JPH0712986A - Decontaminating method for technetium in co-decontamination step in reprocessing process of spent nuclear fuel - Google Patents
Decontaminating method for technetium in co-decontamination step in reprocessing process of spent nuclear fuelInfo
- Publication number
- JPH0712986A JPH0712986A JP14933593A JP14933593A JPH0712986A JP H0712986 A JPH0712986 A JP H0712986A JP 14933593 A JP14933593 A JP 14933593A JP 14933593 A JP14933593 A JP 14933593A JP H0712986 A JPH0712986 A JP H0712986A
- Authority
- JP
- Japan
- Prior art keywords
- extraction
- decontamination
- nuclear fuel
- spent nuclear
- waste liquid
- 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
- 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
- Extraction Or Liquid Replacement (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、発電用原子炉等から生
ずる使用済核燃料の再処理技術の改良に関するものであ
る。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an improvement in the technology for reprocessing spent nuclear fuel generated from a nuclear reactor for power generation.
【0002】[0002]
【従来の技術】使用済核燃料の再処理ピュレックス工程
〔使用済核燃料からのリン酸トリブチル(TBP)−硝
酸系によるU,Puの抽出回収処理〕においては、Tc
(VIII)は非抽出性であると考えられ、Tcに対して
特別な配慮はなされていなかった。しかし、近年、Tc
(VII)が上記工程の共除染工程においてその1部又
は全量がU、Puとともに抽出され、分配工程(UとP
uとの分離)に達することが知られるようになった。2. Description of the Related Art In the Purex process for reprocessing spent nuclear fuel [extraction and recovery process of U and Pu from spent nuclear fuel by tributyl phosphate (TBP) -nitric acid system], Tc
(VIII) was considered to be non-extractable, and no special consideration was given to Tc. However, in recent years, Tc
(VII) is extracted together with U and Pu in the co-decontamination step of the above step together with U and Pu.
It became known that the separation from u) was reached.
【0003】分配工程において、Tcは触媒的に各種の
酸化還元反応を促進し、UとPuとの分離を妨害するこ
とも知られるようになった。そこで、最近、フランスの
UP−3又は六ケ所再処理施設では、使用済核燃料再処
理工程の共除染工程において、抽出されたU、Pu及び
Tcを含む有機相からTcを逆抽出することとしてい
る。It has also become known that in the partitioning process, Tc catalytically promotes various redox reactions and interferes with the separation of U and Pu. Therefore, recently, at the UP-3 or Rokkasho reprocessing facility in France, in the co-decontamination process of the spent nuclear fuel reprocessing process, Tc is back-extracted from the extracted organic phase containing U, Pu and Tc. .
【0004】その逆抽出水溶液にはTc以外に無視でき
ない量のU及びPuが含まれるために、それを更にもう
1つの補助抽出工程に導入してU及びPuのみを抽出溶
媒で抽出回収し、その有機相を主抽出工程にリサイクル
させている。そして補助抽出工程で抽出されなかったT
cを含む水相は高レベル水相廃液に合流させている。Since the back-extracted aqueous solution contains non-negligible amounts of U and Pu other than Tc, it was introduced into another auxiliary extraction step to extract and recover only U and Pu with an extraction solvent. The organic phase is recycled to the main extraction process. And T not extracted in the auxiliary extraction process
The aqueous phase containing c is combined with the high-level aqueous waste liquid.
【0005】[0005]
【発明が解決しようとする課題】従来技術におけるTc
の逆抽出除去法では、Tc逆抽出後に補助抽出工程を設
け、そこでTcを逆抽出した水溶液からの抽出溶媒によ
るU及びPuの回収を行っているが、単に廃棄すべきT
cの処理法としては経費への負担が大きいという問題点
がある。[Problems to be Solved by the Invention] Tc in the prior art
In the reverse extraction removal method of T.sub.c, an auxiliary extraction step is provided after Tc back extraction, in which U and Pu are recovered by an extraction solvent from an aqueous solution in which Tc is back extracted.
The method of treating c has a problem that the cost is heavy.
【0006】[0006]
【課題を解決するための手段】本発明においては、使用
済核燃料の再処理工程の共除染工程におけるU−Pu抽
出、洗浄工程(主抽出工程)の後に置いたTc逆抽出工
程からのTc逆抽出水溶液を、そのまま前に設置された
前記抽出(洗浄)工程に合流させる。そうすることによ
って、Tc逆抽出水溶液に含まれるU及びPuの回収を
主抽出工程の抽出工程で行わせ、Tcは高レベル水相廃
液流に排出させるものである。これにより、本発明にお
いては、U、PuをTcから分離するための補助抽出工
程を必要としないので、プロセス的に極めて処理工程が
簡略化される。In the present invention, in the co-decontamination process of the spent nuclear fuel reprocessing process, the Tc from the Tc back extraction process placed after the U-Pu extraction and washing process (main extraction process). The back extraction aqueous solution is allowed to join the above-mentioned extraction (washing) step installed before. By doing so, U and Pu contained in the Tc back extraction aqueous solution are recovered in the extraction step of the main extraction step, and Tc is discharged to the high-level aqueous phase waste liquid stream. As a result, in the present invention, the auxiliary extraction step for separating U and Pu from Tc is not required, so the processing steps are extremely simplified in terms of process.
【0007】[0007]
【作用】本発明においては、ピュレックス法の基本であ
るリン酸トリブチル(TBP)−硝酸抽出系における、
Tc(VII)の抽出分配特性及びUとZrによる共抽
出効果を実験的に求め、それらのデータ及びその他の公
開データを計算機で処理し、Tc(VII)の分配比計
算式を導出して実施した。In the present invention, in the tributyl phosphate (TBP) -nitric acid extraction system which is the basis of the Purex method,
The extraction distribution characteristic of Tc (VII) and the co-extraction effect by U and Zr were experimentally obtained, and the data and other public data were processed by a computer, and the distribution ratio calculation formula of Tc (VII) was derived. did.
【0008】次いで、この計算式をピュレックス工程の
シミュレーションコードに導入し、各種の第1サイクル
抽出工程フローシートについてTc等各成分の挙動を解
析したところ、Tc逆抽出液の主抽出工程への合流によ
り、U−PuプロダクトについてTcの高い除染(U及
びPuからのTcの除去)係数が得られることが確認さ
れた。Next, this calculation formula was introduced into the simulation code of the Purex process, and the behavior of each component such as Tc was analyzed for various first cycle extraction process flow sheets. It was confirmed that the U-Pu product obtained a high decontamination coefficient of Tc (removal of Tc from U and Pu) by merging.
【0009】[0009]
【実施例】ピュレックス工程(30%TBP−硝酸系)
の工程計算コード:EXTRAにより、平均的な抽出、
洗浄工程(10段)にTc逆抽出工程(6段)を追加し
たフローシートの解析を行った。そのフローシートを図
1に示す。ここでは全てのTcが抽出工程で抽出される
場合を想定し、供給液中のZrの濃度をU濃度(250
g/l)の0.4%(1.0g/l)と大きくとった。
Tc逆抽出工程からの逆抽出水溶液は抽出工程の第4段
に注入される。[Example] Purex process (30% TBP-nitric acid system)
Process calculation code: average extraction by EXTRA,
The flow sheet was analyzed by adding the Tc back extraction step (6 steps) to the washing step (10 steps). The flow sheet is shown in FIG. Here, assuming that all the Tc is extracted in the extraction step, the concentration of Zr in the supply liquid is set to the U concentration (250
It was as large as 0.4% (1.0 g / l) of g / l).
The back extraction aqueous solution from the Tc back extraction step is injected into the fourth stage of the extraction step.
【0010】最後の2段(17、18段)は有機相中の
過剰の硝酸を除去するためのものである。U、Pu、T
c、Zrを含有する使用済核燃料溶解液が抽出段6に導
入され、U、Puを抽出するための抽出溶媒が抽出段1
に導入される。両者は抽出段1から抽出段6の間で向流
接触し、高レベル水相廃液(AW)は抽出段1から排出
され、U、Pu等とともにTc、Zrをも抽出した抽出
溶媒は抽出段6から洗浄段10に移行しながら更に洗浄
処理される。The last two stages (17, 18) are for removing excess nitric acid in the organic phase. U, Pu, T
The spent nuclear fuel solution containing c and Zr is introduced into the extraction stage 6, and the extraction solvent for extracting U and Pu is extracted from the extraction stage 1.
Will be introduced to. Both of them come into countercurrent contact between the extraction stage 1 and the extraction stage 6, the high-level aqueous phase waste liquid (AW) is discharged from the extraction stage 1, and the extraction solvent that also extracts Tc and Zr together with U, Pu, etc. Further cleaning processing is performed while shifting from 6 to the cleaning stage 10.
【0011】低濃度洗浄液が洗浄段10において添加さ
れる。洗浄処理された有機溶媒は抽出工程に付設された
Tc逆抽出工程に導入され、そこで洗浄段16に供給さ
れた高濃度洗浄液と向流接触して共抽出溶媒からTcを
逆抽出する。U及びPu含有抽出溶媒(OP)は洗浄段
17−18によって過剰硝酸を除かれた後洗浄段18か
ら取り出され、Tc含有逆抽出水溶液は洗浄段11で抜
き出されて前工程の抽出段4に戻される。A low-concentration cleaning liquid is added in the cleaning stage 10. The washed organic solvent is introduced into the Tc back-extraction step attached to the extraction step, where it countercurrently contacts with the high-concentration washing solution supplied to the washing stage 16 to back-extract Tc from the co-extraction solvent. The extraction solvent (OP) containing U and Pu is removed from the washing stage 18 after the excess nitric acid is removed by the washing stages 17-18, and the Tc-containing back extraction aqueous solution is extracted in the washing stage 11 to extract the extraction stage 4 of the previous step. Returned to.
【0012】本発明における抽出、洗浄工程で処理され
る主な元素の濃度分布の結果を図2に示す。この図から
Tcの99%以上が抽出工程第1段の水相廃液に含まれ
て流出していることが解る。そして、この水相廃液中の
U及びPuの濃度が1mg/l以下と極めて低いことも
解る。FIG. 2 shows the results of the concentration distribution of the main elements treated in the extraction and washing steps in the present invention. From this figure, it can be seen that 99% or more of Tc is contained in the aqueous phase waste liquid in the first stage of the extraction step and flows out. It is also understood that the concentrations of U and Pu in this aqueous phase waste liquid are extremely low at 1 mg / l or less.
【0013】[0013]
【発明の効果】ピュレックス工程第1サイクルの主抽
出、洗浄工程の後に設置したTc逆抽出工程の逆抽出水
溶液を、新たな抽出工程を追加することなく、そのまま
主抽出、洗浄工程における供給液(使用済核燃料溶解
液)の供給段と抽出溶媒の供給段の間に注入することに
より、Tcを定量的に高レベル水相廃液中に排出するこ
とができる。EFFECT OF THE INVENTION The back extraction aqueous solution of the Tc back extraction step installed after the main extraction and washing steps of the first cycle of the Purex process is directly supplied to the main extraction and washing steps without adding a new extraction step. By injecting between the (spent nuclear fuel solution) supply stage and the extraction solvent supply stage, Tc can be quantitatively discharged into the high-level aqueous phase waste liquid.
【図1】本発明の使用済核燃料の再処理工程の第1リサ
イクルにおけるTc(VII)除去のためのフローシー
トを示す図である。○印の中の数字は流量の相対比を表
している。FIG. 1 is a diagram showing a flow sheet for removing Tc (VII) in the first recycling of the spent nuclear fuel reprocessing step of the present invention. The numbers inside the circles indicate the relative ratios of the flow rates.
【図2】図1のフローシートにおけるTc(VII)、
U(VI)及びPu(IV)の濃度分布を示す図であ
る。FIG. 2 shows Tc (VII) in the flow sheet of FIG.
It is a figure which shows the concentration distribution of U (VI) and Pu (IV).
1ー10 抽出洗浄工程(又は抽出、洗浄段) 11−16 Tc逆抽出工程(又は洗浄段) 17−18 硝酸洗浄工程(又は洗浄段) 1-10 Extraction washing step (or extraction, washing step) 11-16 Tc Back extraction step (or washing step) 17-18 Nitric acid washing step (or washing step)
【手続補正書】[Procedure amendment]
【提出日】平成5年7月13日[Submission date] July 13, 1993
【手続補正1】[Procedure Amendment 1]
【補正対象書類名】図面[Document name to be corrected] Drawing
【補正対象項目名】図2[Name of item to be corrected] Figure 2
【補正方法】変更[Correction method] Change
【補正内容】[Correction content]
【図2】 ─────────────────────────────────────────────────────
[Fig. 2] ─────────────────────────────────────────────────── ───
【手続補正書】[Procedure amendment]
【提出日】平成6年1月12日[Submission date] January 12, 1994
【手続補正1】[Procedure Amendment 1]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】請求項1[Name of item to be corrected] Claim 1
【補正方法】変更[Correction method] Change
【補正内容】[Correction content]
【手続補正2】[Procedure Amendment 2]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0002[Name of item to be corrected] 0002
【補正方法】変更[Correction method] Change
【補正内容】[Correction content]
【0002】[0002]
【従来の技術】使用済核燃料の再処理ピュレックス工程
〔使用済核燃料からのリン酸トリブチル(TBP)−硝
酸系によるU,Puの抽出回収処理〕においては、Tc
(VII)は非抽出性であると考えられ、Tcに対して
特別な配慮はなされていなかった。しかし、近年、Tc
(VII)が上記工程の共除染工程においてその1部又
は全量がU、Puとともに抽出され、分配工程(UとP
uとの分離)に達することが知られるようになった。2. Description of the Related Art In the Purex process for reprocessing spent nuclear fuel [extraction and recovery process of U and Pu from spent nuclear fuel by tributyl phosphate (TBP) -nitric acid system], Tc
(VII) is considered to be non-extractable and no special consideration was given to Tc. However, in recent years, Tc
(VII) is extracted together with U and Pu in the co-decontamination step of the above step together with U and Pu.
It became known that the separation from u) was reached.
Claims (1)
の共除染工程において、ジルコニウム(Zr)、プルト
ニウム(Pu)、ウラニウム(U)との共抽出により、
U−Pu有機プロダクト中に抽出されてくる7価のテク
ネチウム〔Tc(VII)〕を有機相より除去して高レ
ベル水相廃液中に排出させるため、共除染工程の主抽
出、洗浄工程の後にTc逆抽出工程を設置し、逆抽出さ
れたTc含有水溶液を前記主抽出、洗浄工程における供
給液の供給段と抽出溶媒の供給段との間に注入すること
により、Tcを定量的に高レベル水相廃液中に排出する
方法。1. In the co-decontamination process of the spent nuclear fuel reprocessing Purex process, by co-extraction with zirconium (Zr), plutonium (Pu) and uranium (U),
In order to remove the 7-valent technetium [Tc (VII)] extracted in the U-Pu organic product from the organic phase and discharge it into the high-level aqueous phase waste liquid, the main extraction and washing steps in the co-decontamination step After that, a Tc back-extraction step is installed, and the back-extracted Tc-containing aqueous solution is injected between the feed stage of the feed solution and the feed stage of the extraction solvent in the main extraction and washing steps to quantitatively increase Tc. Level Method of discharging into aqueous waste liquid.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14933593A JP3308045B2 (en) | 1993-06-21 | 1993-06-21 | Technetium decontamination method in co-decontamination process of spent nuclear fuel reprocessing |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14933593A JP3308045B2 (en) | 1993-06-21 | 1993-06-21 | Technetium decontamination method in co-decontamination process of spent nuclear fuel reprocessing |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0712986A true JPH0712986A (en) | 1995-01-17 |
JP3308045B2 JP3308045B2 (en) | 2002-07-29 |
Family
ID=15472862
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP14933593A Expired - Fee Related JP3308045B2 (en) | 1993-06-21 | 1993-06-21 | Technetium decontamination method in co-decontamination process of spent nuclear fuel reprocessing |
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JP (1) | JP3308045B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8704032B2 (en) | 2009-11-19 | 2014-04-22 | Santec Corporation | Asbestos-treating agent and method for treating asbestos |
KR20160061635A (en) | 2014-11-24 | 2016-06-01 | 주식회사 비씨이노텍 | asbestos-agent and asbestos treatment method. |
-
1993
- 1993-06-21 JP JP14933593A patent/JP3308045B2/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US8704032B2 (en) | 2009-11-19 | 2014-04-22 | Santec Corporation | Asbestos-treating agent and method for treating asbestos |
KR20160061635A (en) | 2014-11-24 | 2016-06-01 | 주식회사 비씨이노텍 | asbestos-agent and asbestos treatment method. |
Also Published As
Publication number | Publication date |
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JP3308045B2 (en) | 2002-07-29 |
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