JP2902235B2 - How to recover iodine - Google Patents

How to recover iodine

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Publication number
JP2902235B2
JP2902235B2 JP4328961A JP32896192A JP2902235B2 JP 2902235 B2 JP2902235 B2 JP 2902235B2 JP 4328961 A JP4328961 A JP 4328961A JP 32896192 A JP32896192 A JP 32896192A JP 2902235 B2 JP2902235 B2 JP 2902235B2
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JP
Japan
Prior art keywords
iodine
waste
gas
liquid
recovered
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
Application number
JP4328961A
Other languages
Japanese (ja)
Other versions
JPH06157005A (en
Inventor
照雄 佐藤
光済 山口
義夫 吉田
康彦 大谷
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.)
GODO SHIGEN SANGYO KK
Original Assignee
GODO SHIGEN SANGYO KK
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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B7/00Halogens; Halogen acids
    • C01B7/13Iodine; Hydrogen iodide
    • C01B7/14Iodine

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Treating Waste Gases (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、廃棄物中に含有される
沃素又は沃素化合物より経済的かつ安全に沃素を回収す
る方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for economically and safely recovering iodine from iodine or iodine compounds contained in waste.

【0002】[0002]

【従来の技術】沃素は、生活関連用原料として、レント
ゲン造影剤、医薬品、殺菌防黴剤、また工業用として、
触媒安定剤、写真用原料、農業用として飼料添加剤、除
草剤等に使用されており、世界的に貴重な資源である。
沃素又は沃素化合物を含有する廃棄物から高価な沃素を
回収することは、経済的、自然環境保護的、省資源の点
から見ても非常に有益である。前述のように、沃素は種
々製品の原料、中間体、触媒等に使用される。例えば、
有機化合物の合成には沃素が単体あるいは化合物として
使用されるが、使用された全ての沃素が合成に関与する
わけではない。一部は、反応しないでそのまま残った
り、他の化合物になったりする。又、合成物質の純度を
高める精製工程において溶剤を使用すれば、合成物質の
一部が溶剤に溶解したりして、全てが回収されるとは限
らない。従って、製造工程より排出される廃棄物は、沃
素を単体或いは種々の無機及び有機化合物の形で含有
し、その形状も廃液、廃油、汚泥物と様々である。従
来、沃素回収に関して種々の提案がなされている。特に
燃焼法に関する沃素回収には、以下の提案が主になされ
ている。例えば、特公昭54−13234号公報には、
沃素又は沃素化合物を含有する廃棄物を燃焼炉に連続的
に導入して遊離沃素を発生させ、この沃素ガスをチオ硫
酸ナトリウム又は亜硫酸ナトリウム水溶液で吸収する方
法が記載されている。又、特開平1−108102号公
報には、有機化合物、沃素及び/又は沃素化合物、アル
カリ金属化合物を含有する廃棄物から沃素を回収するた
めに使用する沃素回収燃焼炉に関しての記載がなされて
いる。
2. Description of the Related Art Iodine is used as a raw material for daily life, as an X-ray contrast agent, a pharmaceutical, a bactericidal and antifungal agent, and as an industrial product.
It is used as a catalyst stabilizer, a raw material for photography, and as a feed additive and a herbicide for agricultural use, and is a valuable resource worldwide.
Recovering expensive iodine from waste containing iodine or iodine compounds is very advantageous from the viewpoints of economical, environmental protection and resource saving. As described above, iodine is used for raw materials, intermediates, catalysts, etc. of various products. For example,
In the synthesis of organic compounds, iodine is used alone or as a compound, but not all iodine used is involved in the synthesis. Some may remain unreacted or become other compounds. Further, if a solvent is used in a purification step for increasing the purity of a synthetic substance, not all of the synthetic substance may be dissolved in the solvent, and not all of the synthetic substance may be recovered. Therefore, the waste discharged from the manufacturing process contains iodine in the form of a simple substance or various inorganic and organic compounds, and the shape thereof is various, such as waste liquid, waste oil, and sludge. Conventionally, various proposals have been made regarding iodine recovery. In particular, the following proposals are mainly made for iodine recovery relating to the combustion method. For example, Japanese Patent Publication No. 54-13234 discloses that
A method is described in which waste containing iodine or an iodine compound is continuously introduced into a combustion furnace to generate free iodine, and the iodine gas is absorbed by an aqueous solution of sodium thiosulfate or sodium sulfite. Further, Japanese Patent Application Laid-Open No. 1-108102 discloses a combustion furnace for recovering iodine used for recovering iodine from waste containing an organic compound, iodine and / or an iodine compound, and an alkali metal compound. .

【0003】[0003]

【発明が解決しようとする課題】前記従来の方法は、沃
素含有廃棄物から沃素を回収すると言う点では非常に有
益な方法である。しかし、化学薬品を必要以上に使用
し、且つ操作が複雑になるという欠点がある。
The above-mentioned conventional method is a very useful method in that iodine is recovered from iodine-containing waste. However, there are disadvantages in that chemicals are used more than necessary and the operation is complicated.

【0004】[0004]

【課題を解決するための手段】前述の問題を有利に解決
するために、本発明の沃素の回収方法においては、沃素
又は沃素化合物を含有する廃棄物にアルカリ金属化合物
及び溶剤を混合し、その混合物を、燃焼装置を有する燃
焼炉に導入して熱処理し、その熱処理ガス中に含まれる
沃素化合物をアルカリ性の水溶液に吸収させる。
In order to advantageously solve the above-mentioned problems, in the method for recovering iodine of the present invention, an alkali metal compound and a solvent are mixed with a waste containing iodine or an iodine compound. The mixture is introduced into a combustion furnace having a combustion device and heat-treated, and the iodine compound contained in the heat-treated gas is absorbed by an alkaline aqueous solution.

【0005】次に本発明について詳細に説明する。沃素
又は沃素化合物を含有する廃棄物とは、イオヘキソー
ル、イオパミドール等のレントゲン造影剤、5−アセト
アミド−2,4,6−トリヨード−N,N′−ビス
(2,3−ジヒドロキシプロピル)−イソフタルアミド
等のレントゲン造影剤の中間体等及び沃化ナトリウムを
含有する有機溶剤等で、各々の性状は高粘性液体、固体
又は液体である。
Next, the present invention will be described in detail. The waste containing iodine or an iodine compound includes radiographic agents such as iohexol and iopamidol, 5-acetamido-2,4,6-triiodo-N, N'-bis (2,3-dihydroxypropyl) -isophthalamide The properties of each of the intermediates such as X-ray contrast agents and organic solvents containing sodium iodide are highly viscous liquids, solids or liquids.

【0006】本発明において使用されるアルカリ金属化
合物は種々あるが、生じた化合物の取扱い易さ及び経済
的な点から、水酸化ナトリウムが好ましい。水酸化ナト
リウム添加量は、廃棄物中の沃素量に対してアルカリ金
属のモル比が1:1.5以下、好ましくは1:0.6〜1.2
の範囲が良い。
Although there are various alkali metal compounds used in the present invention, sodium hydroxide is preferred from the viewpoints of easy handling of the resulting compound and economy. The amount of sodium hydroxide added is such that the molar ratio of alkali metal to the amount of iodine in the waste is 1: 1.5 or less, preferably 1: 0.6 to 1.2.
Good range.

【0007】溶剤は、燃焼炉の噴霧ノズルを通過させる
為に廃棄物の形状を液状又はスラリー状にするために添
加するもので、廃棄物の種類及び形状によって添加物質
及び量も異なる。一般的には水の使用が好ましいが、廃
棄物によっては、メタノール、エタノール、アセトン等
の有機溶媒を使用することもある。本発明において、沃
素を沃化水素に変えるのに充分な水素化合物を必要とす
るが、取扱い易さから水又は天然ガスが好ましい。
[0007] The solvent is added to make the shape of the waste liquid or slurry in order to pass through the spray nozzle of the combustion furnace, and the added substance and the amount vary depending on the type and shape of the waste. In general, use of water is preferable, but depending on the waste, an organic solvent such as methanol, ethanol, or acetone may be used. In the present invention, a sufficient hydrogen compound is required to convert iodine to hydrogen iodide, but water or natural gas is preferred because of easy handling.

【0008】本発明における熱処理とは、炉内で次式
(1)(2)(3)の様な化学反応を生じさせる様に、
温度を800〜1400℃、好ましくは950〜110
0℃に保持し、空気量を排出ガスの酸素濃度が4〜12
%好ましくは6〜10%となる様に調節する。この反応
に関与しない過剰の可燃性物質は、反応後過剰の空気に
より燃焼され、炉内の温度保持に提供される。 CH4 +2H2 O → CO2 +4H2 ……(1) I2 +H2 → 2HI ……(2) HI+NaOH → NaI+H2 O ……(3)
[0008] The heat treatment in the present invention means that a chemical reaction such as the following formulas (1), (2) and (3) occurs in a furnace.
The temperature is 800-1400 ° C., preferably 950-110
0 ° C and the amount of air was adjusted so that the oxygen concentration of the exhaust gas was 4-12.
%, Preferably 6 to 10%. Excess combustibles that do not participate in the reaction are burned by excess air after the reaction and provided for maintaining the temperature in the furnace. CH 4 + 2H 2 O → CO 2 + 4H 2 (1) I 2 + H 2 → 2HI (2) HI + NaOH → NaI + H 2 O (3)

【0009】温度及び燃焼空気量を、廃棄物の種類、性
質により適当に調節することによって、燃焼炉から排出
されるガス中にはほとんど遊離沃素が存在しない。それ
故、排出ガスを冷却するだけで沃素化合物好ましくは沃
化水素及び沃化ナトリウムを回収出来る利点がある。
By properly adjusting the temperature and the amount of combustion air according to the type and nature of the waste, there is almost no free iodine in the gas discharged from the combustion furnace. Therefore, there is an advantage that the iodine compound, preferably hydrogen iodide and sodium iodide can be recovered only by cooling the exhaust gas.

【0010】アルカリ性の水溶液に吸収させるとは、排
出ガス中の沃化水素及び炭酸ガスを吸収させると回収液
のpHが酸性となり金属材質を腐食する。それを防止す
る為に回収液のpH7.0〜10.0好ましくは8.0〜9.5
の範囲になるように調節する。アルカリ性に調節する化
学薬品は種々あるが、多品種の薬品を使用するのは装置
及び操作が複雑となるので上記に使用した水酸化ナトリ
ウムを使用するのが好ましい。
[0010] To absorb in an alkaline aqueous solution means that when hydrogen iodide and carbon dioxide gas in the exhaust gas are absorbed, the pH of the recovered liquid becomes acidic and the metal material is corroded. In order to prevent this, the pH of the recovered solution is 7.0 to 10.0, preferably 8.0 to 9.5.
Adjust so that it is within the range. Although there are various chemicals for adjusting the alkalinity, it is preferable to use the sodium hydroxide used above because using a variety of chemicals complicates the equipment and operation.

【0011】本発明の方法を実施する工程の一例を図1
に基づき説明する。沃素又は沃素化合物を含有する廃棄
物6を廃棄物濃度調整槽5にて水酸化ナトリウム7及び
水8で一定濃度に調整する。次にこの調整液を燃焼炉1
に導入し、熱処理させる。燃焼炉1内をあらかじめ温度
950〜1100℃に保持しておく。次に水8を一定時
間噴霧した後、廃棄物溶解調整槽5より調整液を燃焼炉
の適当なる位置に導入して噴霧ノズル12で噴霧する。
廃棄物溶解調整槽5の液は噴霧ノズル12を通過するも
のであれば固形物が存在するスラリー状のものでも良
い。熱処理ガスは再度13より空気をいれて完全燃焼さ
せて冷却兼溶解槽2に導入し、ガス温度を90℃以下に
冷却し、ガス中に含有する沃化ナトリウム及び炭酸ナト
リウムの固体を溶解する。冷却塔3で再度50℃以下に
ガスを冷却する。冷却されたガスはデミスター4にて沃
化水素を吸収し、粉塵、ミストを捕集し、排気ガス14
として排出する。排気ガス14中には遊離沃素ガスは存
在せず、排気ガス中の沃素含有量は吸収液中の沃素濃度
及び飛散ミスト量によって異なるが、1mg/m3 N 以下で
ある。(記号m3 N は、0℃、760mmHgの標準状態に換
算したガス体積量である。以下、ガス体積量について
は、この記号を使用する)。水酸化ナトリウム7及び水
8を沃素回収液15の沃素濃度及びpHが一定になる様
にデミスター4より給液し、冷却塔3、冷却兼溶解槽2
を通過させて沃素回収液15を得る。回収液は空冷塔1
6,17で冷却され、循環使用される。沃素回収液15
は沃化ナトリウム及び炭酸ナトリウムを含むアルカリ性
溶液である。この回収液から精製沃素を回収するには、
硫酸等で酸性とした後、塩素を吹き込んで遊離沃素を沈
澱させ、次いで加圧溶融する公知の方法で精製する。こ
の方法では、遊離した沃素の還元剤(チオ硫酸ナトリウ
ム等)又は多量の捕集剤(水酸化ナトリウム)を必要と
しない事及び連続的に処理可能な事などの利点がある。
FIG. 1 shows an example of steps for carrying out the method of the present invention.
It will be described based on. A waste 6 containing iodine or an iodine compound is adjusted to a constant concentration with sodium hydroxide 7 and water 8 in a waste concentration adjusting tank 5. Next, this adjusted liquid is supplied to the combustion furnace 1
And heat-treated. The temperature in the combustion furnace 1 is previously maintained at 950 to 1100 ° C. Next, after the water 8 is sprayed for a certain period of time, the adjusting liquid is introduced from the waste dissolution adjusting tank 5 to an appropriate position in the combustion furnace and sprayed by the spray nozzle 12.
The liquid in the waste dissolution adjusting tank 5 may be a slurry containing solid matter as long as it passes through the spray nozzle 12. The heat treatment gas is introduced again into the cooling and dissolving tank 2 by injecting air from 13 again and introduced into the cooling and dissolving tank 2 to cool the gas temperature to 90 ° C. or lower, and dissolve sodium iodide and sodium carbonate contained in the gas. The gas is cooled again to 50 ° C. or lower in the cooling tower 3. The cooled gas absorbs hydrogen iodide in the demister 4, collects dust and mist, and removes the exhaust gas 14.
To be discharged. There is no free iodine gas in the exhaust gas 14, and the iodine content in the exhaust gas is 1 mg / m 3 N or less, depending on the iodine concentration in the absorbing solution and the amount of scattered mist. (The symbol m 3 N is the gas volume converted to the standard state of 0 ° C. and 760 mmHg. Hereinafter, this symbol is used for the gas volume.) Sodium hydroxide 7 and water 8 are supplied from the demister 4 so that the iodine concentration and pH of the iodine recovery liquid 15 become constant, and the cooling tower 3 and the cooling and dissolving tank 2
And an iodine recovery liquid 15 is obtained. The recovered liquid is air cooling tower 1
It is cooled in 6, 17 and used for circulation. Iodine recovery liquid 15
Is an alkaline solution containing sodium iodide and sodium carbonate. To recover purified iodine from this recovered solution,
After acidification with sulfuric acid or the like, chlorine is blown in to precipitate free iodine, and then purified by a known method of melting under pressure. This method has advantages in that a reducing agent for free iodine (such as sodium thiosulfate) or a large amount of a collecting agent (sodium hydroxide) is not required, and that it can be treated continuously.

【0012】沃素は極めて腐食性の強い元素でほとんど
の金属材料は腐食されてしまう。従って、一般に沃素回
収装置の材質選択は極めて困難である。ところが本発明
では前記において説明した様に排出ガス中に腐食ガスの
割合が少なく、燃焼炉1以後の工程は還元性及び酸化性
腐食作用が極度に抑制された条件下にある。又、その工
程における温度も90℃以下と低く、溶液も弱アルカリ
性であるので安全である。従って、ステンレススチール
及び塩化ビニール等の材質を選択でき、装置設計も容易
であり、経済的且つ安全に沃素を回収出来る利点を多く
有している。
Iodine is an extremely corrosive element, and most metallic materials are corroded. Therefore, it is generally very difficult to select a material for the iodine recovery apparatus. However, in the present invention, as described above, the proportion of corrosive gas in the exhaust gas is small, and the processes after the combustion furnace 1 are under conditions in which the reducing and oxidizing corrosion effects are extremely suppressed. In addition, the temperature in the process is as low as 90 ° C. or less, and the solution is weakly alkaline, so that it is safe. Therefore, materials such as stainless steel and vinyl chloride can be selected, the apparatus can be easily designed, and there are many advantages that iodine can be recovered economically and safely.

【0013】[0013]

【実施例】次に、実施例により本発明の方法を具体的に
説明する。 実施例1 組成がイオヘキソール74重量%、イソプロピルアルコ
ール13重量%、水13重量%である高粘性液体廃棄物
10Kgに、水酸化ナトリウム1Kg、水40Kgを加えて混
合し、51Kgの調整液を作る。沃素含有量は3433g
である。沃素対アルカリ金属モル比は1:0.93であ
る。天然ガス量毎時2m3 N 、空気量毎時20m3 N の燃焼
で温度を一定に保持した燃焼炉に数分間水を噴霧した
後、上記調整液を毎時6Kgで噴霧し、熱処理する。燃焼
炉内温度は調整液を噴霧した後は1050℃に保持する
様に空気量及び天然ガス量を調節する。熱処理された廃
棄物に燃焼炉途中より再度毎時20m3 N の空気を補給す
る。熱処理されたガスは冷却溶解槽2及び冷却塔3、デ
ミスター4を通過させて、冷却、溶解、吸収操作を経て
大気中に排出させる。冷却溶解槽出口ガス温度は85℃
以下、冷却塔出口ガス温度は42℃以下であった。デミ
スターへは毎時50リットルの水及び適当量の水酸化ナ
トリウムを補給し、pH8.5の回収液186リットルを
得た。回収沃素量は3423gで回収率99.6%であっ
た。又、回収液には未分解の廃棄物は検出されなかっ
た。大気中に放出される排ガス中には遊離沃素は検出さ
れず、ミストとして飛散した吸収液中の沃素イオンが0.
9mg/m3 N の濃度で測定された。大気中に逃げた沃素量
は0.7gで、沃素損失率は0.02%であった。排ガス中
の酸素濃度は10%であった。燃焼炉壁に付着した沃化
ナトリウム固形物は沃素量として0.37%であった。
Next, the method of the present invention will be described in detail with reference to examples. Example 1 1 kg of sodium hydroxide and 40 kg of water are added to 10 kg of a highly viscous liquid waste composed of 74% by weight of iohexol, 13% by weight of isopropyl alcohol, and 13% by weight of water, and mixed to prepare a 51 kg adjusted liquid. The iodine content is 3433 g
It is. The molar ratio of iodine to alkali metal is 1: 0.93. After spraying water for several minutes into a combustion furnace in which the temperature is kept constant by burning 2 m 3 N / hour of natural gas and 20 m 3 N / hour of air, the above-mentioned adjusted liquid is sprayed at 6 kg / hour and heat-treated. The temperature in the combustion furnace is adjusted to the air amount and the natural gas amount so as to maintain the temperature at 1050 ° C. after spraying the adjusting liquid. The heat-treated waste is replenished with air at 20 m 3 N / h from the middle of the combustion furnace. The heat-treated gas passes through the cooling / dissolving tank 2, the cooling tower 3, and the demister 4, and is discharged into the atmosphere through cooling, melting, and absorbing operations. Gas temperature of cooling / dissolution tank outlet is 85 ℃
Hereinafter, the cooling tower outlet gas temperature was 42 ° C. or less. The demister was replenished with 50 liters of water and an appropriate amount of sodium hydroxide per hour to obtain 186 liters of a recovered liquid having a pH of 8.5. The recovered iodine amount was 3423 g, and the recovery rate was 99.6%. Also, no undecomposed waste was detected in the recovered liquid. Free iodine is not detected in the exhaust gas released into the atmosphere, and iodine ions in the absorbing solution scattered as mist are 0.
It was measured at a concentration of 9 mg / m 3 N. The amount of iodine that escaped to the atmosphere was 0.7 g, and the iodine loss rate was 0.02%. The oxygen concentration in the exhaust gas was 10%. The solid content of sodium iodide on the combustion furnace wall was 0.37% in terms of iodine.

【0014】回収液186リットルに硫酸を加えてpH
2とした後、塩素を加えて加圧溶融する公知の方法で処
理、精製し、精製沃素結晶3354gを得た。この精製
沃素の純度は99.85%であった。また沃素含有廃棄物
からの精製沃素回収率は97.6%であった。
Sulfuric acid is added to 186 liters of the recovered
After that, the mixture was treated and refined by a known method of adding chlorine and pressurizing and melting to obtain 3354 g of purified iodine crystal. The purity of the purified iodine was 99.85%. The recovery rate of purified iodine from iodine-containing waste was 97.6%.

【0015】実施例2 組成が5−アセトアミド−2,4,6−トリヨード−
N,N′−ビス(2,3−ジヒドロキシプロピル)−イ
ソフタルアミド28重量%、塩化ナトリウム8重量%、
酢酸ナトリウム1重量%、水63重量%の含水固体10
Kgに水酸化ナトリウム0.45Kg、水10Kgを加えて混合
し、20.45Kgの調整液を作る。沃素含有量は1513
gである。沃素対アルカリ金属のモル比は1:0.97で
ある。実施例1と同様に熱処理を行って、pH8.9の回
収液85リットルを得た。回収沃素量は1505gで回
収率99.5%であった。又、回収液には未分解の廃棄物
は検出されなかった。大気中に放出される排ガス中には
遊離沃素は検出されず、ミストとして飛散した吸収液中
の沃素イオンが0.8mg/m3 N の濃度で測定された。大気
中に逃げた沃素量は0.6gで、沃素損失率は0.04%で
あった。排ガス中の酸素濃度は9%であった。燃焼炉壁
に付着した沃化ナトリウム固形物は沃素量として0.44
%であった。
Example 2 Composition of 5-acetamido-2,4,6-triiodo-
28% by weight of N, N'-bis (2,3-dihydroxypropyl) -isophthalamide, 8% by weight of sodium chloride,
1% by weight of sodium acetate and 63% by weight of water 10
0.45 kg of sodium hydroxide and 10 kg of water are added to and mixed with Kg to prepare a preparation of 20.45 kg. The iodine content is 1513
g. The molar ratio of iodine to alkali metal is 1: 0.97. Heat treatment was carried out in the same manner as in Example 1 to obtain 85 liters of a recovered solution having a pH of 8.9. The amount of iodine recovered was 1505 g and the recovery rate was 99.5%. Also, no undecomposed waste was detected in the recovered liquid. No free iodine was detected in the exhaust gas discharged into the atmosphere, and iodine ions in the absorbing solution scattered as mist were measured at a concentration of 0.8 mg / m 3 N. The amount of iodine that escaped to the atmosphere was 0.6 g, and the iodine loss rate was 0.04%. The oxygen concentration in the exhaust gas was 9%. The solid sodium iodide adhered to the combustion furnace wall was 0.44 as iodine.
%Met.

【0016】回収液85リットルに硫酸を加えてpH2
とした後、塩素を加えて加圧溶融する公知の方法で処
理、精製し、精製沃素結晶1474gを得た。この精製
沃素の純度は99.78%であった。また沃素含有廃棄物
からの精製沃素回収率は97.4%であった。
Sulfuric acid is added to 85 liters of the recovered solution to adjust the pH to 2
After that, treatment and purification were carried out by a known method of adding chlorine and adding pressure to melt, thereby obtaining 1474 g of purified iodine crystals. The purity of the purified iodine was 99.78%. The recovery rate of purified iodine from the iodine-containing waste was 97.4%.

【0017】実施例3 組成が沃化ナトリウム12重量%、ジメチルアセトアミ
ド5重量%、ホルムアルデヒド6重量%、メタノール2
重量%、水75重量%の液体20Kgをそのままで熱処理
を行う。沃素含有量は2032gである。沃素対アルカ
リ金属のモル比は1:1である。実施例1と同様に熱処
理を行って、pH9の回収液120リットルを得た。回
収沃素量は2002gで回収率98.5%であった。又、
回収液には未分解の廃棄物は検出されなかった。大気中
に放出される排ガス中には遊離沃素は検出されず、ミス
トとして飛散した吸収液中の沃素イオンが0.9mg/m3 N
の濃度で測定された。大気中に逃げた沃素量は1.0g
で、沃素損失率は0.05%であった。排ガス中の酸素濃
度は7%であった。燃焼炉壁に付着した沃化ナトリウム
固形物は沃素量として1.44%であった。
Example 3 The composition was 12% by weight of sodium iodide, 5% by weight of dimethylacetamide, 6% by weight of formaldehyde, and 2% by weight of methanol.
A heat treatment is performed on 20 kg of a liquid containing 75% by weight of water and 75% by weight of water. The iodine content is 2032 g. The molar ratio of iodine to alkali metal is 1: 1. Heat treatment was performed in the same manner as in Example 1 to obtain 120 liters of a recovery liquid having a pH of 9. The recovered iodine amount was 2002 g and the recovery rate was 98.5%. or,
No undecomposed waste was detected in the recovered liquid. No free iodine was detected in the exhaust gas released into the atmosphere, and 0.9 mg / m 3 N of iodine ions in the absorbing solution scattered as mist was detected.
It was measured at a concentration of 1.0g of iodine escaping into the atmosphere
And the iodine loss rate was 0.05%. The oxygen concentration in the exhaust gas was 7%. The solid content of sodium iodide on the combustion furnace wall was 1.44% in terms of iodine.

【0018】回収液120リットルに硫酸を加えてpH
2とした後、塩素を加えて加圧溶融する公知の方法で処
理、精製し、精製沃素結晶1960gを得た。この精製
沃素の純度は99.81%であった。また沃素含有廃棄物
からの精製沃素回収率は96.5%であった。
Sulfuric acid is added to 120 liters of the collected solution to adjust the pH.
Then, the mixture was treated and refined by a known method of adding chlorine and adding pressure to obtain 1960 g of purified iodine crystals. The purity of the purified iodine was 99.81%. The recovery rate of purified iodine from the iodine-containing waste was 96.5%.

【0019】比較例 比較例として次の試験を行った。実施例3と同様の廃棄
物液体5Kgに硫酸を加えてpH2とし、塩素を加えて加
圧溶融する公知の方法で処理、精製したが遊離した沃素
が溶剤に簡単に溶解し、黒い比重の大きな液体になるだ
けで、精製沃素結晶を得る事は出来なかった。また沃素
含有廃棄物からの精製沃素回収率は0%であった。
Comparative Example The following test was performed as a comparative example. Sulfuric acid was added to 5 kg of the same waste liquid as in Example 3 to adjust the pH to 2, then chlorine was added, and the mixture was treated and purified by a known method, but the released iodine was easily dissolved in the solvent, and the black specific gravity was large. It was not possible to obtain purified iodine crystals just by becoming liquid. The recovery of purified iodine from the iodine-containing waste was 0%.

【0020】[0020]

【発明の効果】本発明によれば、沃素又は沃素化合物を
含有する廃棄物にアルカリ金属化合物及び溶剤を混合
し、その混合物を、燃焼装置を有する燃焼炉に導入して
熱処理し、その熱処理ガス中に含まれる沃素化合物をア
ルカリ性の水溶液に吸収させるので、沃素及び沃素化合
物を含有する様々な廃棄物より、精製沃素を経済的に高
収率で安全に回収することができる。
According to the present invention, a waste containing iodine or an iodine compound is mixed with an alkali metal compound and a solvent, and the mixture is introduced into a combustion furnace having a combustion device and heat-treated. Since the iodine compound contained therein is absorbed by the alkaline aqueous solution, purified iodine can be economically recovered in high yield from various wastes containing iodine and iodine compounds.

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

【図1】本発明の方法を実施するプロセスの一例を示す
フローシートである。
FIG. 1 is a flow sheet showing an example of a process for implementing the method of the present invention.

【符号の説明】[Explanation of symbols]

1 燃焼炉 2 冷却兼溶解槽 3 冷却塔 4 デミスター 5 沃素含有廃棄物溶解調整槽 6 沃素含有廃棄物 7 水酸化ナトリウム 8 水 9 天然ガス 10 空気 11 燃焼装置 12 噴霧ノズル 13 二次空気 14 排出ガス 15 沃素回収液 16 空冷塔 17 空冷塔 Reference Signs List 1 combustion furnace 2 cooling and melting tank 3 cooling tower 4 demister 5 iodine-containing waste dissolution adjusting tank 6 iodine-containing waste 7 sodium hydroxide 8 water 9 natural gas 10 air 11 combustion device 12 spray nozzle 13 secondary air 14 exhaust gas 15 Iodine recovery liquid 16 Air cooling tower 17 Air cooling tower

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23G 7/04 601 F23G 7/04 601L ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI F23G 7/04 601 F23G 7/04 601L

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 沃素又は沃素化合物を含有する廃棄物に
アルカリ金属化合物及び溶剤を混合し、その混合物を、
燃焼装置を有する燃焼炉に導入して熱処理し、その熱処
理ガス中に含まれる沃素化合物をアルカリ性の水溶液に
吸収させることを特徴とする沃素の回収方法。
1. An alkali metal compound and a solvent are mixed with a waste containing iodine or an iodine compound.
A method for recovering iodine, comprising introducing into a combustion furnace having a combustion device, performing heat treatment, and absorbing an iodine compound contained in the heat treatment gas into an alkaline aqueous solution.
JP4328961A 1992-11-16 1992-11-16 How to recover iodine Expired - Lifetime JP2902235B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4328961A JP2902235B2 (en) 1992-11-16 1992-11-16 How to recover iodine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4328961A JP2902235B2 (en) 1992-11-16 1992-11-16 How to recover iodine

Publications (2)

Publication Number Publication Date
JPH06157005A JPH06157005A (en) 1994-06-03
JP2902235B2 true JP2902235B2 (en) 1999-06-07

Family

ID=18216052

Family Applications (1)

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Country Status (1)

Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006104092A (en) * 2004-10-01 2006-04-20 Asahi Kasei Chemicals Corp Manufacturing method of alkylene carbonate

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Publication number Priority date Publication date Assignee Title
US7736617B2 (en) 2005-05-02 2010-06-15 Nippoh Chemicals Co., Ltd. Method for recovering iodine
JP5281754B2 (en) * 2007-03-13 2013-09-04 日宝化学株式会社 Method for producing alkali metal iodide salt solution
CN102865583B (en) * 2012-09-26 2015-03-04 北京航天动力研究所 Device and method for saline organic wastewater immersed incineration quenching treatment
CN103418213A (en) * 2013-08-23 2013-12-04 瓮福(集团)有限责任公司 Iodine replacement device
WO2017134789A1 (en) 2016-02-04 2017-08-10 セントラルケミカル株式会社 Iodine recovery method and recovery apparatus
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006104092A (en) * 2004-10-01 2006-04-20 Asahi Kasei Chemicals Corp Manufacturing method of alkylene carbonate

Also Published As

Publication number Publication date
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