JPH0565837B2 - - Google Patents
Info
- Publication number
- JPH0565837B2 JPH0565837B2 JP59169342A JP16934284A JPH0565837B2 JP H0565837 B2 JPH0565837 B2 JP H0565837B2 JP 59169342 A JP59169342 A JP 59169342A JP 16934284 A JP16934284 A JP 16934284A JP H0565837 B2 JPH0565837 B2 JP H0565837B2
- Authority
- JP
- Japan
- Prior art keywords
- iodine
- adsorbent
- impregnated
- silver
- filled
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Landscapes
- Treating Waste Gases (AREA)
- Water Treatment By Sorption (AREA)
- Electrical Discharge Machining, Electrochemical Machining, And Combined Machining (AREA)
Description
〔発明の利用分野〕
本発明は、ヨウ素除去方法に係り、特に効能殿
ヨウ素が発生する再処理プラント等に適用するの
に好適なヨウ素除去方法に関するものである。
〔発明の背景〕
原子力施設では、周辺住民の放射能被曝を防止
するため、周辺環境に放出される放射能量を低減
するための種々の対策が講じられている。このう
ち、放射性ヨウ素に対しては、これが人体の甲状
腺に選択的に吸収され放射能被曝を増大させるた
め、特に厳格な放出放射能量の低減対策が施され
ている。排ガス低減対策としては、1〜2mmφ程
度の吸着材を充填したヨウ素除去フイルタの設置
が一般的に行なわれている。原子力施設の代表的
なものとしては原子力発電所と核燃料再処理プラ
ントがあげられる。前者では古くから添着炭フイ
ルタが使用されている。一方、後者の核燃料再処
理プラントでは、ヨウ素除去フイルタとして銀添
着吸着材が使用されている。同じヨウ素除去フイ
ルタではあるが、両者のフイルタに要求される性
能は大きく異なる。すなわち、前者の原子力発電
所では、対象とする放射性ヨウ素が短半減期の
131I(半減期8日)で、ヨウ素の濃度が0.1ppbと極
めて低い。一方、再処理プラントでは、対象とす
る放射性ヨウ素が長半減期の129I(半減期1.7×107
年)で、ヨウ素濃度が前者の500000倍の50ppmと
高い。以上のことから、再処理プラント排ガス処
理用の吸着材に対して以下の3つの事が要求され
る。すなわち、(1)ブラントからの放出放射能量を
低減するために129Iを高い効率で除去できるこ
と。(2)吸着材のヨウ素吸着容量が大きく廃棄物と
しての使用済吸着材量が少ないこと、および(3)
129Iを化学的に安定な化合物として半永久的に貯
蔵できること、の3点である。
このような観点から、現状では次の2つの方式
が研究開発、または実用化されている。この2つ
の方式の概要を第1図、第2図に示す。
第1図の方式は銀添着吸着材を充填した吸着塔
1のみで構成されるものである。この方式は、シ
ステムが単純であるため既に実用化されている
が、使用済の銀添着吸着材が直接廃棄されるた
め、高価な銀の使用量が多いという問題点があ
る。
第2図の方式は一度銀添着吸着材でヨウ素を高
い除去効率で吸着除去した後、H2によつて当該
銀添着吸着材を再生し、再生によつて発生したヨ
ウ素を銀よりも安価な鉛添着吸着材に吸着させよ
うとするものである。この方式は、銀添着吸着材
を充填した吸着塔1が2塔と、鉛添着吸着材を充
填した吸着塔2、H2を加熱するヒータ3、クー
ラー4、H2循環ポンプ5とから構成される。吸
着塔1の一方の塔は処理ガスを流しヨウ素を吸着
除去する。他方吸着塔1は、ヒータ3によつて加
熱したH2(500℃)で、再生される。このとき銀
添着吸着材からHI(ヨウ化水素)としてヨウ素が
脱着してくる。吸着塔1を通過したヨウ素を含む
H2はクーラー4で150℃に冷却され、H2循環ポ
ンプ5を介して鉛添着吸着材を充填した吸着塔3
に送られ、ここでヨウ素が吸着される。再生の終
了した吸着塔1は、再び処理ガス中のヨウ素の吸
着除去に使用されるため待機状態となり、ヨウ素
を吸着した鉛添着吸着材は廃棄される。したがつ
て、この方式では、高価な銀の消費量は、再生劣
化に伴ない発生する銀添着吸着材のみとなるた
め、第1図の方式に比べ1/10〜1/20と少ない。し
かしながら、システムが複雑となるため、初期の
設備投資が大きくなること、運転がはん雑となる
ことなどの問題が生ずる。
そこで、システムが単純で銀の消費量も少ない
ヨウ素の除去装置が要求されている。
〔発明の目的〕
本発明の目的は、銀の消費量が少なく高いヨウ
素の除去率を得ることができるヨウ素除去方法を
提供することにある。
〔発明の概要〕
本発明の特徴は、ヨウ素を含むガスの相対湿度
を40%以下にし、この相対湿度40%以下のガス
を、金属銅または金属鉛の少なくともいずれかを
含有する金属を添着した吸着材が充填され、吸着
温度が170℃以下である前段吸着塔内に導き、前
段吸着塔から流出したガスを、銀化合物を添着し
た吸着材を充填した後段吸着塔に供給することに
ある。
〔発明の実施例〕
本発明は以下の実験結果に基づきなされたもの
である。第1表に、種々の元素の中から選定した
3種の金属について、ヨウ素の吸着量を測定した
結果を示す。
[Field of Application of the Invention] The present invention relates to an iodine removal method, and particularly to an iodine removal method suitable for application to reprocessing plants and the like where effective iodine is generated. [Background of the Invention] At nuclear power facilities, various measures are taken to reduce the amount of radioactivity released into the surrounding environment in order to prevent surrounding residents from being exposed to radiation. Of these, radioactive iodine is selectively absorbed by the human thyroid and increases radiation exposure, so particularly strict measures are taken to reduce the amount of radioactivity released. As a measure to reduce exhaust gas, it is common practice to install an iodine removal filter filled with an adsorbent having a diameter of about 1 to 2 mm. Typical nuclear facilities include nuclear power plants and nuclear fuel reprocessing plants. In the former case, impregnated charcoal filters have been used for a long time. On the other hand, in the latter nuclear fuel reprocessing plant, a silver-impregnated adsorbent is used as an iodine removal filter. Although they are the same iodine removal filter, the performance required of the two filters is significantly different. In other words, in the former nuclear power plant, the target radioactive iodine has a short half-life.
131 I (half-life 8 days) and has an extremely low iodine concentration of 0.1 ppb. On the other hand, in the reprocessing plant, the target radioactive iodine is 129 I (half-life 1.7×10 7 ) , which has a long half-life.
year), and the iodine concentration is 50ppm, 500,000 times higher than in the former. From the above, the following three requirements are required for adsorbents for treating exhaust gas from reprocessing plants. That is, (1) 129 I can be removed with high efficiency in order to reduce the amount of radioactivity released from the blunt. (2) The iodine adsorption capacity of the adsorbent is large and the amount of used adsorbent as waste is small; and (3)
There are three points: 129 I can be stored semi-permanently as a chemically stable compound. From this point of view, the following two methods are currently being researched and developed or put into practical use. An outline of these two methods is shown in FIGS. 1 and 2. The system shown in FIG. 1 consists only of an adsorption tower 1 filled with a silver-impregnated adsorbent. This method has already been put into practical use because of its simple system, but it has the problem of using a large amount of expensive silver because the used silver-impregnated adsorbent is directly disposed of. The method shown in Figure 2 uses a silver-impregnated adsorbent to adsorb and remove iodine with high removal efficiency, then regenerates the silver-impregnated adsorbent with H2 , and uses the iodine generated by the regeneration as a material that is cheaper than silver. It is intended to be adsorbed onto a lead-impregnated adsorbent. This system consists of two adsorption towers 1 filled with a silver-impregnated adsorbent, an adsorption tower 2 filled with a lead-impregnated adsorbent, a heater 3 for heating H2 , a cooler 4, and an H2 circulation pump 5. Ru. One of the adsorption towers 1 allows a process gas to flow therethrough and adsorbs and removes iodine. On the other hand, the adsorption tower 1 is regenerated with H 2 (500° C.) heated by the heater 3. At this time, iodine is desorbed from the silver-impregnated adsorbent as HI (hydrogen iodide). Contains iodine passed through adsorption tower 1
The H 2 is cooled to 150°C by a cooler 4 and sent to an adsorption tower 3 filled with lead-impregnated adsorbent via an H 2 circulation pump 5.
, where iodine is adsorbed. The adsorption tower 1 that has been regenerated is placed in a standby state because it is used again to adsorb and remove iodine from the process gas, and the lead-impregnated adsorbent that has adsorbed iodine is discarded. Therefore, in this method, the consumption of expensive silver is reduced to 1/10 to 1/20 compared to the method shown in FIG. 1, since the amount of expensive silver consumed is limited to the silver-impregnated adsorbent generated as a result of regeneration deterioration. However, since the system becomes complicated, problems arise such as a large initial investment in equipment and complicated operation. Therefore, there is a need for an iodine removal device that has a simple system and consumes less silver. [Object of the Invention] An object of the present invention is to provide an iodine removal method that can achieve a high iodine removal rate with less silver consumption. [Summary of the Invention] The present invention is characterized in that the relative humidity of a gas containing iodine is set to 40% or less, and the gas having a relative humidity of 40% or less is impregnated with a metal containing at least either metallic copper or metallic lead. The gas is introduced into a first stage adsorption tower filled with adsorbent and whose adsorption temperature is 170°C or less, and the gas flowing out from the first stage adsorption tower is supplied to a second stage adsorption tower filled with an adsorbent impregnated with a silver compound. [Embodiments of the Invention] The present invention was made based on the following experimental results. Table 1 shows the results of measuring the adsorption amount of iodine for three types of metals selected from various elements.
本発明によれば、相対湿度40%以下のヨウ素を
含むガスを、金属銅または金属鉛の少なくともい
ずれかを含有する金属を添着した吸着材が充填さ
れ、吸着温度が170℃以下である前段吸着塔、及
び銀化合物を添着した吸着材を充填した後段吸着
塔に、順次供給するので、高いヨウ素の除去率が
得られ、かつ銀の消費量を著しく少なくできる。
銀の消費量は、第1図の装置に比べて約1/20にな
る。
According to the present invention, a gas containing iodine with a relative humidity of 40% or less is filled with an adsorbent impregnated with a metal containing at least either metallic copper or metallic lead, and the adsorption temperature is 170°C or less. Since it is sequentially supplied to the column and the subsequent adsorption column filled with an adsorbent impregnated with a silver compound, a high iodine removal rate can be obtained and the amount of silver consumed can be significantly reduced.
The amount of silver consumed is approximately 1/20th that of the device shown in Figure 1.
第1図は従来の銀添着吸着材を充填した吸着塔
単独によるヨウ素除去装置のフローを示す図、第
2図は従来の銀添着吸着材を繰返し使用する場合
のフローを示す図、第3図は金属銅を添着した本
発明の吸着材によるヨウ素吸着量と吸着温度との
関係を示す線図、第4図は金属銅を添着した吸着
材のヨウ素吸着量に及ぼす水蒸気の影響を示す線
図、第5図は本発明の一実施例を示す基本フロー
図、第6図は金属銅を添着した吸着材を充填した
吸着塔内でのヨウ素の吸着分布の一例を示した線
図、第7図は本発明の他の実施例の基本フローを
示す図である。
1……銀添着吸着材を充填した吸着塔、2……
鉛添着吸着材を充填した吸着塔、3……ヒータ、
4……クーラー、5……循環ポンプ、6……銅添
着吸着材を充填した吸着塔、7……ヒータ、8…
…除湿塔。
Figure 1 is a diagram showing the flow of an iodine removal device using only an adsorption tower filled with a conventional silver-impregnated adsorbent, Figure 2 is a diagram showing the flow when a conventional silver-impregnated adsorbent is used repeatedly, and Figure 3 4 is a diagram showing the relationship between the amount of iodine adsorbed by the adsorbent of the present invention impregnated with metallic copper and adsorption temperature, and FIG. 4 is a diagram showing the influence of water vapor on the amount of iodine adsorbed by the adsorbent impregnated with metallic copper. , FIG. 5 is a basic flow diagram showing one embodiment of the present invention, FIG. 6 is a diagram showing an example of the adsorption distribution of iodine in an adsorption tower filled with an adsorbent impregnated with metallic copper, and FIG. The figure is a diagram showing the basic flow of another embodiment of the present invention. 1... Adsorption tower filled with silver-impregnated adsorbent, 2...
Adsorption tower filled with lead-impregnated adsorbent, 3... heater,
4...Cooler, 5...Circulation pump, 6...Adsorption tower filled with copper-impregnated adsorbent, 7...Heater, 8...
...dehumidification tower.
Claims (1)
ヨウ素を含む前記ガスの相対湿度を40%以下に
し、この相対湿度40%以下の前記ガスを、金属銅
または金属鉛の少なくともいずれかを含有する金
属を添着した吸着材が充填され、吸着温度が170
℃以下である前段吸着塔内に導き、前記前段吸着
塔から流出した前記ガスを、銀化合物を添着した
吸着材を充填した後段吸着塔に供給することを特
徴とするヨウ素除去方法。1 In a method for removing iodine from gas,
The relative humidity of the gas containing iodine is set to 40% or less, and the gas with a relative humidity of 40% or less is filled with an adsorbent impregnated with a metal containing at least either metallic copper or metallic lead, and the adsorption temperature is 170
A method for removing iodine, characterized in that the gas is introduced into a first adsorption tower at a temperature of 0.degree.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16934284A JPS6147595A (en) | 1984-08-15 | 1984-08-15 | Device for removing iodine |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16934284A JPS6147595A (en) | 1984-08-15 | 1984-08-15 | Device for removing iodine |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6147595A JPS6147595A (en) | 1986-03-08 |
| JPH0565837B2 true JPH0565837B2 (en) | 1993-09-20 |
Family
ID=15884778
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP16934284A Granted JPS6147595A (en) | 1984-08-15 | 1984-08-15 | Device for removing iodine |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6147595A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0721535U (en) * | 1993-09-20 | 1995-04-18 | 合資会社泉鉄工所 | Paper tube |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6370198A (en) * | 1986-09-12 | 1988-03-30 | 株式会社日立製作所 | Volume-reduction processing method and device for spent nuclear-fuel reprocessing waste liquor |
| JP2008116280A (en) * | 2006-11-02 | 2008-05-22 | Toyobo Co Ltd | Radioactive iodine collecting material and method of collecting the same |
| TWI843706B (en) * | 2017-09-19 | 2024-06-01 | 美商哈尼威爾國際公司 | Heat transfer methods, systems and compositions |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS52127598A (en) * | 1976-04-16 | 1977-10-26 | Hitachi Ltd | Two layers type filter for removing radioactive iodine |
| JPS59112294A (en) * | 1982-12-20 | 1984-06-28 | 株式会社日立製作所 | Equipment for removing radioactive iodine from nuclear fuel reprocessing facilities |
-
1984
- 1984-08-15 JP JP16934284A patent/JPS6147595A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0721535U (en) * | 1993-09-20 | 1995-04-18 | 合資会社泉鉄工所 | Paper tube |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6147595A (en) | 1986-03-08 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| EXPY | Cancellation because of completion of term |