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JP4127580B2 - Treatment method of radioactive gas waste - Google Patents
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JP4127580B2 - Treatment method of radioactive gas waste - Google Patents

Treatment method of radioactive gas waste Download PDF

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Publication number
JP4127580B2
JP4127580B2 JP03908299A JP3908299A JP4127580B2 JP 4127580 B2 JP4127580 B2 JP 4127580B2 JP 03908299 A JP03908299 A JP 03908299A JP 3908299 A JP3908299 A JP 3908299A JP 4127580 B2 JP4127580 B2 JP 4127580B2
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gas
dehumidifier
exhaust gas
hollow fiber
radioactive
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JP2000241587A (en
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修一 阿部
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Toshiba Corp
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Toshiba Corp
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    • 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

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Description

【0001】
【発明の属する技術分野】
本発明は、除湿装置における湿分除去方法を改良した放射性気体廃棄物の処理処理方法に関する。
【0002】
【従来の技術】
一般に、沸騰水型原子炉の冷却材は、炉心を通過する間に中性子照射を受けて、一部が酸素と水素に分解し、その上、さらに3 H,16N,19O等が生じる。また、燃料棒に生じたピンホール等からKrやXeなどの放射性の希ガスが漏洩し、これらの希ガスが冷却材に混入してタービン系に送られている。この他、タービン主復水器へ外気からの漏れ込みがある。
【0003】
これらの放射性気体廃棄物(以下、単に排ガスと称す)により、沸騰水型原子力発電所におけるタービン系は原子炉並に遮蔽設備を施して所内および周辺の健全性を維持する必要がある。
【0004】
ところで、前記排ガスは、一般に非凝縮性であるので、蒸気系統内、特にタービン主復水器の内部に滞留する。このため、従来はタービン主復水器内に滞留する排ガスを空気抽出器により抽気し、活性炭式希ガスホールドアップ塔に導いて処理するようにしている。
【0005】
図2は従来の原子力発電所に設置されている放射性廃棄物処理設備の一例を示すもので、タービン主復水器の内部に滞留した排ガスは空気抽出器1により抽気され、予熱器3,再結合器4および排ガス復水器5から構成される水素再結合装置2に導かれて、水素ガスの再結合および減容処理がなされる。
【0006】
空気抽出器1から水素再結合装置2に導かれた排ガスはまず排ガス中に含まれる酸素と水素が効率よく再結合する温度まで予熱器3で予熱されたのち、下流の再結合器4に導かれ、排ガス中の水素と酸素とが再結合反応により水蒸気となる。さらに、その下流の排ガス復水器5では外部冷却水による冷却水により排ガス中の水蒸気は凝縮されてほとんど水となって排ガス中から分離され、分離された水は図示しないタービン主復水器に戻される。
【0007】
一方、水分が分離除去された排ガスは図2に示すように、除湿装置6に導かれて湿分が十分除去された後、活性炭式希ガスホールドアップ塔7に導かれる。そして、排ガス中に残った放射性ガス(主体はXe,Kr等の希ガス)を活性炭に吸着させ、長時間のホールドアップののち、真空ポンプ8により排気筒9から大気へ放出される。なお、図2中符号10は活性炭式希ガスホールドアップ塔室,11は空調設備,12,13はダクトである。
【0008】
これらの機器は、各々気密あるいはそれに準じた状態の室に分離され、各室は空調が行なわれている。特に、図2に示すように活性炭式希ガスホールドアップ塔室10他の一般空調とは別に、専用空調設備11からダクト12,13を介して空調がなされ、活性炭の吸着性能維持のため、活性炭式希ガスホールドアップ塔入口配管14内を一定温度に保つことができるようになっている。
【0009】
図3は図2で示した従来の除湿装置6廻りの詳細を示すもので、図3中、符号16で示す除湿装置は水蒸気透過係数の大きい中空糸膜17を内蔵する除湿装置16を用い、前記中空糸膜17の二次側に除湿装置16により乾燥された一次側ガスの一部をパージ用とし、主復水器の真空圧により二次側を一次側圧力から低い圧力まで吸引することにより、中空糸膜17の一次側と二次側に水蒸気分圧差を設け、除湿を行うようになっている。
【0010】
なお、図3中、符号18はパージガス流量計,19はパージガス量調整弁,20はパージガス圧力調整弁,21はパージガス圧力調整出口弁,22は除湿装置出口圧力計,24は除湿装置出口流量計,25は除湿装置出口流量調整弁である。
【0011】
【発明が解決しようとする課題】
従来の放射性気体廃棄物の処理方法においては、除湿装置16の二次側を一次側圧力より低い圧力まで吸引する方法として、主復水器の真空圧力を利用していたが、プラント起動停止時に主復水器の真空圧が確保出来ないときは気体廃棄物処理系統を運転出来ないという課題がある。また、定期点検時においても主復水器の真空圧が確保出来ないことで、気体廃棄物処理系統の単独運転が出来ないという課題もある。
【0012】
本発明は上記課題を解決するためになされたもので、主復水器の真空圧を用いることなく、排ガス中の湿分を連続的に除去することができ、高い信頼性が得られる放射性気体廃棄物の処理装置を提供することを目的とする。
【0013】
【課題を解決するための手段】
本発明は、原子力発電プラントから発生した放射性気体廃棄物を主復水器から空気抽出器を通し水素結合装置に導いて再結合器による水素ガスの再結合と排ガス復水器による減容処理を行、前記減容処理した排ガスを中空糸膜を内蔵する除湿装置に導いて湿分を除去した後、活性炭式希ガスホールドアップ塔に導いて遅延処理を行うとともに、前記除湿装置により乾燥された一次側ガスの一部をパージガスとして前記中空糸膜の二次側に供給する放射性気体廃棄物の処理方法において、前記主復水器の真空圧が高い場合は前記中空糸膜の二次側排ガスを主復水器に戻し、前記主復水器の真空圧が低い場合は前記二次側排ガスをパージ用真空ポンプにより前記排ガス復水器の上流側に戻すことを特徴とする。
【0014】
また、前記除湿装置と並列に予備の中空糸膜を内蔵した除湿装置を設け、前記除湿装置外の系統内に設置された露点計により湿度を検知し、所要の湿度が得られなくなった場合、前記予備の中空糸膜を内蔵した除湿装置に前記減容処理した排ガスを導くことを特徴とする。
【0015】
さらに、前記除湿装置の状態を系統内に設置された差圧計により差圧を検知し、系統に差圧異常が生じた場合、前記予備の中空糸膜を内蔵した除湿装置に前記減容処理した排ガスを導くことを特徴とする。
【0016】
【発明の実施の形態】
本発明に係る放射性気体廃棄物の処理方法においては、除湿装置として図1に示した水蒸気透過係数の大きい中空糸膜17aを内蔵する除湿装置16aが用いられ、図2に示した空気抽出器1により引かれ、除湿装置16aの中空糸膜17a内を通過する。
【0017】
この状態で、除湿装置16aにより乾燥された一次側ガスの一部(例えば20%)をパージ用として使用し、中空糸膜の外側に供給し、かつパージ用真空ポンプ38を利用したりして、一次側より低い圧力に吸引する。
【0018】
これにより、中空糸膜17aの一次側と二次側の水蒸気分圧差を大きくすることで水蒸気透過性能が向上し、排ガス中の水蒸気分を最も効率よく除去する。つまり、排ガス中の水蒸気分が中空糸膜を透過して除去され、排ガスの湿度が所要のパーセント以下、例えば40%以下となる。
【0019】
また、前記パージ用真空ポンプ38により吸引された排ガスは、復水器上流側に接続された循環ライン40に戻されることで、プラント停止中においても気体廃棄物処理系の単独運転を可能としている。
【0020】
また、除湿装置16aの状態により所要のパーセント以下の湿度が得れらなくなった場合、系統内に設置された露点計により湿度を検知し、予備の中空糸膜17bを内蔵した除湿装置16bに切り替えることにより除湿性能が確保できるようになる。
【0021】
また、除湿装置の状態により差圧が増大又は減少した場合、系統内に設置された差圧計により差圧を検知し、予備の中空糸膜を内蔵した除湿装置に切り替えることにより除湿性能が確保できるようになる。
【0022】
本発明に係る放射性気体廃棄物の処理方法の一実施の形態を図1〜3を参照して説明する。
図1は排ガス処理装置における除湿装置16(16a,16b)周りの構成を示すもので、図中、除湿装置16a,16bは除湿装置入口弁31a,31bおよび除湿装置出口弁32a,32bを介して並列に接続され、通常運転時には一系統のみが処理運転されるようになっている。
【0023】
処理される湿潤な排ガス(温度;40℃,露点;100 %,圧力;0.8ata)が排ガス復水器5から除湿装置16a,16bに流入する。各除湿装置16a,16b内には図1に示すように水蒸気透過係数の大きい中空糸膜17a,17bがそれぞれ取り付けられており、パージ用真空ポンプ38により吸引された排ガスはこれら各中空糸膜17a,17bの内部を通過するようになっている。
【0024】
除湿装置16a系で運転中へ、排ガスの温度は除湿装置出口露点計23により測定され、系統の許容露点(例えば−20℃)以上となった場合には、警報を発するか、または除湿装置aの入口弁31a及び出口弁32aを閉し、除湿装置入口弁31b及び出口弁32bを開として運転号機を切替ることで、潤湿な排ガスを活性炭希ガスホ−ルドアップ装置へ流さないようにする。
【0025】
また、復水器出口圧力計27により系統の圧力を測定し、系統運転設定圧力(例えば大気圧)以上になった時、復水器出口循環水ライン弁29を開として復水器出口循環ライン圧力調整弁30の調整により、系統の圧力を設定値以内とする。
【0026】
また、除湿装置入口流量計28により各除湿装置16a,16bの処理量に適した流量を除湿装置入口流量調整弁19を調整することによって確保し、系統の安定運転を行っている。
【0027】
これら各除湿装置16a,16bの内部は図1に示すように除湿装置16a,16bにより乾燥された一次側ガスの一部(例えば20%)をパージ用として、パージガス量はパージガス流量計18から除湿装置入口流量計28により測定した排ガス処理量の約20%に当たる量をパージガス量調整弁20を調整することにより確保する。
【0028】
また、パージガスの圧力はパージガス圧力計36の設定圧力により、パージガス圧力調整弁20により圧力を調整されながら、プラント運転中は主復水器により、また、プラント停止中はパージ用真空ポンプ36により、一次側より低い圧力で吸引されるようになっている。
【0029】
パージ用真空ポンプにより吸引された排ガスは循環ライン40により排ガス復水器5の上流へ循環するようにすることで、プラント停止中においてもオフガス(OG)系を単独運転することが出来る。
【0030】
これにより、各中空糸膜17a,17bの内を流れる排ガス中の水蒸気分が各中空糸膜17a,17bを透過して分離除去され、排ガスの相対湿度が所要パーセント、例えばほぼ40%以下となるようになっている。活性炭式希ガスホールドアップ塔7に供給される排ガスは相対湿度を40%以下とする必要があるからである。
【0031】
また、パージ用ガスも処理装置の運転系統に対して、パージガス入口弁34a,34b、パージガス出口弁35a,35bの切り替えにより選択できるようになっている。
【0032】
次に各除湿装置16a,16bにおける湿分除去方法について説明する。
図1において、除湿装置16a側の系統が処理運転されているものとすると、復水器5で蒸気が冷却され、凝縮された排ガスは、系統を吸引する真空ポンプ8(図2参照)により、除湿装置入口弁31aを介して除湿装置16aに導かれ、その中空糸膜17a内を通過する。
【0033】
この際、除湿装置16a内部は、乾燥されたパージガスをパージガス量調整弁19により適切な流量に調整され、そのパージガスをパージガス入口弁34aを介して除湿装置16a内部に流し、水蒸気透過性向上を図る。
【0034】
また、除湿装置16aの内部を真空引きして一次側系統の圧力より低い圧力に保持するために、パージ用真空ポンプ38を利用し、パージガス出口弁35aを介してパージガス圧力計36の設定値によりパージガス圧力調整弁20により圧力調整する。これにより適切な真空引きを実施するので、中空糸膜17a内を流れる排ガス中の水蒸気分は中空糸膜17aを透過して除去され、循環ライン40を経てタービン主復水器の上流側へ戻される。
【0035】
このため、除湿装置16aを通過した後の排ガスは、その相対湿度が所要のパーセント、例えば40%以下となり、除湿装置出口弁32aを介して活性炭式希ガスホールドアップ塔7(図2参照)に導かれて遅延処理がなされる。
【0036】
除湿装置16aにトラブル等が発生し、除湿装置16aの出口の露点計23が設定値より大きくなった場合には除湿装置入口弁31a,除湿装置出口弁32a,パージガス入口弁34aおよびパージガス出口弁35aが閉となる。これとともに、除湿装置入口弁31b,除湿装置出口弁32b,パージガス入口弁34bおよびパージガス出口弁35bが開となり、除湿装置16b側に系統が切り替えられる。
【0037】
また、除湿装置16aにトラブル等が発生し、除湿装置16aの差圧計33が許容値より外れた場合には除湿装置入口弁31a,除湿装置出口弁32a,パージガス入口弁34aおよびパージガス出口弁35aが閉となる。これとともに、除湿装置入口弁31b,除湿装置出口弁32b,パージガス入口弁34bおよびパージガス出口弁35bが開となり、除湿装置16b側に系統が切り替えられる。
【0038】
【発明の効果】
本発明によれば、プラント起動停止時、及びプラント停止中タービン主復水器の真空が確保出来ない期間に排ガス系の運転ができる。また、定期点検中の運転で除湿されない空気が希ガスホ−ルドアップ系に流入することがなくなる。
【図面の簡単な説明】
【図1】本発明に係る放射性気体廃棄物の処理方法の実施の形態を説明するための除湿装置周りを示す系統図。
【図2】従来の放射性気体廃棄物の処理設備を示す系統図。
【図3】図2における脱湿塔周りを示す系統図。
【符号の説明】
1…空気抽出器、2…水素再結合装置、3…排ガス予熱器、4…排ガス再結合器、5…排ガス復水器、6…除湿装置、7…活性炭式希ガスホールドアップ塔、8…真空ポンプ、9…排気筒、10…活性炭式希ガスホールドアップ塔室、11…空調設備、12,13…ダクト、14…活性炭式希ガスホールドアップ塔入口配管、15…除湿装置入口流量調整弁、16,16a,16b…除湿装置、17,17a,17b…中空糸膜、18…パージガス流量計、19…パージガス量調整弁、20…パージガス圧力調整弁、21…パージガス圧力調整出口弁、22…除湿装置出口圧力計、23…除湿装置出口露点計、24…除湿装置出口流量計、25…除湿装置出口流量調整弁、26…復水器出口温度計、27…復水器出口圧力計、28…除湿装置入口流量計、29…復水器出口循環ライン弁、30…復水器出口循環ライン圧力調整弁、31…除湿装置入口弁、32…除湿装置出口弁、33…除湿装置差圧計、34…パージガス入口弁、35…パージガス出口弁、36…パージガス圧力計、37…パージ用真空ポンプ入口弁、38…パージ用真空ポンプ、39…パージ用真空ポンプ出口逆止弁、40…循環ライン。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a radioactive gas waste treatment method improved by a moisture removal method in a dehumidifier.
[0002]
[Prior art]
In general, the coolant of a boiling water reactor is irradiated with neutrons while passing through the core, and a part thereof is decomposed into oxygen and hydrogen, and further, 3 H, 16 N, 19 O and the like are generated. Further, radioactive noble gases such as Kr and Xe leak from pinholes or the like generated in the fuel rods, and these noble gases are mixed into the coolant and sent to the turbine system. In addition, there is leakage from outside air to the turbine main condenser.
[0003]
Due to these radioactive gas wastes (hereinafter simply referred to as exhaust gas), turbine systems in boiling water nuclear power plants need to be shielded in the same manner as nuclear reactors to maintain the soundness in and around the plant.
[0004]
By the way, since the exhaust gas is generally non-condensable, it stays in the steam system, particularly in the turbine main condenser. For this reason, conventionally, the exhaust gas staying in the turbine main condenser is extracted by an air extractor and led to an activated carbon type rare gas hold-up tower for processing.
[0005]
FIG. 2 shows an example of a radioactive waste treatment facility installed in a conventional nuclear power plant. Exhaust gas staying inside the turbine main condenser is extracted by the air extractor 1, and the preheater 3 Guided to the hydrogen recombination device 2 composed of the coupler 4 and the exhaust gas condenser 5, hydrogen gas recombination and volume reduction processing are performed.
[0006]
The exhaust gas introduced from the air extractor 1 to the hydrogen recombination device 2 is first preheated by the preheater 3 to a temperature at which oxygen and hydrogen contained in the exhaust gas are efficiently recombined, and then introduced to the downstream recombiner 4. Furthermore, hydrogen and oxygen in the exhaust gas become water vapor by a recombination reaction. Further, in the exhaust gas condenser 5 downstream thereof, the water vapor in the exhaust gas is condensed by the cooling water by the external cooling water to become almost water and separated from the exhaust gas, and the separated water is sent to a turbine main condenser (not shown). Returned.
[0007]
On the other hand, as shown in FIG. 2, the exhaust gas from which moisture has been separated and removed is led to a dehumidifying device 6, and after moisture has been sufficiently removed, is led to an activated carbon type rare gas holdup tower 7. The radioactive gas remaining in the exhaust gas (mainly a rare gas such as Xe or Kr) is adsorbed on the activated carbon, and after a long hold-up, is released from the exhaust tube 9 to the atmosphere by the vacuum pump 8. In FIG. 2, reference numeral 10 denotes an activated carbon type rare gas hold-up tower, 11 denotes an air conditioner, and 12 and 13 denote ducts.
[0008]
These devices are separated into airtight or similar rooms, and each room is air-conditioned. In particular, as shown in FIG. 2, the activated carbon type rare gas holdup tower 10 is air-conditioned from the dedicated air-conditioning equipment 11 through ducts 12 and 13 separately from other general air conditioning, and activated carbon is used to maintain the adsorption performance of the activated carbon. The inside of the noble gas holdup tower inlet pipe 14 can be kept at a constant temperature.
[0009]
FIG. 3 shows details of the conventional dehumidifying device 6 shown in FIG. 2, and the dehumidifying device indicated by reference numeral 16 in FIG. 3 uses a dehumidifying device 16 incorporating a hollow fiber membrane 17 having a large water vapor transmission coefficient. A part of the primary side gas dried by the dehumidifier 16 on the secondary side of the hollow fiber membrane 17 is used for purging, and the secondary side is sucked from the primary side pressure to a low pressure by the vacuum pressure of the main condenser. Thus, a water vapor partial pressure difference is provided between the primary side and the secondary side of the hollow fiber membrane 17 to perform dehumidification.
[0010]
In FIG. 3, reference numeral 18 is a purge gas flow meter, 19 is a purge gas amount adjusting valve, 20 is a purge gas pressure adjusting valve, 21 is a purge gas pressure adjusting outlet valve , 22 is a dehumidifier outlet pressure meter, and 24 is a dehumidifier outlet flow meter. , 25 is a dehumidifier outlet flow rate adjusting valve.
[0011]
[Problems to be solved by the invention]
In the conventional method for treating radioactive gas waste, the vacuum pressure of the main condenser was used as a method of sucking the secondary side of the dehumidifier 16 to a pressure lower than the primary side pressure. There is a problem that the gas waste treatment system cannot be operated when the vacuum pressure of the main condenser cannot be secured. In addition, there is also a problem that the gas waste treatment system cannot be operated alone because the vacuum pressure of the main condenser cannot be secured even during the periodic inspection.
[0012]
The present invention has been made in order to solve the above-mentioned problems, and it is possible to continuously remove moisture in the exhaust gas without using the vacuum pressure of the main condenser, and to obtain a highly reliable radioactive gas. An object is to provide a waste treatment apparatus.
[0013]
[Means for Solving the Problems]
In the present invention, radioactive gas waste generated from a nuclear power plant is led from a main condenser through an air extractor to a hydrogen bonding apparatus to recombine hydrogen gas by a recombiner and volume reduction treatment by an exhaust gas condenser. gastric row, the volume reduction treated after the exhaust gas was removed moisture leading to the dehumidifier incorporating the hollow fiber membranes, the line delay processing leading to the activated carbon ShikiNozomi gas holdup tower Utotomoni, by the dehumidifier In the method for treating radioactive gas waste, in which a part of the dried primary gas is supplied as a purge gas to the secondary side of the hollow fiber membrane, when the vacuum pressure of the main condenser is high, the hollow fiber membrane The secondary exhaust gas is returned to the main condenser, and when the vacuum pressure of the main condenser is low, the secondary exhaust gas is returned to the upstream side of the exhaust gas condenser by a purge vacuum pump .
[0014]
In addition, when a dehumidifying device having a built-in spare hollow fiber membrane is provided in parallel with the dehumidifying device, the humidity is detected by a dew point meter installed in the system outside the dehumidifying device, and the required humidity cannot be obtained. The exhaust gas subjected to the volume reduction treatment is guided to a dehumidifying device incorporating the spare hollow fiber membrane .
[0015]
Furthermore, the state of the dehumidifier detected differential pressure by the installed differential pressure gauge in the system, if the abnormal pressure differential to the system occurs, and the volume reduction process dehumidifier incorporating a hollow fiber membrane of the preliminary It is characterized by guiding exhaust gas .
[0016]
DETAILED DESCRIPTION OF THE INVENTION
In the method for treating radioactive gas waste according to the present invention, the dehumidifier 16a including the hollow fiber membrane 17a having a large water vapor transmission coefficient shown in FIG. 1 is used as the dehumidifier, and the air extractor 1 shown in FIG. And passes through the hollow fiber membrane 17a of the dehumidifier 16a.
[0017]
In this state, a part (for example, 20%) of the primary gas dried by the dehumidifier 16a is used for purging, supplied to the outside of the hollow fiber membrane, and using the purging vacuum pump 38. Suction to a lower pressure than the primary side.
[0018]
Thereby, the water vapor permeation performance is improved by increasing the water vapor partial pressure difference between the primary side and the secondary side of the hollow fiber membrane 17a, and the water vapor content in the exhaust gas is most efficiently removed. That is, the water vapor content in the exhaust gas is removed through the hollow fiber membrane, and the humidity of the exhaust gas becomes a required percentage or less, for example, 40% or less.
[0019]
Further, the exhaust gas sucked by the purge vacuum pump 38 is returned to the circulation line 40 connected to the upstream side of the condenser so that the gas waste treatment system can be operated independently even when the plant is stopped. .
[0020]
Further, when the humidity of the required percentage or less cannot be obtained due to the state of the dehumidifying device 16a, the humidity is detected by a dew point meter installed in the system, and the dehumidifying device 16b incorporating the spare hollow fiber membrane 17b is switched to. As a result, the dehumidifying performance can be secured.
[0021]
In addition, when the differential pressure increases or decreases depending on the state of the dehumidifying device, the differential pressure is detected by a differential pressure gauge installed in the system, and dehumidifying performance can be ensured by switching to a dehumidifying device incorporating a spare hollow fiber membrane. It becomes like this.
[0022]
An embodiment of a method for treating radioactive gas waste according to the present invention will be described with reference to FIGS.
FIG. 1 shows a configuration around a dehumidifier 16 (16a, 16b) in an exhaust gas treatment device. In the figure, the dehumidifiers 16a, 16b are connected to dehumidifier inlet valves 31a, 31b and dehumidifier outlet valves 32a, 32b. They are connected in parallel, and only one system is processed during normal operation.
[0023]
The wet exhaust gas to be treated (temperature: 40 ° C., dew point: 100%, pressure: 0.8ata) flows from the exhaust gas condenser 5 into the dehumidifiers 16a, 16b. As shown in FIG. 1, hollow fiber membranes 17a and 17b having a large water vapor transmission coefficient are attached to the dehumidifiers 16a and 16b, respectively, and the exhaust gas sucked by the purge vacuum pump 38 is supplied to the hollow fiber membranes 17a. , 17b.
[0024]
During operation with the dehumidifier 16a system, the temperature of the exhaust gas is measured by the dehumidifier outlet dew point meter 23. If the temperature exceeds the allowable dew point of the system (for example, −20 ° C.), an alarm is issued or the dehumidifier a The inlet valve 31a and the outlet valve 32a are closed, the dehumidifier inlet valve 31b and the outlet valve 32b are opened, and the operation number is switched to prevent the humid exhaust gas from flowing into the activated carbon rare gas hold-up device.
[0025]
In addition, when the pressure of the system is measured by the condenser outlet pressure gauge 27 and becomes equal to or higher than the system operation setting pressure (for example, atmospheric pressure), the condenser outlet circulation water line valve 29 is opened to open the condenser outlet circulation line. By adjusting the pressure regulating valve 30, the system pressure is set within the set value.
[0026]
In addition, the dehumidifier inlet flow meter 28 ensures a flow rate suitable for the processing amount of each of the dehumidifiers 16a and 16b by adjusting the dehumidifier inlet flow rate adjustment valve 19, thereby performing stable operation of the system.
[0027]
As shown in FIG. 1, the inside of each dehumidifier 16a, 16b is a part of the primary gas dried by the dehumidifier 16a, 16b (for example, 20%) for purging, and the purge gas amount is dehumidified from the purge gas flow meter 18. An amount corresponding to about 20% of the exhaust gas treatment amount measured by the apparatus inlet flow meter 28 is secured by adjusting the purge gas amount adjusting valve 20.
[0028]
In addition, the pressure of the purge gas is adjusted by the purge gas pressure adjustment valve 20 according to the set pressure of the purge gas pressure gauge 36, while the plant is in operation by the main condenser, and when the plant is stopped by the purge vacuum pump 36, Suction is performed at a lower pressure than the primary side.
[0029]
The exhaust gas sucked by the purge vacuum pump is circulated upstream of the exhaust gas condenser 5 through the circulation line 40, so that the off-gas (OG) system can be operated independently even when the plant is stopped.
[0030]
As a result, the water vapor content in the exhaust gas flowing through the hollow fiber membranes 17a and 17b passes through the hollow fiber membranes 17a and 17b to be separated and removed, and the relative humidity of the exhaust gas becomes a required percentage, for example, approximately 40% or less. It is like that. This is because the exhaust gas supplied to the activated carbon rare gas holdup tower 7 needs to have a relative humidity of 40% or less.
[0031]
The purge gas can be selected by switching the purge gas inlet valves 34a and 34b and the purge gas outlet valves 35a and 35b with respect to the operating system of the processing apparatus.
[0032]
Next, the moisture removal method in each dehumidifier 16a, 16b is demonstrated.
In FIG. 1, assuming that the system on the dehumidifying device 16a side is in operation, steam is cooled by the condenser 5, and the condensed exhaust gas is discharged by a vacuum pump 8 (see FIG. 2) that sucks the system. It is guided to the dehumidifier 16a via the dehumidifier inlet valve 31a and passes through the hollow fiber membrane 17a.
[0033]
At this time, the inside of the dehumidifying device 16a is adjusted to an appropriate flow rate by the purge gas amount adjusting valve 19 inside the dehumidifying device 16a, and the purge gas is caused to flow into the dehumidifying device 16a through the purge gas inlet valve 34a to improve the water vapor permeability. .
[0034]
Further, in order to evacuate the inside of the dehumidifier 16a and maintain it at a pressure lower than the pressure of the primary system, the purge vacuum pump 38 is used, and the set value of the purge gas pressure gauge 36 is set via the purge gas outlet valve 35a. The pressure is adjusted by the purge gas pressure adjustment valve 20. As a result, appropriate vacuuming is performed, so that the water vapor content in the exhaust gas flowing through the hollow fiber membrane 17a is removed through the hollow fiber membrane 17a and returned to the upstream side of the turbine main condenser via the circulation line 40. It is.
[0035]
For this reason, the exhaust gas after passing through the dehumidifier 16a has a relative humidity of a required percentage, for example, 40% or less, and enters the activated carbon type rare gas holdup tower 7 (see FIG. 2) via the dehumidifier outlet valve 32a. Guided and delayed.
[0036]
When trouble occurs in the dehumidifier 16a and the dew point meter 23 at the outlet of the dehumidifier 16a becomes larger than the set value, the dehumidifier inlet valve 31a, the dehumidifier outlet valve 32a, the purge gas inlet valve 34a, and the purge gas outlet valve 35a Is closed. At the same time, the dehumidifier inlet valve 31b, the dehumidifier outlet valve 32b, the purge gas inlet valve 34b, and the purge gas outlet valve 35b are opened, and the system is switched to the dehumidifier 16b side.
[0037]
Further, when trouble or the like occurs in the dehumidifier 16a and the differential pressure gauge 33 of the dehumidifier 16a deviates from the allowable value, the dehumidifier inlet valve 31a, the dehumidifier outlet valve 32a, the purge gas inlet valve 34a, and the purge gas outlet valve 35a are Closed. At the same time, the dehumidifier inlet valve 31b, the dehumidifier outlet valve 32b, the purge gas inlet valve 34b, and the purge gas outlet valve 35b are opened, and the system is switched to the dehumidifier 16b side.
[0038]
【The invention's effect】
According to the present invention, the operation of the exhaust gas system can be performed at the time of starting and stopping the plant and during a period in which the vacuum of the turbine main condenser cannot be secured during the plant stop. In addition, air that is not dehumidified during operation during regular inspections will not flow into the rare gas hold-up system.
[Brief description of the drawings]
FIG. 1 is a system diagram showing the periphery of a dehumidifying device for explaining an embodiment of a method for treating a radioactive gas waste according to the present invention.
FIG. 2 is a system diagram showing a conventional radioactive gas waste treatment facility.
3 is a system diagram showing the periphery of the dehumidification tower in FIG. 2. FIG.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 ... Air extractor, 2 ... Hydrogen recombination device, 3 ... Exhaust gas preheater, 4 ... Exhaust gas recombiner, 5 ... Exhaust gas condenser, 6 ... Dehumidifier, 7 ... Activated carbon type rare gas holdup tower, 8 ... Vacuum pump, 9 ... Exhaust tube, 10 ... Activated carbon type rare gas holdup tower room, 11 ... Air conditioning equipment, 12, 13 ... Duct, 14 ... Activated carbon type rare gas holdup tower inlet piping, 15 ... Dehumidifier inlet flow adjustment valve , 16, 16a, 16b ... dehumidifier, 17, 17a, 17b ... hollow fiber membrane, 18 ... purge gas flow meter, 19 ... purge gas amount adjusting valve, 20 ... purge gas pressure regulating valve 21 ... purge gas pressure regulating Seide port valve, 22 ... Dehumidifier outlet pressure gauge, 23 ... Dehumidifier outlet dew point meter, 24 ... Dehumidifier outlet flow meter, 25 ... Dehumidifier outlet flow control valve, 26 ... Condenser outlet thermometer, 27 ... Condenser outlet pressure gauge 28 ... Dehumidifier inlet flow meter, 29 ... Condenser outlet circulation line valve, 30 ... Condenser outlet circulation line Pressure regulating valve, 31 ... Dehumidifier inlet valve, 32 ... Dehumidifier outlet valve, 33 ... Dehumidifier differential pressure gauge, 34 ... Purge gas inlet valve, 35 ... Purge gas outlet valve, 36 ... Purge gas pressure gauge, 37 ... Purge vacuum pump inlet Valve: 38 ... Purge vacuum pump, 39 ... Purge vacuum pump outlet check valve, 40 ... Circulation line.

Claims (4)

原子力発電プラントから発生した放射性気体廃棄物を、主復水器から空気抽出器を通し水素結合装置に導いて再結合器による水素ガスの再結合と排ガス復水器による減容処理を行、前記減容処理した排ガスを中空糸膜を内蔵する除湿装置に導いて湿分を除去した後、活性炭式希ガスホールドアップ塔に導いて遅延処理を行うとともに、前記除湿装置により乾燥された一次側ガスの一部をパージガスとして前記中空糸膜の二次側に供給する放射性気体廃棄物の処理方法において、
前記主復水器の真空圧が高い場合は前記中空糸膜の二次側排ガスを主復水器に戻し、前記主復水器の真空圧が低い場合は前記二次側排ガスをパージ用真空ポンプにより前記排ガス復水器の上流側に戻すことを特徴とする放射性気体廃棄物の処理方法。
Radioactive gaseous waste generated from nuclear power plants, have rows volume reduction process by recombination and the exhaust gas condenser of hydrogen gas by recombiner led to hydrogen bonding device through the air ejector from main condenser, the volume reduction treated after the exhaust gas was removed moisture leading to the dehumidifier incorporating the hollow fiber membranes, activated carbon ShikiNozomi gas holdup line delay processing leading to tower Utotomoni primary which is dried by the dehumidifier In the method for treating radioactive gas waste, which supplies a part of the side gas as a purge gas to the secondary side of the hollow fiber membrane ,
When the vacuum pressure of the main condenser is high, the secondary side exhaust gas of the hollow fiber membrane is returned to the main condenser, and when the vacuum pressure of the main condenser is low, the secondary side exhaust gas is purged vacuum A method for treating radioactive gas waste, wherein the waste gas is returned to the upstream side of the exhaust gas condenser by a pump .
前記除湿装置と並列に予備の中空糸膜を内蔵した除湿装置を設け、前記除湿装置外の系統内に設置された露点計により湿度を検知し、所要の湿度が得られなくなった場合、前記予備の中空糸膜を内蔵した除湿装置に前記減容処理した排ガスを導くことを特徴とする請求項1記載の放射性気体廃棄物の処理方法。 When a dehumidifying device having a built-in spare hollow fiber membrane is provided in parallel with the dehumidifying device, the humidity is detected by a dew point meter installed in a system outside the dehumidifying device, and when the required humidity cannot be obtained, The method for treating a radioactive gas waste according to claim 1 , wherein the exhaust gas subjected to the volume reduction treatment is guided to a dehumidifying device incorporating a hollow fiber membrane . 前記除湿装置の状態を系統内に設置された露点計により湿度を検知し、放射性気体廃棄物の相対湿度が所定範囲になるように前記パージガスの量を調整することを特徴とする請求項1又は2記載の放射性気体廃棄物の処理方法。Wherein the state of the dehumidifier detects humidity by the installed hygrometer in the system, according to claim 1 the relative humidity of the radioactive gas waste and adjusting the amount of the purge gas to a predetermined range or 2. A method for treating radioactive gas waste according to item 2. 前記除湿装置の状態を系統内に設置された差圧計により差圧を検知し、系統に差圧異常が生じた場合、前記予備の中空糸膜を内蔵した除湿装置に前記減容処理した排ガスを導くことを特徴とする請求項2又は3記載の放射性気体廃棄物の処理方法。When the differential pressure is detected by a differential pressure gauge installed in the system to determine the state of the dehumidifier, and a differential pressure abnormality occurs in the system, the volume-reduced exhaust gas is added to the dehumidifier having the spare hollow fiber membrane built therein. The method for treating a radioactive gas waste according to claim 2 or 3, wherein the radioactive gas waste is treated.
JP03908299A 1999-02-17 1999-02-17 Treatment method of radioactive gas waste Expired - Fee Related JP4127580B2 (en)

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