JPH02196998A - Nuclear power generation facility - Google Patents
Nuclear power generation facilityInfo
- Publication number
- JPH02196998A JPH02196998A JP1015023A JP1502389A JPH02196998A JP H02196998 A JPH02196998 A JP H02196998A JP 1015023 A JP1015023 A JP 1015023A JP 1502389 A JP1502389 A JP 1502389A JP H02196998 A JPH02196998 A JP H02196998A
- Authority
- JP
- Japan
- Prior art keywords
- condensate
- hydrogen
- oxygen
- water
- reactor
- 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
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Classifications
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- 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
Landscapes
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Abstract
Description
【発明の詳細な説明】
〔発明の目的〕
(産業上の利用分野)
本発明は沸騰水型原子炉(BWR)−次系構成材料の腐
食抑制対策として原子炉一次系に水素注入を行う機構を
備えた原子力発電設備に関する。[Detailed description of the invention] [Object of the invention] (Industrial application field) The present invention is a boiling water reactor (BWR) - a mechanism for injecting hydrogen into the primary system of a nuclear reactor as a measure to inhibit corrosion of secondary system constituent materials. Regarding nuclear power generation equipment equipped with
(従来の技術)
原子力発電プラントの原子炉冷却材は高温高圧水の状態
にあり、プラント構造材料は極めて厳しい環境条件下に
ある。上記のような条件にある時、材料の腐食挙動が重
要な問題となり、特にBWRプラントにおいてはオース
テナイト系ステンレス鋼配管の応力腐食割れ(Stre
ss Corrosion Cracking、 以
下SCCと呼ぶ)が内外の大きな関心の的となっている
。(Prior Art) The reactor coolant in a nuclear power plant is in the form of high-temperature, high-pressure water, and the plant structural materials are under extremely harsh environmental conditions. Under the above conditions, the corrosion behavior of the material becomes an important issue, especially in BWR plants, stress corrosion cracking of austenitic stainless steel piping
SS Corrosion Cracking (hereinafter referred to as SCC) has become a subject of great interest at home and abroad.
このSCCという現象は3つの要因、すなわち材料、応
力、環境の3因子が重畳した時に発生するものと一般に
考えられている。新設するBWR原子力発電プラントに
おいては、前記3因子につき十分な考慮を払い応力腐食
割れに対して備えなければならない。It is generally believed that this SCC phenomenon occurs when three factors, namely material, stress, and environment, are superimposed. In a newly constructed BWR nuclear power plant, sufficient consideration must be given to the three factors mentioned above to prepare for stress corrosion cracking.
ところが、既設の原子カプラントにおいては材料、応力
の面からの対策−を施すことは困廻であるため、環境面
から対策を施すことが試みられている。環境側のSCC
発生要因としては原子炉水中の溶存酸素濃度が最大のも
のとなっている。However, since it is difficult to take measures from the viewpoint of materials and stress in existing atomic couplants, attempts have been made to take measures from an environmental viewpoint. Environmental SCC
Dissolved oxygen concentration in the reactor water is the most important factor.
炉心においては水の放射線分解により酸素が発生するた
め、炉水に200〜300ppb程度の酸素が溶存する
ことは避けられない。原子炉温度(285℃)において
は、200ppb前後の溶存酸素はSCCに対して十分
に有意なレベルであり、プラント運転上溶存酸素濃度の
管理は重要である。Since oxygen is generated in the reactor core by radiolysis of water, it is inevitable that about 200 to 300 ppb of oxygen will be dissolved in the reactor water. At the reactor temperature (285° C.), dissolved oxygen of around 200 ppb is at a sufficiently significant level for SCC, and management of dissolved oxygen concentration is important for plant operation.
このためSCCの対策として原子炉への水素注入技術が
開発され、一部のプラントで実用化されつつある。この
技術は給水中に少量の水素を注入して溶存させておき、
これにより酸素、過酸化水素等の酸化性の化学種の発生
を抑制しようとするものである。水素注入により炉水を
適度の還元性雰囲気とした場合、放射線存在下では放射
線化学的に酸素、過酸化水素と、水素との水への再結合
反応が促進される。For this reason, hydrogen injection technology into nuclear reactors has been developed as a countermeasure against SCC, and is being put into practical use in some plants. This technology injects a small amount of hydrogen into the water supply and dissolves it.
This is intended to suppress the generation of oxidizing chemical species such as oxygen and hydrogen peroxide. When reactor water is made into a moderately reducing atmosphere by hydrogen injection, in the presence of radiation, the recombination reaction of oxygen, hydrogen peroxide, and hydrogen into water is promoted radiochemically.
既設プラント(米国ドレステン2号炉)における水素注
入技術の例を第3図につき説明する。An example of hydrogen injection technology in an existing plant (Doresten No. 2 reactor in the United States) will be explained with reference to FIG.
この図は水素注入を行う原子炉一次系の系統図である6
すなわち、炉心1で発生した蒸気はタービン2において
仕事をした後、復水器3に導かれここで冷却凝縮されて
復水する。この復水はポンプ4.復水浄化系5を経由し
て高圧復水ポンプ6゜給水加熱器7.給水ポンプ8によ
り昇温、加圧されて原子炉圧力容器9に注入される。な
お、図中符号10は原子炉再循環ポンプであり、原子炉
圧力容器9内の炉水を強制的に再循環させ、炉心流量を
増加させるものである。上記構成の一次系において、水
素注入は復水浄化系5の下流で高圧復水ポンプの上流に
ある注入点11からなされている。This figure is a system diagram of the primary reactor system that performs hydrogen injection6
That is, the steam generated in the core 1 performs work in the turbine 2, and then is led to the condenser 3, where it is cooled and condensed and condensed. This condensate is pumped 4. High pressure condensate pump 6° feed water heater 7. via condensate purification system 5. The water is heated and pressurized by the feed water pump 8 and then injected into the reactor pressure vessel 9. Note that the reference numeral 10 in the figure is a reactor recirculation pump, which forcibly recirculates the reactor water in the reactor pressure vessel 9 to increase the reactor core flow rate. In the primary system configured as described above, hydrogen is injected from an injection point 11 located downstream of the condensate purification system 5 and upstream of the high-pressure condensate pump.
例示した既設プラント以外のものにおいても前述した注
入点11から注入されている例が多い。Even in plants other than the exemplified existing plants, there are many examples in which water is injected from the injection point 11 described above.
第3図には気体廃棄物処理系をあわせて示している。復
水器3から排出されるオフガスは空気抽出器13.オフ
ガス予熱器14を経てオフガス再結合器15で処理され
、オフガス復水器16を通って気体廃棄物処理系に到る
。水素注入技術においては炉心で放射線分解によって発
生する酸素および水素は再結合反応によって水に戻るも
のの外部から注入した量に相当する水素は余剰水素とし
て気体廃棄物処理系に排出される。この余剰水素は安全
上、気体廃棄物処理系で再結合処理を施す必要があり。FIG. 3 also shows the gaseous waste treatment system. The off-gas discharged from the condenser 3 is sent to the air extractor 13. The gas passes through an off-gas preheater 14, is treated in an off-gas recombiner 15, and passes through an off-gas condenser 16 to reach the gaseous waste treatment system. In hydrogen injection technology, oxygen and hydrogen generated by radiolysis in the reactor core return to water through a recombination reaction, but hydrogen equivalent to the amount injected from the outside is discharged to the gaseous waste treatment system as surplus hydrogen. For safety reasons, this excess hydrogen must be recombined in the gaseous waste treatment system.
気体廃棄物処理系に酸素注入を行い、オフガス再結合器
15で余剰水素と気体廃棄物処理系注入酸素との反応を
行わせ処理している。酸素注入点17は通常、空気抽出
器13とオフガス予熱器14の中間に位置し、酸素注入
機構18から酸素が注入される。Oxygen is injected into the gas waste treatment system, and the off-gas recombiner 15 causes the excess hydrogen to react with the oxygen injected into the gas waste treatment system. Oxygen injection point 17 is typically located intermediate between air extractor 13 and off-gas preheater 14 and is injected with oxygen from oxygen injection mechanism 18 .
第4図はドレスチン2号、ビーチボトム3号。Figure 4 shows Dolestin No. 2 and Beech Bottom No. 3.
ピルグリム、フィッツパトリック、デュアン・アーノル
ドの米国既設プラントにおける水素注入による溶存酸素
濃度の低減効果の試験結果を示す線図である。縦軸は再
循環系で採取したサンプル炉水中の溶存酸素濃度(pp
b)、横軸は給水溶存水素濃度(39m)を示している
。図中、線1(0印)はピーチボトム3号、線2(Δ印
)はドレスデン2号、線3(☆印)はピルグリム、線4
(◇印)はフイッツパトリック、線5(印)はデュアン
・アーノルドをそれぞれ示している。FIG. 2 is a diagram showing test results of the effect of hydrogen injection on reducing dissolved oxygen concentration at existing Pilgrim, Fitzpatrick, and Duane Arnold plants in the United States. The vertical axis is the dissolved oxygen concentration (pp
b), the horizontal axis shows the feed water dissolved hydrogen concentration (39m). In the diagram, line 1 (0 mark) is Peach Bottom 3, line 2 (Δ mark) is Dresden 2, line 3 (☆ mark) is Pilgrim, and line 4
(◇) indicates Fitzpatrick, and line 5 (mark) indicates Duane Arnold.
この第4図から、プラントによって酸素濃度低減効果に
違いはあるものの、給水中の水素濃度を高くしていけば
炉水中の溶存酸素濃度が低下していくことがわかる。From FIG. 4, it can be seen that although the oxygen concentration reduction effect varies depending on the plant, as the hydrogen concentration in the feed water increases, the dissolved oxygen concentration in the reactor water decreases.
上記から明らかなように、水素注入により炉水中の溶存
酸素濃度を低下させることができることは実機において
も立証されており、環境面からのSCC対策として有効
である。As is clear from the above, it has been proven in actual reactors that hydrogen injection can reduce the dissolved oxygen concentration in reactor water, and is an effective measure against SCC from an environmental perspective.
なお、第4図および後述する第5図はつぎの文献から引
用したものである。Note that FIG. 4 and FIG. 5, which will be described later, are taken from the following literature.
R,L、Covan at al、、”Experie
nce with HydrogenWater Ch
emistey in Boiling Water
Reactors”watsr Chemistey
of Nuclear Reactor System
s 4゜BNES、 London、 1986゜一方
、わが国のBWR原子力発電設備においては全く別の目
的で給復水系に酸素注入を実施している。すなわち、復
水および給水系の主に炭素鋼の配管内面に発生した錆等
の腐食生成物が原子炉圧力容器内に流入すると、この腐
食生成物が放射化されて系統内を循環するため、系統全
体が汚染され、運転員等の被ばく線量が増大する。そし
て、従来これを防止するため系統水中に所定濃度で酸素
を溶存させ、配管内面に安定な酸素被膜を形成して錆等
の腐食生成物の発生を防止している。R.L., Covan at al., “Experie.
nce with HydrogenWater Ch
Emistey in Boiling Water
Reactors"watsr Chemistry
of Nuclear Reactor System
s 4゜BNES, London, 1986゜On the other hand, in Japan's BWR nuclear power generation facilities, oxygen is injected into the water supply and condensate systems for a completely different purpose. In other words, when corrosion products such as rust that occur mainly on the inner surface of carbon steel piping in the condensate and water supply systems flow into the reactor pressure vessel, these corrosion products become radioactive and circulate within the system. The entire system will be contaminated and the exposure dose of operators etc. will increase. Conventionally, in order to prevent this, oxygen is dissolved in the system water at a predetermined concentration to form a stable oxygen film on the inner surface of the piping, thereby preventing the generation of corrosion products such as rust.
この給復水酸素注入は従来、復水脱塩器の下流、あるい
は一部のプラントでは復水脱塩器の上流で行われている
。第3図には給復水系酸素注入点19(脱塩器下流の場
合)を示している。そして、その目的は給復水系配管の
内面に安定な酸化被膜を形成させ、腐食生成物の発生を
防止することにあり、前述したSCC対策としての水素
注入実施の有無に係わらず、全く独立に行われてきたも
のである。This feed condensate oxygen injection is conventionally performed downstream of the condensate demineralizer or, in some plants, upstream of the condensate demineralizer. FIG. 3 shows the oxygen injection point 19 of the water supply and condensate system (downstream of the demineralizer). The purpose of this is to form a stable oxide film on the inner surface of the water supply and condensate system piping to prevent the generation of corrosion products, and regardless of whether or not hydrogen injection is carried out as a countermeasure against SCC, it is completely independent. It has been done.
(発明が解決しようとする課題)
さて、従来のBWR原子力発電設備において水素注入を
実施した場合、炉水中の溶存酸素濃度が低減されること
はすでに第4図に示した。この際、主蒸気中の酸素濃度
も同時に低減されることがすでにわかっている。この様
子を第5図に示す、すなわち、炉心部において水の放射
線分解によって発生する酸素および水素は、その大部分
が主蒸気中に移行し、最終的にオフガス系で処理される
。(Problems to be Solved by the Invention) As already shown in FIG. 4, when hydrogen injection is performed in conventional BWR nuclear power generation equipment, the dissolved oxygen concentration in reactor water is reduced. It has already been found that at this time, the oxygen concentration in the main steam is also reduced at the same time. This situation is shown in FIG. 5. Most of the oxygen and hydrogen generated by radiolysis of water in the reactor core are transferred to the main steam and finally treated in the off-gas system.
水素注入時にこの放射線分解による酸素および水素の発
生量が抑制されれば、炉水中の溶存酸素濃度が低下する
のみならず、主蒸気中の酸素濃度そのものが低下する。If the amount of oxygen and hydrogen generated by this radiolysis during hydrogen injection is suppressed, not only the dissolved oxygen concentration in the reactor water will decrease, but also the oxygen concentration itself in the main steam will decrease.
従って、復水器3で凝縮した復水中の溶存酸素濃度も大
幅に低下することになる。−例として、通常運転時に1
0〜20Ppbであった復水中の溶存酸素濃度が水素注
入時にはI PPb以下になったという報告かつぎの文
献に開示されている。Therefore, the dissolved oxygen concentration in the condensed water condensed in the condenser 3 also decreases significantly. - For example, 1 during normal operation.
It is reported in the following literature that the dissolved oxygen concentration in condensate, which was 0 to 20 Pppb, became less than IPPb when hydrogen was injected.
T、Kitabata et al、、”Experi
ence with HydrogenAdditio
n Water Che++1stry in the
Fugen NuclearPower 5tati
on”、 Proc of 1988 JAIF Iv
t Covf onすater Chemistry
in Nuclear Power Plants、J
AIF。T. Kitabata et al., “Experi
ence with Hydrogen Addition
n Water Che++1try in the
Fugen Nuclear Power 5tati
on”, Proc of 1988 JAIF Iv
t Covf onstar Chemistry
in Nuclear Power Plants, J
A.I.F.
Tokyo、 19813゜ このような低酸素濃度の条件になると、復水器。Tokyo, 19813゜ When conditions of such low oxygen concentration occur, the condenser.
ホットウェル、復水配管等の主要構成材料である炭素鋼
からの腐食溶出は増大するという問題が生じる。これは
安定な酸化皮膜を維持するために必要な酸素が供給され
なくなることによる。たとえば新型転換炉「ふげん」に
おける実機水素注入においてはイオン状(溶解性)およ
びクラッド状(不溶解性)の腐食生成物(主要元素はF
e)発生量は共に増大することが上記文献に報告されて
いる。第6図は復水中のFeイオンレベルが水素注入実
施前後に上昇する様子を示している。これによると19
84年の水素注入開始以降、Feイオン濃度は徐々に上
昇し、 3 PPb以下程度で推移していたものが、5
〜1Oppb程度にまで上昇している。A problem arises in that corrosion elution from carbon steel, which is the main constituent material of hot wells, condensate piping, etc., increases. This is because the oxygen necessary to maintain a stable oxide film is no longer supplied. For example, during actual hydrogen injection in the new converter reactor "Fugen", ionic (soluble) and cladding (insoluble) corrosion products (the main element is F
e) It is reported in the above literature that the amount of generation increases together. FIG. 6 shows how the Fe ion level in the condensate increases before and after hydrogen injection. According to this, 19
Since the start of hydrogen injection in 1984, the Fe ion concentration has gradually increased, from 3PPb or below to 5PPb.
It has increased to about ~1 Oppb.
腐食生成物発生の増大は前述のように運転員等の被曝線
量の増大につながるので好ましくない。An increase in the generation of corrosion products is undesirable because it leads to an increase in the radiation dose to operators and the like, as described above.
また、復水浄化系に対しても負荷が増大することとなり
、前置フィルター(粉末樹脂)あるいは混床式復水脱塩
器の逆洗頻度が増加する。このことは、運転員の作業量
の増大とともに廃樹脂、廃液等の廃棄物発生量の増大に
つながる。従って、水素注入時においても復水系の炭素
鋼酸化皮膜が安定に維持されるよう対策を施す必要があ
る。In addition, the load on the condensate purification system increases, and the frequency of backwashing of the pre-filter (powdered resin) or mixed bed condensate demineralizer increases. This leads to an increase in the workload of the operator and an increase in the amount of waste generated such as waste resin and waste liquid. Therefore, it is necessary to take measures to maintain the condensate-based carbon steel oxide film stably even during hydrogen injection.
一方、現状の給復水系酸素注入では、系統水中への酸素
の供給は復水脱塩器の下流側で行っている。すなわち、
この復水脱塩器下流側の配管内面にのみ安定な酸化被膜
が形成されるようにし、この復水脱塩器の上流側の配管
内面で生じた腐食生成物はこの復水脱塩器で除去するよ
うに構成されていた。しかし、実際にはこの復水脱塩器
では系統水中に含まれる腐食生成物のうちの50〜70
%程度しか除去できず、残り30〜50%は原子炉圧力
容器内に流入して系統内を循環してしまい、系統全体の
汚染度が高くなり運転員の被曝線量が増加してしまう不
具合を生じる課題があった。On the other hand, in the current oxygen injection system for water supply and condensation, oxygen is supplied to the system water downstream of the condensate demineralizer. That is,
A stable oxide film is formed only on the inner surface of the pipe on the downstream side of this condensate demineralizer, and corrosion products generated on the inner surface of the pipe on the upstream side of this condensate demineralizer are removed by this condensate demineralizer. It was configured to remove. However, in reality, this condensate demineralizer accounts for 50 to 70% of the corrosion products contained in the system water.
The problem is that only about 30% can be removed, and the remaining 30% to 50% flows into the reactor pressure vessel and circulates within the system, increasing the contamination level of the entire system and increasing the radiation exposure of operators. There were challenges that arose.
本発明は以上の事情にもとづいてなされたものであり、
その目的は、水素注入を実施するBWR原子力発電設備
において復水系の溶存酸素濃度低下に伴う腐食生成物の
発生を確実に防止でき、系統の汚染防止、運転員の被曝
低減を達成できる原子力発電設備を提供することにある
。The present invention has been made based on the above circumstances,
The purpose of this is to reliably prevent the generation of corrosion products associated with a decrease in dissolved oxygen concentration in the condensate system in BWR nuclear power generation facilities that perform hydrogen injection, prevent system contamination, and reduce radiation exposure for operators. Our goal is to provide the following.
(課題を解決するための手段)
本発明は原子炉給水系または原子炉一次系の系統水中に
水素を注入する水素注入機構を備えた原子力発電設備に
おいて、前記原子炉給復水系の腐食生成物発生低減を目
的として前記原子炉一次系の復水器のホットウェル内の
系統水中に過酸化水素を注入する過酸化水素注入機構を
設けかつ復水浄化系の下流側に水素注入機構を設けてな
ることを特徴とする。(Means for Solving the Problems) The present invention provides a nuclear power generation facility equipped with a hydrogen injection mechanism for injecting hydrogen into system water of a reactor water supply system or a reactor primary system, in which corrosion products of the reactor water supply and condensate system are removed. A hydrogen peroxide injection mechanism is provided for injecting hydrogen peroxide into the system water in the hot well of the condenser of the reactor primary system for the purpose of reducing generation, and a hydrogen injection mechanism is provided downstream of the condensate purification system. It is characterized by becoming.
(作用)
水素注入時には復水器から復水浄化系下流の酸素注入点
までの間は極めて低い溶存酸素濃度となり、構成材料で
ある炭素鋼の腐食溶出が促進されてしまうが、復水器ホ
ットウェ、ルから過酸化水素を注入することにより安定
な酸化皮膜を維持し、腐食生成物発生低減を図る。(Function) During hydrogen injection, the concentration of dissolved oxygen between the condenser and the oxygen injection point downstream of the condensate purification system is extremely low, which accelerates corrosion and elution of the carbon steel that is the constituent material. By injecting hydrogen peroxide from the tank, a stable oxide film is maintained and the generation of corrosion products is reduced.
過酸化水素は酸素よりも標準電極電位が高く、腐食のカ
ソード反応として酸素と同等以上に作用する。25℃に
おる標準電極電位の値は次のとうりである。Hydrogen peroxide has a higher standard electrode potential than oxygen, and acts on the cathode of corrosion as well as or better than oxygen. The standard electrode potential values at 25°C are as follows.
従って過酸化水素の注入により復水系の防食を達成する
ことが可能である。Therefore, it is possible to achieve corrosion protection of the condensate system by injection of hydrogen peroxide.
過酸化水素は水に対する溶解性が極めて高く。Hydrogen peroxide has extremely high solubility in water.
復水器ホットウェルから系統水中へ注入した場合、機器
・配管の防食に有効に作用する。これに対し酸素を注入
した場合はその溶解度が小さいため、系統水中に有効に
溶存せず、オフガス系へ移行してしまうことが懸念され
る。また、給復水系で余剰となった過酸化水素は給水加
熱器を経ることにより熱分解して水と酸素とになるため
、原子炉系機器・配管に直接悪影響を及ぼすことはない
。When injected into the system water from the condenser hotwell, it effectively protects equipment and piping from corrosion. On the other hand, when oxygen is injected, its solubility is low, so there is concern that it will not be effectively dissolved in the system water and will migrate to the off-gas system. In addition, excess hydrogen peroxide in the water supply and condensate system is thermally decomposed into water and oxygen through the feed water heater, so it does not have a direct adverse effect on reactor system equipment and piping.
これにより、復水系上流の防食を達成できるとともに炉
心への腐食生成物持ち込みによる運転員の被曝線量増大
を防止できる。また復水浄化装置の逆洗頻度を低減でき
る6さらに、従来、設置されている給水酸素注入が不要
となる。This makes it possible to achieve corrosion protection upstream of the condensate system, and to prevent an increase in the radiation exposure of operators due to the introduction of corrosion products into the reactor core. Furthermore, the frequency of backwashing of the condensate purification device can be reduced6.Furthermore, the conventionally installed water supply oxygen injection becomes unnecessary.
(実施例)
以下、本発明を図面に示す実施例にもとすいて説明する
。(Example) Hereinafter, the present invention will be explained based on an example shown in the drawings.
第1図は本発明の第1の実施例で、水素注入を行う原子
炉一次系と、気体廃棄物処理系の一部を示す系統図であ
る。すなわち、原子炉一次系において、炉心1で発生し
た蒸気はタービン2で仕事をした後、復水器3に導かれ
、この復水器3で冷却凝縮されて復水する。この復水は
ポンプ4.復水浄化系5を経由して高圧復水ポンプ6、
給水加熱器7.給水ポンプ8により昇温、加圧されて原
子炉圧力容器9に注入される。なお、図中lOは原子炉
再循環ポンプであり、原子炉圧力容器9内の炉水を強制
的に再循環させ、炉心流量を増加させるものである。上
記構成の原子炉一次系において。FIG. 1 is a first embodiment of the present invention, which is a system diagram showing a primary reactor system for hydrogen injection and part of a gaseous waste treatment system. That is, in the primary reactor system, steam generated in the reactor core 1 performs work in the turbine 2, and then is led to the condenser 3, where it is cooled and condensed to condense. This condensate is pumped 4. High pressure condensate pump 6 via condensate purification system 5;
Feed water heater7. The water is heated and pressurized by the feed water pump 8 and then injected into the reactor pressure vessel 9. Note that lO in the figure is a reactor recirculation pump, which forcibly recirculates the reactor water in the reactor pressure vessel 9 to increase the reactor core flow rate. In the primary reactor system with the above configuration.
水素注入は復水浄化系5の下流で高圧復水ポンプの上流
にある注入点11からなされている。例示した既設プラ
ント以外のものにおいても前述した注入点から注入され
ている例が多い。Hydrogen injection takes place from an injection point 11 located downstream of the condensate purification system 5 and upstream of the high pressure condensate pump. Even in plants other than the exemplified existing plants, there are many examples in which water is injected from the above-mentioned injection points.
さて、この水素注入技術においては前述したように余剰
水素を気体廃棄物処理系(オフガス系)で再結合処理す
る必要があり、通常、気体廃棄物処理系に酸素注入を行
い、オフガス再結合器で余剰水素とオフガス系注入酸素
との反応を行わせ、処理している。Now, in this hydrogen injection technology, as mentioned above, it is necessary to recombine excess hydrogen in the gaseous waste treatment system (off-gas system), and normally oxygen is injected into the gaseous waste treatment system, and then the off-gas recombiner The excess hydrogen is processed by reacting it with the oxygen injected into the off-gas system.
第1図には気体廃棄物処理系の構成をあわせて示したが
、復水器3から排出されるオフガスは空気抽出器13.
オフガス予熱器14を経てオフガス再結合器15で処理
され、オフガス復水器16を通って気体廃棄物処理され
る。酸素注入点17は空気抽出器13とオフガス予熱器
14の中間に位置し、酸素注入機構18から酸素を注入
する。The configuration of the gaseous waste treatment system is also shown in FIG.
It passes through an off-gas preheater 14, is processed in an off-gas recombiner 15, and passes through an off-gas condenser 16 for gaseous waste treatment. The oxygen injection point 17 is located between the air extractor 13 and the off-gas preheater 14 and injects oxygen from the oxygen injection mechanism 18 .
また、給復水系酸素注入点19からは給復水系の防食の
ため給復水系酸素注入機構20により酸素が注入される
。Furthermore, oxygen is injected from the water supply and condensate system oxygen injection point 19 by a water supply and condensate system oxygen injection mechanism 20 to prevent corrosion of the water supply and condensate system.
このようなりWR原子力発電設備において、本発明では
第1図に示すように原子炉一次系の復水器3のホットウ
ェル内に連通ずる過酸化水素機構21を設け、この過酸
化水素注入機構21から復水器3のホットウェル内の系
統水中に過酸化水素を注入する。この過酸化水素の注入
により、水素注入時においても復水器3から給復水系酸
素注入点19までの間の腐食生成物の発生抑制が可能と
なる。In such a WR nuclear power generation facility, the present invention provides a hydrogen peroxide mechanism 21 that communicates with the hot well of the condenser 3 of the reactor primary system as shown in FIG. Hydrogen peroxide is injected into the system water in the hot well of condenser 3. By injecting hydrogen peroxide, it is possible to suppress the generation of corrosion products between the condenser 3 and the oxygen injection point 19 in the water supply and condensate system even during hydrogen injection.
通常、給復水系の防食に必要とされる酸素量は給水濃度
換算でや< 50ppb以下である。従って、この量に
相当する過酸化水素の量は
)120.→1/202+H,Oの式から給水濃度換算
で、2倍の約100ppb以下となる。Normally, the amount of oxygen required for corrosion protection in water supply and condensate systems is less than <50 ppb in terms of feed water concentration. Therefore, the amount of hydrogen peroxide corresponding to this amount is )120. → From the formula 1/202 + H, O, the feed water concentration is converted to approximately 100 ppb or less, which is twice as much.
第2図は本発明の第2の実施例を示した系統図で、第1
図と同一部分には同一符号で示し、重複する部分の説明
を省略する。第2図は第1図における給復水系酸素注入
機構2oを削除した場合の実施例である。すなわち、給
復水系が十分に防食され、安定な酸化皮膜が維持されて
いれば、復水器3から注入された過酸化水素は給復水系
において大幅に消費されることはない。従って、復水浄
化系5の上流で過酸化水素注入機構21がら100pp
b程度の過酸化水素を注入しておけば、従来の給復水系
酸素注入は不要となる。FIG. 2 is a system diagram showing a second embodiment of the present invention.
Components that are the same as those in the figures are indicated by the same reference numerals, and explanations of overlapping components will be omitted. FIG. 2 shows an embodiment in which the water supply and condensate system oxygen injection mechanism 2o in FIG. 1 is removed. That is, if the water supply and condensate system is sufficiently protected against corrosion and a stable oxide film is maintained, the hydrogen peroxide injected from the condenser 3 will not be significantly consumed in the water supply and condensate system. Therefore, upstream of the condensate purification system 5, the hydrogen peroxide injection mechanism 21 contains 100 pp.
By injecting hydrogen peroxide in an amount of about b, the conventional oxygen injection into the water supply and condensate system becomes unnecessary.
本発明によれば、水素注入を実施するBWRIJK子力
発電設偏力発電設備復水器ホットウェル内に過酸化水素
を注入することによって水素注入時に復水系が低溶存酸
素状態となっても復水系機器・配管の防食が達成され、
被曝低減を図ることができる。また、復水浄化装置の逆
洗頻度を低減することができる。さらに、従来の給復水
系酸素注入が不要となる利点がある。According to the present invention, by injecting hydrogen peroxide into the condenser hot well of the BWRIJK child power generation facility where hydrogen injection is carried out, even if the condensate system is in a low dissolved oxygen state at the time of hydrogen injection, recovery is possible. Corrosion protection of water-based equipment and piping has been achieved,
It is possible to reduce radiation exposure. Furthermore, the frequency of backwashing of the condensate purification device can be reduced. Furthermore, there is an advantage that the conventional oxygen injection into the water supply and condensate system is not necessary.
第1図は本発明の第1の実施例を示す系統図。
第2図は本発明の第2の実施例を示す系統図、第3図は
従来例を示す系統図、第4図および第5図はそれぞれ従
来の水素注入による炉水溶存酸素濃度低減効果および主
蒸気中酸素濃度低減効果を示す特性図、第6図は従来の
水素注入による復水系金属不純物濃度上昇を示す特性図
である。
1・・・炉心 2・・・タービン3・・・復
水器 5・・・復水浄化系9・・・原子炉圧力
容器 11・・・水素注入点12・・・水素注入機構
14・・・オフガス予熱器17・・・酸素注入点
18・・・酸素注入機構19・・・給復水系酸素注入
点
20・・・給復水系酸素注入機構
21・・・過酸化水素注入機構
代理人 弁理士 猪股祥晃(ほか1名)起謙41葦凶ρ
製
顧子棒肇ビシ菅
澹(i碕く寸)に4暫z4賑ンフ駐(fl−馳ヴン竿
(支)
一〇氷中yK4:yg(PPtn)
茅
圓FIG. 1 is a system diagram showing a first embodiment of the present invention. Fig. 2 is a system diagram showing the second embodiment of the present invention, Fig. 3 is a system diagram showing a conventional example, and Figs. 4 and 5 respectively show the effect of reducing dissolved oxygen concentration in reactor water by conventional hydrogen injection. A characteristic diagram showing the effect of reducing oxygen concentration in main steam, and FIG. 6 is a characteristic diagram showing an increase in condensate system metal impurity concentration due to conventional hydrogen injection. 1... Core 2... Turbine 3... Condenser 5... Condensate purification system 9... Reactor pressure vessel 11... Hydrogen injection point 12... Hydrogen injection mechanism
14...Off gas preheater 17...Oxygen injection point
18... Oxygen injection mechanism 19... Water supply condensate system oxygen injection point 20... Water supply condensate system oxygen injection mechanism 21... Hydrogen peroxide injection mechanism Agent Patent attorney Yoshiaki Inomata (and one other person) Kiken 41 Ashikyo rho
4 temporary z4 busy station (fl-chibun rod (branch) 10 ice medium yK4:yg (PPtn) Kayan
Claims (1)
入する水素注入機構を備えた原子力発電設備において、
前記原子炉給復水系の腐食生成物発生低減のために前記
原子炉一次系の復水器のホットウェル内の系統水中に過
酸化水素を注入する過酸化水素注入機構を設けかつ復水
浄化系の下流側に水素注入機構を設けてなることを特徴
とする原子力発電設備。In nuclear power generation equipment equipped with a hydrogen injection mechanism that injects hydrogen into the reactor water supply system or reactor primary system water,
A hydrogen peroxide injection mechanism is provided for injecting hydrogen peroxide into the system water in the hot well of the condenser of the reactor primary system in order to reduce the generation of corrosion products in the reactor feed water condensate system, and a condensate purification system is provided. Nuclear power generation equipment characterized by being provided with a hydrogen injection mechanism on the downstream side of.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1015023A JPH02196998A (en) | 1989-01-26 | 1989-01-26 | Nuclear power generation facility |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1015023A JPH02196998A (en) | 1989-01-26 | 1989-01-26 | Nuclear power generation facility |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH02196998A true JPH02196998A (en) | 1990-08-03 |
Family
ID=11877247
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1015023A Pending JPH02196998A (en) | 1989-01-26 | 1989-01-26 | Nuclear power generation facility |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH02196998A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005291815A (en) * | 2004-03-31 | 2005-10-20 | Hitachi Ltd | Methods for preventing corrosion and thinning of carbon steel |
-
1989
- 1989-01-26 JP JP1015023A patent/JPH02196998A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005291815A (en) * | 2004-03-31 | 2005-10-20 | Hitachi Ltd | Methods for preventing corrosion and thinning of carbon steel |
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