JPH03246496A - Sticking suppressing method for radioactive material of piping or equipment for nuclear power plant - Google Patents
Sticking suppressing method for radioactive material of piping or equipment for nuclear power plantInfo
- Publication number
- JPH03246496A JPH03246496A JP3007517A JP751791A JPH03246496A JP H03246496 A JPH03246496 A JP H03246496A JP 3007517 A JP3007517 A JP 3007517A JP 751791 A JP751791 A JP 751791A JP H03246496 A JPH03246496 A JP H03246496A
- Authority
- JP
- Japan
- Prior art keywords
- piping
- equipment
- power plant
- nuclear power
- adhesion
- 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.)
- Granted
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
- Chemical Treatment Of Metals (AREA)
- Preventing Corrosion Or Incrustation Of Metals (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
[00013 [00013
【産業上の利用分野]
本発明は、−次冷却水系配管のように放射性物質が溶存
している炉水と接して使用される新規な原子力プラント
用配管又は機器の放射性物質の付着抑制方法に関する。
[0002]
【従来の技術】
原子力発電所の一次冷却水系に使用されている配管、ポ
ンプ、弁等はステンレス鋼及びステライト等から構成さ
れている。これらの金属は長期間使用されると腐食損傷
をうけ、構成金属元素が一次冷却水中に溶出し、原子炉
内に持ち込まれる。溶出金属元素は大半が酸化物となっ
て燃料棒に付着し、中性子照射をうける。その結果、6
0Co 、 5Co 、 5’Cr 、 64Mn等の
放射性核種が生成する。これらの放射性核種は一次冷却
水中に再溶出してイオンあるいは不溶性固体成分(以下
、クラッドと称する)として浮遊する。浮遊する一部は
炉水浄化用の脱塩器等で除去されるが、残りは一次冷却
水系を循環しているうちに主にステンレス鋼からなる構
造材表面に付着する。このため、構造材表面における線
量率が高くなり保守9点検を実施する際の作業員の放射
線被曝が問題となっている。
[0003]
このため、構造材の表面線量率の上昇を防止する方法と
して、構造材に付着した放射性物質を除去する方法が検
討され、実施されている。除去方法には現状3つある。
[0004]
(1)機械的洗浄方法
(2)化学的洗浄方法
(3)電気分解による洗浄方法
(1)の方法は主に部品に適用され、たとえば高圧ジェ
ット水により表面を洗浄するものである。しかし、この
方法では密着性の強い放射性物質の除去が困難であり、
また広い範囲を系統的に除染することはできない。事実
、この方法により一時的に線量率を低減しても、その後
の長期的な使用により再び線量率が上昇する傾向にある
。
[0005]
(2)の方法は酸溶液等の薬剤を用いて化学的反応によ
り鋼表面の酸化被膜を溶解し、同被膜中に存在する放射
性物質を除去するものである。この方法の問題は薬剤に
よる構造材の腐食損傷にある。すなわち、被膜を溶解す
る際に構造材も腐食損傷をうけ、また除染後に残留した
微量の薬剤が構造材の応力腐食割れを引き起こす恐れが
ある。
[0006]
(3)の方法も(1)と同様の問題点をもっている。
[0007]
また、放射性物質の付着量を低減させるため、その源で
ある金属元素の溶出を抑制する方法も実施されている。
すなわち、酸素または過酸化水素を給水系内に注入して
構造材の腐食を抑制し、これによって腐食生成物の原子
炉内への持ち込み量を低減するものである。
[0008]
しかし、このよう・な方法を用いても給水系をはじめと
し、−次冷却水系の構造材の腐食を完全に防止すること
はできず、−次冷却水中の放射性物質を無くすことはで
きないため、構造材への放射性物質の付着による表面線
量率の増加がやはり問題として残っている。
[0009][Industrial Application Field] The present invention relates to a method for suppressing the adhesion of radioactive substances to new nuclear power plant piping or equipment used in contact with reactor water in which radioactive substances are dissolved, such as secondary cooling water system piping. . [0002] [0002] Piping, pumps, valves, etc. used in the primary cooling water system of a nuclear power plant are made of stainless steel, Stellite, etc. When these metals are used for a long period of time, they are subject to corrosion damage, and their constituent metal elements are leached into the primary cooling water and brought into the reactor. Most of the eluted metal elements become oxides and adhere to the fuel rods, where they are exposed to neutron irradiation. As a result, 6
Radioactive nuclides such as 0Co, 5Co, 5'Cr, and 64Mn are generated. These radionuclides are re-eluted into the primary cooling water and suspended as ions or insoluble solid components (hereinafter referred to as cladding). Some of the floating water is removed by demineralizers used to purify reactor water, but the rest adheres to the surfaces of structural materials, mainly made of stainless steel, while circulating through the primary cooling water system. For this reason, the dose rate on the surface of the structural material is high, and radiation exposure of workers when performing nine maintenance inspections has become a problem. [0003] Therefore, as a method for preventing an increase in the surface dose rate of structural materials, methods of removing radioactive substances attached to structural materials have been studied and implemented. There are currently three removal methods. [0004] (1) Mechanical cleaning method (2) Chemical cleaning method (3) Electrolytic cleaning method (1) Method is mainly applied to parts, for example, cleaning the surface with high-pressure jet water. . However, with this method, it is difficult to remove highly adhesive radioactive substances.
Furthermore, it is not possible to systematically decontaminate a wide area. In fact, even if the dose rate is temporarily reduced by this method, the dose rate tends to increase again with subsequent long-term use. [0005] The method (2) involves dissolving the oxide film on the steel surface through a chemical reaction using a chemical such as an acid solution, and removing radioactive substances present in the film. The problem with this method is the corrosion damage to the structural materials caused by the chemicals. In other words, when the coating is dissolved, the structural material may also be damaged by corrosion, and there is a risk that the small amount of chemicals remaining after decontamination may cause stress corrosion cracking of the structural material. [0006] The method (3) also has the same problems as (1). [0007] Furthermore, in order to reduce the amount of adhesion of radioactive substances, a method of suppressing the elution of metal elements, which are the source thereof, has also been implemented. That is, oxygen or hydrogen peroxide is injected into the water supply system to suppress corrosion of structural materials, thereby reducing the amount of corrosion products brought into the reactor. [0008] However, even if such a method is used, it is not possible to completely prevent corrosion of the structural materials of the sub-cooling water system, including the water supply system, and it is impossible to eliminate radioactive materials in the sub-cooling water. Therefore, an increase in surface dose rate due to adhesion of radioactive substances to structural materials remains a problem. [0009]
本発明の目的はこれらの問題点を除去し、放射性物質が
溶存している炉水と接して使用される配管又は機器表面
にあらかじめ酸化皮膜を形成することにより原子力プラ
ント用配管又は機器の放射性物質の付着抑制方法を提供
することにある[00101The purpose of the present invention is to eliminate these problems and eliminate radioactive substances from nuclear power plant piping or equipment by forming an oxide film in advance on the surface of piping or equipment used in contact with reactor water in which radioactive materials are dissolved. [00101
【課題を解決するための手段]
本発明は、原子炉々水と接して使用される金属からなる
原子力プラント用配管又は機器の放射性物質の付着抑制
方法において、予め、前記炉水と接する前に、前記原子
力プラント系外で、前記配管又は機器の前記炉水に接す
る表面に微量の溶存酸素を含む脱気された高温高圧の純
水に接触させ、かつ該純水を流動させることによって酸
化皮膜を形成させることを特徴とする原子力プラント用
配管又は機器の放射性物質の付着抑制方法にある。
[0011]
【作用】
原子力プラントの従事者被曝に寄与する主な放射性核種
は60COであることが各種分析の結果(たとえば、G
、 Romeo、Proceedings of Th
e 7th InternationalCongre
ss on Metallic Corrosion、
P1456.1978 )かられかっている。この放
射性核種はγ線の崩壊エネルギー強度が1.17及び1
.33MeVと高く、また半減期が5.26年と長いた
めに、−旦構造材に付着すると長期にわたり表面線量率
を高める原因となる。したがって、線量率を低減するた
めには、この60COの付着をいかに抑制するかが鍵で
ある。
[0012]
一方、プラント炉口りの圧力容器、配管、ポンプ、弁等
の構造材はステンレス鋼、ステライト、インコネル、炭
素鋼よりなるが、接水面積の97%をステンレス鋼が占
める。したがって、ステンレス鋼への放射性物質の付着
を抑制することが被曝低減上、最も有効である。
[0013]
炉水に溶存する放射性核種はステンレス鋼の腐食によっ
て表面に形成される酸化皮膜内にその形成過程で取り込
まれる。ところで、発明者の研究によると放射性核種の
付着速度は皮膜成長速度と相関関係を示すので、皮膜成
長を抑制することは付着低減につながるであろうと推定
された。
[0014]
炉水環境下でのステンレス鋼の皮膜量の増加は時間の対
数則によって表わされる。すなわち、皮膜の成長ととも
にその成長速度は小さくなる。したがって、あらかじめ
適当な非放射性の酸化皮膜を形成しておけば、放射性物
質が溶存している液へ浸せきしたのちの新たな皮膜形成
を抑制することができ、ひいては皮膜形成時に多くみら
れる放射性、物質の付着を抑制できる。
[0015]
ところで、放射性物質の皮膜内への拡散の難易は皮膜組
成及び形態に依存する。60COは2価原子であること
から2価金属を有する結晶構造をもつ酸化皮膜内、60
いα−Fe203を主体とする皮膜をあらかじめ形成し
ておくことか Coの付着抑制上有効であることが判明
し、本発明に至った。
[0016]
酸化皮膜の形成に当っては脱気された微量の溶存酸素を
含む高温高圧の純水によって酸化処理しなければ配管又
は機器表面には強固な前述の酸化皮膜が得られない。ま
た、酸化皮膜の形成は上述の純水によって行われるが、
その加熱は原子力プラント系外で純水の流動によって行
われる。
[0017][Means for Solving the Problems] The present invention provides a method for suppressing the adhesion of radioactive substances to nuclear power plant piping or equipment made of metal that is used in contact with reactor water, in which the , outside the nuclear power plant system, by bringing the surface of the piping or equipment in contact with the reactor water into contact with degassed high-temperature, high-pressure pure water containing a trace amount of dissolved oxygen, and causing the pure water to flow, thereby forming an oxide film. A method for suppressing the adhesion of radioactive substances on piping or equipment for a nuclear power plant, characterized by forming a [0011] [Operation] As a result of various analyzes (for example, G
, Romeo, Proceedings of Th.
e 7th International Congress
ss on Metallic Corrosion,
P1456.1978) is being rejected. This radionuclide has a γ-ray decay energy intensity of 1.17 and 1.
.. Since it is as high as 33 MeV and has a long half-life of 5.26 years, once it adheres to structural materials, it causes an increase in the surface dose rate over a long period of time. Therefore, in order to reduce the dose rate, the key is how to suppress the adhesion of 60CO. [0012] On the other hand, structural materials such as pressure vessels, piping, pumps, and valves at the mouth of the plant are made of stainless steel, Stellite, Inconel, and carbon steel, and stainless steel accounts for 97% of the area in contact with water. Therefore, suppressing the adhesion of radioactive substances to stainless steel is the most effective way to reduce exposure. [0013] Radionuclides dissolved in reactor water are incorporated into an oxide film formed on the surface of stainless steel during its formation process. By the way, according to the inventor's research, since the adhesion rate of radionuclides shows a correlation with the film growth rate, it was presumed that suppressing the film growth would lead to a reduction in adhesion. [0014] The increase in the amount of coating on stainless steel in a reactor water environment is expressed by the logarithmic law of time. That is, as the film grows, its growth rate decreases. Therefore, if a suitable non-radioactive oxide film is formed in advance, it is possible to suppress the formation of a new film after immersion in a solution containing dissolved radioactive substances, and in turn, the radioactive Adhesion of substances can be suppressed. [0015] Incidentally, the difficulty of diffusing radioactive substances into the film depends on the film composition and form. Since 60CO is a divalent atom, it is effective to form a film mainly composed of α-Fe203 in an oxide film with a crystal structure containing divalent metals in order to suppress the adhesion of Co. This discovery led to the present invention. [0016] When forming an oxide film, the above-mentioned strong oxide film cannot be obtained on the surface of piping or equipment unless oxidation treatment is performed using degassed high-temperature, high-pressure pure water containing a trace amount of dissolved oxygen. In addition, the formation of an oxide film is carried out by the above-mentioned pure water,
The heating is performed outside the nuclear plant system by flowing pure water. [0017]
実験例1
表1に示す化学組成を有したステンレス鋼を25ないし
1000時間流速0.5m/sで流動する炉水に浸せき
して、形成する酸化皮膜量および付着した60C。
量を測定した。
1判用土d″″ど’lb’l;jL)%リノ[0018
]Experimental Example 1 Stainless steel having the chemical composition shown in Table 1 was immersed in reactor water flowing at a flow rate of 0.5 m/s for 25 to 1000 hours to determine the amount of oxide film formed and the amount of 60C attached. The amount was measured. 1 size soil d″″d’lb’l;jL)% Reno [0018
]
【表1】
(表1)
ステンレス鋼は浸せき前に表面を機械加工後、脱脂洗浄
した。炉水の60Co濃度は1×10−4μCi /
m lで90%以上がイオンとして存在した。また、温
度は230℃、溶存酸素濃度は150ないし17 op
pb 、 pHは6.9ないし7.2であった。
[00203
1000時間浸せきした場合に形成された酸化皮膜の主
な金属元素組成を表2に示す。約90%が鉄元素である
。
[0021][Table 1] (Table 1) Before immersion, the surface of the stainless steel was machined and then degreased and cleaned. The 60Co concentration in the reactor water is 1 x 10-4 μCi/
More than 90% of the ions existed in the form of ions. In addition, the temperature was 230°C, and the dissolved oxygen concentration was 150 to 17 op.
pb, pH was 6.9 to 7.2. [00203 Table 2 shows the main metal element composition of the oxide film formed when immersed for 1000 hours. Approximately 90% is iron element. [0021]
【表2】
(表2)
[0022]
図1にステンレス鋼単位面積当りに形成された酸化皮膜
中の代表金属元素の量(鉄、コバルト、ニッケル、クロ
ムの総和)の経時変化を示す。100時間以上で対数側
にしたがった増加を示している。
[0023]
一方、図2は付着60CO量の経時変化である。酸化皮
膜量と同様に100時間以上で対数側にしたがって増加
した。
[0024]
したがって、図11図2より60Coの付着速度は酸化
皮膜の成長速度に律速されていことがわかる。また、皮
膜の成長速度はその成長とともにしだいに小さくなって
いる。
[0025]
実験例2
前述のステンレス鋼を25ないし500時間、次に示す
原子力プラント運転条件とほぼ同様の高温高圧の純水に
浸せきし、表面に非放射性の酸化皮膜をあらかじめ形成
した。
[0026]
温度:285℃
溶存酸素濃度:200ppb
電気伝導度:0.1μS/cm
流速: 0 、1 cm/sec
圧カニ 73 kg/cm2
ステンレス鋼を前述の炉水に浸せきし、60Co付着量
の経時変化を調べた。結果を無処理のステンレス鋼とあ
わせて図3に示した。曲線1ないし5は、それぞれ前酸
化処理時間が25時間、50時間、100時間、200
時間および500時間の場合を示す。炉水への浸せき1
00時間以上において前酸化処理したステンレス鋼への
60Coの付着は著しく抑制された。
[0027]
前述の各処理時間によって得られた酸化皮膜厚さと60
Co付着量との関係を図4に示した。酸化処理によって
厚さ300A以上の皮膜を形成することが60C。
の付着抑制にきわめて効果的である。
[0028]
実験例3
前酸化処理として、実験例1に示した5US304鋼を
対象に比較例の水蒸気を使用した場合と本発明の高温高
圧純水による方法を実施した場合を比較した。表3は処
理条件と処理済み試料を実験例1と同条件の炉水に50
0時間浸せきしたのちの60CO付着量を示している。
[0030][Table 2] [0022] Figure 1 shows changes over time in the amounts of representative metal elements (total of iron, cobalt, nickel, and chromium) in the oxide film formed per unit area of stainless steel. It shows an increase according to the logarithmic side after 100 hours or more. [0023] On the other hand, FIG. 2 shows the change over time in the amount of attached 60CO. Similar to the amount of oxide film, it increased logarithmically over 100 hours. [0024] Therefore, it can be seen from FIGS. 11 and 2 that the deposition rate of 60Co is determined by the growth rate of the oxide film. Furthermore, the growth rate of the film gradually decreases as it grows. [0025] Experimental Example 2 The stainless steel described above was immersed for 25 to 500 hours in pure water at a high temperature and high pressure similar to the operating conditions of a nuclear power plant shown below, to form a non-radioactive oxide film on the surface in advance. [0026] Temperature: 285°C Dissolved oxygen concentration: 200 ppb Electrical conductivity: 0.1 μS/cm Flow rate: 0, 1 cm/sec Pressure crab 73 kg/cm2 Stainless steel was immersed in the above-mentioned reactor water, and the amount of 60Co deposited was We investigated changes over time. The results are shown in Figure 3 together with the results for untreated stainless steel. Curves 1 to 5 indicate preoxidation treatment times of 25 hours, 50 hours, 100 hours, and 200 hours, respectively.
The case of time and 500 hours is shown. Immersion in reactor water 1
The adhesion of 60Co to the pre-oxidized stainless steel was significantly suppressed over 00 hours. [0027] Oxide film thickness obtained by each of the above-mentioned treatment times and 60
The relationship with the amount of Co adhesion is shown in FIG. 60C is capable of forming a film with a thickness of 300A or more through oxidation treatment. It is extremely effective in suppressing the adhesion of [0028] Experimental Example 3 A comparison was made between the pre-oxidation treatment of the 5US304 steel shown in Experimental Example 1 using the steam of the comparative example and the method of the present invention using high-temperature, high-pressure pure water. Table 3 shows the treatment conditions and treated samples in reactor water under the same conditions as Experiment 1.
The amount of 60CO deposited after immersion for 0 hours is shown. [0030]
【表3】
(表3)
[0031]
表に示すように、比較例の水蒸気を用いた場合に比べ、
本発明のように高温高圧の純水を用いることにより著し
く60COの付着量を抑制できることを示している。こ
の理由は、蒸気中ではFe(II)を主体とした酸化皮
膜が形成され、炉水中ではこのFe (II)位置に6
0Co (II)が置換、析出しゃすいためであると思
われる。一方高温高圧純水中ではFe(II)を主体と
した安定な被膜が形成され実施例1
原子力プラントで使用された配管1機器等を化学的方法
等により除染し、再使用する場合、除染操作により構造
材表面の酸化皮膜は溶解、剥離しているので、金属素地
が露出しており、再使用時の放射性物質の付着量は図2
と同様の経時変化を示す。そこで、本発明の前酸化処理
を施したのちに再使用することで放射性物質の付着を抑
制することができる。
[0032]
実機の原子力プラントで使用された5US304鋼製配
管2機器に対し化学除染を施した後、酸化皮膜処理無し
と、炉水と接する表面への前酸化処理として、電気伝導
度0.1pS/cm、温度275〜285℃、溶存酸素
濃度350〜38 oppb。
圧カフ 3 kg/cm2の高温高圧純水を用い、20
0時間の前述と同じ0.1cm/秒の流水による酸化処
理を施し、その後、前述の炉水を500時間浸せきして
60c。
の付着量を比較した。その結果、除染処理後に水洗のみ
施したものは0453μCi/cm であるのに対し
、前酸化処理したものは0.11μC1/cm2であり
前酸化処理により約5分の1に60Coの付着量が低減
した。
[0033][Table 3] (Table 3) [0031] As shown in the table, compared to the case of using water vapor in the comparative example,
This shows that the amount of 60CO deposited can be significantly suppressed by using high-temperature, high-pressure pure water as in the present invention. The reason for this is that an oxide film mainly composed of Fe(II) is formed in steam, and in reactor water, this Fe(II) position is 6
This seems to be because 0Co (II) is less likely to be substituted and precipitated. On the other hand, in high-temperature, high-pressure pure water, a stable film mainly composed of Fe(II) is formed. As the oxide film on the surface of the structural material is dissolved and peeled off during the dyeing process, the metal base is exposed, and the amount of radioactive substances deposited upon reuse is as shown in Figure 2.
It shows a similar change over time. Therefore, by performing the pre-oxidation treatment of the present invention and then reusing it, it is possible to suppress the adhesion of radioactive substances. [0032] After chemical decontamination was applied to two pieces of 5US304 steel piping used in an actual nuclear power plant, electrical conductivity was reduced to 0.00% without oxidation film treatment and as pre-oxidation treatment on the surface in contact with reactor water. 1 pS/cm, temperature 275-285°C, dissolved oxygen concentration 350-38 oppb. Pressure cuff Using high temperature, high pressure pure water of 3 kg/cm2,
Oxidation treatment was carried out using running water at a flow rate of 0.1 cm/sec as described above for 0 hours, and then immersed in the above-mentioned reactor water for 500 hours at 60C. The amount of adhesion was compared. As a result, the amount of 60Co deposited was 0.453 μCi/cm2 for the product that was only washed with water after decontamination treatment, while it was 0.11 μC1/cm2 for the product that was pre-oxidized, and the amount of 60Co attached was reduced to about one-fifth by the pre-oxidation treatment. Reduced. [0033]
以上のように、本発明は原子力プラントの配管9機器等
、プラントに設置する前にそれらの炉水に接する表面に
前述のオートクレーブ処理によって酸化皮膜を形成する
ことにより放射性物質の付着を抑制することができ、そ
れらの配管、機器の線量率の上昇を抑え、従事者の被曝
を低減するに好適であり、実用価値も高く、工業的にき
わめて有意義なものである。As described above, the present invention suppresses the adhesion of radioactive substances by forming an oxide film on the surfaces of nine nuclear power plant piping equipment, etc. that come into contact with reactor water by the above-mentioned autoclave treatment before they are installed in the plant. It is suitable for suppressing the increase in the dose rate of those piping and equipment and reducing the radiation exposure of workers, and has high practical value and is extremely meaningful industrially.
【図1】 ステンレス鋼酸化皮膜量と時間との関係を示す線図。[Figure 1] A diagram showing the relationship between the amount of stainless steel oxide film and time.
【図2】[Figure 2]
【図3】 60CO付着量と時間との関係を示す線図。[Figure 3] A diagram showing the relationship between 60CO adhesion amount and time.
【図4】
放射性物質の付着量と酸化皮膜厚さとの関係図を示す線
図。FIG. 4 is a diagram showing the relationship between the amount of radioactive material deposited and the thickness of the oxide film.
【同月 図面 図 時 間 (h) 【図2】 ′I:を開十d″″ご4b’l;3t)%1<ノ[Same month drawing figure Time while (h) [Figure 2] 'I: Open 10d''''Go4b'l;3t)%1<ノ
【図3
】
図
時
間(h)[Figure 3
] Figure time (h)
【図4】[Figure 4]
Claims (1)
プラント用配管又は機器の放射性物質の付着抑制方法に
おいて、予め、前記炉水と接する前に、前記原子力プラ
ント系外で、前記配管又は機器の前記炉水に接する表面
に微量の溶存酸素を含む脱気された高温高圧の純水に接
触させ、かつ該純水を流動させることによって酸化皮膜
を形成させることを特徴とする原子力プラント用配管又
は機器の放射性物質の付着抑制方法。1. In a method for suppressing the adhesion of radioactive substances to nuclear power plant piping or equipment made of metal that is used in contact with reactor water, the piping or equipment is preliminarily removed outside the nuclear power plant system before coming into contact with the reactor water. For use in a nuclear power plant, characterized in that an oxide film is formed by bringing the surface of the equipment in contact with the reactor water into contact with degassed high-temperature, high-pressure pure water containing a trace amount of dissolved oxygen and flowing the pure water. Method for suppressing adhesion of radioactive substances to piping or equipment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3007517A JPH03246496A (en) | 1991-01-25 | 1991-01-25 | Sticking suppressing method for radioactive material of piping or equipment for nuclear power plant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3007517A JPH03246496A (en) | 1991-01-25 | 1991-01-25 | Sticking suppressing method for radioactive material of piping or equipment for nuclear power plant |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57146111A Division JPS5937498A (en) | 1982-08-25 | 1982-08-25 | Nuclear power plants equipped with a function to suppress adhesion of radioactive substances |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH03246496A true JPH03246496A (en) | 1991-11-01 |
| JPH0553400B2 JPH0553400B2 (en) | 1993-08-09 |
Family
ID=11667967
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3007517A Granted JPH03246496A (en) | 1991-01-25 | 1991-01-25 | Sticking suppressing method for radioactive material of piping or equipment for nuclear power plant |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH03246496A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007024644A (en) * | 2005-07-14 | 2007-02-01 | Hitachi Ltd | Radionuclide adhesion suppression method and film forming apparatus for nuclear plant components |
| JP2007192672A (en) * | 2006-01-19 | 2007-08-02 | Hitachi Ltd | Method and apparatus for forming a ferrite film on the surface of a carbon steel member in a nuclear power plant |
| JP2008180740A (en) * | 2008-04-23 | 2008-08-07 | Hitachi-Ge Nuclear Energy Ltd | Nuclear plant components |
| JP2008209418A (en) * | 2008-04-23 | 2008-09-11 | Hitachi-Ge Nuclear Energy Ltd | Radionuclide adhesion suppression method and film forming apparatus for nuclear plant components |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5439791A (en) * | 1977-09-02 | 1979-03-27 | Hitachi Ltd | Operation method of reactor |
| JPS55121197A (en) * | 1979-03-13 | 1980-09-18 | Hitachi Ltd | Method for protecting deposition of radioactive ion |
| JPS5737295A (en) * | 1980-08-18 | 1982-03-01 | Tokyo Shibaura Electric Co | Light water reactor and its operation method |
| JPS5740694A (en) * | 1980-08-26 | 1982-03-06 | Tokyo Shibaura Electric Co | Reactor water degasing device in reactor |
-
1991
- 1991-01-25 JP JP3007517A patent/JPH03246496A/en active Granted
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5439791A (en) * | 1977-09-02 | 1979-03-27 | Hitachi Ltd | Operation method of reactor |
| JPS55121197A (en) * | 1979-03-13 | 1980-09-18 | Hitachi Ltd | Method for protecting deposition of radioactive ion |
| JPS5737295A (en) * | 1980-08-18 | 1982-03-01 | Tokyo Shibaura Electric Co | Light water reactor and its operation method |
| JPS5740694A (en) * | 1980-08-26 | 1982-03-06 | Tokyo Shibaura Electric Co | Reactor water degasing device in reactor |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007024644A (en) * | 2005-07-14 | 2007-02-01 | Hitachi Ltd | Radionuclide adhesion suppression method and film forming apparatus for nuclear plant components |
| JP2007192672A (en) * | 2006-01-19 | 2007-08-02 | Hitachi Ltd | Method and apparatus for forming a ferrite film on the surface of a carbon steel member in a nuclear power plant |
| JP2008180740A (en) * | 2008-04-23 | 2008-08-07 | Hitachi-Ge Nuclear Energy Ltd | Nuclear plant components |
| JP2008209418A (en) * | 2008-04-23 | 2008-09-11 | Hitachi-Ge Nuclear Energy Ltd | Radionuclide adhesion suppression method and film forming apparatus for nuclear plant components |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0553400B2 (en) | 1993-08-09 |
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