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JPH0470243B2 - - Google Patents
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JPH0470243B2 - - Google Patents

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Publication number
JPH0470243B2
JPH0470243B2 JP20556684A JP20556684A JPH0470243B2 JP H0470243 B2 JPH0470243 B2 JP H0470243B2 JP 20556684 A JP20556684 A JP 20556684A JP 20556684 A JP20556684 A JP 20556684A JP H0470243 B2 JPH0470243 B2 JP H0470243B2
Authority
JP
Japan
Prior art keywords
degraded
sulfuric acid
fluidized bed
bed reactor
recovering
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
Application number
JP20556684A
Other languages
Japanese (ja)
Other versions
JPS6186402A (en
Inventor
Nobuyuki Sasao
Akira Tanaka
Akio Umemura
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Doryokuro Kakunenryo Kaihatsu Jigyodan
Mitsubishi Materials Corp
Original Assignee
Doryokuro Kakunenryo Kaihatsu Jigyodan
Mitsubishi Materials Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Doryokuro Kakunenryo Kaihatsu Jigyodan, Mitsubishi Materials Corp filed Critical Doryokuro Kakunenryo Kaihatsu Jigyodan
Priority to JP20556684A priority Critical patent/JPS6186402A/en
Publication of JPS6186402A publication Critical patent/JPS6186402A/en
Publication of JPH0470243B2 publication Critical patent/JPH0470243B2/ja
Granted legal-status Critical Current

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  • Inorganic Compounds Of Heavy Metals (AREA)

Description

【発明の詳細な説明】 技術分野 本発明はウラン濃縮工場で天然ウランあるいは
回収ウランから製造されたUF6を原料として235
を濃縮する際に多量に残留する235濃度の低い劣
化UF6から無水フツ酸を回収再利用する方法に関
する。
[Detailed Description of the Invention] Technical Field The present invention uses UF 6 produced from natural uranium or recovered uranium in a uranium enrichment plant as a raw material to
This invention relates to a method for recovering and reusing hydrofluoric anhydride from degraded UF 6 with a low concentration of 235 that remains in large amounts when concentrating UF6.

従来技術とその問題点 ウラン濃縮工場において残留する劣化UF6の量
は原料UF6の90%近くに達する。この劣化ウラン
は、これまであらゆる用途の可能性が検討された
にもかかわらず、その発生量の多くを振り向けら
れるような用途はなく、大部分が単に貯蔵されて
いる現状である。
Conventional technology and its problems The amount of degraded UF 6 remaining in uranium enrichment plants reaches nearly 90% of the raw material UF 6 . Although all sorts of possible uses for this depleted uranium have been considered, there is currently no use for much of the generated amount, and the majority of it is simply stored.

商業用ウラン濃縮工場の長い運転経験を持つ欧
米でも排出される大量の劣化UF6はシリンダーに
充填して貯蔵しており、その処置に苦慮してい
る。我国においてもウラン濃縮工場の開発が進む
につれて劣化UF6の貯蔵量は増大しつつあり、や
がて商業用ウラン濃縮工場が建設されるようにな
るとその量が膨大なものになることは明らかであ
る。
Even in Europe and the United States, which have long experience operating commercial uranium enrichment plants, large amounts of degraded UF 6 are stored in cylinders, and they are having trouble dealing with it. In Japan, as the development of uranium enrichment plants progresses, the amount of degraded UF 6 stored is increasing, and it is clear that the amount will become enormous if commercial uranium enrichment plants are built.

劣化UF6は現在1基当り数トンないし10トン程
度の鋼製のシリンダーに充填されて貯蔵されてい
るが、用途のないこの物質は殆んど永久的に貯蔵
されねばならない。UF6は著しい腐食性を揺する
化学的に不安定な揮発しやすい物質であるので、
これの大量貯蔵は容器の長期健全性、災害時の安
全性、核物質防護、地域住民の感情等極めて重大
な問題を内蔵している。このような管理面の問題
の他に、UF6の形態で貯蔵すると膨大な量のフツ
素資源の死蔵となるという資源的経済的な欠点も
ある。
Degraded UF 6 is currently stored in steel cylinders weighing between several and 10 tons each, but this substance, which has no use, must be stored almost permanently. Since UF 6 is a chemically unstable volatile substance that exhibits significant corrosive properties,
Storing large amounts of this material has extremely serious problems, including the long-term integrity of the containers, safety in the event of a disaster, protection of nuclear materials, and the sentiments of local residents. In addition to these management problems, there is also the resource-economic drawback that storing UF 6 in the form of fluorine leaves a huge amount of unused fluorine resources.

このような背景から劣化UF6を化学的に安全な
形態で貯蔵すると共にフツ素分を回収して有効活
用できる方法の確立が望まれている。
Against this background, it is desired to establish a method that can store degraded UF 6 in a chemically safe form and recover and effectively utilize the fluorine content.

劣化ウランの貯蔵形態は、ウラン化合物中それ
自身最も安定であり、かつフツ素分を回収すると
いう観点からU3O8が最も好ましい。UF6をU3O8
に変換する方法には湿式法と乾式法がある。湿式
法はUF6を液相反応で加水分解してウラニルイオ
ン含有液を得、これにアンモニアを加えて重ウラ
ン酸アンモニウムを沈殿させるか、あるいは該溶
液に過酸化水素を加えて過酸化ウランを沈殿さ
せ、これ等の沈殿物を分別、乾燥したのち熱分解
してU3O8を得るものである。これに対して乾式
法は例えばUF6に水蒸気を作用させて気相反応に
よつてUO2F2を得、さらにこれに水蒸気を作用
させてU3O8を得るものである。
The most preferable storage form for depleted uranium is U 3 O 8 , which is the most stable of all uranium compounds and from the viewpoint of recovering the fluorine content. UF 6 U 3 O 8
There are wet methods and dry methods for converting. In the wet method, UF 6 is hydrolyzed in a liquid phase reaction to obtain a uranyl ion-containing solution, and ammonia is added to this to precipitate ammonium deuterate, or hydrogen peroxide is added to the solution to precipitate uranium peroxide. U 3 O 8 is obtained by precipitating, separating and drying these precipitates, and then thermally decomposing them. On the other hand, in the dry method, for example, UO 2 F 2 is obtained by a gas phase reaction by reacting steam with UF 6 , and U 3 O 8 is obtained by further reacting with steam.

湿式法は工程数が多く、さらに試薬を多量に用
いるので二次廃棄物の発生が多く、経費が大きい
乾式法は製造工程が単純であり、試薬を殆んど用
いないことから二次廃棄物量が少なく安価な大量
処理に向いている。
The wet method has many steps and uses a large amount of reagents, so it generates a lot of secondary waste, whereas the dry method has a simple manufacturing process and uses almost no reagents, so it generates a lot of secondary waste. It is suitable for low-cost, large-scale processing.

また乾式法によればフツ素分を希HFとして容
易に回収できるという利点もある。
The dry method also has the advantage that the fluorine content can be easily recovered as dilute HF.

副生する希HFは通常一般産業界で利用される
化学薬品であるが、我国の現状では原子力施設で
発生する希HFは国民感情として一般産業界には
受け入れられない。従つてこれを廃棄物化せずに
フツ素分の有効利用を図るためには原子力施設内
での再循環使用が必須であり、その場合フツ素分
はウラン濃縮の原料であるUF6の製造工場へ再循
環できるもの、即ち無水HFの形で回収されなけ
ればならない。またその処理法は二次廃棄物の発
生が少なく大量処理が安価にできる必要がある。
The by-product rare HF is a chemical that is normally used in general industry, but under the current situation in Japan, rare HF generated at nuclear facilities is not accepted by general industry as a national sentiment. Therefore, in order to make effective use of the fluorine content without turning it into waste, it is essential to recycle it within nuclear facilities . must be recovered in the form of anhydrous HF, which can be recycled to In addition, the treatment method must generate less secondary waste and be able to process large quantities at low cost.

希HFから無水HFを回収する方法として、共
沸組成以上の高濃度の希HFを蒸留する方法があ
るが、共沸組成の希HFが残留するため好ましく
ない。この他に、蒸留と電気透析を組合せた方
法、希HFに有機物を添加した蒸留法などがある
が、希HFに硫酸を添加する硫酸抽出蒸留法が無
水フツ酸の純度を高められ、かつ二次廃棄物量を
少なくでき安価な大量処理に適している。
As a method for recovering anhydrous HF from dilute HF, there is a method of distilling dilute HF with a high concentration higher than the azeotropic composition, but this is not preferred because dilute HF with the azeotropic composition remains. Other methods include a combination of distillation and electrodialysis, and a distillation method in which organic matter is added to dilute HF, but the sulfuric acid extractive distillation method, in which sulfuric acid is added to dilute HF, increases the purity of hydrofluoric anhydride and It is suitable for low-cost mass processing because it can reduce the amount of waste.

以上のような従来技術の状況のもとに、本発明
者等は劣化UF6を乾式法によりU3O8に変換し、
同時に副生する希HFを硫酸蒸留法によつて無水
HFとして回収することによつて問題が解決され
ることを見出した。
Under the circumstances of the prior art as described above, the present inventors converted degraded UF 6 to U 3 O 8 by a dry method,
At the same time, the by-product dilute HF is dehydrated by sulfuric acid distillation method.
It has been found that the problem can be solved by recovering it as HF.

今日までのところ廃劣化UF6が乾式気相法によ
つてU3O8に変換されて貯蔵され、同時に副生す
るHFを無水HFの形で回収する処理方式は知ら
れていない。
To date, there is no known treatment method in which waste degraded UF 6 is converted into U 3 O 8 by a dry gas phase method and stored, and at the same time, by-product HF is recovered in the form of anhydrous HF.

発明の構成 即ち、本発明によれば劣化UF6を乾式気相反応
法によつてU3O8に変換し、同時に副生する希HF
を硫酸抽出蒸留法によつて無水HFとして回収す
ることからなる劣化UF6の処理方法が提供され
る。
Structure of the Invention That is, according to the present invention, degraded UF 6 is converted to U 3 O 8 by a dry gas phase reaction method, and at the same time diluted HF as a by-product is converted into U 3 O 8 .
A method for treating degraded UF 6 is provided, which comprises recovering UF 6 as anhydrous HF by a sulfuric acid extractive distillation method.

UF6の乾式法によるU3O8への変換は、流動層
反応装置、ロータリーキルン、スクルーコンベア
ーを備えた反応管等によつて実施することができ
るが、流動層反応装置を用いて行なうのが有利で
ある。この装置によると、貯蔵に適する高密度の
U3O8粉末が得られ、更に、高濃度の希HFが副生
し、無水HFへの処理効率が高められ、同時に二
次廃棄物の発生量を低く抑えられるからである。
Conversion of UF 6 to U 3 O 8 by a dry method can be carried out using a fluidized bed reactor, a rotary kiln, a reaction tube equipped with a screw conveyor, etc.; is advantageous. According to this device, high-density storage suitable for storage
This is because U 3 O 8 powder is obtained, and high-concentration dilute HF is produced as a by-product, increasing the efficiency of processing into anhydrous HF, and at the same time suppressing the amount of secondary waste generated.

実施態様 本発明は具体的に例えば次のように実施され
る。
Embodiment The present invention is specifically carried out, for example, as follows.

添付図面は廃劣化UF6のU3O8への変換を流動
層反応装置を用いて気相反応によつて行ない、こ
れと組合せて硫酸抽出蒸留法により無水HFを得
る方法に使用するプラントの1例の概念を示す。
The attached drawing shows a plant used for converting waste degraded UF 6 into U 3 O 8 by gas phase reaction using a fluidized bed reactor, and in combination with this to obtain anhydrous HF by sulfuric acid extractive distillation method. An example concept is shown.

廃劣化UF6は気化器1で気化され、流動層反応
炉2内の好適位置に設けたノズルにより炉内に導
入される。同時に反応ガスおよび流動化ガスとし
ての水蒸気が導管11より炉の底部から噴射導入
される。ここでUF6と水蒸気の気相反応が生起し
UO2F2の粒子を生じ流動層が形成される。
The waste degraded UF 6 is vaporized in a vaporizer 1 and introduced into the fluidized bed reactor 2 through a nozzle provided at a suitable position within the reactor. At the same time, water vapor as a reaction gas and a fluidizing gas is injected into the furnace from the bottom through a conduit 11. Here, a gas phase reaction between UF 6 and water vapor occurs.
A fluidized bed is formed, producing particles of UO 2 F 2 .

この場合のUO2F2粒子の形成は最初に生じた
微粒子の表面へのコーテイング造粒機構によるも
ので本法の目的である貯蔵に適した高密度のU3
O8を得るのに非常に適する。
In this case, the formation of UO 2 F 2 particles is due to the coating granulation mechanism on the surface of the initially generated fine particles, which is the purpose of this method to form high-density U 3 particles suitable for storage.
Very suitable for obtaining O8 .

生成したUO2F2粒子は流動層の上部からオー
バーフローによつて炉外に排出され第2流動層反
応炉3に送られ、その次に設けられた第3流動層
反応炉4の排出ガスであつて第2流動層反応炉3
の反応ガス兼流動化ガスとしてその底部に導入さ
れるもののなかに多量に含まれる水蒸気によつて
U3O8に転化する。このU3O8は前記同様オーバー
フローにより第3流動層反応炉4に送られ、ここ
で導管12から導入される水蒸気による最終的な
脱F処理が行われ、製品として容器5に受容され
る。
The generated UO 2 F 2 particles are discharged from the upper part of the fluidized bed by overflow and sent to the second fluidized bed reactor 3, and then in the exhaust gas of the third fluidized bed reactor 4 installed. Atte 2nd fluidized bed reactor 3
Due to the large amount of water vapor contained in the reactant gas and fluidizing gas introduced at the bottom of the
Converts to U 3 O 8 . This U 3 O 8 is sent to the third fluidized bed reactor 4 by overflow as described above, where it undergoes a final deF treatment using steam introduced from the conduit 12, and is received in the container 5 as a product.

流動層反応炉2,3から排出される副生HFは
合して凝縮器6に集められ高濃度の希HFとして
回収されるが、これは抽出蒸留塔7に送られる。
抽出蒸留塔7へは導管14により硫酸が供給さ
れ、抽出蒸留により塔頂より無水HFが回収さ
れ、凝縮器8で液化され容器9に受容される。塔
底からは希硫酸が回収されるが、これは導管13
により、硫酸濃縮塔10に送られ、蒸発した水分
は凝縮器15で復水され廃水処理系へ送られる。
これが唯一の二次廃棄物である。濃縮硫酸は塔底
から排出され抽出蒸留塔へ再循環される。
By-product HF discharged from the fluidized bed reactors 2 and 3 is collected together in a condenser 6 and recovered as highly concentrated dilute HF, which is sent to an extractive distillation column 7.
Sulfuric acid is supplied to the extractive distillation column 7 through a conduit 14, and anhydrous HF is recovered from the top of the column by extractive distillation, liquefied in a condenser 8, and received in a container 9. Dilute sulfuric acid is recovered from the bottom of the tower, but this is carried through conduit 13.
The sulfuric acid is sent to the sulfuric acid concentration column 10, and the evaporated water is condensed in the condenser 15 and sent to the wastewater treatment system.
This is the only secondary waste. Concentrated sulfuric acid is discharged from the bottom of the column and recycled to the extractive distillation column.

上記の個々の装置およびその操作は既知である
から、それらについては詳細には述べない。
Since the individual devices mentioned above and their operation are known, they will not be described in detail.

実施例 上に記した装置を用いて本発明方法を実施した
流動層反応炉の反応部の径はいずれも8.3cm、抽
出蒸留塔および硫酸濃縮塔の塔径もまた8.3cmで
あつた。
Example The diameter of the reaction section of the fluidized bed reactor in which the method of the present invention was carried out using the apparatus described above was 8.3 cm, and the diameters of the extractive distillation column and the sulfuric acid concentration column were also 8.3 cm.

操作条件は次の通りであつた。 The operating conditions were as follows.

第1流動層反応炉 反応温度 300℃ UF6供給速度 100g/分 流動化ガス(水蒸気)導入速度 45cm/秒 H2O/U 5.5 生成UO2F2 87.5g/分 第2流動層反応炉 反応温度 700℃ UO2F2供給速度 87.5g/分 流動化ガス速度 45cm/秒 H2O/U 5.0 生成U3O8/UO2F2 67.8/13.1g/分 第3流動層反応炉 温度 700℃ U3O8/UO2F2供給速度 67.8/13.1g/分 流動化ガス速度 24cm/秒 H2O/U 5.0 生成U3O8 79.7g/分 抽出蒸留塔 HF(46wt%HF)供給速度 4/時 硫酸(80wt%H2SO4)供給速度 10/時 生成無水HF 2/時 硫酸濃縮塔 硫酸(70wt%)供給速度 12/時 濃縮硫酸(80wt%)回収速度 10/時 廃水量 2.5/時 このようにして得られたU3O8粉末の物性は1
例として次の通りであつた。
First fluidized bed reactor Reaction temperature 300℃ UF 6 supply rate 100g/min Fluidizing gas (steam) introduction rate 45cm/sec H 2 O/U 5.5 Production UO 2 F 2 87.5g/min Second fluidized bed reactor Reaction Temperature 700℃ UO 2 F 2 Feed rate 87.5g/min Fluidizing gas rate 45cm/sec H 2 O/U 5.0 Production U 3 O 8 /UO 2 F 2 67.8/13.1g/min Third fluidized bed reactor Temperature 700 ℃ U 3 O 8 / UO 2 F 2 supply rate 67.8 / 13.1 g / min Fluidization gas velocity 24 cm / sec H 2 O / U 5.0 produced U 3 O 8 79.7 g / min Extractive distillation column HF (46 wt% HF) supply Speed 4/hour Sulfuric acid (80wt% H 2 SO 4 ) supply rate 10/hour Produced anhydrous HF 2/hour Sulfuric acid concentration tower Sulfuric acid (70wt%) supply rate 12/hour Concentrated sulfuric acid (80wt%) recovery rate 10/hour Waste water volume 2.5/hour The physical properties of the U 3 O 8 powder obtained in this way are 1
An example was as follows.

カサ密度 4.0g/cm3 粒子密度(Heガス置換法) 8.0g/cm3 比表面積(BET法) 1.6m2/g また回収された無水HFは純度99.98%以上であ
つた。
Bulk density: 4.0 g/cm 3 Particle density (He gas replacement method): 8.0 g/cm 3 Specific surface area (BET method): 1.6 m 2 /g The recovered anhydrous HF had a purity of 99.98% or more.

発明の効果 以上の様に本発明は下記の如き秀れた効果を奏
し得る。
Effects of the Invention As described above, the present invention can produce the following excellent effects.

(1) 劣化UF6のU3O8への変換法の中で二次廃棄
物がなく、安価な大量処理に適し、希フツ酸を
容易に得ることができる乾式気相反応法と硫酸
抽出蒸留法とを組合せた方法を用いて劣化UF6
から無水フツ酸を回収することにより、UF6
造工場で利用可能な純度99.98%以上の高純度
無水フツ酸を安価に、二次廃棄物をほとんど出
さずに得ることができ、従来死蔵されている劣
化UF6のフツ素資源を経済的に有効活用を図る
ことができる。更に劣化UF6をU3O8に変換す
ることで従来の劣化UF6貯蔵に比べて貯蔵の安
全性が高められる。
(1) Among the methods for converting degraded UF 6 to U 3 O 8 , the dry gas phase reaction method and sulfuric acid extraction produce no secondary waste, are suitable for inexpensive large-scale processing, and can easily obtain dilute hydrofluoric acid. Degraded UF 6 using a method combined with distillation method
By recovering hydrofluoric anhydride from UF 6 manufacturing plants, it is possible to obtain high-purity hydrofluoric anhydride with a purity of 99.98% or higher, which can be used at UF 6 manufacturing plants, at low cost and with almost no secondary waste. This makes it possible to economically and effectively utilize the degraded UF 6 fluorine resources. Furthermore, converting degraded UF 6 to U 3 O 8 increases storage safety compared to conventional storage of degraded UF 6 .

(2) 劣化UF6のU3O8への変換を流動層反応装置
を使用して実施する事により、同反応装置の特
有な造粒機能により他の変換方法では二次処理
を付加しなければ得難い約4.0g/cm3という貯
蔵に適した高いカサ密度のU3O8を安価に、大
量に、かつ二次廃棄物をほとんど出さずに得る
事ができる。また、本法によれば他法に比べ高
濃度の希フツ酸が副生し、HF処理系での無水
フツ酸への処理効率が高められると共に同処理
系での二次廃棄物の発生量を低く抑えられると
いう利点もある。
(2) By converting degraded UF 6 to U 3 O 8 using a fluidized bed reactor, the unique granulation function of the reactor eliminates the need for secondary treatment in other conversion methods. U 3 O 8 with a high bulk density of approximately 4.0 g/cm 3 suitable for storage, which is difficult to obtain, can be obtained at low cost, in large quantities, and with almost no secondary waste. In addition, according to this method, a higher concentration of dilute hydrofluoric acid is produced as a by-product compared to other methods, increasing the processing efficiency of hydrofluoric anhydride in the HF treatment system, and reducing the amount of secondary waste generated in the same treatment system. It also has the advantage of being able to keep it low.

【図面の簡単な説明】[Brief explanation of the drawing]

添付図面は本発明の方法を実施するための装置
の概念を示す図である。 1……UF6気化器、2……第1流動層反応炉、
3……第2流動層反応炉、4……第3流動層反応
炉、5……U3O8受器、6……フツ酸凝縮器、7
……抽出蒸留塔、8……無水フツ酸凝縮器、9…
…無水フツ酸受器、10……硫酸濃縮塔、11,
12……水蒸気供給管、13……希硫酸移送管、
14……濃縮硫酸移送管、15……廃水凝縮器。
The accompanying drawings illustrate the concept of an apparatus for carrying out the method of the invention. 1... UF 6 vaporizer, 2... first fluidized bed reactor,
3... Second fluidized bed reactor, 4... Third fluidized bed reactor, 5... U 3 O 8 receiver, 6... Hydrofluoric acid condenser, 7
...Extractive distillation column, 8...Fluoric anhydride condenser, 9...
... Fluoric anhydride receiver, 10 ... Sulfuric acid concentration column, 11,
12...Steam supply pipe, 13...Dilute sulfuric acid transfer pipe,
14... Concentrated sulfuric acid transfer pipe, 15... Waste water condenser.

Claims (1)

【特許請求の範囲】 1 劣化UF6を乾式気相反応法によつてU3O8
変換し、同時に副生する希HFを硫酸抽出蒸留法
によつてUF6製造工場で利用可能な無水HFとし
て回収し再利用することからなる劣化UF6から無
水フツ酸を回収再利用する方法。 2 特許請求の範囲第1項記載の劣化UF6から無
水フツ酸を回収再利用する方法であつて、乾式気
相反応法による劣化ウランのU3O8への変換を流
動層反応装置を使用して実施する方法。
[Claims] 1. Degraded UF 6 is converted to U 3 O 8 by a dry gas phase reaction method, and at the same time dilute HF as a by-product is converted to anhydrous UF 6 that can be used at a UF 6 manufacturing plant by a sulfuric acid extractive distillation method. A method for recovering and reusing hydrofluoric anhydride from degraded UF 6 , which consists of recovering and reusing it as HF. 2. A method for recovering and reusing hydrofluoric anhydride from degraded UF 6 as set forth in claim 1, which converts depleted uranium to U 3 O 8 by a dry gas phase reaction method using a fluidized bed reactor. and how to implement it.
JP20556684A 1984-10-02 1984-10-02 Process for recovering anhydrous hydrogen fluoride from deteriorated uf6 and reutilizing thereof Granted JPS6186402A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20556684A JPS6186402A (en) 1984-10-02 1984-10-02 Process for recovering anhydrous hydrogen fluoride from deteriorated uf6 and reutilizing thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20556684A JPS6186402A (en) 1984-10-02 1984-10-02 Process for recovering anhydrous hydrogen fluoride from deteriorated uf6 and reutilizing thereof

Publications (2)

Publication Number Publication Date
JPS6186402A JPS6186402A (en) 1986-05-01
JPH0470243B2 true JPH0470243B2 (en) 1992-11-10

Family

ID=16509011

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20556684A Granted JPS6186402A (en) 1984-10-02 1984-10-02 Process for recovering anhydrous hydrogen fluoride from deteriorated uf6 and reutilizing thereof

Country Status (1)

Country Link
JP (1) JPS6186402A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2700533A1 (en) * 1994-01-17 1994-07-22 Sequoyah Fuels Corp Recovering anhydrous hydrogen fluoride from depleted gaseous uranium hexa:fluoride
CA2137635C (en) * 1994-12-08 2007-09-04 Brian C. Olson Reaction of uranium fluorides with mineral acids to recover hydrogen fluoride
US6352677B1 (en) * 1996-06-04 2002-03-05 Alliedsignal, Inc. Process to produce commercial grade anhydrous hydrogen fluoride (AHF) and uranium oxide from the delfuorination of uranium hexafluoride (UF6)
US8834830B2 (en) 2012-09-07 2014-09-16 Midwest Inorganics LLC Method for the preparation of anhydrous hydrogen halides, inorganic substances and/or inorganic hydrides by using as reactants inorganic halides and reducing agents

Also Published As

Publication number Publication date
JPS6186402A (en) 1986-05-01

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