GB2187973A - Process and apparatus for decontaminating exhaust gas from a fusion reactor fuel cycle - Google Patents
Process and apparatus for decontaminating exhaust gas from a fusion reactor fuel cycle Download PDFInfo
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- G—PHYSICS
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- G21F—PROTECTION AGAINST X-RADIATION, GAMMA RADIATION, CORPUSCULAR RADIATION OR PARTICLE BOMBARDMENT; TREATING RADIOACTIVELY CONTAMINATED MATERIAL; DECONTAMINATION ARRANGEMENTS THEREFOR
- G21F9/00—Treating radioactively contaminated material; Decontamination arrangements therefor
- G21F9/02—Treating gases
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/22—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by diffusion
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8671—Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
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- G—PHYSICS
- G21—NUCLEAR PHYSICS; NUCLEAR ENGINEERING
- G21B—FUSION REACTORS
- G21B1/00—Thermonuclear fusion reactors
- G21B1/11—Details
- G21B1/115—Tritium recovery
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- 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
- Y02E30/10—Nuclear fusion reactors
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Abstract
Process for decontaminating exhaust gas from a fusion reactor fuel cycle of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, in which the at least one heavy hydrogen isotope is liberated from its compound, separated out from the exhaust gas and fed back into the fuel cycle, the compound form being at least one compound which is ammonia or a hydrocarbon, comprising: a) converting the at least one heavy hydrogen-containing compound into its elements in the exhaust gas by cracking the at least one heavy hydrogen containing compound with a cracking medium to liberate the hydrogen isotope, b) passing the liberated hydrogen isotope through a membrane to separate out the liberated hydrogen isotope from the flow of the remaining exhaust gas, and c) discharging the remaining decontaminated exhaust gas into the surrounding air. Apparatus for use in the above process is also described.
Description
SPECIFICATION
Process and apparatus for decontaminating exhaust gas from a fusion reactor fuel cycle of exhaust gas components containing chemically bonded tritium and/or deuterium
BACKGROUND OF THE INVENTION
The present invention relates to a process and an apparatus for decontaminating exhaust gas from a fusion reactor fuel cycle of exhaust gas components containing chemically bonded tritium and/or deuterium, in which tritium and/or deuterium is/are liberated from its/their compounds, separated out from the exhaust gas and fed back into the fuel cycle.
The exhaust gas from a fusion reactor fuel cycle contains about 85%-by-volume noble gases and about 15%-by-volume impurities, including small residual amounts of heavy hydrogen. The impurities accumulate in the form of argon, "tritiated" and/or "deuterated" hydrocarbons, particularly tritiated and/or "deuterated" CH4, tritiated and/or deuterated water and tritiated and/or deuterated ammonia. The exhaust gas must thus be liberated both from free tritium as well as impurities containing tritium and be decontaminated to a value level permissible for emission before the exhaust gas remainder can be released into the surrounding atmosphere.Moreover, it is desirable to recover the tritium and deuterium from their compounds and to feed the tritium and deuterium back into the fuel cycle, not least because it is in this way guaranteed that the tritium is kept from entering the surrounding atmosphere.
A process and an apparatus for decontaminating exhaust gas of tritium and/or deuterium has been suggested by Kerr et al, "Fuel Cleanup System for the Tritium Systems Test Assembly:
Design and Experiments", Proceedings of Tritium Technology in Fission, Fusion and Isotopic
Application, Dayton, Ohio, April 29, 1980, at pages 115 to 118. According to one process described by Kerr et al, the exhaust gas containing the impurities is first passed through an intermediate container, that is, a variable volume surge tank which is used to remove flow fluctuations and provide a constant feed pressure. The exhaust gas is then passed to a first catalytic reactor in which any free oxygen is reduced and combined with hydrogen at 4500K to form water.The exhaust gas is then sent to a molecular sieve bed at 750K in which all impurities are adsorptively removed and are thus separated out from the exhaust gas. When the capacity of the molecular sieve bed is exhausted, it is heated to 400"K to desorb the impurities which are then sent to a second catalytic reactor in the form of an oxygen-supplying packed bed operating at 8000K where the impurities (e.g., ammonia and hydrocarbons) are oxidized into tritium- and/or deuterium-containing water and into tritium- and/or deuterium-free compounds, namely into CO2, N2 and Ar. The tritium- and/or deuterium-containing water then is frozen out at 160 K, and thereafter the frozen water is periodically vaporized.The vapors are fed into a hot uranium metal bed which acts as a getter and which at 7500K transforms (reduces) the water into D- and/or T-containing hydrogen and stable UO2. In lieu of the reduction by means of the uranium metal bed, Kerr et al state that the reduction can also be carried out with the aid of an electrolytic cell when such a cell becomes available.
Kerr et al also describe a process based on hot uranium metal getters. In this process, the exhaust gas, after leaving the variable volume surge tank, enters a primary uranium bed operating at 1170 K. In this bed, impurities are removed by chemical reactions that form uranium oxides, carbides, and nitrides. The inert argon, with traces of the other impurities, passes through the primary uranium bed and is sent to a molecular sieve bed as in the above-described process. The regenerated argon, with a small amount of tritium, is sent from the molecular sieve bed to a titanium bed, at 5000K, which collects DT and passes on an argon stream containing only tenths of a ppm of DT. Kerr et al state that a disadvantage of this process is that operating temperatures of 11 700K cause permeation and material problems.
Kerr et al also describe the use of palladium diffusers, and state that they have numerous disadvantages including the need for elevated pressures, reported poisoning by ammonia and methane, and the fact that they can not produce an impurity an impurity stream free of hydrogen isotopes.
The processes suggested heretofore for decontaminating exhaust gases of tritium and/or deuterium have the following disadvantages: many steps in the process; high temperature and thus the danger of tritium losses through permeation; operation of the oxygen-supplying packed bed (second catalytic reactor) at high temperatures, with which is associated a possible sintering of the packed bed particles as well as an excess of oxygen given off (deactivation), which strains the hot metal getter; transformation of ammonia and hydrocarbons by oxidation at the second catalytic reactor with formation of water and subsequent reduction of the water created by the hot metal getter (strain on the hot metal getter); oxidation of hydrogen to water at the first catalytic reactor and subsequent reduction of the water created by the hot metal getter (strain of the hot metal getter); high radioactive waste solids and creation of nitrogen oxides during NH3 oxidation on the oxygen-supplying packed solids bed (second catalytic reactor).
SUMMARY OF THE INVENTION
An object of the present invention is to provide a process and an apparatus for decontaminating the exhaust gas from a fusion reactor fuel cycle of exhaust gas components which contain tritium and/or deuterium in chemically bonded form.
A further object of the present invention is to provide such a process in which tritium and/or deuterium losses through permeation and the high stresses of the hot metal getter materials, as they appeared in the heretofore known prior art processes, as well as the formation of nitrogen oxides are avoided.
Another object of the present invention is to provide such a process which is energy-saving vis-a-vis the heretofore known prior art processes and which is able to be implemented simply.
A still further object of the present invention is to provide such a process which is able to feed back the liberated tritium and/or deuterium into the fuel cycle without further treatment steps, with the exception of an isotope separation.
Additional objects and advantages of the present invention will be set forth in part in the description which follows and in part will be obvious from the description or can be learned by practice of the invention. The objects and advantages are achieved by means of the processes, instrumentalities and combinations particularly pointed out in the appended claims.
To achieve the foregoing objects and in accordance with its purpose, the present invention provides a process for decontaminating exhaust gas from a fusion react fuel cycle of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, in which the at least one heavy hydrogen isotope is liberated from its compound, separated out from the exhaust gas and fed back into the fuel cycle, the compound form being at least one compound which is ammonia or hydrocarbon, comprising: a) converting the at least one heavy hydrogen containing compound into its elements in the exhaust gas by cracking the at least one heavy hydrogen containing compound with a cracking medium to liberate the hydrogen isotope, b) passing the liberated hydrogen isotope through a membrane to separate out the liberated hydrogen isotope from the flow of the remaining exhaust gas, and c) discharging the remaining decontaminated exhaust gas into the surrounding air.
The medium for cracking ammonia preferably is a membrane made of palladium or made of a palladium-silver alloy or an Ni catalyst. When ammonia and hydrocarbons both are to be cracked, the cracking reactions can take place in successive steps or can occur in a common process step. The separation of the liberated hydrogen isotopes from the exhaust gas can occur in a common process step or can take place in successive steps, when a closed loop operation with gas circulation is selected and the hydrogen isotopes from the cracking of ammonia are separated through the membrane for cracking and the hydrogen isotopes from the cracking of hydrocarbon are separated through the same membrane. In case of a once-through operation an additional membrane would be required.
In a preferred embodiment of the process according to the present invention, the cracking reactions for ammonia and the hydrocarbons are carried out at an Ni-catalyst on a ceramic catalyst support at a temperature ranging between 2500C and 450 C, the membrane is made of palladium or a palladium-silver alloy and surrounds the catalyst, and the catalyst which is inside the membrane is heated simultaneously with the membrane to the reaction temperature.
Preferably, the exhaust gas is first selectively oxidized at an oxidation catalyst to oxidize CO and CO2, then brought into contact with an O2 getter metal at a temperature ranging from 2000C to 4000C in order to eliminate O2 and to reduce water. Preferably, in order to crack the ammonia and hydrocarbons, the exhaust gas then is brought into contact with a hydrogen-isotopepermeable membrane and with an Ni-catalyst at a temperature ranging from 300"C to 450 C.
The apparatus according to the present invention for the purpose of implementing the process comprises an exhaust gas conduit which is channeled into the cycle, and arranged in succession in the conduit in the flow direction of the exhaust gas there is: (a) a buffer vessel for equalizing the gas pressure, (b) a catalyst bed for selectively oxidizing CO into CO2, (c) a heatable metal bed for selectively removing O3 and water from the exhaust gas by means of chemical reaction, (d) a container holding at least one membrane which is selectively permeable to hydrogen isotopes, the contain having a product discharge valve for the hydrogen isotopes, and (e) a heatable bed containing a regeneratable Ni-catalyst and having an inflow and an outflow for a regeneration agent. Preferably, at least one pump is provided to circulate the exhaust gas.
In an alternate embodiment of the apparatus, in lieu of the combination of the container holding the membrane and the heatable bed containing the regeneratable Ni-catalyst, there is an externally-coolable container which is cooled on the outside to a temperature c200 C, the container having: (i) a vessel mounted in the container and made of palladium/or a palladiumsilver alloy. the vessel containing an Ni-catalyst, the vessel having a supply feed conduit for feeding the exhaust gas which is to be decontaminated into the vessel and a discharge conduit for removing the decontaminated exhaust gas from the vessel, (ii) a gas outlet for the hydrogen isotopes separated out from the exhaust gas, and (iii) a heater for the vessel positioned between the vessel and the inner wall of the container.It is especially advantageous when the vessel is designed as a spiral-shaped pipe.
It is to be understood that both the foregoing general description and the following detailed description are exemplary and explanatory, but are not restrictive of the invention.
BRIEF DESCRIPTION OF THE DRAWINGS
Figure 1 shows a schematic representation of one embodiment of an apparatus according to the present invention, in which the cracking of ammonia and the cracking of the hydrocarbons takes place in two separate and different parts of the apparatus.
Figure 2 shows a schematic representation of another embodiment of an apparatus according to the present invention, in which ammonia and hydrocarbons are simultaneously cracked in the same part of the apparatus.
Figure 3 shows a schematic representation of a testing set-up for an experimental process, with which the effectiveness of the process according to the present invention has been ascertained.
Figure 4 is a graph illustrating the effectiveness of the cracking reaction of methane.
Figure 5 is a graph illustrating the effectiveness of the cracking reaction of ammonia.
DETAILED DESCRIPTION OF THE INVENTION
The exhaust gas from the fuel cycle of a fusion reactor has more or less the following composition: 80 to 85 Mol. % He, Ar 15 to 20 Mol. % N(O)3, C(O)4 (0)20, (Q)2,
CO, CO2, N2 and 03. (O=H, D, T)
It is quite obvious that a portion of the heavy hydrogen isotopes can be supplanted by light hydrogen (protium) in the appropriate bondings.
The advantages of the process according to the present invention and the apparatus according to the present invention are to be seen in the fact that
(a) a reduction in the number of treatment steps is achieved,
b) with the exception of the cracking temperature for NO, and CQ4, the maximal operating temperature within the cycle system does not exceed 3000C and therefore no losses of tritium can take place by permeation through metallic walls,
c) a minimization of radioactive waste solids is attained,
d) a reduction of the strain of the oxygen getter (of the metal bed) to a minimum takes place (in the present invention there is no in-situ 03 formation as a result of chemical cracking of ammonia and hydrocarbon at an oxygen-supplying packed bed) (the catalyst bed in the present invention is employed for selective oxidation of CO into CO2); (in the present invention there is no Q2 oxidation to water and therefore there is no subsequent reduction of the water on the oxygen getter),
e) no nitrogen oxide formation takes place and
f) in the event of a combination of cracking of tritiumized and/or deuteriumized impurities ammonia and hydrocarbons with the separation of tritium and/or deuterium: shifting the thermodynamics and kinetics of the chemical reaction in a direction more favorable to the process.
In the prior art process which was discussed above, permeation losses of heavy hydrogen can occur both in the catalytic oxidation of the oxidizable exhaust gas components as well as in the reduction of water to hydrogen in the uranium bed.
In the process according to the present invention, the exhaust gas is introduced as feed gas into a pipeline channeled into the cycle, flows through a buffer vessel and then, at about room temperature (20 to 250C), passes through a packed bed functioning as a catalyst. The packed bed contains, for example hopcalite (CuO/MnO2) or perowskite. From this, oxygen and carbon monoxide contained in the exhaust gas are selectively converted to CO2.
The exhaust gas leaving this catalyst is subsequently passed over a bed, which can, for example, contain uranium metal or titanium metal, at a temperature between about 2000 and about 400 C, preferably at 350 C, in which water is cracked thereby forming hydrogen and, for example, uranium oxide; and oxygen, including any oxygen which possibly was not transformed into carbon dioxide, is gettered.
The exhaust gas leaving this oxygen getter is then conducted through a container which contains one or more membranes made of palladium or of a palladium-silver alloy at a temperature between about 3000 and about 450 C, preferably 4000 to 450 C, and at the membranes the ammonia contained in the exhaust gas is quantitatively cracked. The membranes can be designed as a directly-heated pipe or pipe assembly, which is jacketed around with a cooled external vessel or container. The membranes are selectively permeable to hydrogen isotopes, and thus from this membrane container, the heavy hydrogen which emerged from the cracking process is drawn off, and (if necessary, after passing a hydrogen isotrope separating apparatus) is fed back into the fuel cycle of the fusion reactor.
The exhaust gas liberated from ammonia in this way is then passed through a nickel catalyst packed bed which is heated to a temperature of about 2500 to about 450 , preferably to 450 C, for the purpose of cracking the hydrocarbons, methane in particular. The cracking takes place according to the following formula.
Ni C0O2n+x , 1/2(2n+x)Q2+Cn(Ni), n= 1, 2 etc. (1)
x=O, 2
According to its degree of purity, the remaining gas which leaves the nickel catalyst packed bed can either be discharged directly into the surrounding air or be run through the cycle until it reaches the required purity, whereby it first flows through the buffer vessel again and then the catalyst beds, oxygen getter and containers, as described.
In time, the catalyst is depleted and must be either thrown out or regenerated with hydrogen at a sufficiently high temperature, according to the following formula: C(NI)+2O2 , CQ4 CO, (2) While the known process according to the prior art contains at least 7 process steps whose individual operational temperatures are far removed from one another (the greatest temperature difference between any two successive and consecutive steps amounts to 6400C in the embodiment of the Kerr et al process which employs a catalytic reactor to oxidize all oxidizable components of the exhaust gas), the process according to the present invention is designed so that the three or four steps show significantly smaller temperature differentials on a path in which the temperature rises exclusively.Whereas in the process belonging to the state of the art the catalytic oxidation of all oxidizable components of the exhaust gas takes place at 8000K (527 C), in the process according to the present invention the catalytic oxidation is only selectively applied to oxidize CO into CO2 at low temperatures in the range of 200 to 25 C. In the process according to the present invention, the subsequent reduction of water and the removal of oxygen by means of a getter metal at moderate temperatures, for example, at 250 C, then makes possible the cracking step(s) for ammonia and hydrocarbons.It is immaterial here for the quantitative cracking of ammonia whether or not it is cracked on the palladium membrane or the membrane made of palladium-silver alloy or at the Ni-catalyst.
Referring now to the drawings, there is shown in Fig. 1, a conduit 21 which is channeled into the fuel exhaust gas cycle. Arranged in the conduit of the flow direction of the exhaust gas, there is a buffer vessel 1 which is used to remove flow fluctuations and provide a constant feed pressure. On leaving buffer vessel 1, the exhaust gas enters a packed catalyst bed 2 containing a catalyst, for example, hopcalite, where CO contained in the exhaust gas is selectively oxidized to CO2 at about 200 to about 25 C. The exhaust gas then enters a heatable metal bed 3, which contains an O2 getter metal, for example, uranium metal or titanium metal, which is heated to a temperature of about 200 to about 4000C and which selectively removes oxygen from 02 and Q2 from the exhaust gas by chemical reaction. The exhaust gas leaving metal bed 3 then is conducted to a container 5 which contains one or more membranes 4 made of palladium or a palladium-silver alloy for cracking ammonia into N2 and hydrogen isotopes. Membranes 4 are hydrogen-isotope permeable. Container 5 is provided with a product discharge valve 22 for the hydrogen isotopes which are formed and which penetrate through the walls of membrane 4.The remaining exhaust gas, now liberated from ammonia, is passed to a heatable metal bed 10 which contains nickel catalyst 6 and which is heated to a temperature of about 250 to about 450 C, for the purpose of cracking the hydrocarbons, particularly methane. The cracked gas which leaves bed 10 can be discharged directly into the surrounding air or can be run through the cycle again until it reaches the required purity. One or more pumps 23 are provided in conduit 21 to pump the exhaust gas through the conduit.
Heatable bed 10 is provided with an inflow line 7 for conducting a regenerating agent 9, e.g., 02, into the bed to regenerate nickel catalyst 6, and an outflow line 8 for conducting out of the bed any gaseous products which have formed during the regeneration.
The examples of the apparatus shown in Figs. 1 and 2 are essentially differentiated only by the fact that the combination of (a) the externally-cooled container 5, which holds the membranes 4 which are heated to 450 C, and (b) the bed 10, which is externally-cooled and heated inside to 450 C, in Fig. 1 is replaced by one single part, namely, by the externally-cooled container 11 which, in the example in Fig. 2, is provided with a vessel in the form of a membrane pipe 14, heated to about 400 C, which is mounted in container 11. Membrane pipe
14 preferably is made of palladium or a palladium-silver alloy, preferably is the form of a spirally turned pipe, (shown in Fig. 2 as a section drawing) and contains a nickel catalyst 13 mounted on a ceramic support.
Membrane 14 is provided with an input conduit 15 for the exhaust gas which is to be decontaminated and a discharge conduit 16 for removing the decontaminated exhaust gas. The hydrogen isotopes formed within membrane pipe 14 penetrate through the walls of the membrane and leave through a gas discharge outlet 12 provided in container 11. A heater 18 for heating membrane pipe 14 is positioned in container 11 between membrane pipe 14 and the inner walls 17 of container 11. A cooling jacket 19 surrounds the outside walls of container 11.
The regeneration of the Ni-catalyst 13 charged with carbon takes place through the input of the regeneration agent, for example, through the input of hydrogen 25, by way of gas discharge outlet 12 and membrane pipe 14. First, valves 24 in conduit 21 are closed and valve 27 opened. Then, the hydrogen is passed through gas discharge outlet 12 and penetrates the walls of membrane pipe 14 so that it reaches the nickel catalyst which is inside the membrane pipe.
At about the same operational temperature, about 450 C, the carbon reacts with the Q2 according to equation (2). The resulting methane, mixture 28 is drawn off from membrane pipe 14 through a regeneration agent outlet 26 of conduit 21.
The process according to the present invention was examined for its effectiveness in a testing set-up mode which is represented in Fig. 3. As a replacement here for a real exhaust gas from a fusion reactor fuel cycle, a process gas which was to be treated was simulated by using a gas mixture made up of helium, with up to 15 Mol% ammonia and/or methane, with or without the addition of small amounts of other relevant gases.
In the testing procedure, these gas mixtures were fabricated by inputting the gas helium through input valve 31, ammonia through input valve 32, methane through input valve 33 and other gases through input valve 30. The gas mixtures were conducted through a nickel catalyst bed 36 at a high rate of flow, that is, at a high flow speed, namely at 150 1/h. The nickel catalyst in a quartz pipe, is heated to the desired temperature from the outside with a foldable pipe furnace (not shown in the drawing, indicated rather by heater 37). The pipe furnace is attached onto a fully electronic regulator (not shown in the drawing).
The gas mixture was thereafter conducted through a Pd/Ag membrane 41 which was operated with the aid of a heater 38 at a temperature of s450 C, and the hydrogen formed from the catalytic cracking of methane and ammonia continually separated out through outlet 42. The catalyst vessel 36 as well as the Pd/Ag membrane 41 can each be passed by with a bypass 39 and/or 40.
The composition of the resulting gas was then analyzed with the aid of a gas chromatograph 43, to which is attached a recording integrator 44 using "Porapak Q", "Porapak R" or molecular sieve 5A-columns. In addition to this, a tetrapole mass spectrometer 46 is attached directly to the cycle 52 by way of a gas input system 45. With the gas input system 45, a gas admixture at high pressure (e.g. atmospheric pressure), without changing the percentage composition, can be supplied to the mass spectrometer operated under high vacuum. In order to avoid condensation effects, the gas input system was heated (not shown in the drawing).
A computational device 48, attached by way of a coupling piece 47 to the tetrapole mass spectrometer 46, was employed in the processing and analysis of data. Due to the high sensitivity of mass spectrometry, it is only necessary to take very small numbers of samples for each analysis. Thus, over a period of some hours, samples can practically be taken continuously from the cycle without inducing a fall in pressure in the process. For the tests, a very high flow rate was chosen. Thereby, the conversion per flow-through proved small and the interpretation of the measurement results was able to be, according to the principle of a Batch reactor, easily undertaken. The testing mode also included several pressure regulators 34, manometers 35, an expansion container 49, a flow meter 50 and several pumps 51, as well as valves.
The following examples are given by way of illustration to further explain the principles of the invention. These examples are merely illustrative and are not to be understood as limiting the scope and underlying principles of the invention in any way. All percentages referred to herein are by weight unless otherwise indicated.
Example 1:
Catalytic Cracking of Methane into its Elements.
In the testing procedure described above, a gas admixture of helium and 14.5 Mol % methane was pumped through in the cycle at 450"C over a nickel catalyst on a ceramic support having the commercial designation BASF type G1-22. The cycle volume amounted to 6 liters, the catalyst volume 5 ml.
First Part of the Experiment:
The temperature of the container with the palladium membrane was held at 25 C. The proof of the cracking of methane, in helium as carrier gas, was obtained by mass spectrometrical analysis of the methane and hydrogen content. The result is shown in Fig. 4 in the left-hand side of the curve (up to four hours). At the start of the experiment a cracking of the methane was indicated which nevertheless stagnated after about two hours. An XPS analysis (XPS=photoelectron spectroscopy) of the surface of the catalyst has shown that the carbon produced is in elemental form, and not in carbide form.
Second Part of the Experiment:
However, if the palladium membrane is heated to 400 C, then hydrogen formed by the methane cracking reaction is continuously being extracted from the system. Conditioned on this situation, there takes place a shifting of the chemical balance in the direction of product hydrogen, which has as a consequence that the conversion becomes quantitative (see Fig. 4, right-hand portion of the curve between four and six hours).
Third Part of the Experiment:
The regeneration of the nickel catalyst was achieved by conveying light hydrogen in helium as carrier gas in a temperature range between 2500 to 450 C. The elemental carbon deposited in the nickel catalyst was converted into methane by means of the addition of the hydrogen, and eliminated from the experimental procedure.
Example 2:
Catalytic Cracking of Ammonia into its Elements:
A gas admixture of helium and about 15 Mol % ammonia was run through the testing procedure at a flow rate of 18 I/h. The ammonia here was cracked in the container with the
Pd/Ag membrane (surface 1.2 m2) at 400 C. The mass spectrometrically-measured cracking speed, dependent upon four initial concentration of ammonia, is shown by Fig. 5. The partial pressure of ammonia for the initial concentration worked out at the following: o 87.10 mbar 35.48 mbar
A 14. 14 mbar ~ 9.33 mbar
The reaction speed constants taken from the ammonia cracking worked out to 4x 10 13 molecules per cm2 and second. The conversion is quantitative.
Comparative Example for a Helium-Methane Admixture:
In by-passing the nickel catalyst, an admixture of helium and about 15 Mol % methane was pumped in the cycle over the palladium membrane at a flow speed of 18 1/h for a period of four hours. The temperature of the palladium membrane mounted to 400 C. In terms of mass spectrometry no reduction in the methane content could be detected. This means that at the palladium membrane, ammonia exclusively is being cracked, but not methane. In contrast to this, however, on the nickel catalyst not only methane is cracked but ammonia as well.
It will be understood that the above description of the present invention is susceptible to various modifications, changes and adaptations, and the same are intended to be comprehended within the meaning and range of equivalents of the appended claims.
Claims (20)
1. Process for decontaminating exhaust gas from a fusion reactor fuel cycle of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, in which the at least one heavy hydrogen isotope is liberated from its compound, separated out from the exhaust gas and fed back into the fuel cycle, the compound form being at least one compound which is ammonia or a hydrocarbon, comprising::
a) converting the at least one heavy hydrogen-containing compound into its elements in the exhaust gas by cracking the at least one heavy hydrogen containing compound with a cracking medium to liberate the hydrogen isotope,
b) passing the liberated hydrogen isotope through a membrane to separate out the liberated
hydrogen isotope from the flow of the remaining exhaust gas, and
c) discharging the remaining decontaminated exhaust gas into the surrounding air.
2. Process according to Claim 1, wherein the heavy hydrogen containing compound is ammo
nia, and a membrane made of palladium or palladium-silver alloy or an Ni-catalyst is used as a
medium for cracking the ammonia.
3. Process according to claim 1, wherein the heavy hydrogen containing compound is a hydrocarbon, and an Ni-catalyst is used for cracking the hydrocarbon.
4. Process according to claim 1, wherein the heavy hydrogen containing compound is ammonia and hydrocarbon, and a membrane made of palladium or palladium-silver alloy or an Nicatalyst is used as a medium for cracking the hydrocarbon, and an Ni-catalyzer is used for cracking the hydrocarbon.
5. Process according to Claim 4, wherein the cracking reactions of the ammonia and hydrocarbon occur in successive steps.
6. Process according to Claim 4, wherein the cracking reactions of the ammonia and hydrocarbon occur in a common process step.
7. Process according to Claim 1, comprising, before cracking the heavy hydrogen containing compound: selectively oxidizing the exhaust gas at an oxidation catalyst to oxidize CO into CO2, then bringing the exhaust gas into contact with an O3 getter metal at a temperature of 2000 to 4000C to reduce water and remove 02.
8. Process according to Claim 1, wherein the exhaust gas contains ammonia and hydrocarbon and the membrane is made of palladium or a palladium-silver alloy which surrounds the catalyst, and further comprising carrying out the cracking reactions of ammonia and hydrocarbon at an Nicatalyst on a ceramic catalyst support at a temperature of between 2500C and 450 C, and heating the catalyst within the membrane simultaneously with the membrane to the reaction temperature.
9. Process according to Claim 8, comprising, before cracking the heavy hydrogen containing compounds: selectively oxidizing the exhaust gas at an oxidation catalyst to oxidize CO into CO2, then bringing the exhaust gas into contact with an O2 getter metal at a temperature of 2000 to 4000C to reduce water and remove 02.
10. Process according to Claim 1, wherein the exhaust gas contains ammonia and hydrocarbon, and the cracking of the ammonia and hydrocarbon is performed by contacting the exhaust gas with a hydrogen-isotope-permeable membrane and with an Ni-catalyst at temperatures of from 3000 to 450 C.
11. Process according to Claim 10, comprising, before cracking the heavy hydrogen containing compounds: selectively oxidizing the exhaust gas at an oxidation catalyst to oxidize CO into
CO2, then bringing the exhaust gas into contact with an O3 getter metal at a temperature of 2000 to 4000C to reduce water and remove 02.
12. Process according to claim 1, wherein the exhaust gas contains ammonia and hydrocarbon, and wherein the cracking is performed by first contacting the exhaust gas with a hydrogenisotope-permeable membrane at a temperature of 300 to 450 C to crack the ammonia, and then contacting the exhaust gas with an Ni-catalyst at a temperature of 300 to 450 C.
13. Process according to Claim 12, comprising, before cracking the heavy hydrogen containing compounds: selectively oxidizing the exhaust gas at an oxidation catalyst to oxidize CO into
CO2, then bringing the exhaust gas into contact with an O2 getter metal at a temperature of 2000 to 4000C to reduce water and remove 02.
14. Apparatus for decontaminating exhaust gas from a fusion reactor fuel of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, in which the at least one heavy hydrngen#isotope is liberated from its compound, separated out from the exhaust gas and fed back into the fuel cycle, comprising
an exhaust gas conduit channeled into the cycle, and arranged in succession in the conduit in the flow direction of the exhaust gas::
(a) a buffer vessel for equalizing gas pressure,
(b) a catalyst bed for selectively oxidizing CO into CO2,
(c) a heatable metal bed for removing O2 and Q2 from the exhaust gas by means of chemical reaction,
(d) a container holding at least one heatable membrane which is selectively permeable to hydrogen isotopes, and having a product discharge valve for the hydrogen isotopes, and
(e) a heatable bed containing a regenerable Ni-catalyst, the bed having an inflow and an outflow for a regeneration agent.
15. Apparatus according to claim 14, wherein at least one pump is connected to the conduit.
16. Apparatus for decontaminating exhaust gas from a fusion reactor fuel of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, in which the at least one heavy hydrogen isotope is liberated from its compound, separated out from the exhaust gas and fed back into the fuel cycle, comprising
an exhaust gas conduit channeled into the cycle, and arranged in succession in the conduit in the flow direction of the exhaust gas: :
(a) a buffer vessel for equalizing gas pressure,
(b) a catalyst bed for selectively oxidizing CO into CO2,
(c) a heatable metal bed for removing O3 and 020 from the exhaust gas by means of chemical reaction, and
(d) an externally coolable container, which is cooled on its exterior to a temperature of c200 C, the container having::
(i) a vessel mounted in the container and made of palladium or of a palladium-silver alloy, the vessel containing a Ni-catalyst, the vessel having a supply feed conduit for feeding the exhaust gas which is to be decontaminated into the vessel, and a discharge conduit for removing decontaminated exhaust gas from the vessel,
(ii) a gas discharge outlet for removing the hydrogen isotope separated off from the exhaust gas, and
(iii) a heater for the vessel positioned between the vessel and the inner wall of the container.
17. Apparatus according to Claim 16, wherein the vessel is designed as a spiral-shaped pipe.
18. Apparatus according to claim 17, wherein at least one pump is connected to the conduit.
19. A process for decontaminating exhaust gas as claimed in any one of claims 1 to 13, substantially as hereinbefore described and illustrated.
20. Apparatus for decontaminating exhaust gas from a fusion reactor fuel of exhaust gas components containing at least one heavy hydrogen isotope selected from tritium and deuterium in compound form, substantially as hereinbefore described with reference to the accompanying drawings.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19863606317 DE3606317A1 (en) | 1986-02-27 | 1986-02-27 | METHOD AND DEVICE FOR DECONTAMINATING THE EXHAUST GAS FROM THE FUEL CYCLE OF A FUSION REACTOR OF TRITIUM AND / OR DEUTERIUM IN CHEMICALLY BONDED EXHAUST GAS COMPONENTS |
Publications (3)
Publication Number | Publication Date |
---|---|
GB8704687D0 GB8704687D0 (en) | 1987-04-01 |
GB2187973A true GB2187973A (en) | 1987-09-23 |
GB2187973B GB2187973B (en) | 1989-11-29 |
Family
ID=6295038
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
GB8704687A Expired GB2187973B (en) | 1986-02-27 | 1987-02-27 | Decontaminating exhaust gas from a fusion reactor fuel cycle of exhaust gas components containing chemically bonded tritium and/or deuterium |
Country Status (4)
Country | Link |
---|---|
JP (1) | JPH0833490B2 (en) |
DE (1) | DE3606317A1 (en) |
FR (1) | FR2601181B1 (en) |
GB (1) | GB2187973B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9023132B2 (en) | 2012-01-10 | 2015-05-05 | Alstom Technology Ltd | Method for filtration of harmful gas effluents from a nuclear power plant |
US9126141B2 (en) | 2012-01-10 | 2015-09-08 | Alstom Technology Ltd | Method for filtration of gas effluents from an industrial installation |
US9295941B2 (en) | 2012-01-10 | 2016-03-29 | Alstom Technology Ltd | Method for filtration of gas effluents from an industrial installation |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3731385A1 (en) * | 1987-09-18 | 1989-04-06 | Kernforschungsz Karlsruhe | METHOD FOR DECONTAMINATING THE EXHAUST GAS FROM A FUSION REACTOR |
US5154878A (en) * | 1990-04-30 | 1992-10-13 | Anthony Busigin | Process and apparatus for tritium recovery |
IT1401192B1 (en) * | 2010-06-16 | 2013-07-12 | Enea Agenzia Naz Per Le Nuove Tecnologie L En E Lo Sviluppo Economico Sostenibile | MEMBRANE REACTOR FOR THE TREATMENT OF GAS CONTAINING TRIZIO |
IT1400531B1 (en) * | 2010-06-22 | 2013-06-11 | Commissariat Energie Atomique | PROCESS FOR THE DETRIFICATION OF SOFT HOUSEKEEPING WASTE AND RELATIVE PLANT |
FR2984003B1 (en) | 2011-12-12 | 2014-01-10 | Commissariat Energie Atomique | METHOD AND DEVICE FOR REDUCING THE DEGASSING OF TRIUCED WASTE FROM THE NUCLEAR INDUSTRY |
DE102013109778A1 (en) | 2013-09-06 | 2015-03-12 | Karlsruher Institut für Technologie | Process and apparatus for the continuous recycling of waste gas from a fusion reactor |
CN115285940A (en) * | 2022-08-23 | 2022-11-04 | 中国原子能科学研究院 | Method and system for recovering hydrogen isotopes in process waste gas |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE1238884B (en) * | 1964-01-25 | 1967-04-20 | J F Mahler App Und Ofenbau K G | Process for the production of pure hydrogen |
FR1470361A (en) * | 1965-12-30 | 1967-02-24 | Commissariat Energie Atomique | Carbon dioxide purification process |
FR2061573B1 (en) * | 1969-07-25 | 1974-02-01 | Commissariat Energie Atomique | |
US3926782A (en) * | 1973-02-09 | 1975-12-16 | Mobil Oil Corp | Hydrocarbon conversion |
DE3025494C2 (en) * | 1980-07-04 | 1986-01-16 | Max-Planck-Gesellschaft zur Förderung der Wissenschaften e.V., 3400 Göttingen | Process for removing tritium from a gas mixture |
DE3121125C2 (en) * | 1981-05-27 | 1986-04-10 | Kernforschungsanlage Jülich GmbH, 5170 Jülich | Method for separating hydrogen and / or deuterium and tritium from an inert gas stream and device for carrying out the method in the cooling gas circuit of a gas-cooled nuclear reactor |
US4430293A (en) * | 1981-09-10 | 1984-02-07 | Combustion Engineering, Inc. | Containment hydrogen removal system for a nuclear power plant |
-
1986
- 1986-02-27 DE DE19863606317 patent/DE3606317A1/en active Granted
-
1987
- 1987-02-27 FR FR8702682A patent/FR2601181B1/en not_active Expired - Fee Related
- 1987-02-27 JP JP62043256A patent/JPH0833490B2/en not_active Expired - Fee Related
- 1987-02-27 GB GB8704687A patent/GB2187973B/en not_active Expired
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US9023132B2 (en) | 2012-01-10 | 2015-05-05 | Alstom Technology Ltd | Method for filtration of harmful gas effluents from a nuclear power plant |
US9126141B2 (en) | 2012-01-10 | 2015-09-08 | Alstom Technology Ltd | Method for filtration of gas effluents from an industrial installation |
US9295941B2 (en) | 2012-01-10 | 2016-03-29 | Alstom Technology Ltd | Method for filtration of gas effluents from an industrial installation |
Also Published As
Publication number | Publication date |
---|---|
DE3606317A1 (en) | 1987-09-03 |
JPH0833490B2 (en) | 1996-03-29 |
GB8704687D0 (en) | 1987-04-01 |
GB2187973B (en) | 1989-11-29 |
DE3606317C2 (en) | 1991-09-26 |
FR2601181A1 (en) | 1988-01-08 |
JPS62255894A (en) | 1987-11-07 |
FR2601181B1 (en) | 1992-12-31 |
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PCNP | Patent ceased through non-payment of renewal fee |
Effective date: 19940227 |