JP2013164267A - Radioactive waste liquid processing apparatus and radioactive waste liquid processing method - Google Patents

Abstract

PROBLEM TO BE SOLVED: To provide a radioactive waste liquid processing apparatus and a radioactive waste liquid processing method in which a radioactive waste liquid can be condensed in simple configuration and cost required for condensation can be reduced.SOLUTION: A gas injection mechanism (stirring means) 12 is configured to efficiently transfer to a radioactive waste liquid A thermal energy generated by a nuclear decay of radioactive substances contained in the radioactive waste liquid A. The gas injection mechanism (stirring means) 12 blows gas into the radioactive waste liquid A stored in a storage tank 11, for example, generates a convection in the radioactive waste liquid A and stirs the radioactive waste liquid A. Such a gas injection mechanism (stirring means) 12 is comprised of e.g., a compressor (not illustrated) that sends out the gas and a gas discharge section 14 which discharges the sent-out gas into the storage tank 11 as a gas G for stirring.

Description

  The present invention relates to a radioactive waste liquid treatment apparatus and a radioactive waste liquid treatment method for treating a radioactive waste liquid containing a radioactive substance discharged from a nuclear power plant.

One of the major problems in nuclear power plants is the treatment of radioactive liquid waste. The radioactive liquid waste is subjected to a concentration process of the radioactive substance through steps such as filtration, ion exchange, and evaporation concentration, and then the concentrated radioactive substance is solidified with cement or the like and stored as a stable solid waste.
When filtration or ion exchange treatment is performed, it is necessary to input chemicals for re-separation of radioactive materials, and to treat secondary waste of filtration membranes and ion exchange resins.
In addition, it is desirable to reduce the volume of radioactive waste liquid as much as possible to a stable solid state with a minimum volume. However, in the case of evaporation concentration or solidification treatment, a large amount of heat energy may be input to evaporate moisture. Necessary. For example, Patent Document 1 describes a method for treating a radioactive waste liquid that includes a treatment step in which a concentrated solution is thermally decomposed and melted and solidified.

Japanese Patent No. 29985421

  In the radioactive waste liquid treatment method disclosed in Patent Document 1 described above, it is described that the concentrate is thermally decomposed and melted and solidified by microwave heating. In such a method, the concentrate is pyrolyzed, When melt-solidifying, it is necessary to apply a large amount of heat energy from the outside, and there is a problem that the cost required for heating the waste liquid increases in proportion to the increase in the amount of waste liquid.

  The present invention has been made in view of the above problems, and it is possible to concentrate radioactive waste liquid with a simple configuration, and to reduce the cost required for concentration and radioactive waste liquid treatment. It aims to provide a method.

In order to solve the above problems, some aspects of the present invention provide the following radioactive liquid waste treatment apparatus. That is, the radioactive waste liquid treatment apparatus of the present invention is a radioactive waste liquid treatment apparatus for treating a radioactive waste liquid containing a radioactive substance discharged from a nuclear power plant,
A storage tank for storing the radioactive liquid waste, and a stirring means for stirring the radioactive liquid waste in the storage tank, using the decay heat generated by the nuclear decay, evaporating the water of the radioactive liquid waste as water vapor, The radioactive waste liquid is reduced in volume.

  According to the radioactive liquid waste treatment apparatus having such a configuration, the heat generated by the nuclear decay is efficiently transferred to the entire radioactive liquid waste in the storage tank by the radioactive waste liquid stirring means with respect to the radioactive liquid waste stored in the storage tank. Encourage As a result, compared to conventional radioactive liquid waste treatment equipment that generates water vapor by heating the radioactive liquid waste to concentrate the radioactive liquid waste, it does not require a large amount of energy, such as adding heat energy from the outside, and is radioactive with less energy. It becomes possible to dewater the waste liquid. Therefore, it is possible to concentrate the radioactive liquid waste with a simple configuration, and it is possible to reduce the cost for concentration.

  In addition, in the concentration of radioactive waste liquid, by using evaporation of moisture by decay heat, for example, secondary waste after concentration (ion exchange resin, filtration membrane, compared with concentration using ion exchange resin or filtration membrane) ) Does not occur, the radioactive liquid waste can be concentrated at a low cost.

The stirring means is a gas injection mechanism for blowing a stirring gas into the radioactive liquid waste in the storage tank.
According to the radioactive waste liquid processing apparatus having such a configuration, it is possible to promote effective use of decay heat for agitating the radioactive waste liquid and concentrating the radioactive waste liquid simply by blowing gas into the radioactive waste liquid.

A condenser for condensing water vapor generated in the storage tank to generate condensed water, a concentrator for concentrating the condensed water to generate concentrated water, a reflux pipe for refluxing the concentrated water to the storage tank, Is further provided.
According to the radioactive liquid waste treatment apparatus having such a configuration, decay heat can be more efficiently generated by refluxing the concentrated water generated in the concentrator to the storage tank and using it for nuclear decay.

It further comprises a filtering means for removing radioactive substances contained in the condensed water.
According to the radioactive liquid waste treatment apparatus having such a configuration, it is possible to obtain safe discharged water from which radioactive substances have been removed.

It further comprises reaction means for reacting hydrogen contained in the water vapor generated in the storage tank with oxygen through a catalyst.
According to the radioactive liquid waste treatment apparatus having such a configuration, it is possible to recover and use thermal energy from hydrogen contained in water vapor.

It further comprises heat conduction means for propagating reaction heat generated by the reaction means to the radioactive waste liquid in the storage tank.
According to the radioactive liquid waste treatment apparatus having such a configuration, the radioactive liquid waste can be more efficiently concentrated by recovering the thermal energy from the hydrogen contained in the water vapor and using it for the concentration of the radioactive liquid waste. .

A solidified material injection hole for injecting the solidified material into the storage tank is formed.
According to the radioactive liquid waste treatment apparatus having such a configuration, a solidified material for disposal can be easily formed from the residue of the concentrated radioactive liquid waste.

The radioactive waste liquid treatment method of the present invention is a radioactive waste liquid treatment method for treating a radioactive waste liquid containing a radioactive substance discharged from a nuclear power plant,
In the storage tank for storing the radioactive liquid waste, at least an evaporation step of efficiently using heat generated from nuclear decay of the radioactive substance and evaporating the water of the radioactive liquid waste as water vapor using the decay heat is provided. It is characterized by that.

  According to the radioactive waste liquid processing method having such a configuration, the decay heat generated from the radioactive waste liquid stored in the tank is utilized to efficiently promote the evaporation of moisture in the radioactive waste liquid. As a result, compared to conventional radioactive liquid waste treatment equipment that generates water vapor by heating the radioactive liquid waste to concentrate the radioactive liquid waste, it does not require a large amount of energy, such as adding heat energy from the outside, and is radioactive with less energy. It becomes possible to dewater the waste liquid. Therefore, it is possible to concentrate the radioactive liquid waste with a simple configuration, and it is possible to reduce the cost for concentration.

  In addition, it is possible to concentrate radioactive waste liquid simply by stirring the radioactive waste liquid, so the process of heating the radioactive waste liquid from the outside, or the concentration process using ion exchange resin or filtration membrane, etc. Is no longer necessary. This greatly simplifies the concentration process of the radioactive liquid waste and makes it possible to concentrate and dehydrate the radioactive liquid liquid with a simple process.

The method further comprises a coagulation step of adding a coagulant to the radioactive liquid waste concentrate obtained by the evaporation step to obtain a solidified body.
According to the radioactive liquid waste processing method having such a configuration, a solidified material for disposal can be easily formed from the residue of the radioactive liquid waste after concentration.

  According to the radioactive liquid waste treatment apparatus of the present invention, the decay heat generated from the radioactive liquid waste stored in the storage tank is utilized to efficiently promote the evaporation of moisture in the radioactive liquid waste. As a result, compared to conventional radioactive liquid waste treatment equipment that generates water vapor by heating the radioactive liquid waste to concentrate the radioactive liquid waste, it does not require a large amount of energy, such as adding heat energy from the outside, and is radioactive with less energy. It becomes possible to dewater the waste liquid. Therefore, it is possible to concentrate the radioactive liquid waste with a simple configuration, and it is possible to reduce the cost for concentration.

  In addition, in the concentration of radioactive waste liquid, by using evaporation of moisture by decay heat, for example, secondary waste after concentration (ion exchange resin, filtration membrane, compared with concentration using ion exchange resin or filtration membrane) ) Does not occur, the radioactive liquid waste can be concentrated at a low cost.

It is a schematic block diagram which shows the outline | summary of the radioactive waste liquid processing apparatus (1st embodiment) of this invention. It is a schematic block diagram which shows the outline | summary of the radioactive waste liquid processing apparatus (2nd embodiment) of this invention. It is a schematic block diagram which shows the outline | summary of the radioactive waste liquid processing apparatus (modified example of 2nd embodiment) of this invention. It is a schematic block diagram which shows the outline | summary of the radioactive waste liquid processing apparatus (3rd embodiment) of this invention. It is a schematic block diagram which shows the outline | summary of the radioactive waste liquid processing apparatus (4th embodiment) of this invention.

  Hereinafter, with reference to the drawings, an embodiment of a radioactive waste liquid treatment apparatus and a radioactive waste liquid treatment method according to the present invention will be described. The present embodiment is specifically described for better understanding of the gist of the invention, and does not limit the invention unless otherwise specified. In addition, in the drawings used in the following description, in order to make the features of the present invention easier to understand, there is a case where a main part is shown in an enlarged manner for convenience, and the dimensional ratio of each component is the same as the actual one. Not necessarily.

[First embodiment]
FIG. 1 is a schematic configuration diagram according to the first embodiment of the radioactive liquid waste treatment apparatus of the present invention.
The radioactive waste liquid processing apparatus 10 according to the present embodiment is an apparatus that increases (concentrates) the concentration of radioactive substances contained in the radioactive waste liquid by evaporating the moisture of the radioactive waste liquid as water vapor. The radioactive waste liquid treatment apparatus 10 includes a storage tank 11 that stores the radioactive waste liquid A, and a gas injection mechanism (stirring means) 12 that is provided in the storage tank 11 and promotes the decay of the radioactive waste liquid.

  The storage tank 11 is, for example, a water tank for storing high-level radioactive liquid waste generated when reprocessing spent nuclear fuel in a nuclear power plant centered on a nuclear reactor. The high-level radioactive waste liquid stored in the storage tank 11 (hereinafter sometimes simply referred to as radioactive waste liquid) contains fission products (FP) and transuranium nuclides (TRU / MA), and emits strong radiation over a long period of time. Release across. The radioactive material contained in such radioactive liquid waste causes nuclear decay when emitting strong radiation, and decay heat is generated in the process of nuclear decay.

Nuclear decay is a phenomenon in which an unstable nucleus (radioisotope) undergoes radioactive decay,
Alpha decay that emits alpha particles and turns into a nuclide with two protons and two neutrons reduced, beta decay in which proton and neutron conversion is performed without changing mass number Known are gamma decay, which emits gamma rays by the remaining excess energy, and fission reactions in which heavy and unstable nuclei split into smaller nuclei and change into stable nuclides.

  Decay heat is generated because the radiation energy released during the nuclear decay heats the surrounding material. The energy of decay heat released per hour is larger for unstable nuclides, and its magnitude decreases as the original radioactive material gradually emits radiation and changes to relatively stable nuclides and stable nuclides. To do.

  The gas injection mechanism (stirring means) 12 is a means for efficiently transmitting the thermal energy generated by the nuclear decay of the radioactive substance contained in the radioactive waste liquid A to the radioactive waste liquid A. The gas injection mechanism (stirring means) 12, for example, blows gas into the radioactive waste liquid A stored in the storage tank 11, causes convection in the radioactive waste liquid A, and stirs the radioactive waste liquid A. The gas injection mechanism (stirring means) 12 includes, for example, a compressor (not shown) that sends out gas and a gas discharge unit 14 that discharges the sent gas into the storage tank 11 as a stirring gas G. Yes.

  The stirring gas G discharged into the storage tank 11 is not particularly limited, and examples thereof include air, nitrogen, and a rare gas. When nitrogen or a rare gas is used as the stirring gas G, a gas cylinder or the like for supplying these gases to the compressor may be connected.

  The radioactive waste liquid processing method of this invention using the radioactive waste liquid processing apparatus 10 of the above structures is demonstrated. When concentration of radioactive waste liquid, which is one of radioactive waste liquid treatment, is performed by the radioactive waste liquid treatment method of the present invention, first, a high-level radioactive waste liquid generated when reprocessing spent nuclear fuel such as a nuclear power plant is stored in a storage tank 11. Introduce and store.

Most of the radioactive substances contained in the radioactive liquid waste are present in the form of fine particles, and the radioactive substances are deposited on the bottom of the storage tank 11 when they are left standing for a long time. Since thermal energy due to nuclear decay is generated biased toward the bottom of the storage tank 11, the high-level radioactive liquid waste introduced into the storage tank 11 cannot be efficiently heated.
Next, the gas injection mechanism (stirring means) 12 is operated to discharge (inject) the stirring gas G from the gas discharge unit 14 into the radioactive waste liquid A (evaporation step). When the stirring gas G is sent into the radioactive liquid waste A, convection occurs in the radioactive liquid waste A due to the rising of the bubbles, and the radioactive liquid waste A is stirred.

By stirring the radioactive liquid waste A with the gas G for stirring, the radioactive material is uniformly distributed in the storage tank 11, so that the heat energy generated by the nuclear decay can be uniformly transmitted to the radioactive liquid A.
As a result, the radioactive liquid waste A is efficiently heated, and moisture is released from the storage tank 11 as water vapor H. As a result, moisture is quickly removed from the radioactive liquid waste A, and the radioactive liquid waste A is concentrated (dehydrated). The concentration of the radioactive waste liquid A is preferably performed, for example, to such an extent that moisture is completely removed from the radioactive waste liquid A and the radioactive substance residue is solidified.

  According to the radioactive waste liquid processing apparatus and the radioactive waste liquid processing method of the present invention having the above-described configuration, the nuclear nuclei are generated by the gas injection mechanism (stirring means) 12 serving as the stirring means for the radioactive waste liquid A stored in the storage tank 11. Efficiently promotes the evaporation of moisture in radioactive liquid waste by efficiently using decay heat generated from decay. As a result, compared to conventional radioactive waste liquid treatment equipment that generates water vapor by heating the radioactive waste liquid A for concentration of the radioactive waste liquid A, it does not require a large amount of energy, such as adding heat energy from the outside. The radioactive waste liquid A can be dehydrated with less energy, such as by feeding in the waste water. As a result, it is possible to concentrate the radioactive liquid waste with a simple configuration and to reduce the cost for concentration.

  In addition, in the concentration of radioactive waste liquid, by using evaporation of moisture by decay heat, for example, secondary waste after concentration (ion exchange resin, filtration membrane, compared with concentration using ion exchange resin or filtration membrane) ) Does not occur, the radioactive liquid waste can be concentrated at a low cost.

  Further, when the radioactive liquid waste is concentrated, the radioactive liquid waste A can be concentrated only by stirring the radioactive liquid waste A. For this reason, the process which heats radioactive waste liquid A from the outside, and the concentration process using an ion exchange resin, a filtration membrane, etc. become unnecessary. This makes it possible to greatly simplify the radioactive waste liquid concentration process.

  In the embodiment described above, the radioactive waste liquid is agitated in order to efficiently use the decay heat, but in addition to this, the radioactive waste liquid is mechanically agitated using a screw or the like, The structure which accelerates | stimulates the nuclear decay of the radioactive substance contained in radioactive waste liquid by other methods, such as applying an ultrasonic wave, may be sufficient.

  In addition, when the amount of heat necessary for concentration of the radioactive liquid waste cannot be obtained only by decay heat, it is also preferable to promote the heating of the radioactive liquid waste by introducing high-temperature steam from a boiler or the like.

[Second Embodiment]
FIG. 2 is a schematic configuration diagram according to the second embodiment of the radioactive liquid waste treatment apparatus of the present invention.
The radioactive liquid waste treatment apparatus 20 according to this embodiment is obtained by further adding a treatment mechanism for water vapor generated by decay heat to the radioactive liquid waste treatment apparatus of the first embodiment described above.
The radioactive liquid waste treatment apparatus 20 includes a storage tank 21 that stores the radioactive liquid waste A, a gas injection mechanism (stirring means) 22 that is provided in the storage tank 21 and promotes the decay of the radioactive liquid waste, and a water vapor treatment mechanism 25. It is equipped with. The gas injection mechanism (stirring means) 22 includes a compressor (not shown) that sends out a gas, and a gas discharge unit 24 that discharges the sent gas into the storage tank 21 as a stirring gas G.

The steam treatment mechanism 25 includes a condenser 31, a condensed water tank 32, a concentrator (concentration step) 33, a nuclide removal device (filtering means) 34, a treated water tank 35, and the like.
The water vapor H generated by the decay heat of the radioactive liquid waste A stirred by the gas injection mechanism (stirring means) 22 may contain a trace amount of radionuclide. For this reason, this water vapor H is processed by the water vapor processing mechanism 25.

  The condenser 31 is a heat exchanger, for example, and is liquefied by cooling the water vapor H into droplets. And it is stored in the condensed water tank 32 as condensed water. The concentrator (concentration step) 33 concentrates the content of the radionuclide contained in the condensed water, and increases the radionuclide removal efficiency by the nuclide removal device 34. As such a concentrator (concentration step) 33, for example, a distillation apparatus is used.

  In addition, a reflux pipe 36 for returning a part of the concentrated water generated by the concentrator (concentration step) 33 to the storage tank 21 is provided. The concentrated water refluxed by the reflux pipe 36 can be used to generate decay heat in the storage tank 21, and the generation of decay heat in the storage tank 21 can be promoted more efficiently.

The nuclide removing device (filtering means) 34 removes a small amount of radionuclide contained in the treated water generated by the concentrator (concentration step) 33, and performs adsorption of the radionuclide with a filter medium, for example, activated carbon. The adsorbed activated carbon generated here becomes secondary waste, but the amount of radionuclide contained in the treated water is very small, and the amount generated is small compared to the amount treated with the radioactive waste liquid A.
The treated water after the radionuclide is adsorbed by the nuclide removing device (filtering means) 34 is once stored in the treated water tank 35 and then discharged. The treated water at the time of discharge is water having quality within various discharge standards.

  According to the radioactive liquid waste treatment apparatus 20 having such a configuration, the water vapor H generated by the decay heat of the radioactive liquid waste A is concentrated, and a part of the concentrated water is refluxed to the storage tank 21 via the reflux pipe 36. Generation of decay heat of the radioactive liquid waste A can be further promoted. Further, by removing the radionuclide contained in the treated water generated by the concentrator (concentration step) 33 by the nuclide removing device (filtering means) 34, the treated water can be safely discharged.

  In addition, a part of the process of introducing the stirring gas G from the outside may be omitted by returning a part of the concentrated water obtained from the water vapor H generated by the decay heat of the radioactive liquid waste A to the storage tank 21. It becomes possible to realize further simplification of the concentration process of radioactive liquid waste.

  In addition, as shown in FIG. 3, it is also preferable to further include a used filter medium introduction step P for introducing the filter medium used in the nuclide removal apparatus (filter means) 34 of the radioactive liquid waste treatment apparatus 20, for example, activated carbon, into the storage tank 21. . By introducing the activated carbon (filter medium) after adsorbing the radionuclide contained in the treated water into the storage tank 21 by the used filter medium introduction process P, waste containing radioactive substances can be collected in the storage tank 21. As a result, the solid waste (radioactive material) remaining after concentration (dehydration) of the radioactive liquid waste A in the storage tank 21 and the used used filter medium are consolidated into a solidified body. Processing can be performed.

[Third embodiment]
FIG. 4 is a schematic configuration diagram according to the third embodiment of the radioactive liquid waste treatment apparatus of the present invention.
The radioactive liquid waste treatment apparatus 40 according to this embodiment further adds a reaction mechanism for extracting energy from hydrogen contained in water vapor generated by decay heat to the radioactive liquid waste treatment apparatus of the first embodiment described above. Is.
The radioactive waste liquid treatment apparatus 40 includes a storage tank 41 for storing the radioactive waste liquid A, a gas injection mechanism (stirring means) 42, and a reaction mechanism 45 provided in the storage tank 41. The gas injection mechanism (stirring means) 42 includes a compressor (not shown) that sends out gas, and a gas discharge unit 44 that discharges the sent gas into the storage tank 41 as a stirring gas G.

The reaction mechanism 45 includes a reactor (reaction means) 51, a heat exchanger (heat conduction means) 52, an exhaust gas recirculation pipe 53, and the like.
The water vapor (vapor containing hydrogen) H generated by the decay heat of the radioactive liquid waste A stirred by the gas injection mechanism (stirring means) 22 contains liberated hydrogen. The reactor (reaction means) 51 includes a catalyst for reacting this hydrogen with air or oxygen (oxyhydrogen reaction). As this catalyst, for example, a material containing platinum, palladium or the like can be used. Such a reaction between hydrogen and air or oxygen generates water vapor and heat of reaction. This reaction heat is propagated to a heat exchanger (heat conduction means) 52 formed in the storage tank 41 and used to heat the radioactive waste liquid A stored in the storage tank 41.

  On the other hand, the exhaust gas composed of water vapor generated by the oxyhydrogen reaction in the reactor 51 is refluxed to the gas injection mechanism (stirring means) 42 through the exhaust gas recirculation pipe 53. Then, by releasing the exhaust gas as the stirring gas G from the gas discharge portion 44, the thermal energy contained in the exhaust gas can be used for the evaporation of the radioactive waste liquid A.

  According to the radioactive waste liquid processing apparatus 40 having such a configuration, the radioactive waste liquid A is stirred by the stirring gas G to promote the generation of decay heat, and hydrogen and air contained in the water vapor generated from the radioactive waste liquid A are removed. By reacting in the reactor 51 and using the generated reaction heat for heating the radioactive liquid waste A, the radioactive liquid waste A can be more efficiently concentrated with less energy consumption. Further, the exhaust gas generated in the reactor 51 is refluxed to the gas injection mechanism (stirring means) 42, whereby the stirring gas G can be easily generated.

  Further, by using the exhaust gas generated in the reactor 51 as the stirring gas G, it is possible to omit the process of introducing the stirring gas G from the outside, thereby further simplifying the concentration process of the radioactive liquid waste. It becomes possible.

[Fourth embodiment]
FIG. 5 is a schematic configuration diagram according to the fourth embodiment of the radioactive liquid waste treatment apparatus of the present invention.
The radioactive waste liquid treatment apparatus 60 according to this embodiment is obtained by adding a configuration that facilitates the production of a solidified body to the radioactive waste liquid treatment apparatus of the first embodiment described above.
The radioactive waste liquid treatment apparatus 60 includes a storage tank 61 for storing the radioactive waste liquid A, and a gas injection mechanism (stirring means) 62 provided in the storage tank 61. The gas injection mechanism (stirring means) 62 includes a compressor (not shown) that sends out gas, and a gas discharge section 64 that discharges the sent gas into the storage tank 61 as a stirring gas G.

  Further, the storage tank 61 is formed with a solidified material injection hole 69 for injecting the solidified material into the storage tank 61. The coagulating material is a material for solidifying a high-level radioactive substance generated after concentration and drying of the radioactive liquid waste A to obtain a solidified material for disposal as a geological formation. For example, cement or glass is used.

  In order to uniformly inject the solidified material into the storage tank 61 without unevenness, a large number of the solidified material injection holes 69 are formed, for example, on the entire upper surface 61a of the storage tank 61 at equal intervals. A solidified material for geological disposal can be obtained by uniformly injecting and solidifying a solidified material, for example, cement, from the solidified material injection hole 69 to the radioactive material remaining after concentration (solidification step).

  DESCRIPTION OF SYMBOLS 10 ... Radioactive waste liquid processing apparatus, 11 ... Storage tank, 12 ... Gas injection mechanism (stirring means), G ... Gas for stirring.

Claims (9)

A radioactive liquid waste treatment apparatus for treating radioactive liquid waste containing radioactive substances discharged from a nuclear power plant,
A storage tank for storing the radioactive liquid waste;
And at least stirring means for uniformly stirring the radioactive substance in the storage tank,
A radioactive liquid waste treatment apparatus characterized in that, by using decay heat generated by the nuclear decay, water in the radioactive liquid waste is evaporated as water vapor to reduce the volume of the radioactive liquid waste.   2. The radioactive waste liquid treatment apparatus according to claim 1, wherein the stirring means is a gas injection mechanism for blowing a stirring gas into the radioactive waste liquid in the storage tank.   A condenser for condensing water vapor generated in the storage tank to generate condensed water, a concentrator for concentrating the condensed water to generate concentrated water, a reflux pipe for refluxing the concentrated water to the storage tank, The radioactive waste liquid treatment apparatus according to claim 1, further comprising:   The radioactive waste liquid treatment apparatus according to claim 3, further comprising a filtering means for removing radioactive substances contained in the condensed water.   5. The radioactive liquid waste treatment apparatus according to claim 1, further comprising reaction means for reacting hydrogen contained in the water vapor generated in the storage tank with oxygen through a catalyst.   6. The radioactive waste liquid treatment apparatus according to claim 5, further comprising heat conduction means for propagating reaction heat generated by the reaction means to the radioactive waste liquid in the storage tank.   The radioactive waste liquid treatment apparatus according to any one of claims 1 to 6, wherein a coagulation material injection hole for injecting the coagulation material into the storage tank is formed. A radioactive waste liquid treatment method for treating a radioactive waste liquid containing radioactive substances discharged from a nuclear power plant,
In the storage tank for storing the radioactive liquid waste, at least an evaporation step of efficiently using heat generated from nuclear decay of the radioactive substance and evaporating the water of the radioactive liquid waste as water vapor using the decay heat is provided. A method for treating radioactive liquid waste.   9. The radioactive waste liquid treatment method according to claim 8, further comprising a solidification step of adding a coagulant to the radioactive waste liquid concentrate obtained in the evaporation step to obtain a solidified body.

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