METHOD OF TREATING RADIOACTIVE ION-EXCHANGE RESINS BY OXIDATIVE DECOMPOSITION

Abstract: A method of oxidatively decomposing a radioactive ion-exchange resin is described, the method comprising oxidatively decomposing a radioactive ion-exchange resin containing an an ion-exchange resin with hydrogen peroxide used as an oxidizing agent in the presence of iron and copper ions used as catalysts, wherein the weight ratio of hydrogen peroxide to the ion-exchange resin, that is the ratio of the net weight of hydrogen peroxide to the dry weight of the ion-exchange resin containing an anion-­ exchange resin, is held to be not higher thant 17 and citric acid ions are preliminarily adsorbed on the radioactive ion-exchange resin before it is subjected to decomposition treatment or citric acid ions coexist with the radioactive ion-exchange resin in the oxidatively decomposing system, and an apparatus used for conducting the method is also described.

Description: The present invention relates to a method of chemical decomposition by which the volumes of spent radioactive ion-exchange resins (hereinafter sometimes referred to as waste resins) originating from atomic energy facilities can be reduced. Ion-exchange resins are extensively used in many applications such as purification of water, treatment of wastewaters, and separation of various elements. They are also used in large quantities in the field of atomic energy for the purpose of purifying cooling water in nuclear reactors and treating liquid wastes. Therefore, treatment and disposal of spent waste ion-exchange resins containing radioactive substances has been a serious concern in this field. The method in common use in the technology of disposal of radioactive waste ion-exchange resins is to dehydrate the resins, solidify them by incorporation in cements, plastics, etc., place the solidified wastes in containers, and store them for a prescribed number of years, often almost perpetually. However, the waste resins treated by this method are not reduced significantly in volume and have posed substantial problems in the area of waste storage and management. As described above, no really satisfactory method for treating or finally disposing of the variety of solid wastes that result from the operation of nuclear power plants has yet been established. One of the serious problems that remain to be solved is how to reduce the volume of ion-exchange resins that are discarded after they have been used in the purification of liquid media. Several methods, including combustion (incineration), pyrolysis, and acid decomposition have so far been proposed as techniques for reducing the volumes of waste ion-exchange resins, but none of these have proved to be a complete solution to the problem. The combustion method has the advantage of achieving rapid treatment but, at the same time, it requires complicated off-gas lines for handling dust and tars, and/or produces volatile radioactive compounds. The last-mentioned problem is absent from the pyrolysis method, but, on the other hand, it yields high residual contents of carbonaceous materials, and still requires complicated flow systems as in the case of the incineration method. In the acid decomposition method, up to about 90% of the spent ion-exchange resins can be decomposed by successive treatments with concentrated sulfuric acid and nitric acid at a temperature of about 260°C. Although this method is free from any of the problems associated with the first two methods, it has the disadvantage of generating NOx and SOx. Furthermore, the reaction vessel must be made of an expensive material such as tantalum that is capable of withstanding the extremely high temperatures employed. As a further problem, the volume of the waste resins being treated cannot be reduced to the desired extent, since large quantities of salts form during neutralization of the reaction solution. In order to avoid this problem, a method of decomposing waste resins at about 100°C using hydrogen peroxide and an iron catalyst has been described in Japanese Patent Application (OPI) No. 1446/82 (the term "OPI" as used herein means an "unexamined published Japanese patent application"). This method readily achieves up to 95% decomposition if the waste resin is a cation-exchange resin, but the decomposition of an anion-exchange resin is no higher than 90%. To overcome this disadvantage, it has been proposed that a combination of iron and copper ions could be used as a catalyst when the waste resin is decomposed by oxidation with hydrogen peroxide (Japanese Patent Application (OPI) No. 44700/84). This approach achieves at least 95% decomposition of anion-exchange resins, but if the amount of feed (i.e., anion-exchange resin) is increased, organic sludge containing iron and copper ions will form. Furthermore, the decomposition of waste resins by this method has been found to be highly dependent on the pH of the reaction solution, notwithstanding the previously held view that good decomposition is achieved within the pH range of 3 to 11, with particularly good results being attained in the neighborhood of neutrality. If the organic sludge is formed in a large quantity, it will be accumulated in the reaction vessel (reactor) or pipes to form "secondary" wastes which require another treatment, and may even cause a problem with transportation. Other problems exist in the method of decomposing waste resins with hydrogen peroxide using iron and copper ions as catalysts. First of all, the reaction rate is very slow (at least one to two hours is necessary to convert the waste resin to inorganic matter), and a reactor of large capacity is required. Secondly and because of this slow reaction rate, decomposition must be performed under fairly H₂O₂-rich conditions. Since the running cost of this method is essentially determined by the amount of hydrogen peroxide used, it is important both technically and economically to achieve decomposition with the least possible amount of hydrogen peroxide used. From GB-A-1 574 795 a process for conditioning radioactively contaminated ion-exchange materials, particularly contaminated cationic resins or mixtures of cationic and anionic resins, is known wherein the resin is brought into contact with a base compound in a sufficient quantity to block the active site of the material, the thus treated ion-exchange material is incorporated into an ambient temperature-thermosetting resin and, finally, the latter is cross-linked. The prior art technology also has another problem that has to be solved before it can be employed in practical applications, viz., leakage of radioactivity from mechanical seals in the agitating and mixing apparatus used for achieving accelerated decomposition reaction. An object, therefore, of the present invention is to provide a method by which a radioactive ion-exchange resin, and in particular, a radioactive anion-exchange resin, can be decomposed with hydrogen peroxide used as an oxidizing agent in the presence of iron and copper ions used as catalysts with high percent decomposition being achieved in a short period of treatment with low consumption of hydrogen peroxide and the production of organic sludge being held to minimum levels. Another object of the present invention is to provide an apparatus that can be used to implement the aforementioned method of decomposing a radioactive ion-exchange resin. The first object of the present invention can be attained by a method of oxidatively decomposing a radioactive ion-exchange resin containing an anion-exchange resin with hydrogen peroxide used as an oxidizing agent in the presence of iron and copper ions used as catalysts, wherein the ratio of the net weight of hydrogen peroxide to the dry weight of the ion-exchange resin containing an anion-exchange resin is held to be not higher than 17 and citric acid ions are preliminarily adsorbed on the radioactive ion-exchange resin before it is subjected to decomposition treatment or citric acid ions co-exist with the radioactive ion-exchange resin in the oxidatively decomposing system. According to the present invention the consumption of hydrogen peroxide is reduced and yet a satisfactorily high efficiency of resin decomposition can be attained within a reaction time that is no longer than half of the heretofore required period. According to the present invention the radioactive ion-exchange resin can be crushed into fine particles when or before it is mixed with the oxidizing agent and the catalysts BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is a schematic drawing of a continuous reactor that may be employed in oxidatively decomposing a waste ion-exchange resin by a method in accordance with one embodiment of the present invention; Fig. 2 is a graph showing the relationship between the H₂O₂/resin ratio, sludge weight, and percent resin decomposition; Fig. 3 shows the concept of the process of decomposition of an anion-exchange resin; Fig. 4 is a diagram indicating the mechanisms by which waste ion-exchange resins are decomposed oxidatively; Fig. 5 is a graph showing the effect of citric acid ions on the dissolution of solid matter as related to the solids content; Fig. 6 is a graph showing the relationship of the percent decomposition of OH⁻-H⁺ type mixed resin and citric acid -H⁺ type mixed resin vs the period of treatment of each of the resins; Fig. 7 is a flowsheet of a process for oxidatively decomposing a waste ion-exchange resin according to another embodiment of the present invention; Fig. 8 shows the operating principle of an electromagnetic crusher that is employed in the crushing step of the process shown in Fig. 7; Fig. 9 shows the particle size distribution of a granular ion-exchange resin that was crushed into finer particles by the device shown in Fig. 8; The concentration of the aqueous solution of hydrogen peroxide to be added to the reaction system of oxidative decomposition is not limited to any particular value and conventional 30% or 60% hydrogen peroxide may satisfactorily be used. The method of the present invention is carried out with the ratio of H₂O₂ (on a net weight basis) to the ion-exchange resin feed (dry weight basis) being adjusted to no higher than 17 (i.e., 17/1; hereinafter, the various ratios to which reference is made are expressed as single numbers). The method of the present invention may be carried out within the range of 17 to 3, preferably 17 to 4, more preferably 10 to 4 in H₂O₂/resin ratio. Under H₂O₂-rich conditions, for example, H₂O₂/resin ratio is higher than 20, the method of the present invention need not be used and an appropriate combination of iron and copper catalysts can achieve efficient decomposition of the waste ion-exchange resin while forming a reduced amount of organic sludge. Oxidative reaction should be carried out with the waste ion-exchange resin being dispersed or suspended in water. The volume of the reaction solution is desirably within the range of from about 10 ml to about 30 ml per g of dry resin. The iron and copper ions functioning as catalysts are preferably derived from water-soluble salts such as sulfates, nitrates and chlorides, such as FeSO₄, FeSO₄·7H₂O, Fe(SO₄)(NH₄)₂SO₄·6H₂O, Fe(NH₄)(SO₄)₂·12H₂O, CuSO₄ or CUSO₄·5H₂O. The concentration of iron catalyst used in the reaction system of oxidative decomposition is preferably within the range of from 0.0005 to 0.02 M, and more preferably from 0.002 to 0.15 M. The concentration of copper catalyst is preferably within the range of from 0.002 to 0.15 M, and more preferably from 0.005 to 0.1 M. If these conditions are used, better results are attained in terms of sludge formation and decomposition efficiency. In one embodiment, the H₂O₂/resin ratio is selected to have a value of no higher than 17, and decomposition of a radioactive ion-exchange resin with H₂O₂ in the presence of copper and iron catalysts is effected after the resin is subjected to ion-exchange for citric acid ions in the form of either citric acid or a salt thereof, e.g., sodium citrate. Alternatively, the oxidative decomposition of a radioactive ion-exchange resin is carried out under a pH value of no higher than 17 and in the presence of either citric acid or a salt thereof. By the coexistence of a citric acid or a salt thereof, it is meant that the radioactive ion-exchange resin adsorbs the citric acid ions in an amount of 70% or more, preferably 80% or more, and most preferably 90% or more based on a total ion-exchangeable ability of ion-exchange resin to be treated, the ion-exchangeable ability being represented by an equivalent per gram. The anion-exchange resin used in the present invention preferably includes a strong alkaline anion-exchange resin which is commercially available, for example, SNA-1 (trademark for product produced by Mitsubishi Kasei Corporation) having the following repeating units. The cation-exchange resin used together with the above described anion-exchange resin used in the present invention preferably includes a strong acidic cation-exchange resin which is commercially available, for example, SKN-1 (trademark for product produced by Mitsubishi Kasei Corporation) having the following repeating units. The method of the present invention may be implemented with a continuous or batch reactor for effecting oxidative decomposition of the resin feed. The apparatus for use in the methods of the present invention comprise a number of ferromagnetic working media, a non-magnetic vessel for holding said working media, two moving field generators placed on top and bottom of said vessel, an inlet for supplying the radioactive ion-exchange resin, an inlet for supplying the oxidizing agent, and an inlet for supplying the catalyst, said apparatus being so designed that the radioactive ion-exchange resin charged into said vessel is crushed into fine particles and mixed with the also charged oxidizing agent and catalysts by the movement of said working media that is created by the electromagnetic force produced as a result of the interaction between said working media and moving magnetic fields. Fig. 1 is a schematic drawing of a continuous reactor. A reaction vessel indicated by 1 is charged with an aqueous solution of the necessary catalysts and a waste ion-exchange resin. The charged reaction solution is stirred with a magnetic stirrer 2. The temperature of the reaction system is held constant by means of a water bath 3. A constant flow of an aqueous solution of hydrogen peroxide is fed into the reaction vessel through an inlet 4. The concentrations of the catalysts are held substantially constant by supplying a concentrated catalyst solution through an inlet 5. The catalyst concentrations may be set by any suitable method; they may be held substantially constant throughout the reaction; alternatively, the concentrations may be set in the initial period and left uncontrolled for the rest of the reaction period. Satisfactory treatments are possible if the concentrations of catalysts in the reaction solution before and after the reaction are kept within the ranges specified herein. The waste ion-exchange resin may be fed in a continuous manner. Decomposition can be accomplished if the reaction temperature is within the range of from ambient temperatures to 100°C and temperatures of at least 90°C are preferably employed in order to attain a higher percentage of decomposition. The reaction vessel is preferably equipped with a stirrer. The theoretical background for the accomplishment of the present invention is described hereinafter. Fig. 2 is a graph showing the relationship between the H₂O₂/resin ratio, sludge weight, and percent decomposition. The H₂O₂/resin ratio means the amount of hydrogen peroxide (in grams for 100% H₂O₂) consumed for decomposing one gram on a dry weight basis of the ion-exchange resin. Before the present invention, the technology of oxidative decomposition of waste ion-exchange resins has been discussed assuming H₂O₂/resin ratios of about 20 [see, for example, the working examples given in the specification of Japanese Patent Application (OPI) No. 44700/84]. If the matrix of a waste ion-exchange resin to be treated is polystyrene, a H₂O₂/resin ratio of approximately 6.5 is sufficient to achieve 100% decomposition of polystyrene and the H₂O₂ supplied is more than necessary if higher H₂O₂/resin ratios are employed. As shown in Fig. 2, sludge formation is negligible if the H₂O₂/resin ratio is about 20, but an increasing amount of sludge will form if the ratio becomes 17 or lower by reducing the amount of H₂O₂ used. As already mentioned, discussion of the prior art technology for oxidative decomposition of waste ion-exchange resins has been made on the basis of H₂O₂/resin ratios Of about 20 or more, and no attention has been paid to the formation of organic sludge. The present inventors noted the occurrence of sludge formation and unravelled the process of its formation and the factors that were involved as a result of conducting intensive studies in this aspect. The present invention has been accomplished on the basis of these findings. Fig. 3 shows the concept of the process of decomposition of an anion-exchange resin. In the process of its decomposition, an anion-exchange resin is converted to soluble organic matter and insoluble organic matter (i.e., sludge which actually is a mixture of organic matter, iron, and copper), and the soluble organic matter is eventually decomposed into water and CO₂ gas. Under H₂O₂-rich conditions (H₂O₂/resin ratio ≧ 20), the organic sludge is completely decomposed to leave no residues, but if the H₂O₂/resin ratio is 17 or below, part of the organic sludge is left as residue. As already shown, if the ion-exchange resin is assumed to be solely made of polystyrene, the hydrogen peroxide supplied is excessive even if the H₂O₂/resin ratio is 10, and yet sludge formation is inevitable. Therefore, if one wants to perform oxidative decomposition of waste resins at low H₂O₂/resin ratios, it is important to achieve efficient treatment by minimizing the occurrence of sludge formation. Anion-exchange resins are known to have the following relationship between adsorbed ionic species and the efficiency of their decomposition. SO₄ type > OH type > Cl type high → (decomposition) → low The proportions of ionic species adsorbed on two typical waste ion-exchange resins are listed in Table 1, from which one can see that Amber IRA 400C as a typical anion-exchange resin (product of Rohmand Haas) contains 80% OH⁻ and 20% Cl⁻. The above-indicated relationship suggests that the Cl⁻ content (20%) of this anion-exchange resin is detrimental to the purpose of decomposing it in an efficient manner. Therefore, one may reasonably expect that this resin could be decomposed with increased efficiency by adsorbing SO₄²⁻ and other anions on it before it is subjected to decomposition. Adsorbed ionic species in waste resins Cation-exchange resin (Amberlite IR 120L) Anion-exchange resin (Amber IRA 400C) Ion Adsorbed Amount (eq/ℓ) % Ion Adsorbed amount (eq/ℓ) % Cr³⁺ 8.0 x 10⁻² <1 Cl⁻ 280 x 10⁻³ 20 Fe²⁺ 4.6 x 10⁻² 2 OH⁻ 1120 x 10⁻³ 80 Co²⁺ 2.0 x 10⁻³ <1 Ni²⁺ 320 x 10⁻³ 17 Cu²⁺ 1.0 x 10⁻³ <1 Ag⁺ 3.0 x 10⁻³ <1 H⁺ 1520 x 10⁻³ 80 Total 100 100 The selectivity for adsorption of ions by an anion-exchange resin decreases in the following order: citric acid ion > SO₄²⁻ > I⁻ > NO₃⁻ > CrO₄²⁻ > Br⁻ > SCN⁻ > Cl⁻ > F⁻. Therefore, the SO₄²⁻ ion is more readily adsorbed than the Cl⁻ ion and the citric acid ion is more easily adsorbed than any other ionic species. A Cl⁻ form resin is less decomposable than other types of anion-exchange resins, and this is assumed to be because the Cl⁻ ion is an inhibitor of the OH radical forming reaction. The present inventors have first discovered that citric acid type anion-exchange resins can be decomposed with high efficiency, and this discovery is based on their success in unravelling the peculiar mechanism behind the oxidative decomposition of anion-exchange resins. As Fig. 4 shows, the process of decomposition of waste resins differs greatly between cation-exchange and anion-exchange resins. The cation-exchange resin which is comparatively easy to decompose undergoes a solid-liquid reaction (see Fig. 4 ) in which its structure is readily destroyed and dissolved in the reaction solution. This reaction proceeds very rapidly. In the subsequent liquid-liquid reaction, the resin is oxidatively decomposed to yield water and carbon dioxide as the final decomposition products. The behavior of the anion-exchange resin which is intended to be decomposed by the method of the present invention differs greatly from the cation-exchange resin. The major difference is that the anion-exchange resin will not be readily dissolved as a result of solid-liquid reaction. If the resin remains solid, the efficiency of its decomposition is low and this is one of the factors that render the anion-exchange resin highly refractory to the existing decomposition techniques. The mechanism by which the resin remains solid is identified in Fig. 4 under the heading "sludge formation", which is discussed hereinafter in detail. An anion-exchange resin removes radioactive ions from water in accordance with the following reaction: R-N⁺OH⁻ + Rad⁻ ⇄ R-N⁺Rad⁻ + OH⁻ wherein R represents the matrix (polystyrene) of ion-exchange resin, Rad⁻ represents radioactive ion, and N represents nitrogen. Since R-N⁺ does not have very high affinity for OH⁻, it readily dissociates from OH⁻ and combines with any other anion that is available. As shown in Table 1, most of the waste resins extracted from plants for purifying nuclear reactor cooling water are of the OH⁻ type. In the process of oxidative decomposition, the resin undergoes dissolution in the reaction solution and produces COOH. By the term "dissolution" is usually meant that the resin is disintegrated into fine particles of a size of no larger than 0.45 µm. In this case, the particles are believed to be composed of C and H, and may be expressed as P-COO⁻H⁺ (where P signifies the matrix of the fine particles). During reaction, both solid matters and soluble components exist in the solution and R-N⁺OH⁻ reacts with P-COO⁻H⁺ to form R-N⁺-COO-P which adheres to the active sites of the residual R-N⁺OH⁻ in succession until the resin undergoes re-solidifcation to form sludge. Based on this assumption, the present inventors reasoned as follows: since the product of oxidative decomposition of an anion-exchange resin is anionic, sludge formation could be prevented by inactivating the ion-exchange capacity of the resin and this may be achieved by attaching ionic species that have strong affinity for the anion-exchange resin. As already noted, the selectivity for adsorption of ions by an anion-exchange resin decreased in the order of: citric acid ion > SO₄²⁻ > I⁻ > NO₃⁻ > CrO₄²⁻ > Br⁻ > SCN⁻ > Cl⁻ > F⁻. Apparently, citric acid is more readily adsorbed than any other of the ionic species listed above. The structure of sodium citrate is expressed by and its adsorption takes places at the sites of -COO⁻. Therefore, if citric acid is preliminarily adsorbed on the anion-exchange resin to be decomposed, the intended reaction can be effected in an efficient manner without allowing any substantial amount of sludge to form. The effect of citric acid ions on the dissolution of solid matter is shown in Fig. 5. Clearly, an anion-exchange resin that was converted to the citric acid form exhibited a substantially linear relationship between the solids concentration in terms of carbon content and the rate of their dissolution. On the other hand, a non-citric acid type anion-exchange resin displayed reduced dissolution rates in the high solids-content region because of the occurrence of sludge formation. The effectiveness of the citric acid type anion-exchange resin is therefore clear. By utilizing the difference in adsorbability between SO₄²⁻ and Cl⁻ ions and its relationship to the percent decomposition of an anion-exchange resin to which these anions had been adsorbed and a mixture thereof with a cation-exchange resin, citric acid ions were adsorbed on an anion-exchange resin which was then subjected to oxidative decomposition treatment. In the experiment, two types of resins were used, one being a mixture of OH⁻ and H⁺ form resins, and the other being a mixture of citric acid and H⁺ form resins. It should also be mentioned that OH⁻ and Cl⁻ form anion-exchange resins can be readily converted to the citric acid type by adsorbing citric acid or a salt thereof through routine regeneration techniques. In performing oxidative decomposition on these resins, the H₂O₂/resin ratio and the period of treatment should be carefully determined. In consideration of the relationship between the H₂O₂ feed (g) and the ion-exchange resin to be treated, the H₂O₂/resin ratio is preferably set to a value of no higher than 10 and the treatment is preferably completed within a period of 60 min. The results of the experiment described above are shown in the following Tables 2 and 3 and in Fig. 6 . Table 2 shows the percent decomposition of the mixed resin of OH⁻ and H⁺ types for varying reaction times of 120, 60, 30 and 15 min with the feed of hydrogen peroxide (g) held constant. Table 3 shows the results for the mixed resin of citric acid and H⁺ types. Fig. 6 shows the relationship of percent decomposition vs the period of treatment of each of the mixed resins. The above results show the following: when the reaction time was 60 min which was half the period required in the prior art, both types of mixed resin could be decomposed by about 95%; when the reaction time was further reduced to 30 min , the efficiency of decomposition of the OH⁻-H⁺ form resin was markedly decreased but the mixed resin of citric acid and H⁺ types could still be decomposed by 95%. As will be understood from the foregoing explanation, the present invention provides a method by which an anion-exchange resin or a mixture thereof with a cation-exchange resin is oxidatively decomposed with hydrogen peroxide in the presence of a combined catalyst of iron and copper. According to the invention, citric acid ions are preliminarily adsorbed on the anion-exchange resin before oxidative decomposition is effected, and by so doing, the resin can be decomposed at an economical H₂O₂/resin ratio of no higher than 10 and within a reaction time of no longer than half of the heretofore required period, and yet a satisfactorily high efficiency of decomposition can be attained. The objects of the present invention can be attained by crushing a granular waste citric acid form ion-exchange resin into finer particles before it is oxidatively decomposed with hydrogen peroxide in the presence of a mixed catalyst of iron and copper ions. The crushing of the waste ion-exchange resin serves to increase its specific surface area so that its reaction with the oxidizing agent (H₂O₂) in the subsequent step of oxidative decomposition can be carried out with an increased efficiency. As a result, the consumption of hydrogen peroxide can be decreased to a H₂O₂/resin ratio of 17 or below, or even to 10 or below, and yet a high efficiency of decomposition can be attained within a shorter period of reaction time. In the crushing step, the waste citric acid form ion-exchange resin is crushed into fine particles having an average diameter of preferably, 400 µm or less, more preferably 200 µm or less, and most preferably from 100 µm to 5 µm. Fig. 7 is a flowsheet of this method of the present invention for oxidatively decomposing a waste ion-exchange resin. A granular waste resin is first fed into the crushing stage at which it is crushed into finer particles, which are then introduced into subsequent stage of oxidative decomposition, in which the crushed resin is subjected to oxidative decomposition with hydrogen peroxide in the presence of a mixed catalyst of iron and copper ions. An electromagnetic crusher is advantageously used as a means for crushing the ion-exchange resin. As shown schematicaliy in Fig. 8, this crusher has the following three components: a vessel 8 that is made of a corrosion-resistant non-magnetic material and which contains a number of spindle-shaped working media 7 that are formed of a ferromagnetic material; and two moving field generators 9 and 10 placed on top and bottom of the vessel 8. Moving field generators are well known as linear motors and each consists of an iron core equipped with a multi-phase AC winding that is disposed along the magnetic poles of the core. When current is supplied to the multi-phase AC windings, moving magnetic fields are induced in opposite directions as indicated by arrows ₁ and ₂. An electromagnetic force is then produced in the vessel 8 by the interaction between the working media 7 and the moving fields and as a result, the working media 7 in the vessel 8 are lifted and start to revolve about their center of gravity while moving around in the vessel 8 in either direction of the movement of the magnetic fields. When a granular waste ion-exchange resin is supplied into the vessel 8 at this stage, the resin is brought into violent contact with the working media 7 and is crushed into finer particles indicated by numeral 11a in Fig. 8. The power of the electromagnetic crushing method described above is very strong and the present inventors confirmed by experiment that this method was capable of crushing a granular ion-exchange resin into finer particles by a treatment of only few minutes. The results of the experiment are shown in Fig. 9. In the experiment, Diaion of Mitsubishi Chemical Industries, Limited was used as the resin sample to be treated; it consisted of particles ranging in size from 420 to 1,190 µm and was based on a polystyrene matrix. By performing the electromagnetic crushing method on this resin, it could be crushed into particles of a size of no larger than 200 µm (average size, 30 to 50 µm) within a few minutes. An apparatus of the type shown in Fig. 1 is employed in the oxidative decomposition stage of the process shown in Fig. 7. Crushing a granular ion-exchange resin into finer particles before it is decomposed oxidatively with the particles suspended in the reaction solution in the reaction vessel offers the following advantages: the specific surface area of the resin is appreciably increased and the chance of its contact with chemicals is sufficiently increased to permit efficient progress of subsequent oxidative decomposition. As a consequence, the H₂O₂/resin ratio, which is a measure of H₂O₂ consumption, and the decomposition period are significantly reduced. The foregoing description is directed to the use of the present invention for the purpose of decomposing radioactive ion-exchange resins originating from atomic energy facilities but it should of course be understood that the concept of the present invention can equally be applied to the decomposition of spent waste ion-exchange resins occurring in other industrial fields.

Claims: A method of oxidatively decomposing a radioactive ion-exchange resin containing an anion-exchange resin with hydrogen peroxide used as an oxidizing agent in the presence of iron and copper ions used as catalysts, wherein the ratio of the net weight of hydrogen peroxide to the dry weight of the ion-exchange resin containing an anion-exchange resin is held to be not higher than 17 and citric acid ions are preliminarily adsorbed on the radioactive ion-exchange resin before it is subjected to decomposition treatment or citric acid ions co-exist with the radioactive ion-exchange resin in the oxidatively decomposing system. A method according to Claim 1, wherein the concentration of iron ions is within the range of from 0.0005 mol/l to 0.02 mol/l. A method according to Claim 1, wherein the concentration of iron ions is within the range of from 0.0005 mol/l to 0.02 mol/l and that of copper ions is within the range of from 0.002 mol/l to 0.15 mol/l. A method according to Claim 1, wherein the pH of the reaction system is adjusted to be within the range of from 1 to 5. A method according to Claim 1, wherein the radioactive ion-exchange resin is crushed into fine particles before the addition of the oxidizing agent and the catalysts. A method according to Claim 1, wherein the radioactive ion-exchange resin is crushed into fine particles as it is mixed with the oxidizing agent and the catalysts. An apparatus for use in the methods of Claims 1 to 6 comprising a number of ferromagnetic working media, a non-magnetic vessel for holding said working media, two moving field generators placed on top and bottom of said vessel, an inlet for supplying the radioactive ion-exchange resin, an inlet for supplying the oxidizing agent, and an inlet for supplying the catalyst, said apparatus being so designed that the radioactive ion-exchange resin charged into said vessel is crushed into fine particles and mixed with the also charged oxidizing agent and catalysts by the movement of said working media that is created by the electromagnetic force produced as a result of the interaction between said working media and moving magnetic fields.

Inventors: HOSHIKAWA, HIROSHI FUJI ELECTRIC CO., LTD., ISHIKAWA, TUYOSHI FUJI ELECTRIC CO., LTD., MORIOKA, TAKAYUKI FUJI ELECTRIC CO., LTD., MOTOYAMA, NOBUYUKI FUJI ELECTRIC CO., LTD., SUZUKI, SIZUO FUJI ELECTRIC CO., LTD., TAKAHASHI, TAKEO FUJI ELECTRIC CO., LTD., UEDE, TOSHIO FUJI ELECTRIC CO., LTD.
Applicants: FUJI ELECTRIC CO., LTD.
Application year: 1987
Main classification: G21F9
IPC codes: G21F9