JP2017198644A - Detoxification device for detoxifying radioactively contaminated water in nuclear facility - Google Patents
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Abstract
Description
本発明は、原子力発電所・使用済み核燃料再処理工場等で発生する放射能汚染水を無害化する装置に関するものである。放射性原子を核変換して無害化する装置である。 The present invention relates to an apparatus for detoxifying radioactively contaminated water generated in nuclear power plants, spent nuclear fuel reprocessing plants, and the like. It is a device that transmutates radioactive atoms to make them harmless.
超音波洗浄器では、気泡が発生し、成長し、壊れる。これらの一連の気泡運動はキャビテーションと呼ばれている。微小な気泡が水中に存在し、微細なゴミ(固体微粒子)の表面や、容器壁等に形成されるキズや窪みに気体が補足されている。超音波による圧力振動が気泡を発生させ、気泡は、正の圧力の半周期において収縮し、負の圧力の半周期において膨脹する気泡振動繰り返し、不均等拡散機構による面積効果と殻効果によって図1のように成長していく。さらに、超音波の強さが強力になると、急激な収縮運動が起り、瞬間的に気泡内部では数千度・数百気圧以上の極限環境になる(図2)。この圧壊という気泡運動がソノケイストリーと呼ばれる超音波化学作用の源であり、身近な眼鏡洗浄、金属加工やプラスチック射出成型のバリ取りの衝撃波になる([非特許文献1])。 In an ultrasonic cleaner, bubbles are generated, grow and break. This series of bubble motion is called cavitation. There are minute bubbles in the water, and the gas is supplemented to the surface of fine dust (solid fine particles), scratches and dents formed on the container wall and the like. Pressure vibrations caused by ultrasonic waves generate bubbles, and the bubbles contract in the half cycle of positive pressure and expand in the half cycle of negative pressure. It will grow like Furthermore, when the intensity of the ultrasonic wave becomes strong, a rapid contraction movement occurs, and an extreme environment of several thousand degrees and several hundred atmospheres or more is instantaneously generated inside the bubble (FIG. 2). This crushing bubble motion is the source of ultrasonic chemistry called sonochemistry, and it becomes a shock wave for deburring familiar glasses cleaning, metal processing and plastic injection molding ([Non-Patent Document 1]).
超音波キャビテーションの気泡が圧壊する時、気液界面で水分子がOHラジカルと水素原子Hに分解される。このことは、ベンゼン環に塩素原子3個が結合したトリクロロフェノールが分解されて、次第に透明な液が着色して来ることから実証される。トリクロロフェノールの分解着色は、OHラジカルと塩素原子Clが発生する次亜塩素酸HOCl溶液で既に確認されている。 When the bubbles of ultrasonic cavitation are crushed, water molecules are decomposed into OH radicals and hydrogen atoms H at the gas-liquid interface. This is proved by the fact that trichlorophenol having 3 chlorine atoms bonded to the benzene ring is decomposed and the transparent liquid gradually becomes colored. The decomposition coloring of trichlorophenol has already been confirmed in a hypochlorous acid HOCl solution in which OH radicals and chlorine atom Cl are generated.
図3のように、水分子は水素結合によって繋がり、巨大分子を構成している。水素結合H−Oの乖離熱は〜30KJ/molで、水素分子H−Hの乖離熱436KJ/molよりずっと小さい。この関係は、水素ガスからよりも水からの方が水素原子Hが容易に分離されることを示している。 As shown in FIG. 3, water molecules are connected by hydrogen bonds to form a macromolecule. The heat of dissociation of hydrogen bonds HO is ˜30 KJ / mol, which is much smaller than the heat of dissociation of hydrogen molecules H—H, 436 KJ / mol. This relationship indicates that hydrogen atoms H are more easily separated from water than from hydrogen gas.
原子力発電所の炉心循環水、使用済み核燃料プールの冷却水、核燃料再処理施設の処理水では、軽水が中性子を繰り返し浴びて、軽水の水素原子が重水素原子Dに、さらに重水素原子Dがトリチウム原子Tに変換されて、重水、トリチウム水に変わる。制御棒に含まれる硼素、中性子吸収液の硼酸からのBが、さらに、加圧水型原子炉でpH調整のために添加されるLiOHからのLiが、中性子を吸収して、BまたはLi+n→He+Tの反応でトリチウムができるのでトリチウム水が多くなる。 In nuclear power plant core circulating water, spent nuclear fuel pool cooling water, nuclear fuel reprocessing facility treated water, light water is repeatedly exposed to neutrons, light water hydrogen atoms become deuterium atoms D, and deuterium atoms D further. It is converted into tritium atom T and converted into heavy water or tritium water. Boron contained in the control rod, B from boric acid in the neutron absorbing liquid, and Li from LiOH added for pH adjustment in the pressurized water reactor absorb neutrons, and B or Li + n → He + T Since tritium is formed by the reaction, the amount of tritium water increases.
軽水、重水、トリチウム水は水素結合(図3)によって繋がり、巨大分子を構成している。これらの水素結合を、超音波キャビテーションの気泡圧壊で容易に切ることができる。その時、気泡内部は太陽表面に近い数千度・数百気圧以上の極限状態になる。
太陽表面では重水素DとトリチウムTが核融合してヘリウムと中性子が発生し、その放出エネルギーで輝き続ける(図4)。地上で太陽をつくる核融合は、重水素とトリチウムを磁場で閉じ込めて核融合させるものである。核燃料汚染水を超音波キャビテーションさせることは、重水素DとトリチウムTからヘリウムが生まれる核融合を空間の1点で瞬間に実現することである。Light water, heavy water, and tritium water are connected by hydrogen bonds (FIG. 3) to form a macromolecule. These hydrogen bonds can be easily broken by bubble collapse of ultrasonic cavitation. At that time, the inside of the bubble is in an extreme state of several thousand degrees and several hundred atmospheres close to the solar surface.
On the surface of the sun, deuterium D and tritium T fuse together to generate helium and neutrons, which continue to shine with their released energy (Fig. 4). Nuclear fusion, which creates the sun on the ground, involves deuterium and tritium confined in a magnetic field and fused. Ultrasonic cavitation of nuclear fuel-contaminated water is to instantly realize nuclear fusion in which helium is born from deuterium D and tritium T at one point in space.
近年、常温核融合の事例が散見される([非特許文献2,3])。いずれも共通することは、重水素Dと金属のパラジウムPdの組合せである。パラジウムは水素を吸蔵し、その体積比率は935倍と大きい。田中貴金属工業株式会社のパラジウム水素透過薄膜は、水素だけを通す選択透過性を利用して水素ガスの精製を実現している。水素分子はパラジウム薄膜の中で水素原子に分離し、薄膜を通過して外に出ると水素分子に戻ると想定されている。三菱重工からの報告では、重水素を透過させるパラジウム多層膜の内部のセシウムCs原子が、原子番号の大きい原子に核変換している(図5)。 In recent years, there are some cases of cold fusion ([Non-Patent Documents 2 and 3]). What is common to both is a combination of deuterium D and metallic palladium Pd. Palladium occludes hydrogen and its volume ratio is as large as 935 times. Tanaka Kikinzoku Kogyo Co., Ltd.'s palladium hydrogen permeable thin film realizes hydrogen gas purification by utilizing selective permeability that allows only hydrogen to pass through. It is assumed that hydrogen molecules are separated into hydrogen atoms in the palladium thin film and return to hydrogen molecules when they pass through the thin film and go out. According to a report from MHI, cesium Cs atoms inside a palladium multilayer that allows deuterium to pass through are transmuted to atoms with a large atomic number (FIG. 5).
中性子を含まない水素原子核よりも、中性子を余分に1個含む重水素原子核の方が、さらに、中性子を余分に2個含むトリチゥム原子核の方が不安定なので、トリチウム水が含まれる放射能汚染水の方が、核変換無害化処理は容易である。そして、核分裂するウランやプルトニウム、核分裂した放射性元素は不安定であるので、容易に安定な元素に核変換されると想定される。但し、水に溶けて居なければならない。このように、凶を吉に転ずるのが本特許の意図である。
超音波キャビテーションによって、放射能汚染水に太陽表面と同様な極限状態をつくるためには、強力な超音波装置が必要である。 In order to create an extreme state similar to the solar surface in radioactively contaminated water by ultrasonic cavitation, a powerful ultrasonic device is required.
そして、散在・漂在する微小気泡の圧壊点が、パラジウム表面で起らなければならない。そのためには、パラジウム表面が同様に水中に散在して表面積が大きく、水の流れがあることである。 And the crushing point of the scattered microbubbles must occur on the palladium surface. To that end, the palladium surface is likewise scattered in the water, has a large surface area and has a flow of water.
福島第1原発の放射能汚染水は100万トンに近い大量である。重元素の核分裂放射性元素を除いた60万トンのトリチウム水の放射能強度は420万ベクレル/リットルである。
トリチウムの崩壊半減期12.3年から概算すると、崩壊前トリチウム原子の個数は3×1014/リットルとなり、自然水の軽水分子の個数3×1025/リットル、自然水に含まれる重水分子の個数4×1021/リットルと比較すると、極端に薄い濃度である。超大量の稀薄放射能汚染水を処理しなければならない。しかし、108個/mm3(1mm3当り1億個)の濃度である。簡単な構造で増設容易な装置が望まれる。The amount of radioactively contaminated water from the Fukushima Daiichi nuclear power plant is close to 1 million tons. The radioactivity intensity of 600,000 tons of tritium water excluding heavy fission radioactive elements is 4.2 million becquerels / liter.
When the decay half-life of tritium is estimated from 12.3 years, the number of tritium atoms before decay is 3 × 10 14 / liter, the number of light water molecules in natural water is 3 × 10 25 / liter, and the number of heavy water molecules contained in natural water is Compared with the number 4 × 10 21 / liter, the concentration is extremely thin. An extremely large amount of dilute radioactively contaminated water must be treated. However, the density is 10 8 pieces / mm 3 (100 million pieces per 1 mm 3 ). A device that has a simple structure and can be easily added is desired.
パラジウムをメッキまたはスパッタ法で被覆した耐蝕性のSUS316L線の網または穴開き(パンチ)板を核変換反応槽に林立させる。反応槽の底から垂直方向に超音波が放射する。垂直なパラジウム被覆の網または穴開き(パンチ)板と直角にキャビテーション気泡が漂い、パラジウム表面と衝突する。連続処理の場合は、直方体の反応槽の給水側から出水側に緩やかに水が流れる。 Corrosion-resistant SUS316L wire mesh or perforated (punch) plates coated with palladium by plating or sputtering are planted in the transmutation reactor. Ultrasonic waves are emitted vertically from the bottom of the reaction vessel. Cavitation bubbles drift perpendicular to the vertical palladium-covered net or perforated (punch) plate and collide with the palladium surface. In the case of continuous treatment, water gently flows from the water supply side to the water discharge side of the rectangular parallelepiped reaction tank.
核変換反応槽の底には外付けで超音波振動子が並ぶ。その出力強度は、超音波振動子箱にした場合は1W/cm2以上のものを採用する。キャビテーションが均一に発生するように、定在波が発生しないように、隣接各超音波振動子の放射位相をずらす。An ultrasonic transducer is arranged on the bottom of the transmutation reaction tank. The output intensity is 1 W / cm 2 or more when an ultrasonic vibrator box is used. The radiation phases of adjacent ultrasonic transducers are shifted so that standing waves do not occur so that cavitation occurs uniformly.
原子力施設で発生する重水、トリチウム水が混合されている放射能汚染水から、トリチウムがヘリウムに変換されて無害化される。
トリチウム水、さらに原子番号の大きい核分裂放射性元素が含まれる放射能汚染水が核変換されて無害化される。From radioactively contaminated water mixed with heavy water and tritium water generated at nuclear facilities, tritium is converted to helium and rendered harmless.
Radioactive contaminated water containing tritium water and fissionable radioactive elements with higher atomic numbers is transmuted and rendered harmless.
▲1▼核変換反応処理槽(図7):下記仕様の槽を直並列に多数設置する。
・深さ90cm、幅44cm、長さ220cm。
・処理槽底外付けに超音波振動子が並ぶ。強度は2W/cm2である。
・給水ホースは上から入り底から出水、出水口は70cm高さにある流水連続型。
・反応槽は、SUS316以上の耐蝕性ステンレス。
・放射能汚染水の飛散と、トリチウム水の蒸散を塞ぐために蓋をする。
・蓋の材質は放射能強度に拠るが、トリチウム水の場合は透明樹脂蓋にする。
▲2▼処理流量・流速・処理量
・流量: 5リットル/分、
・有効断面積: 40cm×50cm=2000cm2、
・流速: 2.5cm/分=150cm/時、到達長さ1.5m/時
・処理量:5リットル/分×60分=300リットル/時、300リットル/時×24時=7.2トン/日
▲3▼D−T反応による発熱量と水温上昇
・D−T反応による放出エネルギー:3.5+14.1=17.6Mev
1ev=1.6×10−19J 1Mev=1.6×10−13J
17.6Mev=17.6×1.6×10−13J=2.8×10−12J
1時間の処理量=300リットルの反応個数:300リットル×(3×1014/リットル)〜1017
2.8×10−12J×1017/(300リットル×1000cc)〜1J/cc
4.2J=1calなので水温昇温は無視できる程小さい。
▲4▼反応槽底に並べる超音波振動子箱からの発熱と水温上昇
・2W/cm2×(20cm×30cm)=1200W 1W=1J/秒 3600J/時
・1200W×10台=12000W/槽
・12000×3600J=4.3×107J〜107cal
・107cal/(1時間の処理水量300リットル=3×105cc)=33℃の水温上昇。
・給水温度〜20℃とすると〜50℃の出水になるので、蒸散を塞ぐため蓋をする。(1) Transmutation reaction treatment tank (Fig. 7): Many tanks with the following specifications are installed in series and parallel.
-Depth 90 cm, width 44 cm, length 220 cm.
-Ultrasonic transducers are arranged on the bottom of the treatment tank. The intensity is 2 W / cm 2 .
-The water supply hose enters from the top and flows out from the bottom, and the water outlet is a continuous running water with a height of 70 cm.
-The reaction tank is SUS316 or higher corrosion resistant stainless steel.
・ Cover to block the scattering of radioactively contaminated water and the evaporation of tritium water.
-The material of the lid depends on the radioactivity intensity, but in the case of tritium water, use a transparent resin lid.
(2) Processing flow rate, flow rate, processing amount-Flow rate: 5 liters / minute,
Effective cross-sectional area: 40 cm × 50 cm = 2000 cm 2
・ Flow rate: 2.5 cm / min = 150 cm / hour, reaching length: 1.5 m / hour ・ Processing amount: 5 liter / minute × 60 minutes = 300 liter / hour, 300 liter / hour × 24 hour = 7.2 tons / Day (3) calorific value due to DT reaction and rise in water temperature Release energy by DT reaction: 3.5 + 14.1 = 17.6 Mev
1ev = 1.6 × 10 −19 J 1Mev = 1.6 × 10 −13 J
17.6 Mev = 17.6 × 1.6 × 10 −13 J = 2.8 × 10 −12 J
1 hour throughput = 300 liter reaction number of 300 liters × (3 × 10 14 / l) 10 17
2.8 × 10 −12 J × 10 17 / (300 liters × 1000 cc) to 1 J / cc
Since 4.2J = 1cal, the water temperature rise is negligibly small.
(4) Heat generation and water temperature rise from the ultrasonic vibrator box arranged at the bottom of the reaction tank 2 W / cm 2 × (20 cm × 30 cm) = 1200 W 1 W = 1 J / second 3600 J / hour 1200 W × 10 units = 12000 W / tank 12000 × 3600J = 4.3 × 10 7 J to 10 7 cal
10 7 cal / (treated water volume for 1 hour 300 liters = 3 × 10 5 cc) = 33 ° C. water temperature rise.
・ If the water supply temperature is 20 ° C, the water discharge will be 50 ° C, so cover it to prevent transpiration.
福島第一原発の放射能汚染水の処理、その他の原子力発電所から放水されている放射能汚染水の処理、六ケ所村再処理工場の放射能汚染水の無害化処理が可能になる。また、試験使用・少量使用されるアイソトープの廃棄無害化処理に応用できる。その場合は、重水に溶かして処理する。 The treatment of radioactive contaminated water from the Fukushima Daiichi nuclear power plant, the treatment of radioactive contaminated water discharged from other nuclear power plants, and the detoxification treatment of radioactive contaminated water at the Rokkasho Reprocessing Plant will be possible. It can also be applied to the detoxification treatment of isotopes used for testing and small quantities. In that case, dissolve in heavy water and treat.
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