JPH09203792A - Method for separating and recovering platinum group elements - Google Patents
Method for separating and recovering platinum group elementsInfo
- Publication number
- JPH09203792A JPH09203792A JP1037996A JP1037996A JPH09203792A JP H09203792 A JPH09203792 A JP H09203792A JP 1037996 A JP1037996 A JP 1037996A JP 1037996 A JP1037996 A JP 1037996A JP H09203792 A JPH09203792 A JP H09203792A
- Authority
- JP
- Japan
- Prior art keywords
- platinum group
- group element
- nitric acid
- anion
- exchange resin
- 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.)
- Granted
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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
-
- 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
- Treatment Of Water By Ion Exchange (AREA)
- Removal Of Specific Substances (AREA)
- Inorganic Compounds Of Heavy Metals (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
(57)【要約】
【課題】 白金族元素は工業的に極めて利用価値が高い
希少金属原料であるが、使用済み核燃料の再処理工場の
廃液に含まれる白金族元素を分離回収する有効な方法が
確立されておらず、廃棄物処理処分工程において白金族
元素による妨害が発生し、かつ、希少金属原料である白
金族元素の安定確保が依然困難な状態である等の課題が
あった。
【解決手段】 白金族元素を含有する硝酸溶液に、亜硝
酸あるいは亜硝酸塩を添加して前記白金族元素のアニオ
ンニトロ錯体を生成させるアニオンニトロ錯体生成工程
と、硝酸溶液をアニオン交換樹脂と接触させて溶液中の
前記白金族元素を選択的に吸着させる吸着工程と、アニ
オン交換樹脂を錯化剤を含有する水溶液と接触させて白
金族元素を溶離回収する溶離回収工程とを備えたもので
ある。
(57) [Abstract] [Problem] Platinum group element is a rare metal raw material that is industrially extremely valuable, but an effective method for separating and recovering the platinum group element contained in the waste liquid of the spent nuclear fuel reprocessing plant. However, there is a problem that the platinum group element is disturbed in the waste treatment and disposal process, and it is still difficult to stably secure the platinum group element which is a rare metal raw material. SOLUTION: An anion nitro complex formation step of forming an anion nitro complex of the platinum group element by adding nitrous acid or nitrite to a nitric acid solution containing a platinum group element, and bringing the nitric acid solution into contact with an anion exchange resin. And an elution recovery step of contacting the anion exchange resin with an aqueous solution containing a complexing agent to elute and recover the platinum group element in the solution. .
Description
【0001】[0001]
【発明の属する技術分野】この発明は、使用済み核燃料
の再処理工場で発生する廃液や使用済み核燃料の溶解残
滓の硝酸溶解液等、白金族元素を含有する溶液から白金
族元素を分離回収する白金族元素の分離回収方法に関す
るものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention separates and recovers a platinum group element from a solution containing a platinum group element, such as a waste liquid generated at a reprocessing plant for spent nuclear fuel or a nitric acid solution of a dissolved residue of the spent nuclear fuel. The present invention relates to a method for separating and recovering platinum group elements.
【0002】[0002]
【従来の技術】ルテニウム(Ru),ロジウム(R
h),パラジウム(Pd)等の白金族元素は、装飾品の
みならず、電子材料,電気材料として電器産業の分野
や、触媒として合成化学、石油化学、自動車産業等の分
野において利用されている極めて重要な金属元素であ
る。しかしながら、白金族元素の天然鉱物資源は乏し
く、その埋蔵と生産は極端に限られた国に偏っており、
このため、白金族元素の供給体制は極めて脆弱である。
特に、現在日本における白金族元素の鉱山はほとんど無
く、その全てを海外からの輸入に頼っており、価格も極
めて高く、原料供給の確保は重要な課題となっている。2. Description of the Related Art Ruthenium (Ru), Rhodium (R)
h), Platinum group elements such as palladium (Pd) are used not only in ornaments but also in the fields of electric appliances as electronic materials and electric materials, and in fields such as synthetic chemistry, petrochemistry and automobile industries as catalysts. It is a very important metal element. However, the natural mineral resources of platinum group elements are scarce, and their reserves and production are concentrated in extremely limited countries,
Therefore, the supply system of platinum group elements is extremely weak.
In particular, there are almost no platinum group element mines in Japan at present, all of which rely on imports from overseas, the prices are extremely high, and securing raw material supply is an important issue.
【0003】一方、原子力発電所で発生する使用済み核
燃料中には相当量の白金族元素が含まれている。例え
ば、通常の燃焼度の軽水炉使用済み燃料1t当たりに含
まれる白金族元素の量は、ルテニウム1900g,ロジ
ウム320g,パラジウム850g程度である。もしこ
れらの白金族元素が全量回収され、その放射能が利用可
能なレベルまで低減されれば、現在日本における化学触
媒利用量をパラジウムで約36%,ロジウムで約60
%,ルテニウムでほぼ100%満足することができる計
算となる。On the other hand, the spent nuclear fuel generated in a nuclear power plant contains a considerable amount of platinum group elements. For example, the amount of platinum group element contained per 1 t of spent fuel of a normal burnup in a light water reactor is about 1900 g of ruthenium, 320 g of rhodium, and 850 g of palladium. If all of these platinum group elements are recovered and their radioactivity is reduced to a usable level, the amount of chemical catalyst used in Japan is currently about 36% for palladium and about 60% for rhodium.
%, Ruthenium is almost 100% satisfied.
【0004】現在工業的に行われているピューレクス法
と呼ばれる使用済み燃料の再処理プロセスでは、使用済
み燃料を硝酸で溶解した後、溶媒抽出法によりウラン
(U),プルトニウム(Pu)を抽出分離して再利用し
ている。白金族元素は他の多種な核分裂生成物と共に抽
出残液に残り、放射性廃液として処理される。この廃液
は、硝酸回収工程や蒸発濃縮工程を経て高レベル廃液と
なり、最終的にはガラス固化体の形で地層深部に貯蔵さ
れ処分される計画が進められている。In the spent fuel reprocessing process called the purex method, which is currently used industrially, after dissolving the spent fuel with nitric acid, uranium (U) and plutonium (Pu) are extracted and separated by a solvent extraction method. And reused. Platinum group elements remain in the extraction residual liquid together with various other fission products, and are treated as radioactive waste liquid. This waste liquid becomes a high-level waste liquid through a nitric acid recovery process and an evaporative concentration process, and is finally planned to be stored and disposed in the deep strata in the form of a vitrified body.
【0005】上記再処理プロセスにおいて白金族元素は
いずれの工程でも分離回収されていない。そのため、高
レベル廃液の保管や貯蔵期間において白金族元素のコロ
イド状沈殿物が析出し、廃液のハンドリングや均一な固
化体の形成が困難となる。また、高レベル廃液のガラス
固化工程では、揮発しやすい放射性のルテニウム酸化物
が生成されるため、高温処理時に揮発拡散する恐れがあ
り、これを解決するために、高価で複雑なルテニウム除
去設備が必要とされる。In the reprocessing process, the platinum group element is not separated and recovered in any step. For this reason, colloidal precipitates of platinum group elements are deposited during storage of the high-level waste liquid and during the storage period, which makes it difficult to handle the waste liquid and form a uniform solidified body. In addition, in the vitrification process of high-level waste liquid, radioactive ruthenium oxide, which is easily volatilized, is generated, so there is a risk of volatilization and diffusion during high-temperature processing.To solve this, expensive and complicated ruthenium removal equipment is required. Needed.
【0006】使用済み燃料中の白金族元素は溶解工程で
一部が不溶残滓となるが、そのかなりの部分は硝酸に溶
解されて溶解液中に存在する。これらの元素の溶解量は
燃料の燃焼度、使用する硝酸溶液の濃度、さらに溶解温
度等の条件によるが、通常パラジウムはほとんど全量,
ルテニウムは60〜90%程度が溶解するとされてい
る。なお、通常の溶解条件では、ロジウムの大部分は溶
解されずに不溶残滓に残されるが、この残滓をさらに高
い温度に上げたり、強い酸化剤(例えば過酸化水素,IV
価セリウムイオン,II価銀イオン)を添加することよ
り、そのほとんど全量を溶解することができる。A part of the platinum group element in the spent fuel becomes an insoluble residue in the dissolution process, but a considerable part thereof is dissolved in nitric acid and exists in the solution. The dissolved amount of these elements depends on the burnup of the fuel, the concentration of the nitric acid solution used, the melting temperature, etc.
It is said that about 60 to 90% of ruthenium is dissolved. Under normal dissolution conditions, most of rhodium remains undissolved and remains in the insoluble residue, but this residue is raised to a higher temperature, or a strong oxidizing agent (for example, hydrogen peroxide, IV
By adding valent cerium ions and II valent silver ions), almost all of them can be dissolved.
【0007】溶解されたこれらの白金族元素は、燃料溶
解液中に存在するウラン,プルトニウム等の核燃料物質
のほかに、ネプツニウム(Np),アメリシウム(A
m),キュリウム(Cm)等のマイナアクチノイド元
素、セシウム(Cs)等のアルカリ金属元素、バリウム
(Ba),ストロンチウム(Sr)等のアルカリ土類金
属元素、ネオジム(Nd),セリウム(Ce)等の希土
類金属元素、モリブデン(Mo),ジルコニウム(Z
r),テルル(Te)等の多種多様な核分裂生成物と共
存している。These dissolved platinum group elements are neptunium (Np) and americium (A) in addition to nuclear fuel substances such as uranium and plutonium existing in the fuel solution.
m), minor actinide elements such as curium (Cm), alkali metal elements such as cesium (Cs), alkaline earth metal elements such as barium (Ba) and strontium (Sr), neodymium (Nd), cerium (Ce), etc. Rare earth metal elements, molybdenum (Mo), zirconium (Z
r) and tellurium (Te) coexist with various fission products.
【0008】燃料溶解液中の白金族元素は前記再処理工
程を経て、最終的には高レベル放射性廃液中に移行す
る。この廃液には、少量のウラン、プルトニウム抽出残
留物及び硝酸に溶解された白金族元素及び上記核分裂生
成物のほとんど全量が含まれている。これらの溶液は複
雑な組成及び多様な化学的性質に加え、強い放射能を持
っているため、その中の有価元素の分離回収に関して
は、まだ効果的な方法が確立されていないのが現状であ
る。The platinum group element in the fuel solution is finally transferred to the high-level radioactive liquid waste through the reprocessing step. This effluent contains small amounts of uranium, plutonium extraction residues, and platinum group elements dissolved in nitric acid and almost all of the fission products. In addition to their complicated composition and diverse chemical properties, these solutions have strong radioactivity, and as a result, effective methods have not yet been established for the separation and recovery of valuable elements in them. is there.
【0009】[0009]
【発明が解決しようとする課題】上述のように、白金族
元素は工業的に極めて利用価値が高いが国内での供給が
できない希少金属原料であり、使用済み核燃料の再処理
工場で発生する廃液から白金族元素が分離回収されれば
希少金属原料の安定確保が行えるとともに、再処理工場
廃棄物の処理処分プロセス性能の向上、廃液の放射能レ
ベルの低減に大きく貢献して有益である。これにもかか
わらず、従来は使用済み核燃料の再処理工場の廃液から
白金族元素を分離回収する有効な方法が確立されておら
ず、廃棄物処理処分工程において白金族元素による妨害
が発生し、かつ、希少金属原料である白金族元素の安定
確保が依然困難な状態である等の課題があった。As described above, the platinum group element is a rare metal raw material that has an extremely high utility value industrially but cannot be supplied domestically, and is a waste liquid generated in a reprocessing plant for spent nuclear fuel. If the platinum group element is separated and recovered from the above, it is possible to secure a stable supply of rare metal raw materials, improve the processing performance of the reprocessing plant waste, and contribute greatly to the reduction of the radioactivity level of the waste liquid. Despite this, conventionally, an effective method for separating and recovering platinum group elements from the waste liquid of the spent nuclear fuel reprocessing plant has not been established, and interference with platinum group elements occurs in the waste treatment and disposal process, In addition, there is a problem that it is still difficult to stably secure the platinum group element, which is a rare metal raw material.
【0010】この発明は上記のような課題を解決するた
めになされたもので、使用済み核燃料の再処理工場で発
生する廃液、使用済み核燃料の溶解残滓の硝酸溶解液な
どの白金族元素を含有する溶液から、白金族元素を高収
率、高純度で分離回収することができる白金族元素の分
離回収方法を得ることを目的とする。The present invention has been made to solve the above problems, and contains a platinum group element such as a waste liquid generated at a reprocessing plant for spent nuclear fuel and a nitric acid solution of the dissolved residue of the spent nuclear fuel. It is an object of the present invention to provide a method for separating and recovering a platinum group element capable of separating and recovering a platinum group element with high yield and high purity from a solution.
【0011】[0011]
【課題を解決するための手段】請求項1記載の発明に係
る白金族元素の分離回収方法は、ルテニウム,ロジウ
ム,パラジウム等の白金族元素を含有する硝酸溶液に、
亜硝酸あるいは亜硝酸塩を添加して前記白金族元素のア
ニオンニトロ錯体を生成させるアニオンニトロ錯体生成
工程と、前記アニオンニトロ錯体生成工程を経た硝酸溶
液をアニオン交換樹脂と接触させ、前記硝酸溶液中の前
記白金族元素を前記アニオン交換樹脂に選択的に吸着さ
せる吸着工程とを備えたものである。A method for separating and recovering a platinum group element according to the present invention is a nitric acid solution containing a platinum group element such as ruthenium, rhodium or palladium.
Anion nitro complex formation step of adding nitrous acid or nitrite to form an anion nitro complex of the platinum group element, and the nitric acid solution that has undergone the anion nitro complex formation step is contacted with an anion exchange resin, And an adsorption step of selectively adsorbing the platinum group element on the anion exchange resin.
【0012】請求項2記載の発明に係る白金族元素の分
離回収方法は、吸着工程において白金族元素を吸着させ
たアニオン交換樹脂を、チオ尿素,アンモニア等の錯化
剤を含有する水溶液と接触させ、前記アニオン交換樹脂
に吸着した前記白金族元素を溶離回収する溶離回収工程
を前記吸着工程の後に備えたものである。In the method for separating and recovering a platinum group element according to a second aspect of the present invention, the anion exchange resin having the platinum group element adsorbed in the adsorption step is contacted with an aqueous solution containing a complexing agent such as thiourea or ammonia. Then, an elution recovery step of elution recovery of the platinum group element adsorbed on the anion exchange resin is provided after the adsorption step.
【0013】請求項3記載の発明に係る白金族元素の分
離回収方法は、アニオンニトロ錯体生成工程において亜
硝酸あるいは亜硝酸塩を添加する前に、硝酸溶液中の硝
酸イオン濃度を2mol/l以下、水素イオン濃度を
0.01〜2mol/lの範囲内に調整するイオン濃度
調整工程を備えたものである。In the method for separating and recovering platinum group elements according to the third aspect of the present invention, the concentration of nitric acid ion in the nitric acid solution is 2 mol / l or less before adding nitrous acid or nitrite in the anion nitro complex forming step. It is provided with an ion concentration adjusting step of adjusting the hydrogen ion concentration within the range of 0.01 to 2 mol / l.
【0014】請求項4記載の発明に係る白金族元素の分
離回収方法は、使用済み核燃料の再処理工程で発生する
廃液、または使用済み核燃料の溶解残滓の硝酸溶解液を
白金族元素を含有する硝酸溶液として、これに請求項1
から請求項3のうちのいずれか1項記載の発明を適用す
るものである。In the method for separating and recovering platinum group elements according to the present invention, the waste liquid generated in the reprocessing step of the spent nuclear fuel or the nitric acid solution of the dissolved residue of the spent nuclear fuel contains the platinum group elements. Claim 1 as a nitric acid solution
Therefore, the invention according to any one of claims 3 to 4 is applied.
【0015】本発明者等は、まず、使用済み核燃料の再
処理工程で発生する廃液、使用済み核燃料の溶解残滓の
硝酸溶解液などの白金族元素を含有する硝酸溶液(これ
らの溶液を以下「処理液」ともいう。)から白金族元素
を分離回収するために、硝酸および亜硝酸イオンを含む
水溶液におけるルテニウム,ロジウム,パラジウムおよ
び上記処理液中に含まれる他の各種金属元素に対する代
表的なアニオン交換樹脂の吸着特性を調べてきた。The inventors of the present invention first describe nitric acid solutions containing platinum group elements such as waste liquid generated in the reprocessing step of spent nuclear fuel and nitric acid dissolved liquid of the dissolved residue of spent nuclear fuel (these solutions are referred to as " (Also referred to as "treatment liquid"), a typical anion for ruthenium, rhodium, palladium in an aqueous solution containing nitric acid and nitrite ions and various other metal elements contained in the treatment liquid in order to separate and recover platinum group elements. We have investigated the adsorption properties of exchange resins.
【0016】特に、硝酸溶液におけるこれらの金属元素
の吸着性に対する亜硝酸イオンの添加効果に着目して鋭
意研究を重ねた結果、亜硝酸イオンの存在下によりルテ
ニウム,ロジウム,パラジウムの各白金族元素のアニオ
ン交換樹脂への吸着性が著しく増大することを見出し
た。In particular, as a result of intensive studies focusing on the effect of addition of nitrite ion on the adsorption of these metal elements in a nitric acid solution, the platinum group elements of ruthenium, rhodium and palladium were found to exist in the presence of nitrite ion. It was found that the adsorptivity of the above to the anion exchange resin is remarkably increased.
【0017】ルテニウム,ロジウム,パラジウムの各白
金族元素のアニオン交換樹脂への吸着性に対する亜硝酸
イオン添加の効果について測定した結果の一例を示す。
図1は、一般に使用される4級アンモニウム基アニオン
交換樹脂を用い、0.1mol/lの硝酸水溶液におけ
るこれらの白金族元素の吸着分配係数の亜硝酸イオン濃
度依存性を示すグラフである。なお、溶液中の亜硝酸イ
オン濃度は亜硝酸ナトリウム(NaNO2 )の添加によ
り調節した。吸着分配係数は、吸着平衡時における(樹
脂中の金属濃度/溶液中の金属濃度)として定義され
る。An example of the results of the measurement of the effect of the addition of nitrite ion on the adsorption of each platinum group element of ruthenium, rhodium and palladium on the anion exchange resin is shown.
FIG. 1 is a graph showing the nitrite ion concentration dependence of the adsorption partition coefficient of these platinum group elements in a 0.1 mol / l nitric acid aqueous solution using a commonly used quaternary ammonium group anion exchange resin. The concentration of nitrite ion in the solution was adjusted by adding sodium nitrite (NaNO 2 ). The adsorption partition coefficient is defined as (metal concentration in resin / metal concentration in solution) at adsorption equilibrium.
【0018】図1より、ルテニウム,ロジウム,パラジ
ウム各元素に対する吸着分配係数は、NaNO2 の添加
により著しく増大し、0.1〜1.0mol/lの亜硝
酸イオンの存在下では、これらの白金族元素の吸着分配
係数は数百倍に増大し、数百ないし数千といった大きな
値を示すことがわかる。即ち、このような亜硝酸イオン
濃度の条件下では、溶液中におけるこれらの白金族元素
がアニオン交換樹脂に強く吸着されて溶液側から樹脂側
に移行することになる。From FIG. 1, the adsorption partition coefficient for each element of ruthenium, rhodium and palladium is remarkably increased by the addition of NaNO 2 , and in the presence of 0.1 to 1.0 mol / l of nitrite ion, the platinum content of these platinum elements is increased. It can be seen that the adsorption distribution coefficient of the group element increases several hundred times and shows a large value of several hundreds to several thousands. That is, under such conditions of nitrite ion concentration, these platinum group elements in the solution are strongly adsorbed by the anion exchange resin and migrate from the solution side to the resin side.
【0019】なお、亜硝酸イオンの存在下における、ル
テニウム,ロジウム,パラジウムの各白金族元素のアニ
オン交換樹脂への吸着促進効果は、アニオン交換樹脂の
交換基の種類や構造にはほとんど依存せず、本発明者ら
が1級〜3級アミン基,ピリジン基,ジピロリル基,ベ
ンズイミダゾル基,アンモニウム基を交換基とするアニ
オン交換樹脂をそれぞれ用いて測定したところ、図1と
ほとんど同様な結果が得られた。即ち、通常市販されて
いる高分子ポリマーを基体とするアニオン交換樹脂で
は、いずれもほぼ同様な吸着性の促進効果が認められ
た。The effect of promoting adsorption of each platinum group element of ruthenium, rhodium and palladium to the anion exchange resin in the presence of nitrite ion is almost independent of the type and structure of the exchange group of the anion exchange resin. When the present inventors measured using anion exchange resins having a primary to tertiary amine group, a pyridine group, a dipyrrolyl group, a benzimidazole group, and an ammonium group as an exchange group, respectively, the results were almost the same as in FIG. was gotten. That is, almost all of the anion exchange resins based on high molecular weight polymers which are commercially available have the similar adsorbing effect.
【0020】ルテニウム,ロジウム,パラジウムの各白
金族元素は周期表中の第VIII族の第2遷移金属元素であ
り、これらの金属イオンであるRu3+,Rh3+,Pd2+
は、強い配位結合力を有する窒素原子を含む亜硝酸イオ
ン(NO2 -)と安定な錯体を形成する。このため、亜硝
酸イオン存在下の溶液中では、NO2 -イオン濃度の増加
とともにこれらの金属イオンと結合するNO2 -の配位数
が増大し、負電荷をもつようになったこれらの金属ニト
ロ錯体はアニオン交換樹脂に強い吸着性を示すようにな
る。Each of the platinum group elements of ruthenium, rhodium and palladium is the second transition metal element of Group VIII in the periodic table, and Ru 3+ , Rh 3+ and Pd 2+ which are these metal ions.
Forms a stable complex with a nitrite ion (NO 2 − ) containing a nitrogen atom having a strong coordination bond. Therefore, in a solution in the presence of nitrite ions, the coordination number of NO 2 − that binds to these metal ions increases as the NO 2 − ion concentration increases, and these metals become negatively charged. The nitro complex becomes strongly adsorbable to the anion exchange resin.
【0021】一方、硝酸溶液におけるこれらの白金族元
素以外の金属元素、とりわけ前記使用済み核燃料の再処
理工場で発生する廃液や使用済み核燃料の溶解残滓の硝
酸溶解液中に含まれるCs等のアルカリ金属元素、B
a,Sr等のアルカリ土類金属元素、Y,Nd,Ce等
の希土類金属元素、Mo,Zr,Te等の核分裂生成物
元素、U,Pu,Np,Am,Cm等のアクチノイド元
素といった共存元素のアニオン交換樹脂への吸着性は、
亜硝酸または亜硝酸塩の添加によりほとんど変化しない
ことが認められた。On the other hand, metal elements other than these platinum group elements in the nitric acid solution, especially alkali such as Cs contained in the nitric acid solution of the waste solution of the spent nuclear fuel reprocessing plant or the dissolved residue of the spent nuclear fuel. Metal element, B
Alkali earth metal elements such as a and Sr, rare earth metal elements such as Y, Nd and Ce, fission product elements such as Mo, Zr and Te, and coexisting elements such as actinide elements such as U, Pu, Np, Am and Cm. The adsorptivity of to the anion exchange resin is
It was observed that the addition of nitrite or nitrite hardly changed.
【0022】さらに、Cs,Ba,Sr,Y,Nd,C
e,Am,Cm,Mo,Zr等の共存元素は、硝酸溶液
中ではアニオンニトラト錯体を形成せずいずれもカチオ
ンの形で存在するため、アニオン交換樹脂にはまったく
吸着されない。また、U,Pu,Npは硝酸イオン濃度
が2mol/l以上の比較的濃厚な硝酸溶液中ではアニ
オンニトラト錯体を形成するためアニオン交換樹脂によ
く吸着されるが、硝酸イオン濃度2mol/l、特に
1.5mol/l以下ではアニオン錯体が形成されない
ためU,Pu,Npはほとんど吸着されない。Further, Cs, Ba, Sr, Y, Nd, C
The coexisting elements such as e, Am, Cm, Mo, and Zr do not form an anion nitrato complex in the nitric acid solution and all exist in the form of cation, and are not adsorbed to the anion exchange resin at all. U, Pu, and Np form an anion nitrato complex in a relatively concentrated nitric acid solution having a nitrate ion concentration of 2 mol / l or more, and thus are well adsorbed on an anion exchange resin. Particularly, at 1.5 mol / l or less, since an anion complex is not formed, U, Pu and Np are hardly adsorbed.
【0023】従って、処理液中の硝酸イオン濃度を約2
mol/l以下に調整し、亜硝酸または亜硝酸塩を添加
してルテニウム,ロジウム,パラジウム各白金族元素の
アニオンニトロ錯体を形成させた後、アニオン交換樹脂
にこれらの白金族元素のみを選択的に吸着させて、溶液
中に共存する他の元素から分離することが可能である。Therefore, the concentration of nitrate ion in the treatment liquid is about 2
After adjusting to less than mol / l, nitrite or nitrite is added to form an anion nitro complex of platinum group elements of ruthenium, rhodium and palladium, and then only these platinum group elements are selectively applied to the anion exchange resin. It is possible to adsorb and separate from other elements that coexist in the solution.
【0024】また本発明者等は、アニオン交換樹脂に吸
着された白金族元素を溶離回収するため、さらに鋭意な
検討を重ねた結果、次の方法を見いだした。すなわち、
処理液中からルテニウム,ロジウム,パラジウム等の白
金族元素を吸着させた後のイオン交換樹脂を、次いで、
チオ尿素(SC(NH2 )2 )またはアンモニア(NH
3 )含有水溶液と接触させ、イオン交換樹脂に吸着した
白金族元素を溶離回収する。Further, the inventors of the present invention have made further intensive studies to elute and recover the platinum group elements adsorbed on the anion exchange resin, and as a result, have found the following method. That is,
The ion exchange resin after adsorbing platinum group elements such as ruthenium, rhodium, and palladium from the treatment liquid,
Thiourea (SC (NH 2 ) 2 ) or ammonia (NH
3 ) Contact with the containing aqueous solution to elute and recover the platinum group element adsorbed on the ion exchange resin.
【0025】以下、本発明を、(1)イオン濃度調整工
程、(2)アニオンニトロ錯体生成工程、(3)吸着工
程、(4)溶離回収工程に分けてさらに詳細に説明す
る。The present invention will be described in more detail below by dividing it into (1) ion concentration adjusting step, (2) anion nitro complex forming step, (3) adsorption step, and (4) elution recovery step.
【0026】(1)イオン濃度調整工程 本発明では、まず使用済み核燃料の再処理工程で発生す
る廃液、使用済み核燃料の溶解残滓の硝酸溶解液などの
白金族元素を含有する硝酸溶液(以下「処理液」ともい
う。)の中の硝酸濃度を0.01〜2mol/lの範
囲、好ましくは、0.1〜1.5mol/lの範囲に調
整しておく。(1) Ion Concentration Adjusting Step In the present invention, first, a nitric acid solution containing a platinum group element such as a waste liquid generated in a reprocessing step of a spent nuclear fuel and a nitric acid solution of a dissolved residue of the spent nuclear fuel (hereinafter referred to as “ The concentration of nitric acid in "treatment liquid") is adjusted in the range of 0.01 to 2 mol / l, preferably 0.1 to 1.5 mol / l.
【0027】これらの溶液中の硝酸イオン濃度が2mo
l/l以上になると、溶液中に共存するU4+,U
O2 2+,Pu4+,Np4+ 等の金属イオンが溶液中に多量
に存在するNO3 -イオンとアニオン錯体を形成する。こ
れらのアニオン錯体はアニオン交換体に強い吸着性を呈
するため、白金族元素との分離が困難になる。The nitrate ion concentration in these solutions is 2 mo.
When it becomes 1 / l or more, U 4+ , U coexisting in the solution
Metal ions such as O 2 2+ , Pu 4+ , and Np 4+ form an anion complex with NO 3 − ions existing in a large amount in the solution. Since these anion complexes have strong adsorptivity to anion exchangers, it is difficult to separate them from platinum group elements.
【0028】また、溶液中の水素イオン濃度が2mol
/l以上になると、溶液中の多量なH+ が後ほど添加す
るNO2 -イオンと結合して亜硝酸分子を生成する。この
亜硝酸は熱や光などによって分解しやすく、その分解に
よって生じる酸化窒素ガスは次の吸着工程においてカラ
ム式吸着を行う際にカラム操作の妨害となる。The hydrogen ion concentration in the solution is 2 mol.
Above 1 / l, a large amount of H + in the solution combines with NO 2 − ions to be added later to generate nitrite molecules. This nitrous acid is easily decomposed by heat, light, etc., and the nitric oxide gas generated by the decomposition interferes with the column operation when performing column-type adsorption in the next adsorption step.
【0029】また、溶液中の水素イオン濃度が0.01
mol/l以下では、溶液中の白金族元素をはじめ多種
の金属元素のイオンが加水分解反応により水酸化物を形
成して沈澱し、後の吸着工程でのイオン交換体への吸着
性が低下してしまう。以上の理由により、本発明では処
理液中の硝酸濃度を0.01〜2mol/lの範囲に調
整する。なお、溶液中の硝酸濃度の調整は硝酸または純
水を添加することによって容易に行うことができ、ま
た、場合により公知の化学脱硝法や電解脱硝法によって
行うこともできる。The hydrogen ion concentration in the solution is 0.01
At mol / l or less, ions of various metal elements including platinum group elements in the solution form hydroxides by the hydrolysis reaction and precipitate, and the adsorptivity to the ion exchanger decreases in the subsequent adsorption step. Resulting in. For the above reasons, in the present invention, the nitric acid concentration in the treatment liquid is adjusted to the range of 0.01 to 2 mol / l. The nitric acid concentration in the solution can be easily adjusted by adding nitric acid or pure water, and in some cases, known chemical denitration method or electrolytic denitration method can be used.
【0030】(2)アニオンニトロ錯体生成工程 上記の硝酸濃度調整後の処理液に、NO2 -イオン含有試
薬を添加し、溶液中の白金族イオンのニトロ錯体を生成
させる。当然のことながら、NO2 -イオン含有試薬の添
加量は処理液中のルテニウム,ロジウム,パラジウムの
存在量に応じる必要がある。上記濃度の硝酸溶液中で
は、これらの金属の酸化状態はRu(III)、Rh(III
)、Pd(II)であり、それぞれのアニオンニトロ錯
体を生成させるには少なくともルテニウム,ロジウムに
は4倍モル量、パラジウムには3倍モル量が必要であ
る。なお、これらの金属ニトロ錯体の最大配位数はルテ
ニウム,ロジウムは6配位、パラジウムは4配位であ
る。[0030] (2) an anion nitro complexation step above treatment solution after nitric acid concentration adjustment, NO 2 - was added ion-containing reagents to produce a nitro complexes of platinum group ions in solution. As a matter of course, the addition amount of the NO 2 − ion-containing reagent needs to correspond to the existing amounts of ruthenium, rhodium, and palladium in the treatment liquid. In the nitric acid solution having the above concentration, the oxidation states of these metals are Ru (III) and Rh (III
) And Pd (II), and at least a 4-fold molar amount for ruthenium and rhodium and a 3-fold molar amount for palladium are required to form the respective anion nitro complexes. The maximum coordination number of these metal nitro complexes is 6 for ruthenium and rhodium, and 4 for palladium.
【0031】本発明者らの実験結果によれば、溶液中の
これらの金属の存在量に対して、最大配位数のニトロ錯
体の生成に必要な化学量論量の1〜4倍のNO2 -イオン
を添加することにより、ほぼ吸着分配係数の最大値を得
ることができる。これ以上のNO2 -イオンを添加する
と、溶液中の過剰なNO2 -イオンがアニオン交換樹脂に
競争吸着することとなり吸着分配係数は低下してしま
う。図1は上記のような吸着分配係数と溶液中のNO2 -
イオン濃度との関係を示しているものである。また、過
剰なNO2 -イオンの存在下では、上述したように、酸化
窒素ガスの発生による吸着操作への妨害も発生する。According to the results of the experiments conducted by the inventors of the present invention, the stoichiometric amount of NO required to form the maximum coordination number nitro complex is 1 to 4 times the NO amount with respect to the existing amount of these metals in the solution. By adding 2 - ions, the maximum value of the adsorption partition coefficient can be obtained. If more NO 2 − ions are added, excess NO 2 − ions in the solution will be competitively adsorbed on the anion exchange resin, and the adsorption distribution coefficient will be reduced. Figure 1 is NO adsorption distribution coefficient in solution as described above 2 -
It shows the relationship with the ion concentration. Further, in the presence of excess NO 2 − ions, as described above, the generation of nitric oxide gas also interferes with the adsorption operation.
【0032】なお、NO2 -イオン含有試薬として特に限
定する必要はないが、アニオン交換体に吸着性を持たず
安価であるアルカリ金属,アンモニウム,アルカリ土類
金属の亜硝酸塩を好ましく用いることができる。また、
処理液に対し適当な還元剤の添加または電解還元等の手
法を施すことによって、直接NO2 -イオンを生成させる
ことも可能である。[0032] Incidentally, NO 2 - is not particularly necessary to limit as ion-containing reagent, can be preferably used alkali metal is inexpensive without adsorption onto anion exchanger, ammonium, nitrite of an alkaline earth metal . Also,
It is also possible to directly generate NO 2 − ions by adding a suitable reducing agent to the treatment liquid or performing a technique such as electrolytic reduction.
【0033】(3)吸着工程 処理液調整工程で得られた溶液をアニオン交換樹脂と接
触させることにより、溶液中のルテニウム,ロジウム,
パラジウムのみが樹脂に吸着されて溶液相から樹脂相に
移行し溶液中の他の元素から分離される。なお、ルテニ
ウムは主にニトロシル・ニトロのアニオン錯体、ロジウ
ムとパラジウムはアニオンニトロ錯体の形で樹脂に交換
吸着される。(3) Adsorption step By contacting the solution obtained in the treatment solution adjusting step with an anion exchange resin, ruthenium, rhodium,
Only palladium is adsorbed by the resin, moves from the solution phase to the resin phase, and is separated from other elements in the solution. Note that ruthenium is mainly exchanged and adsorbed on the resin in the form of anion complex of nitrosyl / nitro, and rhodium and palladium are in the form of anion nitro complex.
【0034】吸着操作には公知のカラム式およびバッチ
式を好ましく利用することができる。すなわち、カラム
式では、イオン交換樹脂をカラムに詰めて処理液を通液
し、溶液中のルテニウム,ロジウム,パラジウムを樹脂
に吸着させる。バッチ式では、容器に処理液およびイオ
ン交換樹脂を入れて攪拌または振とうし、溶液中のルテ
ニウム,ロジウム,パラジウムを樹脂に吸着させる。使
用するイオン交換樹脂の形状は特に限定するものではな
く、通常工業的によく利用される粒径数十〜数百ミクロ
ン程度のマクロポア型,ゲル型または担体担持型の球状
樹脂粒を好ましく用いることができる。また、吸着温度
も特に限定することなく、通常工業的に容易に実現する
室温から80℃程度の範囲で良い。なお、温度を上げる
ことによって吸着速度をある程度促進することが可能で
ある。Known column type and batch type can be preferably utilized for the adsorption operation. That is, in the column type, the ion exchange resin is packed in a column, the treatment solution is passed through, and ruthenium, rhodium, and palladium in the solution are adsorbed on the resin. In the batch system, the treatment liquid and the ion exchange resin are put in a container and stirred or shaken to adsorb ruthenium, rhodium and palladium in the solution onto the resin. The shape of the ion exchange resin to be used is not particularly limited, and it is preferable to use spherical resin particles of macropore type, gel type or carrier-supporting type having a particle size of about several tens to several hundreds of microns which is usually used industrially. You can Also, the adsorption temperature is not particularly limited, and may be in the range of room temperature to 80 ° C. which is usually industrially easily realized. It is possible to accelerate the adsorption rate to some extent by raising the temperature.
【0035】(4)溶離回収工程 上記吸着工程を経てアニオン交換樹脂に吸着されたルテ
ニウム,ロジウム,パラジウムを溶離回収するために、
本発明者らは種々の溶離剤および溶離条件を鋭意検討
し、その結果、チオ尿素(SC(NH2)2)およびアン
モニア(NH3 )がこれらの白金族元素の極めて優れた
溶離剤であることを見いだした。(4) Elution recovery step In order to elute and recover ruthenium, rhodium and palladium adsorbed on the anion exchange resin through the adsorption step,
The present inventors diligently studied various eluents and elution conditions, and as a result, thiourea (SC (NH 2 ) 2 ) and ammonia (NH 3 ) are extremely excellent eluents for these platinum group elements. I found a thing.
【0036】これらの試薬は窒素原子の配位結合を通し
て上記白金族イオンと強い錯形成能力を有しMXn 2+、
MXn 3+(M=Ru,Rh,Pd、X=SC(NH2)2
またはNH3 、n=1〜6)といった安定なカチオン錯
体を形成する。このため、アニオン交換樹脂に吸着され
た白金族ニトロ錯体はこれらの溶離剤との配位子置換反
応により樹脂から溶離される。チオ尿素試薬は水溶性で
あり、これを水または希硝酸水溶液に溶かして0.1〜
数mol/lチオ尿素溶液として好ましく用いられる。
一方、NH3 溶離液としては市販アンモニア水を0.1
〜数mol/l程度に薄めて使えばよい。なお、溶離液
としてのこれらの試薬濃度は特に限定するものではな
い。一方、溶離剤の使用量は、当然のことながら上記白
金族元素の吸着量に応じる必要があり、本発明者らの検
討結果によれば白金族元素吸着量の2倍モル量以上、好
ましくは4倍モル量以上使用すれば吸着した白金族イオ
ンを完全に溶離することができる。These reagents have a strong complex-forming ability with the above platinum group ion through a coordinate bond of a nitrogen atom, MX n 2+ ,
MX n 3+ (M = Ru, Rh, Pd, X = SC (NH 2 ) 2
Alternatively, a stable cation complex such as NH 3 , n = 1 to 6) is formed. Therefore, the platinum group nitro complex adsorbed on the anion exchange resin is eluted from the resin by a ligand substitution reaction with these eluents. The thiourea reagent is water-soluble and can be dissolved in water or dilute nitric acid solution to
It is preferably used as a several mol / l thiourea solution.
On the other hand, as the NH 3 eluent, commercially available aqueous ammonia is used as 0.1
It may be used by diluting to about several mol / l. The concentrations of these reagents as the eluent are not particularly limited. On the other hand, as a matter of course, the amount of the eluent used needs to correspond to the amount of the platinum group element adsorbed, and according to the results of the study conducted by the present inventors, it is at least twice the molar amount of the platinum group element adsorbed. The adsorbed platinum group ion can be completely eluted by using a 4-fold molar amount or more.
【0037】なお、上記の溶離操作は吸着工程で記載し
たカラム式およびバッチ式と同様な方法で行うことがで
き、樹脂を溶離剤溶液と接触させることにより、樹脂に
吸着されたルテニウム,ロジウム,パラジウム各金属イ
オンが溶出し樹脂相から溶液相に移行して分離回収され
る。溶離操作の温度も吸着工程と同様に工業的に容易に
実現する室温から80℃程度の範囲で良い。The above-mentioned elution operation can be carried out in the same manner as in the column type and batch type described in the adsorption step. By contacting the resin with an eluent solution, ruthenium, rhodium, Palladium Each metal ion is eluted and transferred from the resin phase to the solution phase for separation and recovery. The temperature of the elution operation may be in the range of room temperature to about 80 ° C. which is industrially easily realized as in the adsorption step.
【0038】[0038]
【発明の実施の形態】以下、この発明の実施の一形態を
説明する。 実施の形態1.以下の実施の形態において、この発明に
よる白金族元素の分離回収方法を、使用済み核燃料の再
処理廃液を模擬した処理液に対して適用して分離回収試
験を行った一例を、試験手順に従って示す。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS One embodiment of the present invention will be described below. Embodiment 1. In the following embodiment, an example of performing a separation and recovery test by applying the method for separating and recovering a platinum group element according to the present invention to a treatment liquid simulating a reprocessing waste liquid of a spent nuclear fuel will be shown according to a test procedure. .
【0039】1.処理液調整 分離回収目的の白金族元素である、ルテニウム(R
u),ロジウム(Rh),パラジウム(Pd)の各硝酸
塩、および核分裂生成物の代表元素としてのストロンチ
ウム(Sr),ネオジム(Nd)の各硝酸塩を、0.1
mol/l硝酸水溶液に溶解して、これを使用済み核燃
料の模擬再処理廃液として分離試験用の処理液とし、こ
の処理液に亜硝酸塩としての亜硝酸ナトリウムを添加し
て、処理液の組成を以下のようにした(イオン濃度調整
工程,アニオンニトロ錯体生成工程)。 Ru 985.6mg/l Sr 783.4mg/l Rh 249.6mg/l Nd 1327.6mg/l Pd 796.1mg/l NO3 - 約0.2mol/l NaNO2 1.0mol/l H+ 約0.2mol/l なお、以下の分離試験でカラムに導入した処理液の総量
は30mlである。1. Preparation of treatment liquid Ruthenium (R
u), rhodium (Rh) and palladium (Pd) nitrates, and strontium (Sr) and neodymium (Nd) nitrates as representative elements of fission products,
It is dissolved in a mol / l nitric acid aqueous solution, and this is used as a simulated reprocessing waste liquid of spent nuclear fuel as a treatment liquid for a separation test. Sodium nitrite as a nitrite is added to this treatment liquid to determine the composition of the treatment liquid. The procedure was as follows (ion concentration adjusting step, anion nitro complex forming step). Ru 985.6mg / l Sr 783.4mg / l Rh 249.6mg / l Nd 1327.6mg / l Pd 796.1mg / l NO 3 - about 0.2mol / l NaNO 2 1.0mol / l H + about 0 0.2 mol / l The total amount of the treatment liquid introduced into the column in the following separation test was 30 ml.
【0040】2.カラム準備 白金族元素の吸着および溶離・回収はカラム式により行
った。カラムとしては内径1cm、長さ30cmのガラ
スカラムを用い、このカラム中に、アニオン交換樹脂と
して交換容量3.4meq/g−resinの石英担持
型ベンズイミダゾル基アニオン交換樹脂を高さ25cm
まで充填し、カラム全体を60℃の一定温度に保温し
た。2. Column preparation Adsorption, elution and recovery of platinum group elements were performed by a column method. A glass column having an inner diameter of 1 cm and a length of 30 cm was used as a column, and a quartz-supporting benzimidazole group anion exchange resin having an exchange capacity of 3.4 meq / g-resin was used as an anion exchange resin in the column with a height of 25 cm.
And the whole column was kept at a constant temperature of 60 ° C.
【0041】3.吸着 上記カラムの上端より、上記処理液を送液ポンプにより
5ml/minの流速で供給して、アニオン交換樹脂へ
の白金族元素の吸着を行った(吸着工程)。3. Adsorption The treatment liquid was supplied from the upper end of the column by a liquid feed pump at a flow rate of 5 ml / min to adsorb the platinum group element on the anion exchange resin (adsorption step).
【0042】4.カラム洗浄 続いて、上記カラムに濃度0.1mol/lの硝酸水溶
液50mlを上記と同様な操作により通液して、アニオ
ン交換樹脂の隙間およびカラム内壁の洗浄を行った。4. Column Washing Subsequently, 50 ml of a nitric acid aqueous solution having a concentration of 0.1 mol / l was passed through the column in the same manner as above to wash the gap between the anion exchange resin and the inner wall of the column.
【0043】5.溶離・回収 次いで、0.5mol/lチオ尿素含有の0.1mol
/l硝酸溶液50mlを上記と同様な操作によりカラム
に供給した(溶離回収工程)。5. Elution and recovery Next, 0.1 mol containing 0.5 mol / l thiourea
50 ml of a 1 / l nitric acid solution was supplied to the column by the same operation as above (elution recovery step).
【0044】6.採取・分析 カラムに通液した期間にカラム下端から流出した溶液
を、フラクションコレクタにより10mlずつ採取して
ゆき、各フラクション採取液中の金属濃度を、ICP
(誘導結合高周波プラズマ)発光分析により定量分析
し、流出液量と流出液中の各金属濃度との関係を求め
た。その結果を図2に示す。6. Sampling / Analysis The solution flowing out from the lower end of the column during the period of passing through the column was collected by a fraction collector by 10 ml, and the metal concentration in each fraction collected liquid was measured by ICP.
(Inductively coupled high frequency plasma) Quantitative analysis was performed by emission analysis to determine the relationship between the amount of effluent and the concentration of each metal in the effluent. The result is shown in FIG.
【0045】図2に示したように、処理液中のストロン
チウムおよびネオジムはアニオン交換樹脂に吸着され
ず、供給された処理液およびそれに続く洗浄液とともに
流出し、一方、ルテニウム,ロジウム,およびパラジウ
ムの各白金族元素は、吸着工程においてアニオン交換樹
脂に強く吸着され、溶離・回収工程において供給された
チオ尿素溶離液により有効に溶離され、ストロンチウ
ム,ネオジムと良好に分離された。As shown in FIG. 2, strontium and neodymium in the treatment liquid are not adsorbed by the anion exchange resin and flow out together with the supplied treatment liquid and the subsequent cleaning liquid, while ruthenium, rhodium, and palladium are discharged. The platinum group element was strongly adsorbed on the anion exchange resin in the adsorption step, and was effectively eluted by the thiourea eluent supplied in the elution / recovery step, and was well separated from strontium and neodymium.
【0046】以上の白金族元素の分離回収方法による、
模擬再処理廃液からの白金族元素の回収率は、ルテニウ
ム99.2%,ロジウム98.1%,パラジウム99.
6%であった。According to the above method for separating and recovering platinum group elements,
The recovery rates of platinum group elements from the simulated reprocessing waste liquid were ruthenium 99.2%, rhodium 98.1%, and palladium 99.%.
It was 6%.
【0047】以上のように、この実施の形態1によれ
ば、使用済み核燃料の再処理廃液等の白金族元素を含有
する溶液から、白金族元素を高収率、高純度で分離回収
することが可能であり、このような方法を用いることに
より、希少な白金族元素をリサイクルして安定供給を確
保することが可能となるとともに、再処理工場廃棄物の
処理処分プロセス性能の向上を図り、廃液の放射能レベ
ルを低減することが可能となる。As described above, according to the first embodiment, the platinum group element can be separated and recovered in a high yield and a high purity from the solution containing the platinum group element such as the spent reprocessing waste liquid of the spent nuclear fuel. By using such a method, it is possible to recycle the rare platinum group elements and secure a stable supply, and at the same time, improve the processing and disposal process performance of the reprocessing plant waste, It is possible to reduce the radioactivity level of the waste liquid.
【0048】[0048]
【発明の効果】以上のように、請求項1記載の発明によ
れば、ルテニウム,ロジウム,パラジウム等の白金族元
素を含有する硝酸溶液に、亜硝酸あるいは亜硝酸塩を添
加して前記白金族元素のアニオンニトロ錯体を生成さ
せ、次にこの硝酸溶液をアニオン交換樹脂と接触させて
溶液中の前記白金族元素を前記アニオン交換樹脂に選択
的に吸着させるように構成したので、白金族元素を含有
する溶液から白金族元素を陰イオンの形にしてアニオン
交換樹脂に吸着させて分離回収することが可能となり、
希少金属原料である白金族元素をリサイクルして安定供
給を確保することが可能となる効果がある。As described above, according to the invention of claim 1, the nitric acid solution or the nitrite salt is added to the nitric acid solution containing the platinum group element such as ruthenium, rhodium and palladium, and the platinum group element is added. Of the platinum group element in the solution by contacting the nitric acid solution with the anion exchange resin to selectively adsorb the platinum group element in the solution. It becomes possible to separate and collect the platinum group element from the solution in the form of anion by adsorbing it on the anion exchange resin,
There is an effect that the platinum group element, which is a rare metal raw material, can be recycled to secure a stable supply.
【0049】請求項2記載の発明によれば、白金族元素
を吸着させたアニオン交換樹脂を、チオ尿素,アンモニ
ア等の錯化剤を含有する水溶液と接触させて、前記アニ
オン交換樹脂に吸着した前記白金族元素を溶離回収する
ように構成したので、白金族元素を吸着させたアニオン
交換樹脂から白金族元素を有効に溶離回収することがで
き、特に、錯化剤としてチオ尿素またはアンモニアを用
いた場合には極めて有効に溶離回収することが可能とな
る。従って、白金族元素を含有する溶液から白金族元素
を高収率で分離回収することが可能となり、希少金属原
料である白金族元素をリサイクルして安定供給を確保す
ることが可能となる効果がある。According to the second aspect of the present invention, the anion exchange resin having the platinum group element adsorbed thereon is brought into contact with an aqueous solution containing a complexing agent such as thiourea or ammonia and adsorbed on the anion exchange resin. Since the platinum group element is configured to be eluted and recovered, the platinum group element can be effectively eluted and recovered from the anion exchange resin having the platinum group element adsorbed, and particularly, thiourea or ammonia is used as a complexing agent. In such a case, the elution and recovery can be performed very effectively. Therefore, it becomes possible to separate and recover the platinum group element from the solution containing the platinum group element in a high yield, and it is possible to recycle the platinum group element which is a rare metal raw material and secure a stable supply. is there.
【0050】請求項3記載の発明によれば、アニオンニ
トロ錯体生成工程において亜硝酸あるいは亜硝酸塩を添
加する前に、硝酸溶液中の硝酸イオン濃度を2mol/
l以下、水素イオン濃度を0.01〜2mol/lの範
囲内に調整するように構成したので、硝酸溶液中に共存
する他の金属元素のイオンと区別して白金族元素のアニ
オンニトロ錯体のみをアニオン交換樹脂に吸着させて白
金族元素を選択的に分離回収することが可能となり、亜
硝酸分子の生成・分解により生じる酸化窒素ガスによる
カラム式吸着の際のカラム操作妨害を防止することがで
き、また、硝酸溶液中の白金族元素が加水分解反応によ
り水酸化物を形成して沈澱することによるアニオン交換
樹脂への吸着性低下を防止することができ、以上によ
り、白金族元素を高収率、高純度で分離回収することが
可能となり、希少金属原料である白金族元素をリサイク
ルして安定供給を確保することが可能となる効果があ
る。According to the invention of claim 3, before the addition of nitrous acid or nitrite in the step of forming an anion nitro complex, the concentration of nitrate ion in the nitric acid solution is set to 2 mol / mol.
Since it is configured to adjust the hydrogen ion concentration within the range of 0.01 to 2 mol / l, the anion nitro complex of the platinum group element is distinguished from the ions of other metal elements coexisting in the nitric acid solution. It is possible to selectively separate and collect platinum group elements by adsorbing on an anion exchange resin, and prevent column operation interference during column adsorption by nitric oxide gas generated by the generation and decomposition of nitrite molecules. In addition, it is possible to prevent the platinum group element in the nitric acid solution from deteriorating the adsorptivity to the anion exchange resin due to the formation and precipitation of the hydroxide due to the hydrolysis reaction. Rate and high purity can be separated and recovered, and the platinum group element, which is a rare metal raw material, can be recycled to ensure a stable supply.
【0051】請求項4記載の発明によれば、使用済み核
燃料の再処理工程で発生する廃液、または使用済み核燃
料の溶解残滓の硝酸溶解液を白金族元素を含有する硝酸
溶液として、これに請求項1から請求項3のうちのいず
れか1項記載の発明を適用するように構成したので、使
用済み核燃料の再処理工程で発生する廃液や使用済み核
燃料の溶解残滓から白金族元素を高収率、高純度で分離
回収することが可能となり、希少金属原料である白金族
元素の安定供給を確保することができるとともに、再処
理工場廃棄物の処理処分プロセス性能の向上を図り、廃
液の放射能レベルを低減することができる効果がある。According to the fourth aspect of the present invention, the waste liquid generated in the reprocessing step of the spent nuclear fuel or the nitric acid solution of the dissolved residue of the spent nuclear fuel is treated as a nitric acid solution containing a platinum group element, Since the invention according to any one of claims 1 to 3 is applied, a high yield of platinum group elements can be obtained from the waste liquid generated in the reprocessing step of the spent nuclear fuel and the dissolved residue of the spent nuclear fuel. Rate and high purity, it is possible to separate and recover, and it is possible to secure a stable supply of platinum group elements that are rare metal raw materials, improve the processing and disposal process performance of reprocessing plant waste, and radiate waste liquid. There is an effect that the performance level can be reduced.
【図1】アニオン交換樹脂へのルテニウム,ロジウム,
パラジウム各白金族元素の吸着分配係数の亜硝酸イオン
濃度依存性の測定結果を示すグラフ図である。FIG. 1 Ruthenium, rhodium, and anion exchange resin
It is a graph which shows the measurement result of the nitrite ion concentration dependence of the adsorption distribution coefficient of each palladium platinum group element.
【図2】この発明の実施の形態1による使用済み核燃料
の模擬再処理廃液のカラム分離試験結果を示すグラフ図
である。FIG. 2 is a graph showing a column separation test result of a simulated reprocessing waste liquid of spent nuclear fuel according to Embodiment 1 of the present invention.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 G21F 9/06 581 G21F 9/06 581J ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location G21F 9/06 581 G21F 9/06 581J
Claims (4)
白金族元素を含有する硝酸溶液に、亜硝酸あるいは亜硝
酸塩を添加して前記白金族元素のアニオンニトロ錯体を
生成させるアニオンニトロ錯体生成工程と、前記アニオ
ンニトロ錯体生成工程を経た硝酸溶液をアニオン交換樹
脂と接触させ、前記硝酸溶液中の前記白金族元素を前記
アニオン交換樹脂に選択的に吸着させる吸着工程とを備
えたことを特徴とする白金族元素の分離回収方法。1. An anion nitro complex producing step of producing an anion nitro complex of the platinum group element by adding nitrous acid or nitrite to a nitric acid solution containing a platinum group element such as ruthenium, rhodium or palladium, An adsorption step of bringing the nitric acid solution that has undergone the anion nitro complex formation step into contact with an anion exchange resin, and selectively adsorbing the platinum group element in the nitric acid solution onto the anion exchange resin. Method for separating and recovering elements.
たアニオン交換樹脂を、チオ尿素,アンモニア等の錯化
剤を含有する水溶液と接触させ、前記アニオン交換樹脂
に吸着した前記白金族元素を溶離回収する溶離回収工程
を前記吸着工程の後に備えたことを特徴とする請求項1
記載の白金族元素の分離回収方法。2. The anion exchange resin having adsorbed the platinum group element in the adsorption step is brought into contact with an aqueous solution containing a complexing agent such as thiourea or ammonia to elute the platinum group element adsorbed on the anion exchange resin. An elution recovery step for recovery is provided after the adsorption step.
A method for separating and recovering the platinum group element described.
硝酸あるいは亜硝酸塩を添加する前に、硝酸溶液中の硝
酸イオン濃度を2mol/l以下、水素イオン濃度を
0.01〜2mol/lの範囲内に調整するイオン濃度
調整工程を備えたことを特徴とする請求項1または請求
項2記載の白金族元素の分離回収方法。3. Before adding nitrous acid or nitrite in the step of forming an anion nitro complex, the nitric acid solution has a nitric acid concentration of 2 mol / l or less and a hydrogen ion concentration of 0.01 to 2 mol / l. The method for separating and recovering a platinum group element according to claim 1 or 2, further comprising an ion concentration adjusting step for adjusting.
済み核燃料の再処理工程で発生する廃液、または使用済
み核燃料の溶解残滓の硝酸溶解液であることを特徴とす
る請求項1から請求項3のうちのいずれか1項記載の白
金族元素の分離回収方法。4. A nitric acid solution containing a platinum group element is a waste liquid generated in a reprocessing step of a spent nuclear fuel or a nitric acid solution of a dissolved residue of the spent nuclear fuel. Item 4. A method for separating and recovering a platinum group element according to any one of Item 3.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP01037996A JP3611658B2 (en) | 1996-01-24 | 1996-01-24 | Methods for separating and recovering platinum group elements |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP01037996A JP3611658B2 (en) | 1996-01-24 | 1996-01-24 | Methods for separating and recovering platinum group elements |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH09203792A true JPH09203792A (en) | 1997-08-05 |
| JP3611658B2 JP3611658B2 (en) | 2005-01-19 |
Family
ID=11748506
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP01037996A Expired - Fee Related JP3611658B2 (en) | 1996-01-24 | 1996-01-24 | Methods for separating and recovering platinum group elements |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3611658B2 (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7291202B2 (en) | 2003-09-26 | 2007-11-06 | Sumitomo Metal Mining Co., Ltd. | Process for mutual separation of platinum group metals |
| JP2014055331A (en) * | 2012-09-13 | 2014-03-27 | Sanyo Shoten:Kk | Method for separating/recovering platinum group element |
| RU2685618C2 (en) * | 2014-06-18 | 2019-04-22 | Джонсон Мэтти Паблик Лимитед Компани | Separation of metals |
| CN113213487A (en) * | 2021-04-20 | 2021-08-06 | 云龙县铂翠贵金属科技有限公司 | Comprehensive utilization method of vinyl silane high-boiling residues |
| WO2023170354A1 (en) * | 2022-03-10 | 2023-09-14 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Process for the purification of ruthenium with respect to technetium and metal impurities in an aqueous nitric acid solution |
| JP7808230B1 (en) * | 2025-09-01 | 2026-01-28 | 松田産業株式会社 | Palladium recovery method |
-
1996
- 1996-01-24 JP JP01037996A patent/JP3611658B2/en not_active Expired - Fee Related
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7291202B2 (en) | 2003-09-26 | 2007-11-06 | Sumitomo Metal Mining Co., Ltd. | Process for mutual separation of platinum group metals |
| JP2014055331A (en) * | 2012-09-13 | 2014-03-27 | Sanyo Shoten:Kk | Method for separating/recovering platinum group element |
| RU2685618C2 (en) * | 2014-06-18 | 2019-04-22 | Джонсон Мэтти Паблик Лимитед Компани | Separation of metals |
| US10513752B2 (en) | 2014-06-18 | 2019-12-24 | Johnson Matthey Public Limited Company | Interseparation of metals |
| CN113213487A (en) * | 2021-04-20 | 2021-08-06 | 云龙县铂翠贵金属科技有限公司 | Comprehensive utilization method of vinyl silane high-boiling residues |
| WO2023170354A1 (en) * | 2022-03-10 | 2023-09-14 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | Process for the purification of ruthenium with respect to technetium and metal impurities in an aqueous nitric acid solution |
| FR3133390A1 (en) * | 2022-03-10 | 2023-09-15 | Commissariat A L'energie Atomique Et Aux Energies Alternatives | PROCESS FOR PURIFYING RUTHENIUM AGAINST TECHNETIUM AND METALLIC IMPURITIES IN AQUEOUS NITRIC ACID SOLUTION |
| JP7808230B1 (en) * | 2025-09-01 | 2026-01-28 | 松田産業株式会社 | Palladium recovery method |
Also Published As
| Publication number | Publication date |
|---|---|
| JP3611658B2 (en) | 2005-01-19 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Swain et al. | Separation and recovery of ruthenium: a review | |
| JP3677013B2 (en) | Method for separating and recovering elements from radioactive liquid waste | |
| US5372794A (en) | Process for the separation of certain elements from aqueous solutions resulting from the reprocessing of spent nuclear fuels | |
| Rizvi et al. | Recovery of fission product palladium from acidic high level waste solutions | |
| Poineau et al. | Technetium chemistry in the fuel cycle: combining basic and applied studies | |
| CN102458649B (en) | New adsorbent, Its Preparation Method And Use | |
| US5508010A (en) | Method of separating fission molybdenum | |
| Wu et al. | Adsorption and separation behavior of palladium (II) from simulated high-level liquid waste using a novel silica-based adsorbents | |
| JP3611658B2 (en) | Methods for separating and recovering platinum group elements | |
| JP3366485B2 (en) | Method for separation and recovery of platinum group elements and technetium | |
| Pospiech | Studies on platinum recovery from solutions after leaching of spent catalysts by solvent extraction | |
| Jarvinen et al. | Separation of pertechnetate from uranium in a simulated UREX processing solution using anion exchange extraction chromatography | |
| Pokhitonov et al. | Palladium in irradiated fuel. Are there any prospects for recovery and application? | |
| Lee et al. | Ion exchange characteristics of palladium and rhodium from a simulated radioactive liquid waste | |
| Paul et al. | A sulfur-based adsorbent for the removal of palladium from aqueous waste: Comprehensive study on the preparation, characterization, adsorption and breakthrough modeling | |
| JP2003215292A (en) | Method for separating and recovering americium, curium and rare earth elements | |
| Lee et al. | Ion exchange characteristics of palladium from nitric acid solution by anion exchangers | |
| Lee et al. | Ion exchange characteristics of rhodium and ruthenium from a simulated radioactive liquid waste | |
| JP3889322B2 (en) | Separation of americium and curium from heavy rare earth elements | |
| Scadden et al. | The radiochemistry of molybdenum | |
| Lee et al. | Precipitation characteristics of palladium from a simulated radioactive liquid waste by ascorbic acid | |
| RU2639884C1 (en) | Method of palladium extraction from high-active rafinat of extraction cycle of refined nuclear fuel processing (versions) | |
| JP2001074886A (en) | Process for separation recovery of plutonium | |
| Nemati et al. | Separation of zirconium and hafnium from chloride solution using strongly basic anion resins | |
| JPS6293320A (en) | Method for recovering technetium |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20040210 |
|
| A521 | Written amendment |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20040323 |
|
| TRDD | Decision of grant or rejection written | ||
| A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20040921 |
|
| A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20041020 |
|
| R150 | Certificate of patent or registration of utility model |
Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
| LAPS | Cancellation because of no payment of annual fees |