JPS5928279B2 - Main condenser - Google Patents
Main condenserInfo
- Publication number
- JPS5928279B2 JPS5928279B2 JP51094222A JP9422276A JPS5928279B2 JP S5928279 B2 JPS5928279 B2 JP S5928279B2 JP 51094222 A JP51094222 A JP 51094222A JP 9422276 A JP9422276 A JP 9422276A JP S5928279 B2 JPS5928279 B2 JP S5928279B2
- Authority
- JP
- Japan
- Prior art keywords
- main condenser
- gas
- space
- hot well
- main
- 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
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
Landscapes
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
- Structure Of Emergency Protection For Nuclear Reactors (AREA)
Description
【発明の詳細な説明】
本発明は沸騰水形原子力発電設備の主復水器に関するも
のである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a main condenser for a boiling water nuclear power generation facility.
沸騰水形原子力発電は原子炉で発生せしめた高温蒸気に
よってタービンを廻し発電を行なうが、発電に使用され
た蒸気は主復水器によって水にもどされ再び原子炉内に
送り込まれる。Boiling water nuclear power generation uses high-temperature steam generated in a nuclear reactor to rotate a turbine and generate electricity, but the steam used to generate electricity is converted back to water by a main condenser and sent back into the reactor.
主復水器で凝縮しなかった非凝縮性の気体は、所謂気体
廃棄物として脱放射化され大気中に放出される。Non-condensable gases that are not condensed in the main condenser are deradiated and released into the atmosphere as so-called gaseous waste.
第1図は主復水器関係の構成を示すものであって、原子
炉1で発生した蒸気は高圧タービン2及び低圧タービン
3を通った後、主復水器4に送られ、ここで凝縮した水
は再び原子炉1に戻される。Figure 1 shows the configuration of the main condenser. Steam generated in the reactor 1 passes through a high-pressure turbine 2 and a low-pressure turbine 3, and then is sent to the main condenser 4, where it is condensed. The water is returned to the reactor 1 again.
主復水器4内で凝縮しなかった気体は空気抽出器5によ
り抽出され、排ガス予熱器6で予熱された後、水素及酸
素は排ガス結合器7で水となり、排ガス復水器8で除か
れる。Gas that is not condensed in the main condenser 4 is extracted by an air extractor 5, and after being preheated by an exhaust gas preheater 6, hydrogen and oxygen become water in an exhaust gas combiner 7, and are removed in an exhaust gas condenser 8. It will be destroyed.
その他の排ガスはホールドアツプパイプ9及び希ガスホ
ールドアツプ装置10によって脱放射化され、排気筒1
1から大気に放出される。Other exhaust gases are deradiated by the hold up pipe 9 and rare gas hold up device 10, and are deradiated by the exhaust pipe 1.
1 is released into the atmosphere.
第2図は、主復水器の構造を示すもので、主復水器4の
内部には多数の冷却管12が配列されている蒸気室13
が設けられ、主復水器4の上部より導入された蒸気は、
冷却管12の間を通り、この際冷却管12内を流れる海
水によって冷却され、大部分は凝縮水となる。FIG. 2 shows the structure of the main condenser. Inside the main condenser 4, there is a steam chamber 13 in which a large number of cooling pipes 12 are arranged.
is provided, and the steam introduced from the upper part of the main condenser 4 is
It passes between the cooling pipes 12 and is cooled by the seawater flowing inside the cooling pipes 12, and most of it becomes condensed water.
凝縮水は主復水器4の下部にもうけられているホットウ
ェル14の屋根15の上に落ちる。The condensed water falls onto the roof 15 of the hot well 14 located at the bottom of the main condenser 4.
屋根15は傾針がつけられているので、凝縮水は流れ落
ち、ホットウェル14の両端から水路に流れ込む。Since the roof 15 is sloped, the condensed water flows down and flows into the water channel from both ends of the hot well 14.
一方、主復水器4の冷却管12の間を通っている間に凝
縮しなかった蒸気および非凝縮性気体は主復水器4の中
心部に設けられている気相部16を通って、気体排出配
管17から主復水器4の外部に導かれる。On the other hand, steam and non-condensable gas that did not condense while passing between the cooling pipes 12 of the main condenser 4 pass through the gas phase section 16 provided in the center of the main condenser 4. , are led to the outside of the main condenser 4 from the gas exhaust pipe 17.
このような主復水器の構造から明らかなように、従来は
、非凝縮性気体は主復水器内には殆んど滞留することな
く、気体廃棄物処理系に導かれていた。As is clear from such a structure of the main condenser, conventionally, non-condensable gas was guided to the gaseous waste treatment system without remaining in the main condenser.
従って、原子炉で発生した蒸気と共に、主復水器に流入
してくる放射性の気体は、殆んどその放射能を減衰する
ことなく気体廃棄物処理系に移行している。Therefore, the radioactive gas flowing into the main condenser together with the steam generated in the nuclear reactor is transferred to the gaseous waste treatment system with almost no attenuation of its radioactivity.
原子炉で発生する放射性気体には、原子炉内の燃料棒が
破損しリークしてくるクリプトン又はキセノンよりなる
核分裂生成物と、原子炉水の放射線分解などにより発生
する窒素(N)−16などよりなる放射化ガスとがある
。The radioactive gases generated in nuclear reactors include fission products such as krypton or xenon that leak when fuel rods inside the reactor break, and nitrogen (N)-16 that is generated due to radiolysis of reactor water. There is a radioactive gas consisting of:
前者の核分裂生成物は燃料棒の破損を生じなければ殆ん
ど問題はなく、たとえ燃料棒の破損により放射性気体を
発生しても気体廃棄物処理系における放射線の漏洩は殆
んど問題はない。The former type of fission products poses almost no problem unless the fuel rods are damaged, and even if radioactive gas is generated due to fuel rod damage, there is almost no problem with radiation leakage in the gaseous waste treatment system. .
これに対して放射化ガスは燃料の破損には関係なく生成
し、主蒸気と共に主復水器内に流入してくるもので、こ
の放射化ガス中でN−16はエネルギーが非常に高い(
6〜7MeVのγ線を放射)ため、発電所運転中は空気
抽出器5、排ガス予熱器6などへの人の立入りを殆んど
不可能にしており、さらに、排ガス結合器7、排ガス復
水器8においてもその影響が大きい。On the other hand, activated gas is generated regardless of fuel damage and flows into the main condenser together with the main steam, and N-16 in this activated gas has extremely high energy (
6 to 7 MeV), it is almost impossible for people to enter the air extractor 5, exhaust gas preheater 6, etc. while the power plant is in operation. This influence is also large on the water dispenser 8.
即ち、例えば、電気出力100万kw級の発電所の空気
抽出器5の表面の線量率は約5 rer11/hr度で
あり、排ガス予熱器6、排ガス結合器7の表面における
線量率は約0.3 rem / hrから1 rem/
hrである。That is, for example, the dose rate on the surface of the air extractor 5 of a power plant with an electric output of 1 million kW class is about 5 rer11/hr degree, and the dose rate on the surfaces of the exhaust gas preheater 6 and the exhaust gas combiner 7 is about 0. .3 rem/hr to 1 rem/
It is hr.
このため、従来の原子力発電所では、空気抽出器5、排
ガス予熱器6、排ガス結合器7などの機器は遮蔽壁で囲
まれた中に設置され、これによって遮蔽壁の附近の通路
の線量率の軽減をはかつている。For this reason, in conventional nuclear power plants, equipment such as the air extractor 5, exhaust gas preheater 6, exhaust gas combiner 7, etc. is installed inside a shielding wall, which increases the dose rate in the passage near the shielding wall. We are trying to reduce the
このため100(1’771から150cIrLの遮蔽
壁をもうけ、遮蔽壁には、これら機器の故障した場合に
立入るための遮蔽を考慮した構造の出入口が設けである
が、これら機器表面の線量率が非常に高いため、実質上
は発電所の運転中に、これら機器の保修などの作業を行
なうことは不可能であった。For this reason, a shielding wall with a capacity of 100 (1'771 to 150 cIrL) has been constructed, and the shielding wall has an entrance and exit structure that takes into consideration the shielding for entering in the event of a malfunction of these devices, but the dose rate on the surface of these devices Because of the extremely high amount of electricity, it was virtually impossible to carry out maintenance work on these devices while the power plant was in operation.
例えば、発電所運転中に空気抽出器5の付近に近よるこ
とのできる時間は約1分程度であり、このため、修理が
不可避の場合には発電所を停止して作業を実施せねばな
らなかった。For example, while the power plant is operating, you can only get close to the air extractor 5 for about one minute, so if repairs are unavoidable, the power plant must be stopped to carry out the work. There wasn't.
従って、従来の沸騰水形の原子力発電所では、空気抽出
器、排ガス予熱器などの周囲の遮蔽壁の厚さが非常に厚
く、その結果、発電所内の遮蔽壁の占めるスペースが大
きく、発電所の建家自体が大きくなりコストが高くなる
。Therefore, in a conventional boiling water nuclear power plant, the thickness of the shielding wall around the air extractor, exhaust gas preheater, etc. is very thick, and as a result, the space occupied by the shielding wall in the power plant is large, and the power plant The building itself becomes larger and the cost increases.
空気抽出器、排ガス予熱器などの周辺の線量率が高く、
発電所を運転しながらの保修、修理が不可能である。The dose rate is high around the air extractor, exhaust gas preheater, etc.
It is impossible to maintain or repair the power plant while it is operating.
万一、これら機器が故障した場合、発電所全体の運転を
停止して作業をすることになり、稼動率の低下により商
業用の炉としてはコスト高となる等の欠点を有していた
。If any of these devices were to fail, the operation of the entire power plant would have to be shut down, resulting in lower operating rates and higher costs for commercial furnaces.
本発明は、沸騰水形原子力発電設備の主復水器に続く廃
棄物処理系における機器表面線量率の軽減を目的とする
もので、蒸気室内に設けられている気相部と、該気相部
を通過した非凝縮性気体を外部に設けられている気体廃
棄物処理系に排出する排出口と、一連の復水通路及び該
復水通路の上部に前記蒸気室と仕切られて形成−されて
いる空間部を有するホットウェルとを有する主復水器に
おいて、前記非凝縮性気体をその一端から前記空間部に
導入し、該空間部を経由して他端から前記排気口に導出
し放射能を減衰せしめる流路を有していることを特徴と
するものである。The present invention aims to reduce the equipment surface dose rate in the waste treatment system following the main condenser of boiling water nuclear power generation equipment. an exhaust port for discharging the non-condensable gas that has passed through the chamber to an external gaseous waste treatment system, a series of condensate passages, and an upper part of the condensate passages that is partitioned from the steam chamber. In a main condenser having a hot well having a space, the non-condensable gas is introduced into the space from one end, and is led out to the exhaust port from the other end via the space and radiated. It is characterized by having a flow path that attenuates the power.
以下、実施例を図面によって説明する。Examples will be described below with reference to the drawings.
第3図は、その一実施例の構造を示すもので、第2図の
符号と同一番号は同一部分を示している。FIG. 3 shows the structure of one embodiment, and the same numbers as those in FIG. 2 indicate the same parts.
この装置が第2図の従来の主復水器と異なるところは、
気相部16を直接気体排出配管17に接続していない点
であり、気相部16が非凝縮性気体配管18を通ってホ
ットウェル14の水路の水面上部空間部19を接続され
、主復水器最終段水路20の上部に位置するホットウェ
ル14の屋根15に接続する配管21で気体排出配管1
1に接続している点である。The difference between this device and the conventional main condenser shown in Figure 2 is that
The gas phase part 16 is not directly connected to the gas discharge pipe 17, and the gas phase part 16 is connected to the space 19 above the water surface of the water channel of the hot well 14 through the non-condensable gas pipe 18. Gas discharge pipe 1 is connected to the pipe 21 that connects to the roof 15 of the hot well 14 located at the upper part of the final stage water channel 20.
This is the point where it is connected to 1.
ホットウェル14は、第3図の縦断面図及び第4図の横
断面図に示す如く、主復水器4の底部にもうけられ、テ
ーパーを有する屋根15を有し、主復水器4の底部と屋
根15との間には、その上下がそれぞれ屋根15と主復
水器の底部に固定される一定間隔で保持された隔壁22
を有し、この隔壁22の側面は、相対向する主復水器の
側壁に交互に固定されており、ホットウェルの両端部に
は凝縮水の初段水路23を形成し、中央部の底部には復
水出口24がもうけられており、初段水路23よりホッ
トウェル15に入った凝縮水はホットウェル14の隔壁
22によって形成された蛇行する流路を通って復水出口
24より復水系を出てゆく。As shown in the vertical cross-sectional view of FIG. 3 and the cross-sectional view of FIG. 4, the hot well 14 is provided at the bottom of the main condenser 4 and has a tapered roof 15. Between the bottom and the roof 15, there is a partition wall 22 held at a constant interval whose upper and lower sides are fixed to the roof 15 and the bottom of the main condenser, respectively.
The side walls of this bulkhead 22 are alternately fixed to the opposing side walls of the main condenser, and an initial water channel 23 for condensed water is formed at both ends of the hot well, and a condensed water channel 23 is formed at the bottom of the center part. A condensate outlet 24 is provided, and the condensed water that enters the hot well 15 from the first stage waterway 23 passes through the meandering flow path formed by the partition wall 22 of the hot well 14 and exits the condensate system from the condensate outlet 24. I'm going to go.
又、ホットウェル14に非凝縮性気体配管18を通り入
った非凝縮性気体は、隔壁22によって形成された蛇行
する凝縮水流路上の蛇行空間を通って配管21を経て気
体排出配管17より主復水器を出るよう構成されている
。In addition, the non-condensable gas that has entered the hot well 14 through the non-condensable gas pipe 18 passes through the meandering space on the meandering condensed water flow path formed by the partition wall 22, passes through the pipe 21, and returns from the main gas discharge pipe 17. Configured to exit the water bowl.
従って、主復水器4の上部から入った蒸気およびN−1
6などの非凝縮性気体は、冷却管12の間を通っている
間に、蒸気は凝縮し、主復水器4の初段水路23に集め
られ、順次、ホットウェル14内の蛇行流路を移行し、
復水出口24より、復水系を出てゆく、一方、非凝縮性
の気体は、気相部16より非凝縮性気体配管18を通り
、主復水器4両側の初段水路23側に導かれ、水路の水
面上部の空間部19を凝縮水と同じ蛇行流路を通ってホ
ットウェル14を通過し、ホットウェル14の頂部を経
て気体排出配管17から主復水器4外に出て、空気抽出
器5へ導かれる。Therefore, the steam entering from the upper part of the main condenser 4 and the N-1
While the non-condensable gas such as 6 passes between the cooling pipes 12, the steam is condensed and collected in the first stage waterway 23 of the main condenser 4, and is sequentially passed through the meandering flow path in the hot well 14. transition,
On the other hand, non-condensable gas exits the condensate system from the condensate outlet 24 and is guided from the gas phase section 16 through the non-condensable gas piping 18 to the first-stage water channel 23 side on both sides of the main condenser 4. , passes through the hot well 14 through the space 19 above the water surface of the water channel through the same meandering flow path as the condensed water, passes through the top of the hot well 14, exits the gas discharge pipe 17 to the outside of the main condenser 4, and the air is It is guided to the extractor 5.
このように非凝縮性気体をホットウェル14の凝縮水水
路の上部の空内部19を通す場合には、非凝縮性気体は
、第2図の如き従来の場合よりも約20秒、主復水器4
内に滞留させておくことが可能となる。In this way, when the non-condensable gas is passed through the hollow space 19 above the condensate water channel of the hot well 14, the non-condensable gas flows into the main condensate water for about 20 seconds compared to the conventional case as shown in FIG. Vessel 4
It is possible to keep it inside.
一般に、放射能は時間の経過と共に指数関数的に減衰す
るが、第5図はN−16の復水器のホールドアツプ時間
(sec)と減衰率との関係を示すもので、この図から
N−16は滞留時間のわづかな差により放射能強度に大
きな差異があることを示しており、その半減期が約7秒
である点から考えると、本実施例の如く、主復水器4内
の滞留時間を約20秒長くしたことによって、主復水器
4を出た直後のN−16の放射能強度は、従来の場合の
1/10となることを示しており、従って、空気抽出器
などの表面線量率も1/10となる。Generally, radioactivity decays exponentially over time, but Figure 5 shows the relationship between the hold-up time (sec) and the decay rate of the N-16 condenser. -16 indicates that there is a large difference in radioactivity intensity due to a slight difference in residence time, and considering that its half-life is approximately 7 seconds, it is assumed that the main condenser 4 By increasing the residence time in the condenser by approximately 20 seconds, the radioactivity intensity of N-16 immediately after leaving the main condenser 4 is 1/10 that of the conventional case. The surface dose rate of extractors etc. will also be 1/10.
このように機器表面の線量率が1/10に低減した場合
には、発電所運転中でも空気抽出器などの機器に近づく
ことが可能となり、パトロール、保修作業が十分実施可
能である、遮蔽壁の厚さを従来よりも20CrrL以上
薄くすることが可能となり、建家内のスペースの有効活
用が可能となり、かつ、コンクリートの量で1.50m
3(約340トン)節減することができ、建設コストの
低減ができる。If the dose rate on the equipment surface is reduced to 1/10 in this way, it will be possible to approach equipment such as air extractors even while the power plant is operating, and it will be possible to conduct patrols and maintenance work. It is now possible to reduce the thickness by more than 20 CrrL than before, making it possible to effectively utilize space within the building, and reducing the amount of concrete to 1.50 m.
3 (approximately 340 tons), and construction costs can be reduced.
機器が故障した場合でも簡単な修理は発電所を停止せず
に行なうことができるため、発電所の稼動率が向上でき
る等の効果を有する。Even if equipment breaks down, simple repairs can be made without stopping the power plant, which has the effect of improving the operating rate of the power plant.
以上の如く、本発明は、沸騰水形原子力発電設備の主復
水器に続く廃棄物処理系における機器表面線量率の軽減
を可能にするものであって、原子力発電所における被ば
く低減も可能となるもので工業上の効果は大なるもので
ある。As described above, the present invention makes it possible to reduce the equipment surface dose rate in the waste treatment system following the main condenser of boiling water nuclear power generation equipment, and also makes it possible to reduce exposure at nuclear power plants. This has great industrial effects.
第1図は原子力発電設備の主復水器に続く廃棄物処理系
の系統図、第2図は従来の主復水器の縦断面図、第3図
は本発明の主復水器の一実施例の縦断面図、第4図は同
じくその要部の横断面図、第5図は復水器のホールドア
ツプ時間と減衰率との関係を示す特性曲線図である。
符号の説明、4・・・・・・主復水器、12・・・・・
・冷却管、13・・・・・・蒸気室、14・・・・・・
ホットウェル、16・・・・・・気相部、17・・・・
・・気体排出配管、18・・・・・・非凝縮性気体配管
。Fig. 1 is a system diagram of the waste treatment system following the main condenser of a nuclear power generation facility, Fig. 2 is a vertical cross-sectional view of a conventional main condenser, and Fig. 3 is an illustration of the main condenser of the present invention. FIG. 4 is a longitudinal cross-sectional view of the embodiment, and FIG. 4 is a cross-sectional view of the main part thereof. FIG. 5 is a characteristic curve diagram showing the relationship between the hold-up time and the attenuation rate of the condenser. Explanation of symbols, 4...Main condenser, 12...
・Cooling pipe, 13...Steam room, 14...
Hot well, 16... Gas phase section, 17...
...Gas discharge piping, 18...Non-condensable gas piping.
Claims (1)
過した非凝縮性気体を外部に設けられている気体廃棄物
処理系に排出する排出口と、一連の復水通路及び該復水
通路の上部に前記蒸気室と仕切られて形成されている空
間部を有するホットウェルとを有する主復水器において
、前記非凝縮性気体をその一端から前記空間部に導入し
、該空間部を経由して他端から前記排気口に導出し放射
能を減衰せしめる流路を有していることを特徴とする主
復水器。 2 前記ホットウェルの空間部が、複数個の隔壁によっ
て形成され、外周端より中心に向って蛇行する中高の頂
部を有する空間より構成され、前記一端が前記外周端に
位置し、前記他端が前記頂部に位置している特許請求の
範囲第1項記載の主復水路。[Claims] 1. A gas phase section provided in the steam chamber, an outlet for discharging non-condensable gas that has passed through the gas phase section to a gaseous waste treatment system provided outside, and a series of A main condenser having a condensate passage and a hot well having a space formed above the condensate passage to be partitioned from the steam chamber, the non-condensable gas is supplied from one end to the space. What is claimed is: 1. A main condenser comprising a flow path for introducing radioactivity into the air and leading it out from the other end to the exhaust port via the space to attenuate radioactivity. 2. The space of the hot well is formed by a plurality of partition walls and has a medium-high top meandering from the outer peripheral end toward the center, one end of which is located at the outer peripheral end, and the other end of which is located at the outer peripheral end. The main return channel according to claim 1, which is located at the top.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51094222A JPS5928279B2 (en) | 1976-08-06 | 1976-08-06 | Main condenser |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51094222A JPS5928279B2 (en) | 1976-08-06 | 1976-08-06 | Main condenser |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5320003A JPS5320003A (en) | 1978-02-23 |
| JPS5928279B2 true JPS5928279B2 (en) | 1984-07-11 |
Family
ID=14104278
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51094222A Expired JPS5928279B2 (en) | 1976-08-06 | 1976-08-06 | Main condenser |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5928279B2 (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS59145484A (en) * | 1983-02-07 | 1984-08-20 | Hitachi Ltd | Condenser |
| JPS59153094A (en) * | 1983-02-17 | 1984-08-31 | Mitsubishi Heavy Ind Ltd | Method of deaerating from condensate |
| US6269867B1 (en) * | 1994-12-02 | 2001-08-07 | Hitachi, Ltd | Condenser and power plant |
| JP3735405B2 (en) * | 1995-12-15 | 2006-01-18 | 株式会社東芝 | Condenser |
| JP6760900B2 (en) * | 2017-08-09 | 2020-09-23 | 日立Geニュークリア・エナジー株式会社 | Boiling water reactor |
-
1976
- 1976-08-06 JP JP51094222A patent/JPS5928279B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5320003A (en) | 1978-02-23 |
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