の採水流量を減らし通水流速
を低くすることで、プラント起動前に復水脱塩塔10から
溶出するTOCが給復水系に蓄積する量を低減すること
が可能となる。
Further, as shown in FIG. 4, the TOC elution from the ion exchange resin has a clear dependence on the water flow rate, and the lower the water flow rate, the less the TOC elution tends to be. is there. Therefore, when system water is passed at a flow rate lower than the 100% rated flow rate, such as during the water supply / condensation system purification operation before the plant is started, all the condensate demineralization towers 10 are always used to collect water. By reducing the flow rate of sampled water for each desalting tower and lowering the water flow rate, it is possible to reduce the amount of TOC eluted from the condensate desalting tower 10 before the plant is started to accumulate in the feed / condensate system.

【0023】図5にプラント起動前の給復水再循環浄化
運転時における給水及び原子炉水TOC濃度経時変化の
実例を示す。図5において、復水脱塩塔10の出口から採
水していた制御棒駆動装置(CRD)の冷却水を停止す
ると、給水のTOC濃度の上昇傾向が認められる。これ
は、CRD冷却水が復水脱塩塔10の出口から供給されて
いる場合には、原子炉1に持ち込まれるCRD冷却水中
のTOC成分が、原子炉1内の照射燃料からのγ線等に
より分解され、TOC濃度の低い原子炉水が復水器7に
ブローされ給復水のTOC濃度を低く押える効果をもた
らしていたものが、CRD冷却水の停止により、給復水
中のTOCの炉内における分解が促進されなくなったた
めに生じた現象である。
FIG. 5 shows an actual example of changes over time in the feedwater and reactor water TOC concentrations during the supply / condensate recirculation purification operation before the start of the plant. In FIG. 5, when the cooling water of the control rod drive device (CRD) that has been drawing water from the outlet of the condensate demineralization tower 10 is stopped, the TOC concentration of the feed water tends to increase. This is because when the CRD cooling water is supplied from the outlet of the condensate demineralization tower 10, the TOC component in the CRD cooling water brought into the reactor 1 is γ-rays or the like from the irradiation fuel in the reactor 1. However, the reactor water with a low TOC concentration was blown to the condenser 7 and had the effect of holding down the TOC concentration of the feed and condensate water to a low level. It is a phenomenon caused by the fact that decomposition in the interior is no longer promoted.

【0024】以上述べたように、原子炉起動前の給復水
のTOCを低減・抑制するためには復水器の真空度上昇
後に復水脱塩塔10を「採水」するとともに「採水」期間
は極力短くし、「採水」塔数は全塔とし復水脱塩塔10の
通水流速を極力低くすることが有効である。また、照射
燃料からのγ−線によりTOCの分解を促進することは
一次系内のTOC濃度低減の為の有効な手段となる。
As described above, in order to reduce / suppress the TOC of the supply / condensation water before the reactor is started, the condensate demineralization tower 10 is "collected" and "collected" after the vacuum degree of the condenser is increased. It is effective to make the “water” period as short as possible and set all the “water sampling” towers to the lowest flow rate of the condensate demineralization tower 10. Further, promoting the decomposition of TOC by γ-rays from the irradiated fuel is an effective means for reducing the TOC concentration in the primary system.

【0025】すなわち、図1において、原子炉起動前に
は、復水器7の水を復水ポンプ8をもちいて給復水再循
環浄化ライン5で循環する場合、復水器7の真空度上昇
により系統水の溶存酸素濃度が下がるまでは復水脱塩塔
10には通水せず復水フィルタ9のみを通水し、復水脱塩
塔バイパスライン12を使用した給復水再循環浄化運転を
行う。また、給復水のTOC濃度を下げるために、復水
脱塩塔下流のスピルオーバライン13を使い、CRD冷却
水ライン16から復水の一部を原子炉1に連続的に供給す
ることで炉内の照射燃料からのγ−線等によりTOCの
分解を促進しTOC濃度の低い原子炉水を原子炉冷却材
浄化系3を経由させ、復水器ブローダウンライン4をも
ちいて復水器にブローすることで、給復水系のTOC濃
度を下げることが出来る。尚、燃料貯蔵プール14に、照
射済み燃料が保管されている場合には燃料プール内の照
射燃料がTOCの効果的な分解を促進することとなるた
め、常時スピルオーバを使用して復水を燃料プールに通
水し、燃料プール浄化系を経由して復水器にブローダウ
ンする方法もTOC濃度低減の効果的対策となる。
That is, in FIG. 1, when the water in the condenser 7 is circulated in the supply / condensate recirculation purification line 5 by using the condenser pump 8 before the reactor is started, the degree of vacuum of the condenser 7 is set. Condensate demineralization tower until dissolved oxygen concentration of system water decreases due to rise
Water is not passed through 10 but only the condensate filter 9 is passed through, and a condensate recirculation purification operation using a condensate demineralization tower bypass line 12 is performed. Further, in order to reduce the TOC concentration of the condensate of the feed water, the spillover line 13 downstream of the condensate demineralization tower is used, and a part of the condensate is continuously supplied from the CRD cooling water line 16 to the reactor 1. The TOC decomposition is promoted by γ-rays, etc. from the irradiated fuel inside the reactor, and the reactor water with a low TOC concentration is passed through the reactor coolant purification system 3 and used as a condenser using the condenser blowdown line 4. By blowing, the TOC concentration in the water supply / condensation system can be lowered. When the irradiated fuel is stored in the fuel storage pool 14, the irradiated fuel in the fuel pool promotes effective decomposition of TOC, so spillover is always used to fuel the condensate. A method of passing water through the pool and blowing it down to the condenser via the fuel pool purification system is also an effective measure for reducing TOC concentration.

【0026】本発明の実施態様は次のとおりである。 (1)原子炉起動時に給復水系から持ち込まれるTOC
が原子炉内で熱または放射線分解することにより生成す
るイオン不純物によって炉水水質が悪化することを防
止,抑制または緩和するために、原子炉起動前の給復水
のTOCを低減する。その方法として、復水脱塩塔を復
水器の真空度上昇後に採水する。この採水は復水脱塩塔
の採水塔数を全塔とし、復水脱塩塔の採水流速を遅くす
ること。 (2)復水脱塩塔内のイオン交換樹脂からのTOC溶出
が給復水に濃縮することを避けるために、原子炉起動前
の給復水浄化は脱塩塔を採水せず復水フィルタのみで実
施すること。 (3)復水脱塩塔インサービスによりTOCが給復水中
に混入した場合、そのTOCを効率的に除去するため
に、復水脱塩塔インサービスに先立ち復水フィルタを逆
洗・再生インサービスすること。 (4)原子炉起動前の給復水中に存在するTOCをプラ
ント起動前に効率的に除去するために、原子炉または燃
料プールに給復水の1部を連続または間欠的に供給して
照射済み燃料からのγ線によりTOCを分解し、生成イ
オン不純物を原子炉冷却材浄化系,燃料プール浄化系で
除去し、TOC濃度の低い水を給復水系に戻し、原子炉
起動前の給復水のTOC濃度を低減すること。
The embodiment of the present invention is as follows. (1) TOC brought in from the water supply / condensation system at reactor startup
In order to prevent, suppress, or mitigate the deterioration of the water quality of the reactor water due to ionic impurities generated by thermal decomposition or radiolysis in the reactor, the TOC of the feed / condensate water before the reactor is started is reduced. As a method, the condensate demineralization tower collects water after raising the vacuum degree of the condenser. For this water sampling, the total number of water collection towers of the condensate demineralization tower should be set, and the water flow speed of the condensate demineralization tower should be slowed. (2) Condensation water In order to avoid the TOC elution from the ion exchange resin in the demineralization tower from concentrating in the condensate water, the condensate water purification before reactor startup does not collect water in the demineralization tower Do only with filters. (3) When TOC is mixed in the condensate water by condensate demineralization tower in-service, in order to remove the TOC efficiently, the condensate filter is backwashed and regenerated before the condensate demineralization tower in-service. To serve. (4) In order to efficiently remove TOC existing in the water supply / condensation water before the reactor startup before the plant is started, a part of the supply / condensation water is continuously or intermittently supplied to the reactor or the fuel pool for irradiation. TOC is decomposed by γ-rays from the spent fuel, the produced ion impurities are removed by the reactor coolant purification system and the fuel pool purification system, and the water with low TOC concentration is returned to the feed / condensation system to restore the charge before starting the reactor. To reduce the TOC concentration of water.

【0027】[0027]

【発明の効果】本発明によれば、復水脱塩塔のインサー
ビス期間を短くすることによって、復水脱塩塔から溶出
するTOCの給復水での温度上昇を避けることができ
る。また、復水器を真空度上昇以降に復水脱塩塔を全塔
インサービスすることで復水脱塩塔からのTOC溶出を
抑制することができる。さらに、原子力発電プラントの
起動にあたり、復水脱塩塔をインサービスする場合には
復水フィルタをあらかじめ全塔逆洗再生しておくことで
効率的なTOCの除去を図ることができる。
According to the present invention, by shortening the in-service period of the condensate demineralization tower, it is possible to avoid an increase in the temperature of the TOC that is eluted from the condensate demineralization tower during the condensate supply. Further, the TOC elution from the condensate demineralization tower can be suppressed by in-service all the condensate demineralization towers after the degree of vacuum of the condenser is increased. Further, when the condensate demineralization tower is in-service at the time of starting the nuclear power plant, the TOC can be efficiently removed by previously rewashing all the condensate filters by backwashing.

【0028】また、原子炉起動前の給復水再循環浄化運
転時に給復水を強制的に原子炉または燃料プールに送
り、照射済み燃料から出るγ線によりTOCの分解を促
進し原子炉冷却材浄化系ろ過脱塩塔,燃料プール浄化系
ろ過脱塩塔によってTOC分解生成物イオンを除去する
ことは有効なTOC除去方法となる。これらの方法によ
ってプラント起動時に給水系から持ち込まれるTOCが
原子炉において熱または放射線分解し、生成するイオン
不純物による炉水の水質悪化を抑制・回避することがで
きる。
Further, during the feed / condensate recirculation purification operation before the reactor is started, the feed / condensate is forcibly sent to the reactor or the fuel pool, and the TOC decomposition is promoted by the γ-rays emitted from the irradiated fuel to cool the reactor. It is an effective TOC removal method to remove TOC decomposition product ions by a material purification system filtration desalting tower and a fuel pool purification system filtration desalting tower. By these methods, TOC brought in from the water supply system at the time of plant startup is thermally or radiolytically decomposed in the nuclear reactor, and deterioration of the water quality of the reactor water due to ionic impurities generated can be suppressed or avoided.

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

【図1】本発明に係る給復水の全有機炭素抑制・低減方
法の一実施例を適用するための原子力発電プラントの給
復水系および原子炉再循環系を示す系統図。
FIG. 1 is a system diagram showing a feed / condensation system and a nuclear reactor recirculation system of a nuclear power plant to which an embodiment of a method for suppressing / reducing total organic carbon of feed / condensation water according to the present invention is applied.

【図2】図1の復水脱塩塔内のイオン交換樹脂のTOC
溶出速度と使用年数との関係を示す曲線図。
2 is a TOC of the ion exchange resin in the condensate demineralization tower of FIG.
The curve figure which shows the relationship between a dissolution rate and the years of use.

【図3】図1の復水中に空気飽和水とN2 をバブリング
した際のTOC濃度と通水時間との関係を示す曲線図。
FIG. 3 is a curve diagram showing the relationship between TOC concentration and water passage time when bubbling air-saturated water and N 2 in the condensate of FIG. 1.

【図4】図1の復水におけるTOC溶出挙動の通水流速
依存性を示す曲線図。
FIG. 4 is a curve diagram showing the dependence of TOC elution behavior in condensate water of FIG. 1 on water flow velocity.

【図5】図1のプラントの原子炉水と給水におけるTO
C濃度と経過時間との関係を示す曲線図。
FIG. 5: TO in reactor water and water supply of the plant of FIG.
The curve diagram which shows the relationship between C density | concentration and elapsed time.

【符号の説明】 1…原子炉、2…再循環ポンプ、3…原子炉冷却材浄化
系、4…復水器ブローダウン、5…給復水再循環浄化ラ
イン、6…タービン、7…復水器、8…復水ポンプ、9
…復水フィルタ、10…復水脱塩塔、11…復水フィルタバ
イパスライン、12…復水脱塩塔バイパスライン、13…ス
ピルオーバライン、14…燃料貯蔵プール、15…燃料プー
ル浄化系、16…CRD冷却水ライン、17…給水ライン、
18…出口側ライン、19…戻りライン、20…原子炉再循環
系。
[Explanation of Codes] 1 ... Reactor, 2 ... Recirculation pump, 3 ... Reactor coolant purification system, 4 ... Condenser blowdown, 5 ... Condensed water recirculation purification line, 6 ... Turbine, 7 ... Condenser Water bottle, 8 ... Condensate pump, 9
… Condensate filter, 10… Condensate demineralizer, 11… Condensate filter bypass line, 12… Condensate demineralizer bypass line, 13… Spillover line, 14… Fuel storage pool, 15… Fuel pool purification system, 16 … CRD cooling water line, 17… water supply line,
18 ... Exit line, 19 ... Return line, 20 ... Reactor recirculation system.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 タービンからの蒸気を凝縮する復水器
と、この復水器に連設した復水フィルタと復水脱塩塔と
を有する復水浄化ラインおよび前記復水脱塩塔を通過し
た復水を原子炉へ給水する給水ラインとを備えた沸騰水
型原子力発電プラントの給復水の全有機炭素抑制・低減
方法において、前記復水フィルタのみで原子炉起動前の
復水浄化を行うとともに、前記復水脱塩塔のインサービ
スを前記原子炉起動直前の復水器の真空度上昇後行うこ
とを特徴とする給復水の全有機炭素抑制・低減方法。
1. A condensate purifying line having a condenser for condensing steam from a turbine, a condensate filter connected to the condenser, and a condensate demineralizer, and a condensate demineralizer passing through the condensate purification line. In the method for suppressing / reducing total organic carbon in the feedwater / condensation water of a boiling water nuclear power plant equipped with a water supply line for supplying the condensed water to the reactor, the condensate water is purified by the condensate filter only before the reactor is started. A method for suppressing / reducing total organic carbon in feed / condensation water, which is performed while the in-service of the condensate demineralization tower is performed after the vacuum degree of the condenser is raised immediately before the reactor is started.
JP3260106A 1991-10-08 1991-10-08 Suppressing/reducing method for all organic carbon of feed/condense water Pending JPH05100081A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3260106A JPH05100081A (en) 1991-10-08 1991-10-08 Suppressing/reducing method for all organic carbon of feed/condense water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3260106A JPH05100081A (en) 1991-10-08 1991-10-08 Suppressing/reducing method for all organic carbon of feed/condense water

Publications (1)

Publication Number Publication Date
JPH05100081A true JPH05100081A (en) 1993-04-23

Family

ID=17343373

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3260106A Pending JPH05100081A (en) 1991-10-08 1991-10-08 Suppressing/reducing method for all organic carbon of feed/condense water

Country Status (1)

Country Link
JP (1) JPH05100081A (en)

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