JP2000206290A - Treatment device for adsorbent for metal element - Google Patents

Treatment device for adsorbent for metal element

Info

Publication number
JP2000206290A
JP2000206290A JP843899A JP843899A JP2000206290A JP 2000206290 A JP2000206290 A JP 2000206290A JP 843899 A JP843899 A JP 843899A JP 843899 A JP843899 A JP 843899A JP 2000206290 A JP2000206290 A JP 2000206290A
Authority
JP
Japan
Prior art keywords
adsorbent
column
funnel
metal element
container
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.)
Pending
Application number
JP843899A
Other languages
Japanese (ja)
Inventor
Hitoshi Yamakawa
比登志 山川
Shoichi Kubo
庄一 久保
Kiminobu Nakamura
仁宣 中村
Tsugio Nakagawa
次男 中川
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.)
Mitsubishi Nuclear Fuel Co Ltd
Original Assignee
Mitsubishi Nuclear Fuel Co Ltd
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 Mitsubishi Nuclear Fuel Co Ltd filed Critical Mitsubishi Nuclear Fuel Co Ltd
Priority to JP843899A priority Critical patent/JP2000206290A/en
Publication of JP2000206290A publication Critical patent/JP2000206290A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E30/00Energy generation of nuclear origin
    • Y02E30/30Nuclear fission reactors
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To make it possible to extract an adsorbent adsorbing metal elements from a container without scattering them. SOLUTION: A funnel 27 whose circumferential face is shaped like a truncated cone and which is made of wire gauge is placed on the downstream side inside a column 2 to be filled with an adsorbent 1. A lower opening 27b of the funnel 27 is connected to an outlet 26 of the column 2 and communicates with a recovery container 13 through an exhaust pipe 12 outside the column 2. An extraction valve 14 is fitted onto the exhaust pipe 12 to perform an opening and closing operation. A space 28 whose section partitioned by the column 2 and the funnel 27 is an approximate right triangle and which is shaped annularly is connected with an exhaust pipe 17. When metal elements are adsorbed, a radioactive liquid waste is separated from the adsorbent 1 in the space 28 through the wire gauge of the funnel 27 and is exhausted. When the adsorbent 1 is dried, hot air is also separated from it by the funnel 27. The adsorbent 1 that is dried and granulated is guided and exhausted from the inside of the column 2 by the funnel 27 and is housed in the recovery container 13.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、ウランやクロム等
の金属元素を不溶性タンニン等の吸着剤に吸着させて回
収処理等するための金属元素吸着剤の処理装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for treating a metal element adsorbent for adsorbing a metal element such as uranium or chromium onto an adsorbent such as insoluble tannin and performing a recovery treatment.

【0002】[0002]

【従来の技術】従来、ウラン、トリウム、超ウラン元素
などのアクチニド元素、カドミウム、鉛、クロム、水銀
及び鉄を含む重金属元素、或いはコバルト、セシウム、
ストロンチウム等の金属元素を吸着するための金属元素
の吸着剤として、縮合型タンニンを原料とする安定化し
たゲル状組成物からなる吸着剤があり、この吸着剤は本
発明者らによって、特開平5−66291号公報等によ
り、その製造方法と金属元素の吸着分離方法が提案され
ている。この吸着剤は、上記公報に開示されているよう
に柿渋を含まない天然に多量に存在する縮合型タンニン
を原料として例えば縮合型タンニン粉末をアンモニア水
に溶解してアルデヒド水溶液を混合してゲル状組成物を
生成し、このゲル状組成物を熟成したり加熱する等して
安定化することで得られる。安定化したゲル状組成物は
水や酸やアルカリのいずれに対しても不溶な組成物とな
る。
2. Description of the Related Art Conventionally, actinide elements such as uranium, thorium and transuranium elements, heavy metal elements including cadmium, lead, chromium, mercury and iron, or cobalt, cesium,
As an adsorbent of a metal element for adsorbing a metal element such as strontium, there is an adsorbent composed of a stabilized gel-like composition using condensed tannin as a raw material. JP-A-5-66291 proposes a production method and a method for adsorbing and separating a metal element. This adsorbent is prepared by dissolving condensed tannin powder in ammonia water and mixing with an aqueous aldehyde solution using, for example, a condensed tannin which is present in a large amount and does not contain persimmon astringent as disclosed in the above-mentioned publication. It is obtained by producing a composition and stabilizing the gel composition by aging or heating. The stabilized gel composition becomes a composition insoluble in any of water, acid and alkali.

【0003】そしてこのようにして得られた吸着剤は、
核燃料製造工程から発生するウラン、トリウム及び海水
中のウランの吸着性能に優れるだけでなく、再処理工程
から発生する超ウラン元素であるキュリウム、アメリシ
ウム、ネプツニウム、プルトニウム、更には金属元素を
取り扱う工程から発生するカドミウム、鉛、六価クロ
ム、水銀、鉄、コバルト、セシウム、ストロンチウム等
の多種の金属元素の吸着性能に優れている。また金属を
吸着したこの吸着剤は、有毒ガスを発生することなく焼
却可能であるため、焼却により吸着剤の容積を大きく減
少して固体廃棄物の発生量を少なくすることができる。
また吸着した金属元素によっては、固形物は不純物を含
まない金属酸化物になるため、再利用を図ることもでき
る。更にこの吸着剤はゲル状組成物であるためにその形
態が崩れにくく、吸着した金属元素をゲル状組成物から
容易に溶解させて金属を回収及び精製することができ
る。
[0003] The adsorbent thus obtained is
It not only excels in the adsorption performance of uranium, thorium, and uranium in seawater generated from the nuclear fuel production process, but also from the process of handling the transuranium elements, curium, americium, neptunium, plutonium, and further metal elements generated from the reprocessing process. It has excellent adsorption performance for various metal elements such as cadmium, lead, hexavalent chromium, mercury, iron, cobalt, cesium, and strontium. In addition, since the adsorbent having adsorbed the metal can be incinerated without generating toxic gas, the volume of the adsorbent can be greatly reduced by incineration, and the amount of solid waste generated can be reduced.
Further, depending on the metal element adsorbed, the solid substance becomes a metal oxide containing no impurities, and thus can be reused. Furthermore, since this adsorbent is a gel composition, its form is not easily collapsed, and the adsorbed metal element can be easily dissolved from the gel composition to recover and purify the metal.

【0004】ところで、核燃料を取り扱う工程において
排出されるウランまたは超ウラン元素等を含む廃液から
ウランまたは超ウラン元素等の金属元素を吸着させるに
は、例えば充填筒であるカラム内に機械的手段等で所望
のサイズに砕解されたゲル状組成物の吸着剤を所望の高
さまで充填し、この状態で放射性廃液をカラム内に供給
して吸着剤にウランまたは超ウラン元素等の金属元素を
吸着させる。吸着は吸着剤の吸着能力の破過に達するま
で行われる。このようにして金属元素が吸着された吸着
剤はカラム内に緊密に充填された状態となり容易に抜き
出しができない。このような使用済みの吸着剤の乾燥及
び抜き出しに関する処理は図5に示す工程により行われ
る。図5において、金属元素が吸着された吸着剤1を充
填したカラム2の上蓋3(または下底でもよい)を解体
してカラム2から手動で吸着剤1をかき出すか、吸引機
で吸引する等して乾燥用バット4に収納載置する(同図
(a)参照)。次にこれら乾燥用バット4を箱形乾燥機
5内に収容して加熱し吸着剤1を乾燥させる(同図
(b)参照)。そして乾燥した吸着剤1をフードボック
ス6によって回収容器7に充填し(同図(c)参照)、
燃焼する等して廃棄物の容積を減少させ、特定の金属元
素にあっては不純物を含まない金属酸化物として回収し
て再利用する。
By the way, in order to adsorb a metal element such as uranium or transuranium from a waste liquid containing uranium or transuranium discharged in a process of handling nuclear fuel, for example, mechanical means or the like is installed in a column which is a packed cylinder. Fill the adsorbent of the gel composition disintegrated to the desired size to the desired height, supply the radioactive waste liquid into the column in this state, and adsorb the metal element such as uranium or transuranium element to the adsorbent Let it. Adsorption is carried out until breakthrough of the adsorption capacity of the adsorbent is reached. The adsorbent on which the metal element has been adsorbed in this manner is in a state of being tightly packed in the column and cannot be easily extracted. The processing for drying and extracting the used adsorbent is performed by the steps shown in FIG. In FIG. 5, the upper lid 3 (or the lower bottom may be disassembled) of the column 2 filled with the adsorbent 1 on which the metal element has been adsorbed, and the adsorbent 1 is manually scraped out of the column 2 or sucked by a suction machine or the like. Then, it is stored and placed on the drying vat 4 (see FIG. 3A). Next, these drying vats 4 are housed in a box-shaped dryer 5 and heated to dry the adsorbent 1 (see FIG. 2B). Then, the dried adsorbent 1 is filled into the collection container 7 by the food box 6 (see FIG. 3C),
The volume of the waste is reduced by burning or the like, and a specific metal element is recovered as a metal oxide containing no impurities and reused.

【0005】[0005]

【発明が解決しようとする課題】ところが、このような
使用済み吸着剤の取り出し方法では、カラム2内の吸着
剤1の粒子間に水分を含んでいるために吸着剤1の流動
性が極めて悪く、容易にカラム2から抜き出すことがで
きない。そのため、カラム2の上蓋3または下底を解体
して手動で吸着剤1をかき出さなければならないため
に、その作業が重労働となる上に長時間かかるという問
題があり、掻き出し作業中等に放射性廃棄物が飛散する
等して周辺汚染のおそれが生じる。しかもカラム2だけ
でなく乾燥用バット4、乾燥機5、フードボックス6等
多くの機器が必要となり、コスト高になるという欠点も
ある。本発明は、このような実情に鑑みて、飛散の恐れ
がなく容易に吸着剤を取り出せるようにした金属元素吸
着剤の処理装置を提供することを目的とする。
However, in such a method for removing the used adsorbent, the fluidity of the adsorbent 1 is extremely poor because water is contained between the particles of the adsorbent 1 in the column 2. Cannot be easily extracted from the column 2. Therefore, since the upper lid 3 or the lower bottom of the column 2 must be dismantled and the adsorbent 1 must be manually scraped out, the work becomes labor intensive and takes a long time. There is a risk of peripheral contamination due to scattering of objects. In addition, not only the column 2 but also many other devices such as a drying vat 4, a dryer 5, a food box 6, and the like are required, resulting in a disadvantage that the cost is increased. In view of such circumstances, an object of the present invention is to provide a processing device for a metal element adsorbent capable of easily taking out the adsorbent without fear of scattering.

【0006】[0006]

【課題を解決するための手段】本発明に係る金属元素吸
着剤の処理装置は、金属元素を吸着するための吸着剤が
収納された容器内に金属元素を含有した溶液を供給して
溶液中の金属元素を吸着剤に吸着させて乾燥させ、この
吸着剤を排出するようにした金属元素吸着剤の処理装置
において、容器内には、吸着剤を収容してその流出をガ
イドすると共に溶液を通過させるガイド部が配設され、
吸着剤を容器から取り出すための開閉手段が設けられて
いることを特徴とする。容器内の吸着剤はガイド部まで
充填収納されており、金属元素を含有した溶液を容器に
流して金属元素を吸着剤に吸着させて吸着剤の吸着能力
の破過に達するまで吸着させ、その過程で吸着剤を通過
して金属元素を奪われた後の溶液または吸着剤に到達す
る前の溶液はガイド部の面を通過(透過)することで吸
着剤と分離されまたは吸着剤中に浸透する。また金属元
素が吸着された使用済みの吸着剤は乾燥後に開閉部材を
開に切り換えることでガイド部の面に沿って流出してカ
ラムから取り出され、回収できる。尚、ガイド部はテー
パ状に形成されていて上部開口は容器の内面に当接し下
部開口は容器の排出口に接続されていてもよい。
A metal element adsorbent treatment apparatus according to the present invention supplies a solution containing a metal element into a container containing an adsorbent for adsorbing the metal element, and supplies the solution containing the metal element to the container. The metal element is adsorbed on the adsorbent and dried, and the adsorbent is discharged in the treatment device for the metal element adsorbent. A guide part to pass through is arranged,
An opening / closing means for removing the adsorbent from the container is provided. The adsorbent in the container is filled and stored up to the guide portion, and a solution containing the metal element is flowed into the container to adsorb the metal element to the adsorbent and adsorb until the adsorbent reaches a breakthrough in the adsorption capacity. The solution after passing through the adsorbent and deprived of the metal element in the process or the solution before reaching the adsorbent passes through (permeates) the guide surface and is separated from the adsorbent or permeates into the adsorbent I do. Further, the used adsorbent having the metal element adsorbed thereon flows out along the surface of the guide portion and is taken out of the column and recovered by switching the open / close member after drying. The guide portion may be formed in a tapered shape, the upper opening may be in contact with the inner surface of the container, and the lower opening may be connected to the outlet of the container.

【0007】またガイド部の周囲には、容器とガイド部
で仕切られた空間が形成され、この空間に排出用の配管
または供給用の配管が接続されていてもよい。ガイド部
の面を通過して吸着剤と分離された溶液は空間から排出
配管を通して排出される。或いは容器の空間に供給され
た溶液はガイド部を通して吸着剤を通過する。またガイ
ド部は少なくとも一部が網目状に形成されまたは少なく
とも一部に孔が開けられていてもよい。ガイド部を通過
する溶液は、ガイド部の面の網目または孔を通して流通
され、吸着剤はこの網目または孔を通過することなくガ
イド部に沿って流出させられる。
Further, a space separated by the container and the guide portion may be formed around the guide portion, and a discharge pipe or a supply pipe may be connected to this space. The solution separated from the adsorbent after passing through the surface of the guide portion is discharged from the space through the discharge pipe. Alternatively, the solution supplied to the space of the container passes through the adsorbent through the guide portion. Further, at least a part of the guide portion may be formed in a mesh shape or a hole may be formed in at least a part. The solution passing through the guide portion is circulated through a mesh or a hole in the surface of the guide portion, and the adsorbent is discharged along the guide portion without passing through the mesh or the hole.

【0008】[0008]

【発明の実施の形態】以下、本発明の実施の形態を図1
乃至図3により説明するが、上述した従来技術と同一の
部分には同一の符号を用いて説明する。図1は本発明の
実施の形態による吸着剤の処理装置の概略構成図、図2
は金属元素が充填されたカラムを含む取り出し機構の要
部構成図、図3は吸着剤の吸着乾燥処理及び取り出し工
程を示すフローチャートである。図1に示す吸着剤の処
理装置10において、充填筒、例えばカラム2内には上
述した縮合型タンニンを原料とするゲル状組成物からな
る不溶性タンニンで構成される吸着剤1が充填されてお
り、図示しない廃液タンクから供給配管11を介して供
給される溶液、例えば放射性廃液がカラム2の上部2a
から流入して吸着剤1で放射性廃液に含まれるウランや
トリウム等の金属元素が吸着されるようになっている。
またこの処理装置10では、図1及び図2に示すように
カラム2の下部2bに排出管12を介して回収容器13
が設けられており、排出管12には開閉切り替え操作可
能な抜き出しバルブ14が開閉手段として設けられ、開
弁することでカラム2内の吸着剤1が回収容器13内に
排出され得るようになっている。
FIG. 1 is a block diagram showing an embodiment of the present invention.
3 to FIG. 3, the same parts as those in the above-described prior art will be described using the same reference numerals. FIG. 1 is a schematic configuration diagram of an apparatus for treating an adsorbent according to an embodiment of the present invention, and FIG.
FIG. 3 is a main part configuration diagram of a take-out mechanism including a column filled with a metal element, and FIG. 3 is a flowchart showing an adsorption drying process and a take-out process of an adsorbent. In the adsorbent treatment apparatus 10 shown in FIG. 1, a filling cylinder, for example, a column 2 is filled with the adsorbent 1 composed of the insoluble tannin composed of the gel composition using the above-mentioned condensed tannin as a raw material. A solution supplied from a waste liquid tank (not shown) via the supply pipe 11, for example, a radioactive waste liquid is supplied to the upper portion 2 a of the column 2.
And metal elements such as uranium and thorium contained in the radioactive waste liquid are adsorbed by the adsorbent 1.
Further, in this processing apparatus 10, as shown in FIGS.
The discharge pipe 12 is provided with a withdrawal valve 14 that can be switched between open and closed, as an opening and closing means. By opening the valve, the adsorbent 1 in the column 2 can be discharged into the collection container 13. ing.

【0009】カラム2の上部2aには配管15を介して
空気加熱器16が接続されており、ここで加熱された空
気を熱風としてカラム2の上部2aに供給するようにな
っている。そしてカラム2の下部2b領域には吸着剤1
を通過した熱風や放射性廃液を排出する排出配管17が
連通され、排出配管17には内部の熱風の排気温度を測
定する排気温度測定手段18が設けられている。ここ
で、吸着剤1に供給される熱風の温度は、吸着剤1やカ
ラム2に付着する放射性廃液等に含まれる物質、例えば
硝酸化合物が分解して発熱したり体積膨張することのな
いように、このような物質が分解する温度より低温に設
定するものとし、ウランなどを含む放射性廃液では例え
ば約140℃に設定し、給気温度測定手段19で測定さ
れる。
An air heater 16 is connected to the upper part 2a of the column 2 via a pipe 15, and the heated air is supplied to the upper part 2a of the column 2 as hot air. The adsorbent 1 is located in the lower 2b area of the column 2.
A discharge pipe 17 for discharging the hot air or the radioactive waste liquid passing therethrough is connected to the discharge pipe 17, and the discharge pipe 17 is provided with exhaust temperature measuring means 18 for measuring the exhaust temperature of the internal hot air. Here, the temperature of the hot air supplied to the adsorbent 1 is adjusted so that the substance contained in the radioactive waste liquid or the like adhering to the adsorbent 1 or the column 2, for example, a nitric acid compound is not decomposed and generates heat or expands in volume. The temperature is set lower than the temperature at which such a substance is decomposed. For a radioactive waste liquid containing uranium or the like, the temperature is set to, for example, about 140 ° C., and the temperature is measured by the supply air temperature measuring means 19.

【0010】排気温度測定手段18と給気温度測定手段
19は制御手段20を介して空気加熱器16に接続され
ており、熱風によってカラム2内の吸着剤1が乾燥させ
られる際、乾燥が進む状態では排気温度はほぼ一定の温
度T0として測定されるが、乾燥が終了すると排気温度
がT0を越えた温度T1となり、漸次昇温するが、この
排気温度T1を検知すると、制御手段20によって空気
加熱器16がOFFされ、熱風の供給が停止されるよう
になっている。尚、温度T0は例えば35℃〜50℃程
度とし、排気温度T1は例えば80℃程度とする。また
カラム2には配管22を介して水などの洗浄液を上部2
aから供給する洗浄液供給手段23が接続されている。
The exhaust gas temperature measuring means 18 and the supply air temperature measuring means 19 are connected to the air heater 16 via the control means 20, and when the adsorbent 1 in the column 2 is dried by hot air, the drying proceeds. In this state, the exhaust gas temperature is measured as a substantially constant temperature T0. However, when drying is completed, the exhaust gas temperature rises to a temperature T1 exceeding T0 and gradually rises. The heater 16 is turned off, and the supply of hot air is stopped. The temperature T0 is, for example, about 35 ° C. to 50 ° C., and the exhaust temperature T1 is, for example, about 80 ° C. A washing liquid such as water is supplied to the column 2 through the pipe 22.
The cleaning liquid supply means 23 supplied from a is connected.

【0011】また図2に示すカラム2及び抜き出しバル
ブ14を含む吸着剤の取り出し機構25において、カラ
ム2の下部2b中央には排出管12に連通する排出口2
6が形成されており、略円筒状のカラム2内の下方には
ガイド部として略円錐台周面形状をなすロート27が装
着されている。このロート27は適宜の金属材料からな
る金網で形成され、円錐台周面形状の最大内径をなす上
部開口27aはカラム2の内周面に当接すると共に最小
内径をなす下部開口27bは排出口26に連結されてい
る。そのため、上部開口27aはカラム2の内径とほぼ
同一の径とされ、下部開口27bは排出口26の内径と
ほぼ同一の径とされている。カラム2の下部2bには周
面2cとロート26の周面とで仕切られた空間28が形
成され、排出配管17に連通している。
In the adsorbent removal mechanism 25 including the column 2 and the extraction valve 14 shown in FIG. 2, a discharge port 2 communicating with the discharge pipe 12 is provided at the center of the lower part 2b of the column 2.
6, a funnel 27 having a substantially frustoconical peripheral surface shape is mounted as a guide portion below the substantially cylindrical column 2. The funnel 27 is formed of a metal mesh made of a suitable metal material, and an upper opening 27a having a maximum inner diameter of a truncated conical peripheral surface is in contact with the inner peripheral surface of the column 2 and a lower opening 27b having a minimum inner diameter is provided with an outlet 26. It is connected to. Therefore, the upper opening 27a has a diameter substantially the same as the inner diameter of the column 2, and the lower opening 27b has a diameter substantially the same as the inner diameter of the outlet 26. A space 28 is formed in the lower part 2b of the column 2 and is partitioned by the peripheral surface 2c and the peripheral surface of the funnel 26, and communicates with the discharge pipe 17.

【0012】本実施の形態による吸着剤の処理装置10
は上述のように構成されており、次に吸着剤1の吸着乾
燥及び取り出しの処理方法について図3に示すフローチ
ャートに沿って説明する。ウランなどの金属元素を含む
放射性廃液からウランなどの金属元素だけを吸着分離す
るために、カラム2内には砕解されたゲル状組成物から
なる吸着剤1が充填されており、上部2aからカラム2
内に放射性廃液を供給して(ステップ101)金属元素
だけを高い吸着率を以て吸着剤2に吸着させることがで
きる。そして、金属元素がほとんど吸着除去された廃液
はカラム2内の下方でロート27の周面である金網を通
過して空間28内に流れ出る。この空間28から排出配
管17を介してカラム2外部に排出される(ステップ1
02)。吸着剤1はウランなどの金属元素について極め
て高い吸着能力を有するためにカラム2から排出される
放射性廃液中の金属元素の残留割合を測定することでカ
ラム2中の吸着剤1が破過点に達していることを確認で
きる。吸着剤1の吸着能力が破過に到達した時点で放射
性廃液の供給を停止し、吸着工程が終了する。この状態
で、カラム2内の吸着剤1には金属元素が吸着されてカ
ラム2内に緊密に充填されており吸着剤1は容易に抜き
取ることができない状態にある。
An adsorbent processing apparatus 10 according to the present embodiment.
Is configured as described above. Next, a processing method for adsorption drying and removal of the adsorbent 1 will be described with reference to a flowchart shown in FIG. In order to adsorb and separate only the metal element such as uranium from the radioactive waste liquid containing the metal element such as uranium, the column 2 is filled with an adsorbent 1 composed of a pulverized gel-like composition, Column 2
By supplying a radioactive waste liquid into the inside (step 101), only the metal element can be adsorbed on the adsorbent 2 with a high adsorption rate. The waste liquid from which most of the metal elements have been adsorbed and removed flows out into the space 28 through the wire mesh which is the peripheral surface of the funnel 27 below the column 2. The gas is discharged from the space 28 to the outside of the column 2 via the discharge pipe 17 (step 1).
02). Since the adsorbent 1 has an extremely high adsorption capacity for metal elements such as uranium, measuring the residual ratio of the metal element in the radioactive waste liquid discharged from the column 2 allows the adsorbent 1 in the column 2 to reach a breakthrough point. You can confirm that it has been reached. When the adsorption capacity of the adsorbent 1 reaches the breakthrough, the supply of the radioactive waste liquid is stopped, and the adsorption step is completed. In this state, the metal element is adsorbed on the adsorbent 1 in the column 2 and is tightly packed in the column 2, so that the adsorbent 1 cannot be easily removed.

【0013】次に洗浄液供給手段23から洗浄液として
例えば水をカラム2内に供給して通液し、カラム2内に
残留する放射性廃液を押し出してロート27を通過させ
て空間28及び排出配管17から排出させる(ステップ
103)。このときウラン等の金属元素は吸着剤1に吸
着されているため、水などの洗浄液中に溶け出すことは
ない。ここで、水をカラム2内に通液しないで乾燥処理
すると、残存する放射性廃液中のフッ化アンモニウムや
その他の硝酸系の塩類が乾燥して析出し、吸着剤が固着
されてしまい、カラム2からの排出が困難になる。そし
て空気加熱器16で加熱された空気が例えば温度約14
0℃程度の熱風として配管15を通してカラム2に供給
され、吸着剤1を乾燥させる(ステップ104)。吸着
剤1を通気された熱風はロート27の金網を通して空間
28内に排出されて排出配管17を通して外部に排気さ
れる。吸着剤1を通気する際、吸着剤1に含まれている
水分の気化熱として熱が奪われるために、吸着剤1を通
過した熱風は温度が低下して例えば35℃〜50℃程度
の排気温度T0となって排出される。この排気温度は排
気温度測定手段18によって検出される。吸着剤1の乾
燥が進むにつれて吸着剤1の体積が小さくなり、カラム
2内の高さも図1及び図2でh1から徐々に低下し、乾
燥終了時には高さh2程度まで減容(例えば1/5の体
積になる)する。この間、熱風の排気温度は継続して熱
を奪われるためにほぼ一定の温度T0に維持される。
Next, for example, water is supplied from the cleaning liquid supply means 23 as a cleaning liquid into the column 2 and flows therethrough. Radioactive waste liquid remaining in the column 2 is extruded and passed through the funnel 27 to pass through the space 28 and the discharge pipe 17. It is discharged (step 103). At this time, since the metal element such as uranium is adsorbed by the adsorbent 1, it does not dissolve in the cleaning liquid such as water. Here, if the drying treatment is performed without passing water through the column 2, ammonium fluoride and other nitric acid salts in the remaining radioactive waste liquid are dried and precipitated, and the adsorbent is fixed, and the column 2 Emission from ash becomes difficult. The air heated by the air heater 16 has a temperature of about 14
The hot air of about 0 ° C. is supplied to the column 2 through the pipe 15 to dry the adsorbent 1 (Step 104). The hot air that has passed through the adsorbent 1 is discharged into the space 28 through the wire mesh of the funnel 27 and is discharged outside through the discharge pipe 17. When the adsorbent 1 is ventilated, heat is taken away as heat of vaporization of water contained in the adsorbent 1, so that the temperature of the hot air that has passed through the adsorbent 1 decreases and the hot air that has passed through the adsorbent 1 is exhausted at, for example, about 35 ° C to 50 ° C. It is discharged at the temperature T0. This exhaust gas temperature is detected by the exhaust gas temperature measuring means 18. As the drying of the adsorbent 1 proceeds, the volume of the adsorbent 1 decreases, and the height in the column 2 also gradually decreases from h1 in FIGS. 1 and 2, and at the end of drying, the volume is reduced to about the height h2 (for example, 1 / 5). During this time, the exhaust temperature of the hot air is maintained at a substantially constant temperature T0 because heat is continuously taken away.

【0014】吸着剤1の乾燥が完了すると、熱風が吸着
剤1を通過する際に熱を奪われなくなり排気温度がT0
から次第に上昇する。排気温度測定手段18で測定され
る排気温度がT0より上昇してT1(例えば80℃)と
なると、制御手段20で空気加熱器16の駆動を停止さ
せ、熱風供給が終了して乾燥工程が終了する。吸着剤1
が乾燥すると、吸着剤1は収縮して流動性に優れた顆粒
状になる。この状態で、抜き出しバルブ14を開けばカ
ラム2内の顆粒状の吸着剤1はロート27でガイドされ
て排出口26、排管12を通して流出し容易に回収容器
13内に収納される。このようにして吸着剤1の容積を
大幅に減少させてカラム2から容易に排出回収できる。
その後、吸着剤1は焼却処理することで、不溶性タンニ
ンからなる吸着剤1を分解でき、ウラン等の金属元素を
金属酸化物として高い純度で回収でき、二次廃棄物の発
生を防止できる。
When the drying of the adsorbent 1 is completed, the heat is not deprived when the hot air passes through the adsorbent 1, and the exhaust temperature becomes T0.
Gradually rises from. When the exhaust gas temperature measured by the exhaust gas temperature measuring means 18 rises from T0 to T1 (for example, 80 ° C.), the control means 20 stops driving the air heater 16 and the hot air supply ends and the drying step ends. I do. Adsorbent 1
When is dried, the adsorbent 1 shrinks and becomes a granule having excellent fluidity. In this state, if the extraction valve 14 is opened, the granular adsorbent 1 in the column 2 is guided by the funnel 27, flows out through the discharge port 26 and the discharge pipe 12, and is easily stored in the collection container 13. In this way, the volume of the adsorbent 1 is greatly reduced, and the adsorbent 1 can be easily discharged and collected from the column 2.
Thereafter, the adsorbent 1 can be decomposed by incineration to decompose the adsorbent 1 made of insoluble tannin, and a metal element such as uranium can be recovered as a metal oxide with high purity, thereby preventing generation of secondary waste.

【0015】上述のように本実施の形態によれば、金属
元素の吸着時には金属元素が吸着された後の放射性廃液
をロート27の金網を通してカラム2内で容易に吸着剤
1から分離して排出でき、乾燥時には熱風をロート27
の金網を通してカラム2内で分離して外部に排気できる
上に、乾燥後の吸着剤1の回収時には顆粒状となった吸
着剤1をロート27で排出口26までガイドして排出管
12を介して容易に回収容器13に回収でき、簡単な吸
着剤1の取り出し機構25によって、放射性廃液や乾燥
用の熱風を吸着剤1から容易に分離排出できる上に吸着
剤1の取り出しが容易に行える。しかも放射性廃液やウ
ラン等の放射性金属元素を飛散させずに周辺汚染を生じ
ることもなくカラム2から取り出すことができる。
As described above, according to the present embodiment, when the metal element is adsorbed, the radioactive waste liquid after the metal element is adsorbed is easily separated from the adsorbent 1 in the column 2 through the wire mesh of the funnel 27 and discharged. Hot air can be used for drying
Can be separated out in the column 2 through the wire mesh and exhausted to the outside. In addition, when the adsorbent 1 after drying is recovered, the granulated adsorbent 1 is guided to the outlet 26 by the funnel 27 through the outlet pipe 12. The radioactive waste liquid and hot air for drying can be easily separated and discharged from the adsorbent 1 and the adsorbent 1 can be easily taken out by the simple adsorbent 1 take-out mechanism 25. In addition, radioactive waste liquid and radioactive metal elements such as uranium can be taken out of the column 2 without scattering and without causing peripheral contamination.

【0016】次に図4は本実施の形態による吸着剤の処
理装置10の変形例を示すものであり、この処理装置1
0では、放射性廃液をカラム2に供給するための供給配
管11がカラム2の下部2b付近に接続されて空間28
に連通しており、吸着剤1を通過した廃液をカラム外部
に排出する排出配管17はカラム2の上部2a付近に接
続されている。そのため、金属元素の吸着時には放射性
廃液はカラム2内に供給されて空間28からロート27
を透過して吸着剤に浸透して下方から上方に流れ、上部
2aの排出配管17から排出されることになる。尚、こ
の場合、洗浄液供給手段23の洗浄液と空気加熱器16
で加熱された熱風も同様に配管22と配管15からカラ
ム2内を下流から上流に流れるものとなる。或いは、図
1に示す実施の形態のように上流から下流に流しても良
い。
FIG. 4 shows a modification of the adsorbent processing apparatus 10 according to the present embodiment.
0, the supply pipe 11 for supplying the radioactive waste liquid to the column 2 is connected near the lower portion 2b of the column 2 and the space 28
And a discharge pipe 17 for discharging the waste liquid that has passed through the adsorbent 1 to the outside of the column is connected near the upper portion 2a of the column 2. Therefore, when the metal element is adsorbed, the radioactive waste liquid is supplied into the column 2 and is discharged from the space 28 to the funnel 27.
, Penetrates the adsorbent, flows upward from below, and is discharged from the discharge pipe 17 in the upper portion 2a. In this case, the cleaning liquid of the cleaning liquid supply means 23 and the air heater 16
Similarly, the hot air heated by the above flows from the pipe 22 and the pipe 15 in the column 2 from downstream to upstream. Alternatively, it may flow from upstream to downstream as in the embodiment shown in FIG.

【0017】尚、上述の実施の形態ではガイド部として
金網で形成されたロート27を用いたが、ロート27を
構成するテーパ状の周面は金網などの網目状の構成に限
定されることなく通液及び通気性の材質または構成であ
ればよく、例えば多孔質の焼結メタル製の周面やパンチ
孔などの適宜数の小孔が穿孔された周面などで構成して
もよい。また金網や孔等は必ずしもロート27の周面全
体に形成されている必要はなく一部に形成されていても
よい。尚、本発明による吸着剤1の処理装置10は、上
述したウランを含む放射性廃液などの廃棄物に限定され
ることなく、核燃料製造工程から発生するウラン、トリ
ウム、再処理工程から発生する超ウラン元素であるキュ
リウム、アメリシウム、ネプツニウム、プルトニウム、
更に金属元素を取り扱う工程から発生するカドミウム、
鉛、六価クロム、水銀、鉄、コバルト、セシウム、スト
ロンチウム等の多種の金属元素を含む廃液、ウランを含
む海水等を含む各種の溶液からこれら金属元素を吸着し
た吸着剤1の乾燥及び取り出しに用いることができる。
またカラム2は容器を構成する。
In the above-described embodiment, the funnel 27 formed of a wire mesh is used as the guide portion. However, the tapered peripheral surface of the funnel 27 is not limited to a mesh-like structure such as a wire mesh. Any material or configuration may be used as long as it is liquid-permeable and air-permeable, and may be, for example, a porous sintered metal peripheral surface or a peripheral surface formed with an appropriate number of small holes such as punch holes. Further, the wire mesh, the holes, and the like do not necessarily need to be formed on the entire peripheral surface of the funnel 27, and may be formed on a part thereof. In addition, the treatment apparatus 10 for the adsorbent 1 according to the present invention is not limited to waste such as the above-mentioned radioactive waste liquid containing uranium, but includes uranium and thorium generated from a nuclear fuel production process, and transuranium generated from a reprocessing process. The elements curium, americium, neptunium, plutonium,
Cadmium generated from the process of handling metal elements,
For drying and taking out the adsorbent 1 that adsorbs these metal elements from various solutions including wastewater containing various metal elements such as lead, hexavalent chromium, mercury, iron, cobalt, cesium and strontium, and seawater containing uranium Can be used.
The column 2 constitutes a container.

【0018】[0018]

【発明の効果】以上説明したように、本発明に係る金属
元素吸着剤の処理装置は、容器内に吸着剤を収容してそ
の流出をガイドすると共に溶液を通過させるガイド部が
配設され、吸着剤を容器から取り出すための開閉手段が
設けられているから、金属元素の吸着時には金属元素が
吸着された後の溶液をガイド部を通して容易に吸着剤か
ら分離して排出でき、乾燥後の吸着剤の回収時には顆粒
状となった吸着剤をガイド部で誘導して容易に外部に排
出して回収でき、簡単な構成によって溶液等を吸着剤と
容易に分離排出できる上に吸着剤の取り出しが容易に行
える。しかも吸着剤や金属元素等を飛散させることなく
容器から取り出すことができる。
As described above, the apparatus for treating a metal element adsorbent according to the present invention is provided with a guide section for accommodating the adsorbent in a container, guiding the outflow thereof, and passing the solution. An opening / closing means for removing the adsorbent from the container is provided, so that when the metal element is adsorbed, the solution after the metal element has been adsorbed can be easily separated from the adsorbent through the guide section and discharged, and the adsorbed substance after drying When collecting the adsorbent, the granulated adsorbent can be guided by the guide part and easily discharged to the outside, and can be easily collected and recovered.With a simple structure, the solution etc. can be easily separated and discharged from the adsorbent, and the adsorbent can be taken out. Easy to do. In addition, the adsorbent and the metal element can be taken out of the container without being scattered.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 本発明の実施の形態による吸着剤の処理装置
の要部構成図である。
FIG. 1 is a main part configuration diagram of an adsorbent processing apparatus according to an embodiment of the present invention.

【図2】 図1に示す処理装置の吸着剤取り出し機構を
示す概略断面図である。
FIG. 2 is a schematic sectional view showing an adsorbent removing mechanism of the processing apparatus shown in FIG.

【図3】 実施の形態による吸着剤の処理装置における
吸着剤の処理過程を示すフローチャートである。
FIG. 3 is a flowchart showing a process of treating the adsorbent in the adsorbent treating apparatus according to the embodiment.

【図4】 実施の形態による吸着剤の処理装置の変形例
を示す要部構成図である。
FIG. 4 is a main part configuration diagram showing a modification of the adsorbent processing apparatus according to the embodiment.

【図5】 従来の吸着剤の処理方法における、金属元素
が吸着された吸着剤の乾燥と取り出し工程を示す図であ
り、(a)はカラムから乾燥用バットに吸着剤を移し替
える工程、(b)は吸着剤を乾燥させる工程、(c)は
回収容器に吸着剤を移し替える工程を示す図である。
FIG. 5 is a diagram showing a step of drying and taking out an adsorbent on which a metal element is adsorbed in a conventional method of treating an adsorbent, wherein (a) shows a step of transferring the adsorbent from a column to a drying vat; (b) is a diagram illustrating a process of drying the adsorbent, and (c) is a diagram illustrating a process of transferring the adsorbent to a collection container.

【符号の説明】[Explanation of symbols]

1 吸着剤 2 カラム 10 吸着剤の処理装置 12 排出管 14 抜き出しバルブ 17 排出配管 25 吸着剤の取り出し機構 27 ロート 28 空間 DESCRIPTION OF SYMBOLS 1 Adsorbent 2 Column 10 Adsorbent processing apparatus 12 Discharge pipe 14 Extraction valve 17 Discharge pipe 25 Adsorbent take-out mechanism 27 Funnel 28 Space

───────────────────────────────────────────────────── フロントページの続き (72)発明者 中村 仁宣 茨城県那珂郡東海村大字舟石川622番地1 三菱原子燃料株式会社内 (72)発明者 中川 次男 茨城県那珂郡東海村大字舟石川622番地1 三菱原子燃料株式会社内 Fターム(参考) 4G066 AB06A AB06B AB29A AB29B BA28 CA12 CA46 CA49 CA50 DA08  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Hitoshi Nobumura 622-1, Funashiishikawa, Tokai-mura, Naka-gun, Ibaraki Prefecture Inside Mitsubishi Nuclear Fuel Co., Ltd. (72) Inventor Tsugio Nakagawa 622, Funai-ishikawa, Tokai-mura, Naka-gun, Ibaraki Address 1 F term in Mitsubishi Nuclear Fuel Co., Ltd. (reference) 4G066 AB06A AB06B AB29A AB29B BA28 CA12 CA46 CA49 CA50 DA08

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 金属元素を吸着するための吸着剤が収納
された容器内に金属元素を含有した溶液を供給して溶液
中の金属元素を吸着剤に吸着させて乾燥させ、この吸着
剤を排出するようにした金属元素吸着剤の処理装置にお
いて、 前記容器内には、吸着剤を収容してその流出をガイドす
ると共に前記溶液を通過させるガイド部が配設され、 前記吸着剤を容器から取り出すための開閉手段が設けら
れていることを特徴とする金属元素吸着剤の処理装置。
1. A solution containing a metal element is supplied into a container containing an adsorbent for adsorbing a metal element, and the metal element in the solution is adsorbed by the adsorbent and dried. In the apparatus for treating a metal element adsorbent that is discharged, a guide portion that accommodates the adsorbent, guides the outflow thereof, and passes the solution is disposed in the container, and the adsorbent is removed from the container. An apparatus for treating a metal element adsorbent, comprising an opening / closing means for taking out the metal element.
JP843899A 1999-01-14 1999-01-14 Treatment device for adsorbent for metal element Pending JP2000206290A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP843899A JP2000206290A (en) 1999-01-14 1999-01-14 Treatment device for adsorbent for metal element

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP843899A JP2000206290A (en) 1999-01-14 1999-01-14 Treatment device for adsorbent for metal element

Publications (1)

Publication Number Publication Date
JP2000206290A true JP2000206290A (en) 2000-07-28

Family

ID=11693144

Family Applications (1)

Application Number Title Priority Date Filing Date
JP843899A Pending JP2000206290A (en) 1999-01-14 1999-01-14 Treatment device for adsorbent for metal element

Country Status (1)

Country Link
JP (1) JP2000206290A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003279687A (en) * 2002-03-25 2003-10-02 Japan Nuclear Cycle Development Inst States Of Projects Actinide containing waste liquid treatment equipment
JP2011242356A (en) * 2010-05-21 2011-12-01 Toshiba Corp Drying apparatus and drying method for radioactive waste
JP2016211885A (en) * 2015-04-30 2016-12-15 株式会社神鋼環境ソリューション Device for absorbing radioactive materials, and method for using the same
JP2016211918A (en) * 2015-05-01 2016-12-15 株式会社神鋼環境ソリューション Adsorption tower and water processing facility

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003279687A (en) * 2002-03-25 2003-10-02 Japan Nuclear Cycle Development Inst States Of Projects Actinide containing waste liquid treatment equipment
JP2011242356A (en) * 2010-05-21 2011-12-01 Toshiba Corp Drying apparatus and drying method for radioactive waste
JP2016211885A (en) * 2015-04-30 2016-12-15 株式会社神鋼環境ソリューション Device for absorbing radioactive materials, and method for using the same
JP2016211918A (en) * 2015-05-01 2016-12-15 株式会社神鋼環境ソリューション Adsorption tower and water processing facility

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