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JPS5941922B2 - Bromine recovery method - Google Patents

Bromine recovery method

Info

Publication number
JPS5941922B2
JPS5941922B2 JP1333579A JP1333579A JPS5941922B2 JP S5941922 B2 JPS5941922 B2 JP S5941922B2 JP 1333579 A JP1333579 A JP 1333579A JP 1333579 A JP1333579 A JP 1333579A JP S5941922 B2 JPS5941922 B2 JP S5941922B2
Authority
JP
Japan
Prior art keywords
bromine
resin
anion exchange
gas
basic anion
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP1333579A
Other languages
Japanese (ja)
Other versions
JPS55109201A (en
Inventor
一成 井川
光雄 菊地
昭 山根
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.)
Tosoh Corp
Original Assignee
Toyo Soda Manufacturing 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 Toyo Soda Manufacturing Co Ltd filed Critical Toyo Soda Manufacturing Co Ltd
Priority to JP1333579A priority Critical patent/JPS5941922B2/en
Priority to IL59279A priority patent/IL59279A/en
Priority to AU55301/80A priority patent/AU536419B2/en
Publication of JPS55109201A publication Critical patent/JPS55109201A/en
Publication of JPS5941922B2 publication Critical patent/JPS5941922B2/en
Expired legal-status Critical Current

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  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】 本発明は臭素を含有するガス力1ら臭素を回収する方法
に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for recovering bromine from a bromine-containing gas source.

詳(7くは、臭素を含有するガスと強塩基性陰イオン交
換樹脂とを接触させ、臭素を吸着させる工程、臭素を吸
着した該樹脂を60〜130℃に加熱して臭素を樹脂か
ら脱着する工程とから成る臭素の回収方法を提供するも
のである。
Details (7) A step in which a gas containing bromine is brought into contact with a strongly basic anion exchange resin to adsorb bromine, and the resin that has adsorbed bromine is heated to 60 to 130°C to desorb bromine from the resin. The present invention provides a method for recovering bromine, which comprises the steps of:

臭素を製造する方法としては、原料によって、(1)ニ
ガリ法、(2)海水法、(3)天然カン水洗に分けられ
、我が国では主として海水法を採用している。
Methods for producing bromine are divided into (1) the bittern method, (2) the seawater method, and (3) natural can washing, depending on the raw material.In Japan, the seawater method is mainly used.

海水法には亜硫酸ガス法と力性ソーダ吸収法かある。The seawater method includes the sulfur dioxide gas method and the hydric soda absorption method.

亜硫酸ガス法は海水に硫酸を加えてp)Iを約3に調整
したのち、塩素を吹き込み臭素を遊離させる。
In the sulfur dioxide gas method, sulfuric acid is added to seawater to adjust p)I to about 3, and then chlorine is blown in to liberate bromine.

(1式)。2NaBr+C1−+Br2+2NaCV
(1)これを、発生塔上部から流下させ下
部より、空気を吹き込んで、臭素を海水中より追い出す
(発生ガスとよぶ) 次に、この発生ガスに亜硫酸ガスを吹き込んで臭気を臭
化水素に還元し硫酸と共に水に吸収させる(2式)。
(1 set). 2NaBr+C1-+Br2+2NaCV
(1) This is allowed to flow down from the top of the generation tower, and air is blown from the bottom to drive out bromine from the seawater (referred to as generated gas).Next, sulfur dioxide gas is blown into this generated gas to convert the odor into hydrogen bromide. Reduce and absorb into water together with sulfuric acid (2 formulas).

B r 2 +802 + 2H2()” 2HB r
+H2804(2)次に、これを蒸留塔の上部より流
下し下部より水蒸気と塩素を吹き込むと臭化水素は塩素
によっで酸化され、遊離した臭素は、水蒸気とともに留
出する(3式)。
B r 2 +802 + 2H2()” 2HB r
+H2804 (2) Next, when this is allowed to flow down from the top of the distillation column and steam and chlorine are blown into the bottom, hydrogen bromide is oxidized by chlorine, and the liberated bromine is distilled out together with the steam (Equation 3).

2HBr+C1−)Br2+2HCl(3)これを冷却
、凝縮したのち水を分離して和製臭素をとり、再蒸留に
よって精製して製品とするものである。
2HBr+C1-)Br2+2HCl (3) After this is cooled and condensed, water is separated to obtain Japanese bromine, which is purified by redistillation to produce a product.

又、力性ソーダ吸収法は前記発生ガスを力性ソーダ水溶
液に吸収させ(4式)、つぎに硫酸を加えて臭素を遊離
させ(5式)水蒸気蒸留で臭素を回収する方法である。
The hydric soda absorption method is a method in which the generated gas is absorbed into an aqueous hydric soda solution (Formula 4), then sulfuric acid is added to liberate bromine (Formula 5), and the bromine is recovered by steam distillation.

3Br +6NaOH−+5NaB’r+NaBrO3
+3HO(4) 5NaBr+NaBrO3−t−3H2804→3Br
2+3Na2S04+3H20(5)海水中の臭素濃度
は、60〜651119/lと低いので、前述したよう
な、塩素を吹き込み遊離した臭素を空気で追い出す方法
では、発生ガスの臭素濃度は発生条件によって異なるが
せいぜい0.7〜0.8〜/lである。
3Br +6NaOH-+5NaB'r+NaBrO3
+3HO(4) 5NaBr+NaBrO3-t-3H2804→3Br
2+3Na2S04+3H20 (5) The bromine concentration in seawater is as low as 60 to 651119/l, so in the method described above, in which chlorine is blown in and freed bromine is expelled with air, the bromine concentration in the generated gas varies depending on the generation conditions, but at most It is 0.7-0.8-/l.

したがって、この発生ガスから臭素を回収する為に、亜
硫酸ガス法にあっては、亜硫酸ガスと蒸留用塩素が必要
であり、力性ソーダ吸収法にあっては、力性ソーダと硫
酸が必要である。
Therefore, in order to recover bromine from this generated gas, the sulfur dioxide gas method requires sulfur dioxide gas and chlorine for distillation, and the hydric soda absorption method requires hydric soda and sulfuric acid. be.

これら薬剤は、(2)〜(5)式で示される様に多量必
要であるから、製造コストの大きなウェイトを占めてい
るのが現状である。
Since these drugs are required in large quantities as shown in formulas (2) to (5), they currently account for a large portion of the manufacturing cost.

本発明は、これら問題点を考え臭素濃度の低いガスから
効率よく臭素を回収する方法を見出すべく鋭意研究した
結果見出されたものである。
The present invention was discovered as a result of intensive research in consideration of these problems and in order to find a method for efficiently recovering bromine from gas with a low bromine concentration.

すなわち、本発明法によれば、(1)力性ソーダや亜硫
酸ガスなどの薬剤を全く使わないので、原材料費を大巾
に低減できる。
That is, according to the method of the present invention, (1) no chemicals such as hydrolytic soda or sulfur dioxide gas are used, so raw material costs can be greatly reduced.

(2)腐蝕性の強い硫酸を使わないので材質的に有利で
ある。
(2) It is advantageous in terms of materials because it does not use highly corrosive sulfuric acid.

水溶液中の臭素が強塩基性陰イオン交換樹脂に吸着され
ることは公知のことであり、(6)〜(9)式のように
ポリハライドを形成し、イオン交換するもの古いわれて
いる。
It is well known that bromine in an aqueous solution is adsorbed by a strongly basic anion exchange resin, and methods that form polyhalides and perform ion exchange as shown in formulas (6) to (9) are old.

J、Aveston は、飽和臭素水を用いて臭素の
吸着量を測定している。
J. Aveston measured the amount of bromine adsorbed using saturated bromine water.

それによると、交換容量3.74 eq/kgdry
resinの強塩基性陰イオン交換樹脂アンバーライト
IRA−400で27.Oeq/kg−dry ree
sinである。
According to it, the exchange capacity is 3.74 eq/kg dry.
27. with resin's strongly basic anion exchange resin Amberlite IRA-400. Oeq/kg-dry ree
It is sin.

(Chemistry andIndustry、Se
p、14 、1238(1957’) ) 。
(Chemistry and Industry, Se
p, 14, 1238 (1957')).

又、この性質を利用し、強塩基性陰イオン交換樹脂を用
いて、直接海水から臭素を回収しようという日本特許第
212,506号がある。
Additionally, there is Japanese Patent No. 212,506 which attempts to utilize this property to directly recover bromine from seawater using a strongly basic anion exchange resin.

これは海水に酸化剤を加え臭素を遊離せしめ、アンバー
ライトIRA−400などの強塩基性陰イオン交換樹脂
に吸着後、、力性ソーダと亜硫酸ソーダとの混合水溶液
などで脱着させる吉いうものである。
This is done by adding an oxidizing agent to seawater to liberate bromine, adsorbing it to a strongly basic anion exchange resin such as Amberlite IRA-400, and then desorbing it with a mixed aqueous solution of sodium hydroxide and sodium sulfite. be.

又、遊離した臭素を含む溶液を連続流動床法で処理し、
臭素を強塩基性陰イオン交換樹脂に吸着させることが米
国特許第307’5830号(こ開始されている。
In addition, a solution containing liberated bromine is treated with a continuous fluidized bed method,
Adsorption of bromine onto strongly basic anion exchange resins was initiated by US Pat. No. 307'5830.

又、米国特許第3037845号には亜硫酸水溶液を用
いて効率良く脱着する方法が開始されている。
Further, US Pat. No. 3,037,845 discloses a method for efficiently desorbing sulfite using an aqueous sulfite solution.

しかし、これら公知方法は水溶液中の臭素を強塩基性陰
イオン交換樹脂に吸着させるものであり、又、吸着した
臭素の脱着にはすべて臭素と反応性の薬剤を使用してお
り、本発明法を示唆するものはない。
However, these known methods involve adsorbing bromine in an aqueous solution onto a strongly basic anion exchange resin, and all of the methods use agents reactive with bromine to desorb the adsorbed bromine. There is nothing to suggest that.

本発明者らの研究の結果、ガス中の臭素は、たとえ希薄
であっても容易に強塩基性陰イオン交換樹脂に吸着され
、吸着された臭素は反応性の薬剤を使用しなくても60
℃以上に加熱することによって容易に脱着することが分
った。
As a result of the research conducted by the present inventors, bromine in the gas is easily adsorbed on a strongly basic anion exchange resin even if it is diluted, and the adsorbed bromine is
It was found that it can be easily desorbed by heating above ℃.

試みに、臭素濃度65/Q/7の海水に酸下性で塩素を
吹き込み臭素を遊離させた水溶液を強塩基性陰イオン交
換樹脂アンバーライトI RA400を充填したカラム
に通し、飽和吸着した時点の吸着量を測定したところ、
わずか0.7 e q/l−we t res inで
あった。
In an attempt, an aqueous solution in which bromine was released by blowing chlorine into seawater with a bromine concentration of 65/Q/7 under acid conditions was passed through a column packed with strong basic anion exchange resin Amberlite I RA400. When the amount of adsorption was measured,
It was only 0.7 eq/l-wet resin.

更に、この樹脂に水蒸気をあて、100℃に加熱したが
臭素はほとんど脱着しなかった。
Further, this resin was exposed to steam and heated to 100°C, but almost no bromine was desorbed.

以下、本発明をさらに詳細に説明する。The present invention will be explained in more detail below.

本発明に必要な樹脂は、第4級アンモニウムアニオン樹
脂で、通常、最強塩基性もしくは、強塩基性陰イオン交
換樹脂と呼ばれているものである。
The resin necessary for the present invention is a quaternary ammonium anion resin, which is usually called the most basic or strongly basic anion exchange resin.

弱塩基性陰イオン交換樹脂は吸着量が低い上に加熱して
も脱着せず、場合によっては樹脂が変質する。
Weakly basic anion exchange resins have a low adsorption amount and do not desorb even when heated, and in some cases the resin deteriorates.

強塩基性樹脂としては、米国ロームアンドハース社製の
アンバーライトIRA−400番台、アンバーライ1−
−900番台、アンバーリストA−26、アンバーリス
トA−27、アンバーリストA−29などがある。
Examples of strong basic resins include Amberlyte IRA-400 series and Amberlye 1- manufactured by Rohm and Haas Co., Ltd.
-900 series, Amberlist A-26, Amberlist A-27, Amberlist A-29, etc.

これら強塩基性樹脂は通常塩素型で市販されているので
、回収臭素に塩素の混入が好ましくない場合は、あらか
じめ臭化ソーダなどの臭素化合物水溶液で臭素型にして
おくのが良い。
These strong basic resins are usually commercially available in the chlorine form, so if it is undesirable for the recovered bromine to be contaminated with chlorine, it is best to convert it into the bromine form in advance with an aqueous solution of a bromine compound such as sodium bromide.

塩素の混入が差しつかえない場合は、市販のまま使用し
−Cも良い。
If contamination with chlorine is not a problem, use -C as it is commercially available.

又、市販の状態及び水溶液で臭素型にした樹脂には水分
が含まれているので必要に応じ乾燥してから用いるこさ
ができる。
Moreover, since commercially available resins and resins made into brominated form in aqueous solutions contain water, they can be dried before use if necessary.

臭素を含むガスに水分が水蒸気さしであるいはミストと
して含まれる場合は、吸着量が低下する。
When a gas containing bromine contains moisture in the form of steam or mist, the adsorption amount decreases.

ガス中の臭素濃度が5 In9/ 1以上の場合は、そ
の影響は小さいが、それ以下の場合、例えばいわゆる発
生ガスのように1〜/l以下の場合はそのガス中に含ま
れる水分の影響は太きい。
If the bromine concentration in the gas is 5 In9/1 or higher, the effect is small, but if it is lower than that, for example, in the case of so-called generated gas, where it is 1 to 1/l or less, the effect of moisture contained in the gas is likely. It's thick.

そのような水分を含んだガスを対象とする時は、脱着の
良い多孔性の強塩基性陰イオン交換樹脂が望ましい。
When dealing with such a gas containing moisture, a porous, strongly basic anion exchange resin with good desorption properties is desirable.

特に望ましいのは、交換容量が犬でかつ気孔率モ大きい
樹脂、例えばアンバーリストA−26である。
Particularly desirable are resins with a high exchange capacity and high porosity, such as Amberlyst A-26.

発生ガスには、蒸気圧分の水蒸気の他に若干のミストが
含まれているので、それら水分を除去してから樹脂き接
触させるさより一層効果的である。
Since the generated gas contains some mist in addition to water vapor corresponding to the vapor pressure, it is more effective to contact the resin after removing the water.

強塩基性陰イオン交換樹脂吉ガスを接触させる方法は特
に限定されないが、樹脂の吸着能を最大限に利用する意
味で、固定床で連続的に接触せしめるか、あるいはガス
を充填塔の下部より供給し上昇流を与え、流動床を形成
せしめ接触させるのが良い。
The method of contacting the strongly basic anion exchange resin with the gas is not particularly limited, but in order to make the most of the adsorption capacity of the resin, it may be brought into contact continuously in a fixed bed, or the gas may be brought into contact with the gas from the bottom of a packed column. It is preferable to supply and give an upward flow to form a fluidized bed and bring them into contact.

なお後者の場合は、二段ないしそれ以上くりかえすのが
艮い。
In the latter case, it is best to repeat it two or more times.

温度は、40℃を越えると吸着量が低下するので、それ
以下であることが望ましい。
If the temperature exceeds 40°C, the amount of adsorption decreases, so it is desirable that the temperature is lower than that.

吸着した臭素を樹脂から脱着させる場合は、吸着塔力)
ら樹脂の一部又は全部を抜き出し脱着処理しても良いし
、又吸着塔に充填したまま脱着処理しても良い。
When desorbing adsorbed bromine from the resin, adsorption tower power)
A part or all of the resin may be extracted and desorbed, or the resin may be desorbed while being filled in the adsorption tower.

臭素の吸着量が6.7eq/1−dry −resin
である強塩基性塩イオン交換樹脂アンバーライト40
0の脱着率は温度によって第−表のように変化し、60
℃以上で著しい脱着率を示した。
Bromine adsorption amount is 6.7eq/1-dry-resin
Strong basic salt ion exchange resin Amberlite 40
The desorption rate of 0 changes depending on the temperature as shown in table 60.
It showed a remarkable desorption rate above ℃.

脱着は、ごく少量の空気を吹き込みなから油浴を用いて
外部刃口熱することによって行なった。
Desorption was carried out by blowing in a very small amount of air and then heating the external cutting edge using an oil bath.

なお、イオン交換樹脂は耐熱性が不完全であるので13
0℃以下で脱着することが望ましい。
Note that ion exchange resins have incomplete heat resistance, so 13
It is desirable to desorb at temperatures below 0°C.

又、脱着における加熱には加熱水蒸気を樹脂と直接接触
させて用いると同一温度でも脱着率が上昇することが認
められた。
Furthermore, it has been found that when heated steam is used in direct contact with the resin for heating during desorption, the desorption rate increases even at the same temperature.

それは力ロ熱水蒸気によって樹脂が若干膨潤し脱着しや
すくなる為と思われる。
This is thought to be because the resin swells slightly due to the thermal steam, making it easier to desorb.

なお、加熱水蒸気を使用した場合は、水蒸気が脱着した
臭素のキャリヤーともなるので好都合である。
In addition, when heated steam is used, it is convenient because the steam also serves as a carrier for the desorbed bromine.

脱着した樹脂は再び吸着用として再使用するこ吉ができ
る。
The desorbed resin can be reused for adsorption.

一刀、このようにして回収した臭素は冷却によって凝縮
させれば液体臭素さして得ることができる。
Bromine recovered in this way can be condensed by cooling to obtain liquid bromine.

以下実施例で説明する。This will be explained below using examples.

実施例 1 0一ムアンドハース社製アンバーライトIRA−400
を臭素型にしてから40℃で真空乾燥した。
Example 1 Amberlite IRA-400 manufactured by 01 M&Haas Co., Ltd.
was made into a bromine form and dried under vacuum at 40°C.

この樹脂を100rrllカラムに充填し、臭素濃度2
0 m9/l!の臭素空気混合ガスを上部より100m
17 sec の流速で通した。
This resin was packed into a 100rrll column, and the bromine concentration was 2.
0 m9/l! of bromine air mixed gas 100m from the top.
The flow rate was 17 sec.

7.5時間後にかつ色に変化した吸着ゾーンが下部にま
で移動したので通気を止めた。
After 7.5 hours, the adsorption zone that changed color moved to the bottom, so ventilation was stopped.

吸着量を測定したら、6.7eq/1−dry re
sinであり、吸着は略完全であった。
After measuring the adsorption amount, 6.7eq/1-dry re
sin, and the adsorption was almost complete.

この樹脂を別の容器に移し、100℃の水蒸気を尚てた
ところ66係が脱着した。
When this resin was transferred to another container and exposed to steam at 100° C., 66 was detached.

その臭素の収量は35gであった。The yield of bromine was 35 g.

又、脱着樹脂をもう一度吸着力ラムに移し、同様のテス
トをしたところ、初回に脱着した量だけ再び吸着し、は
ぼ全量脱着した。
Also, when the desorption resin was transferred to the adsorption ram again and the same test was conducted, only the amount that was desorbed the first time was adsorbed again, and almost the entire amount was desorbed.

実施例 2 0一ムアンドハース社の多孔性強塩基性陰イオン交換樹
脂アンバーリストA−26を臭素型にしてから40℃で
真空乾燥し、その200m1をカラムに充填した。
Example 2 A porous strongly basic anion exchange resin Amberlyst A-26 manufactured by Munich & Haas was converted into a bromine form, vacuum dried at 40°C, and 200 ml of the resultant was packed into a column.

65m9/lの濃度で臭素化物を含む海水を硫酸でpH
3,0とし塩素ガスを吹き込み臭素を遊離させた。
Seawater containing bromide at a concentration of 65 m9/l was pH adjusted with sulfuric acid.
The temperature was adjusted to 3.0 and chlorine gas was blown in to liberate bromine.

空気で臭素を追い出し、20℃における飽和水蒸気圧の
水分を含む臭素濃度0.8〜/lの発生ガスを得た。
Bromine was expelled with air to obtain a generated gas containing water at a saturated vapor pressure at 20° C. and having a bromine concentration of 0.8 to 1/l.

このガスを上記カラムに上部から100m1/sec
の流速で通気した。
This gas is fed into the above column from the top at 100ml/sec.
Aerated at a flow rate of .

240時間後にかつ色に変化した吸着ゾーンが下部に到
達したので通気を止めた。
After 240 hours, the adsorption zone that changed color reached the bottom, so the ventilation was stopped.

吸着量を測定したところ4.2eq/A’−dry
resinであり、吸着はほぼ完全であった。
The adsorption amount was measured and was 4.2 eq/A'-dry.
It was resin, and the adsorption was almost complete.

この樹脂を半分ずつ別の容器に移し、一方は100℃の
水蒸気を白で、一刀はごく少量の空気を吹き込みながら
100℃に外部加熱した。
One half of this resin was transferred to another container, and one half was heated externally to 100°C while 100°C water vapor was blown in, and the other was heated to 100°C while blowing a very small amount of air.

前者の脱着率は42%で臭素の収量は14.1g、後者
のそれは37%で臭素の収量は12.4.9であった。
The desorption rate of the former was 42% and the yield of bromine was 14.1 g, and the desorption rate of the latter was 37% and the yield of bromine was 12.4.9 g.

次に脱着樹脂を両刀合せ、もう一度同様のテストを繰り
返したきころ、脱着した量だけ再び吸着した。
Next, the same test was repeated once again using the desorbing resin, and only the amount that had been desorbed was adsorbed again.

100℃の水蒸気を当てたところ脱着率は、2回目の吸
着量に対して100%強であった。
When water vapor at 100° C. was applied, the desorption rate was over 100% of the adsorption amount in the second time.

Claims (1)

【特許請求の範囲】 1 臭素を含有するガスから臭素を回収するに際し、臭
素を含有するガスと強塩基性陰イオン交換樹脂さを接触
させる工程、臭素を吸着した該樹脂を60〜130℃に
加熱して臭素を脱着する工程とから成る臭素の回収方法
。 2 強塩基性陰イオン交換樹脂として、多孔性の強塩基
性陰イオン交換樹脂を用いることを特徴とする特許請求
の範囲1項記載の方法。 3 樹脂の加熱手段として水蒸気を直接に接触させるこ
とを特徴とする特許請求の範囲1または2記載の方法。
[Claims] 1. When recovering bromine from a bromine-containing gas, a step of bringing the bromine-containing gas into contact with a strongly basic anion exchange resin, and heating the bromine-adsorbed resin to 60 to 130°C. A method for recovering bromine comprising the step of desorbing bromine by heating. 2. The method according to claim 1, characterized in that a porous strong basic anion exchange resin is used as the strong basic anion exchange resin. 3. The method according to claim 1 or 2, characterized in that the resin is heated by direct contact with water vapor.
JP1333579A 1979-02-09 1979-02-09 Bromine recovery method Expired JPS5941922B2 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
JP1333579A JPS5941922B2 (en) 1979-02-09 1979-02-09 Bromine recovery method
IL59279A IL59279A (en) 1979-02-09 1980-01-31 Method of recovery of bromine
AU55301/80A AU536419B2 (en) 1979-02-09 1980-02-07 Recovering bromine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1333579A JPS5941922B2 (en) 1979-02-09 1979-02-09 Bromine recovery method

Publications (2)

Publication Number Publication Date
JPS55109201A JPS55109201A (en) 1980-08-22
JPS5941922B2 true JPS5941922B2 (en) 1984-10-11

Family

ID=11830249

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1333579A Expired JPS5941922B2 (en) 1979-02-09 1979-02-09 Bromine recovery method

Country Status (1)

Country Link
JP (1) JPS5941922B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57129804A (en) * 1981-02-03 1982-08-12 Toyo Soda Mfg Co Ltd Recovering method for bromine
US5900044A (en) * 1987-09-11 1999-05-04 E. I. Du Pont De Nemours And Company Organic separation from HF

Also Published As

Publication number Publication date
JPS55109201A (en) 1980-08-22

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