JPH0723917B2 - Treatment method of recovered nitric acid from nuclear fuel reprocessing step - Google Patents
Treatment method of recovered nitric acid from nuclear fuel reprocessing stepInfo
- Publication number
- JPH0723917B2 JPH0723917B2 JP7533291A JP7533291A JPH0723917B2 JP H0723917 B2 JPH0723917 B2 JP H0723917B2 JP 7533291 A JP7533291 A JP 7533291A JP 7533291 A JP7533291 A JP 7533291A JP H0723917 B2 JPH0723917 B2 JP H0723917B2
- Authority
- JP
- Japan
- Prior art keywords
- nitric acid
- electrolytic cell
- nuclear fuel
- reprocessing step
- electrolysis
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
- Y02E30/30—Nuclear fission reactors
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
Landscapes
- Water Treatment By Electricity Or Magnetism (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、核燃料再処理工程から
の回収硝酸の処理方法の改良に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an improved method for treating recovered nitric acid from a nuclear fuel reprocessing step.
【0002】[0002]
【従来の技術】使用ずみ核燃料を再処理する代表的なプ
ロセスでは、前処理工程におけるヨウ素の追い出しと、
プルトニウム精製工程におけるPu酸化のためにNOx
を使用し、廃液の形で硝酸が回収される。2. Description of the Related Art A typical process for reprocessing spent nuclear fuel is to remove iodine in a pretreatment step,
NO x for Pu oxidation in plutonium purification process
Is used to recover nitric acid in the form of waste liquid.
【0003】この回収硝酸は、低レベルではあるが放射
性物質を含有しているため、たとえばカセイソーダで中
和して硝酸ナトリウムに変え、蒸発濃縮をして、最終的
には固化体として貯蔵している。 このような処理方法
は、低レベルの放射能をもった固体廃棄物を大量に発生
させるので、改善が望まれていた。Since the recovered nitric acid contains radioactive substances at a low level, it is neutralized with caustic soda, converted into sodium nitrate, evaporated and concentrated, and finally stored as a solidified product. There is. Since such a treatment method generates a large amount of solid waste having a low level of radioactivity, improvement has been desired.
【0004】出願人は、この回収硝酸を分解、とくに電
気分解してNOxを発生させ、これを再処理工程で利用
することによって、上記の従来技術では避けられなかっ
た固体廃棄物の発生をなくし、それにより廃棄物量を低
減するシステムを発明して、すでに開示した(特願平2
−231847)。The applicant decomposed the recovered nitric acid, particularly electrolyzing it to generate NO x , and utilizing this in the reprocessing step, the generation of solid waste, which was inevitable in the above-mentioned prior art, was generated. We have invented a system that eliminates this, thereby reducing the amount of waste, and has already disclosed it (Japanese Patent Application No.
231847).
【0005】出願人はまた、回収硝酸の処理を再処理工
程とは独立して行なわなければならず、従って硝酸の分
解により発生したNOxを再利用できない場合にそなえ
て、触媒を利用してNOxにNH3を作用させてこれを還
元し、N2に変えることにより無害化して放出可能にす
るとともに、廃棄物処理工程に回す放射性廃棄物の量を
低減する方法をも確立して、やはり開示した(特願平2
−231848)。The Applicant has also used a catalyst in case the treatment of the recovered nitric acid has to be carried out independently of the reprocessing step and therefore the NO x generated by the decomposition of the nitric acid cannot be reused. Establishing a method to reduce the amount of radioactive waste that is sent to the waste treatment process, while making NH 3 act on NO x to reduce it and change it to N 2 to detoxify and release it, I also disclosed it (Japanese Patent Application No. 2)
-231848).
【0006】発明者らは、上記したような新しい知見を
総合して、核燃料再利用工程からの回収硝酸を処理し、
処理の生成物であるNOxを、処理工程を実施する状況
に応じて、再処理工程へ供給して再利用し、または無害
化して放出することにより、最終的に廃棄物処理工程へ
回して固化体の形にすべき廃棄物の量を低減した処理方
法を提供すること、とくに回収硝酸の確立された電解技
術を提供することを意図してさらに研究を進め、図1に
示すように、核燃料再処理工程からの回収硝酸を電解槽
に導いて、電解液中のHNO3濃度が5Mを下回らない
条件下に電解を行ない、発生したNOxを再処理工程に
供給して再利用するか、または触媒を用いてNH3と反
応させることにより還元処理して無害化したのち放出
し、電解槽からの希薄硝酸を蒸留により濃縮し、濃縮硝
酸の一部または全部を電解槽に循環して再度電解するこ
とからなるシステムを確立し、これもすでに提案した
(特願平2−235023)。The inventors of the present invention have combined the above new findings to treat the nitric acid recovered from the nuclear fuel recycling process,
Depending on the situation in which the treatment process is carried out, the NO x that is the product of the treatment is supplied to the retreatment process for reuse, or it is detoxified and released, and finally sent to the waste treatment process. Further research was carried out with the intention of providing a treatment method with a reduced amount of waste that should be in the form of a solidified body, and in particular to provide an established electrolysis technique for recovered nitric acid, and as shown in FIG. Whether the recovered nitric acid from the nuclear fuel reprocessing step is introduced into the electrolytic cell and electrolyzed under the condition that the HNO 3 concentration in the electrolytic solution does not fall below 5M, and the generated NO x is supplied to the reprocessing step for reuse. , Or using a catalyst to react with NH 3 for reduction treatment to detoxify and then release, dilute nitric acid from the electrolytic cell is concentrated by distillation, and part or all of the concentrated nitric acid is circulated to the electrolytic cell. A system consisting of electrolyzing again Stand City, which was also already proposed (Japanese Patent Application No. 2-235023).
【0007】[0007]
【発明が解決しようとする課題】本発明の第一の目的
は、これらの処理技術で行なう硝酸の電解における電流
効率を向上させ、エネルギーを有効に使用することにあ
る。 第二の目的は、電解処理すべき硝酸の量の多少に
かかわらず高い電流効率で電解を実施することにある。
第三の目的は、電解により発生するNOxとO2の任意
の割合の混合物を得ることにある。SUMMARY OF THE INVENTION The first object of the present invention is to improve the current efficiency in the electrolysis of nitric acid carried out by these treatment techniques and to effectively use the energy. The second purpose is to carry out electrolysis with high current efficiency regardless of the amount of nitric acid to be electrolyzed.
The third purpose is to obtain a mixture of NO x and O 2 generated by electrolysis in an arbitrary ratio.
【0008】[0008]
【課題を解決するための手段】上記第一の目的を達成す
る本発明の回収硝酸の処理方法は、核燃料再処理工程か
らの回収硝酸を電解槽に導いて、電解液中のHNO3濃
度が5Mを下回らない条件下に電解を行ない、発生した
NOxを再処理工程に供給して再利用するか、または触
媒を用いてNH3と反応させることにより還元処理して
無害化したのち放出し、電解槽からの希薄硝酸を蒸留に
より濃縮し、濃縮硝酸の一部または全部を電解槽に循環
して再度電解することからなり、電解槽内の電解液を線
速度1m/h以上の速度で循環させながら電解を行なう
ことを特徴とする。The method for treating recovered nitric acid according to the present invention, which achieves the first object described above, introduces the recovered nitric acid from the nuclear fuel reprocessing step into an electrolytic cell so that the concentration of HNO 3 in the electrolytic solution is increased. Electrolysis is performed under the condition of not less than 5M, and the generated NO x is supplied to the reprocessing step for reuse, or is reacted with NH 3 using a catalyst for reduction treatment to render it harmless and then released. , Dilute nitric acid from the electrolytic cell is concentrated by distillation, and a part or all of the concentrated nitric acid is circulated to the electrolytic cell to electrolyze again, and the electrolytic solution in the electrolytic cell is fed at a linear velocity of 1 m / h or more. It is characterized in that electrolysis is performed while circulating.
【0009】上記第二および第三の目的を達成する本発
明の回収硝酸の処理方法は、核燃料再処理工程からの回
収硝酸を電解槽に導いて、電解液中のHNO3濃度が5
Mを下回らない条件下に電解を行ない、発生したNOx
を再処理工程に供給して再利用するか、または触媒を用
いてNH3と反応させることにより還元処理して無害化
したのち放出し、電解槽からの希薄硝酸を蒸留により濃
縮し、濃縮硝酸の一部または全部を電解槽に循環して再
度電解することからなり、電極間にカチオン交換膜を隔
膜として配置して電解を行なうことを特徴とする。In the method for treating recovered nitric acid of the present invention which achieves the second and third objects, the recovered nitric acid from the nuclear fuel reprocessing step is introduced into the electrolytic cell so that the HNO 3 concentration in the electrolytic solution is 5%.
NO x generated by electrolysis under conditions not lower than M
Is supplied to the reprocessing step for reuse, or is reacted with NH 3 using a catalyst to reduce and detoxify and then release the diluted nitric acid from the electrolytic cell by distillation to concentrate concentrated nitric acid. Part or all of the above is circulated in the electrolytic cell for electrolysis again, and the electrolysis is performed by disposing a cation exchange membrane as a diaphragm between the electrodes.
【0010】電解槽の電極材料は、陽極として非溶解性
のもの、代表的には白金を用いる。陰極は電解液に耐え
るものであれば任意であるが、黒鉛が好適である。As the electrode material of the electrolytic cell, a non-dissolving material, typically platinum, is used as the anode. The cathode is arbitrary as long as it can withstand the electrolytic solution, but graphite is preferable.
【0011】[0011]
【作用】電解の対象とする硝酸の濃度を5M以上とする
ことは、さきの発明に関して述べたように、浴電圧の上
昇とそれに伴うN2OやH2の発生を抑えて、NOxガス
を選択的に発生させるために必要な条件である。 これ
もさきの出願で説明したように、核燃料再処理工程から
回収される余剰硝酸は、濃度が10N程度であるから、
この硝酸を直接、硝酸濃度が5N程度に低下するまで電
解し、これを蒸留により10N程度に濃縮して、図1の
フローに示すように循環させる。As described above with respect to the invention, the concentration of nitric acid to be electrolyzed to 5 M or more suppresses the increase in bath voltage and the accompanying generation of N 2 O and H 2 , thereby reducing NO x gas. Is a condition necessary to selectively generate. As described in the previous application, the concentration of the excess nitric acid recovered from the nuclear fuel reprocessing step is about 10N,
This nitric acid is directly electrolyzed until the nitric acid concentration decreases to about 5N, concentrated to about 10N by distillation, and circulated as shown in the flow chart of FIG.
【0012】電解により発生したNOxガスは、いわゆ
る乾式脱硝の技術、すなわちNOxに対してアンモニア
を加え、貴金属系触媒を用いて温度200〜450℃で
接触的に還元し、N2にすることによって無害化する。The NO x gas generated by electrolysis is so-called dry denitration technology, that is, ammonia is added to NO x , and catalytically reduced at a temperature of 200 to 450 ° C. using a noble metal catalyst to form N 2 . To make it harmless.
【0013】蒸留装置においては、塔頂から硝酸を含ん
だ水が留出し、塔底から濃縮された硝酸が得られる。
水は、放射性物質を含んでいないから、必要な中和を行
なって放出することができる。 濃縮硝酸は、電解槽に
循環させて再度電解して処理することができるが、一部
は抜き出して廃棄しなければならない。 この廃液は放
射能があるから、放射性廃棄物処理の工程に従って処理
する。In the distillation apparatus, nitric acid-containing water is distilled out from the top of the column, and concentrated nitric acid is obtained from the bottom of the column.
Since water does not contain radioactive substances, it can be released with the necessary neutralization. The concentrated nitric acid can be circulated in the electrolytic cell and electrolyzed again for treatment, but a part of the concentrated nitric acid must be extracted and discarded. Since this waste liquid is radioactive, it should be treated according to the radioactive waste treatment process.
【0014】硝酸の電解において電流効率が低くなる原
因としては、下記の電極反応(1)および(2)より
も、(3)の反応が進む確率が高くなることや、 (陰極)NO2前躯体+e=NO2↑ (1) (陽極)O2前躯体=O2↑+e (2) (液中)NO2前躯体+O2前躯体=H+NO3〜
(3) 陰極側の電解生成物であるNOxまたは中間生成物(同
定はされていない)が電解液中を拡散して、陽極側で酸
化されることが考えられる。The cause of the lower current efficiency in the electrolysis of nitric acid is that the reaction (3) is more likely to proceed than the following electrode reactions (1) and (2), and (cathode) before NO 2 Body + e = NO 2 ↑ (1) (Anode) O 2 precursor = O 2 ↑ + e (2) (In liquid) NO 2 precursor + O 2 precursor = H + NO 3 ~
(3) It is conceivable that NO x or an intermediate product (not identified), which is an electrolytic product on the cathode side, diffuses in the electrolytic solution and is oxidized on the anode side.
【0015】そこで、電解液を循環させてある限度以上
の流速で移動させることにより、陰極反応生成物が陽極
で再酸化されることを防ぐという対策が有効になる。
カチオン交換膜のようにイオンの移動を妨げることがで
きる隔膜や、還元生成したNOxの拡散を抑制すること
ができる隔膜を用いた場合は、電解液の流動によらず再
酸化防止の効果が得られる。 つまり、同一設備を用い
て、処理の対象とする液量の多少に関係なく常に高い電
流効率を実現することができる。Therefore, it is effective to prevent the cathode reaction product from being reoxidized at the anode by circulating the electrolyte and moving it at a flow rate higher than a certain limit.
When a membrane that can prevent the movement of ions such as a cation exchange membrane or a membrane that can suppress the diffusion of NO x produced by reduction is used, the effect of preventing reoxidation does not depend on the flow of the electrolytic solution. can get. That is, using the same equipment, it is possible to always achieve high current efficiency regardless of the amount of liquid to be treated.
【0016】隔膜の使用は、陰極で発生するNOx と陽
極で発生するO2とを別々にとり出すことを可能にする
から、NOxの核燃料再処理工程への再利用に当って、
任意の割合のNOx/O2混合物を供給することができ
る。Since the use of the diaphragm makes it possible to separately take out NO x generated at the cathode and O 2 generated at the anode, in recycling NO x to the nuclear fuel reprocessing step,
NO x / O 2 mixture in any proportion can be supplied.
【0017】[0017]
【実施例】図2に示すフローの実験装置を組み立てた。
電解槽(1)には定電流定電圧電源(2)から直流電
流を供給し、陽極(11)の材料に白金、陰極(12)
の材料に黒煙を使用して、電流密度0.05A/cm2で
硝酸水溶液を電解した。隔膜(13)の材料としてスル
フォン酸型カチオン交換膜を使用して電解槽を二つの室
に分け、電解液は、循環ポンプ(3)および(4)で、
電解槽とタンク(5)および(6)との間に循環させ
た。EXAMPLE An experimental apparatus having the flow shown in FIG. 2 was assembled.
A direct current is supplied to the electrolytic cell (1) from a constant current / constant voltage power supply (2), and the anode (11) is made of platinum and the cathode (12).
The black nitric acid was used as the material of (1) to electrolyze the aqueous nitric acid solution at a current density of 0.05 A / cm 2 . A sulfonic acid type cation exchange membrane is used as the material of the diaphragm (13) to divide the electrolytic cell into two chambers, and the electrolytic solution is circulated by the circulation pumps (3) and (4).
It was circulated between the electrolyzer and tanks (5) and (6).
【0018】定流量バルブ(14)および(15)から
タンク内にキャリアガスとして窒素を供給し、発生ガス
を取り出した。 ガスは、冷却器(16)および(1
7)でミストを除去したのち、定流量バルブ(18)を
通してその一部を取り出し、NOx計(7)で組成と濃
度とを測定した。 残りのガスは、オゾン発生器(8)
で発生させたオゾンにより全量を酸化したのち、カセイ
ソーダ水溶液を入れたアルカリトラップ(9)で吸収
し、吸収液を滴定してNOx量を求めた。Nitrogen was supplied as a carrier gas into the tank from the constant flow valves (14) and (15), and the generated gas was taken out. The gas is cooled by the coolers (16) and (1
After removing the mist in 7), a part of the mist was taken out through the constant flow valve (18), and the composition and concentration were measured by the NO x meter (7). The rest of the gas is the ozone generator (8)
After the total amount was oxidized by the ozone generated in 1., it was absorbed by an alkali trap (9) containing an aqueous solution of caustic soda, and the absorption liquid was titrated to determine the NO x amount.
【0019】硝酸濃度8Mの水溶液を電解の対象とし
て、循環流量をLV(線速度)0.2〜2.5m/hの
範囲で変化させた。 隔膜を使用した場合と使用しない
場合の両方について、発生NOxの全量を算出した。A circulating flow rate was changed within a range of LV (linear velocity) of 0.2 to 2.5 m / h with an aqueous solution having a nitric acid concentration of 8 M as an object of electrolysis. The total amount of NO x generated was calculated both with and without the diaphragm.
【0020】その結果を図3に示す。 隔膜を用いない
場合、LV=1.0m/h以上の流速の範囲では高い電
流効果が得られるが、それ以下の流量範囲では流量の低
下に伴って電流効率が低下した。 一方、隔膜を用いた
場合には、循環流量に関係なく高い電流効率が得られて
いる。The results are shown in FIG. When a diaphragm is not used, a high current effect can be obtained in the flow velocity range of LV = 1.0 m / h or more, but in the flow rate range of LV = 1.0 m / h or more, the current efficiency decreases as the flow rate decreases. On the other hand, when the diaphragm is used, high current efficiency is obtained regardless of the circulation flow rate.
【0021】[0021]
【発明の効果】本発明の方法によれば、さきに提案した
発明の効果、すなわち核燃料再処理工程からの回収硝酸
を電解により分解してNOxを発生させ、これを状況に
応じて再処理工程へ供給して再利用するなり、接触還元
により無害化して大気中に放出するなり、任意に選択で
きること、および電解により生じた希薄硝酸は、蒸留に
より濃縮して電解槽へ循環させ再度電解の対象とするこ
とにより、最終的に固化処理すべき放射性廃棄物の量を
著しく低減することができるという利益を享受し、高い
電流効率の実現により省エネルギーと処理コスト低減の
要請にこたえることができる。According to the method of the present invention, the effect of the present invention proposed previously, i.e. to generate NO x is decomposed to recover nitric acid from nuclear fuel reprocessing step by electrolytic reprocessing in accordance with this situation It can be supplied to the process for reuse, be harmless by catalytic reduction and be released into the atmosphere, or can be arbitrarily selected, and dilute nitric acid produced by electrolysis can be concentrated by distillation and circulated to an electrolytic cell for re-electrolysis. By targeting, it is possible to enjoy the advantage that the amount of radioactive waste to be finally solidified can be significantly reduced, and it is possible to meet the demands for energy saving and treatment cost reduction by realizing high current efficiency.
【0022】本発明の方法のうち隔膜を使用した態様に
よるときは、電解液の流量を任意に設定できるから、処
理すべき回収硝酸の量にかかわらず、同一の設備を使用
できる。 それにより設備の簡易化がはかれ、設備費を
低減できる。 さらに陰極と陽極を分離した結果、それ
ぞれの発生ガスを別々に回収でき、NO/O2の比率を
調節することによって、核燃料再処理設備へ戻して再利
用するNO/NO2の割合を調整することができる。According to the method of the present invention in which a diaphragm is used, the flow rate of the electrolytic solution can be arbitrarily set, so that the same equipment can be used regardless of the amount of recovered nitric acid to be treated. This simplifies the equipment and reduces the equipment cost. Further, as a result of separating the cathode and the anode, the respective generated gases can be recovered separately, and by adjusting the NO / O 2 ratio, the ratio of NO / NO 2 to be returned to the nuclear fuel reprocessing facility and reused is adjusted. be able to.
【図1】 本発明の処理方法の工程を示すフローチャー
ト。FIG. 1 is a flowchart showing steps of a processing method of the present invention.
【図2】 本発明の方法を実験した装置の構成を示す
図。FIG. 2 is a diagram showing the configuration of an apparatus for which the method of the present invention was tested.
【図3】 本発明の実施例における硝酸の電解のデータ
であって、電解槽内の電解液流の線速度に対するNOx
発生量および陰極電流効率を示すグラフ。FIG. 3 is data of electrolysis of nitric acid according to an embodiment of the present invention, showing NO x with respect to a linear velocity of an electrolytic solution flow in an electrolytic cell.
The graph which shows the generation amount and cathode current efficiency.
1 電解槽 2 定電圧定電流電源 3,4 循環ポンプ 5,6 タンク 7 NOx計 8 オゾン発生器 9 アルカリ液 11 陽極 12 陰極 13 隔膜 16,17 ミストセパレーター 14,15,18 定流量バルブ1 electrolytic cell 2 constant-voltage constant-current power supply 3 and 4 circulating pump 5,6 tank 7 NO x eight ozone generator 9 lye 11 anode 12 cathode 13 diaphragm 16, 17 mist separator 14, 15 and 18 constant flow valve
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平4−110795(JP,A) 特開 平4−110796(JP,A) 特開 平4−115197(JP,A) 特公 昭60−38999(JP,B2) ─────────────────────────────────────────────────── --Continued from the front page (56) References JP-A-4-110795 (JP, A) JP-A-4-110796 (JP, A) JP-A-4-115197 (JP, A) JP-B Sho-60- 38999 (JP, B2)
Claims (3)
槽に導いて、電解液中のHNO3濃度が5Mを下回らな
い条件下に電解を行ない、発生したNOxを再処理工程
に供給して再利用するか、または触媒を用いてNH3と
反応させることにより還元処理して無害化したのち放出
し、電解槽からの希薄硝酸を蒸留により濃縮し、濃縮硝
酸の一部または全部を電解槽に循環して再度電解するこ
とからなり、電解槽内の電解液を線速度1m/h以上の
速度で循環させながら電解を行なうことを特徴とする核
燃料再処理工程からの回収硝酸の処理方法。1. The recovered nitric acid from the nuclear fuel reprocessing step is introduced into an electrolytic cell, electrolysis is performed under conditions where the HNO 3 concentration in the electrolytic solution does not fall below 5 M, and the generated NO x is supplied to the reprocessing step. It is reused as a catalyst or is reacted with NH 3 using a catalyst to reduce the detoxification after detoxification and then released. The diluted nitric acid from the electrolytic cell is concentrated by distillation, and part or all of the concentrated nitric acid is electrolyzed. A method for treating recovered nitric acid from a nuclear fuel reprocessing step, characterized in that the electrolytic solution is circulated in a tank and electrolyzed again, and electrolysis is performed while circulating an electrolytic solution in the electrolytic cell at a linear velocity of 1 m / h or more. .
槽に導いて、電解液中のHNO3濃度が5Mを下回らな
い条件下に電解を行ない、発生したNOxを再処理工程
に供給して再利用するか、または触媒を用いてNH3と
反応させることにより還元処理して無害化したのち放出
し、電解槽からの希薄硝酸を蒸留により濃縮し、濃縮硝
酸の一部または全部を電解槽に循環して再度電解するこ
とからなり、電極間にカチオン交換膜を隔膜として配置
して電解を行なうことを特徴とする核燃料再処理工程か
らの回収硝酸の処理方法。2. The nitric acid recovered from the nuclear fuel reprocessing step is introduced into an electrolytic cell, electrolysis is performed under conditions where the HNO 3 concentration in the electrolytic solution does not fall below 5 M, and the generated NO x is supplied to the reprocessing step. It is reused as a catalyst or is reacted with NH 3 using a catalyst to reduce the detoxification after detoxification and then released. The diluted nitric acid from the electrolytic cell is concentrated by distillation, and part or all of the concentrated nitric acid is electrolyzed. A method for treating recovered nitric acid from a nuclear fuel reprocessing step, which comprises circulating in a tank to perform electrolysis again and disposing a cation exchange membrane as a diaphragm between electrodes to perform electrolysis.
鉛を使用して実施する請求項1または2の処理方法。3. The treatment method according to claim 1 or 2, which is carried out by using platinum as the anode material and graphite as the cathode material of the electrolytic cell.
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7533291A JPH0723917B2 (en) | 1991-04-08 | 1991-04-08 | Treatment method of recovered nitric acid from nuclear fuel reprocessing step |
FR9110723A FR2666441B1 (en) | 1990-08-31 | 1991-08-29 | PROCESS FOR TREATING RECOVERED NITRIC ACID FROM NUCLEAR FUEL PROCESSING STEPS. |
GB9118496A GB2250853B (en) | 1990-08-31 | 1991-08-29 | Method of treating nitric acid recovered from spent nuclear fuel reprocessing process |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7533291A JPH0723917B2 (en) | 1991-04-08 | 1991-04-08 | Treatment method of recovered nitric acid from nuclear fuel reprocessing step |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH04310283A JPH04310283A (en) | 1992-11-02 |
JPH0723917B2 true JPH0723917B2 (en) | 1995-03-15 |
Family
ID=13573197
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP7533291A Expired - Lifetime JPH0723917B2 (en) | 1990-08-31 | 1991-04-08 | Treatment method of recovered nitric acid from nuclear fuel reprocessing step |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0723917B2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113929185A (en) * | 2021-09-26 | 2022-01-14 | 中国原子能科学研究院 | A kind of method for treating radioactive waste liquid containing nitric acid by electrolytic cell |
-
1991
- 1991-04-08 JP JP7533291A patent/JPH0723917B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
---|---|
JPH04310283A (en) | 1992-11-02 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0412175B1 (en) | Method for removing nitrogen compounds from a liquid | |
US3719570A (en) | Electrolytic process | |
JP4549849B2 (en) | New collection process | |
JP2006297206A (en) | Electrolytic treatment method and apparatus for ammonia nitrogen-containing waste water | |
JPH03504937A (en) | Method for removing nitrogen oxide from waste gas and recovering it as nitric acid | |
JP3984414B2 (en) | NH3-containing wastewater treatment apparatus and treatment method | |
EP0291330A2 (en) | Ground-water treatment | |
CN111321423B (en) | Method for recovering sulfuric acid from waste sulfuric acid containing hydrogen peroxide | |
JPH07100466A (en) | Method for treating waste water | |
JP2009106884A (en) | Water treatment and gas treatment apparatus | |
JPH0723917B2 (en) | Treatment method of recovered nitric acid from nuclear fuel reprocessing step | |
JPH08155463A (en) | Method and apparatus for decomposing ammoniacal nitrogen nitric-nitrogen and/or nitrous-nitrogen | |
JP3615814B2 (en) | Method and apparatus for removing nitrate and / or nitrite nitrogen | |
JP2731299B2 (en) | Volume reduction method for low-level concentrated waste liquid | |
JP2556221B2 (en) | Oxidation method of trivalent plutonium to tetravalent plutonium | |
GB2206341A (en) | Treatment of organically-based waste matter | |
JPH0736038B2 (en) | Treatment method of recovered nitric acid from nuclear fuel reprocessing step | |
JPH07299465A (en) | Electrolytic treatment of waste water and anode used therefor | |
JP2504311B2 (en) | Method for reducing the amount of radioactive waste generated from nuclear fuel reprocessing processes | |
EP0696228B1 (en) | A method for converting ammonia in a gas stream to nitrogen | |
JPH08254597A (en) | Method for treating waste liquid containing ammoniac nitrogen and organic substance | |
Turaev et al. | Regeneration by membrane electrolysis of an etching solution based on copper chloride | |
JP3981424B2 (en) | Decomposition method of halogenated ethylene | |
GB2250853A (en) | Method of treating nitric acid recovered from spent nuclear fuel reprocessing process. | |
JP2745278B2 (en) | Treatment method for precious metal cyanide bath plating wastewater and washing water |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 19950905 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20080315 Year of fee payment: 13 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20090315 Year of fee payment: 14 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20090315 Year of fee payment: 14 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20100315 Year of fee payment: 15 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20100315 Year of fee payment: 15 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20110315 Year of fee payment: 16 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20110315 Year of fee payment: 16 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20120315 Year of fee payment: 17 |
|
EXPY | Cancellation because of completion of term | ||
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20120315 Year of fee payment: 17 |