JPS5914013B2 - Purification method of prominated diphenyl ether - Google Patents

Purification method of prominated diphenyl ether

Info

Publication number
JPS5914013B2
JPS5914013B2 JP12776976A JP12776976A JPS5914013B2 JP S5914013 B2 JPS5914013 B2 JP S5914013B2 JP 12776976 A JP12776976 A JP 12776976A JP 12776976 A JP12776976 A JP 12776976A JP S5914013 B2 JPS5914013 B2 JP S5914013B2
Authority
JP
Japan
Prior art keywords
bromine
diphenyl ether
reducing agent
crystals
main component
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
JP12776976A
Other languages
Japanese (ja)
Other versions
JPS5353629A (en
Inventor
良昭 野口
淳良 山内
政次 関戸
一徳 田辺
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.)
Mitsui Toatsu Chemicals Inc
Original Assignee
Mitsui Toatsu Chemicals Inc
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 Mitsui Toatsu Chemicals Inc filed Critical Mitsui Toatsu Chemicals Inc
Priority to JP12776976A priority Critical patent/JPS5914013B2/en
Publication of JPS5353629A publication Critical patent/JPS5353629A/en
Publication of JPS5914013B2 publication Critical patent/JPS5914013B2/en
Expired legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、ブロム化ジフェニルエーテルの精製法に関す
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for purifying brominated diphenyl ether.

近年、日本国内および諸外国においてプラスチック類の
難燃化に対する規制が強化されておりこれに伴つて各種
の難燃剤についての研究が盛んに行われている。
In recent years, regulations regarding the flame retardancy of plastics have been tightened in Japan and other countries, and research on various flame retardants has been actively conducted.

デカブロムジフェニルエーテルまたはこれを主成分とす
るブロム化ジフェニルエーテルは臭素含有量が高い固体
であり、しかも熱分解温度が高い等、添加型の難燃剤と
して極めて優れた性能を有しており、各種プラスチック
特に、ポリエナレン、ポリプロピレン、ポリスチレン等
のポリオレフィン類の難燃化剤として非常に有用なこと
が既に知られている。
Decabromidiphenyl ether or brominated diphenyl ether containing it as the main component is a solid with a high bromine content and has a high thermal decomposition temperature, so it has extremely excellent performance as an additive flame retardant, especially for various plastics. It is already known that it is very useful as a flame retardant for polyolefins such as polyenalene, polypropylene, and polystyrene.

デカブロムジフェニルエーテルまたはこれを主成分とす
るブロム化ジフェニルエーテルの製造法5 としては、
過剰の臭素中でジフェニルエーテルを臭素化する方法、
発煙硫酸中でジフェニルエーテルと臭素を反応させる方
法、ジブロムエタン、ジクロルエタン、テトラクロルエ
タン等の有機溶媒中でジフェニルエーテルと臭素を反応
させる方法・o 等、種々の製造法が知られている。
Method 5 for producing decabrominated diphenyl ether or brominated diphenyl ether containing it as the main component is as follows:
A method for brominating diphenyl ether in excess bromine,
Various production methods are known, such as a method in which diphenyl ether and bromine are reacted in fuming sulfuric acid, and a method in which diphenyl ether and bromine are reacted in an organic solvent such as dibromoethane, dichloroethane, or tetrachloroethane.

しかし、これらの方法で製造されたデカブロムジフェニ
ルエーテルまたはこれを主成分とするブロム化ジフェニ
ルエーテルはいづれも晶析の際にその結晶中に臭素を内
包するため、その除去が問題であつた。結15晶中に臭
素が内包されている場合には、デカブロムジフェニルエ
ーテルまたはこれを主成分とするブロム化ジフェニルエ
ーテルを各種プラスチックに添加配合して成型する際、
内包された臭素が、遊離するため、作業環境が汚染され
、さらにまた、フ0 成形機や金型の腐蝕が起る。本発
明者らは、この結晶中の包含臭素の除去方法につき、種
々検討を行なつた結果、これらの包含臭素は、有機溶媒
や、還元剤あるいは無機塩基の水溶液等による洗浄操作
のみでは除去出来ず、ク5 結晶を溶解、再結晶するか
、もしくは微粉砕することが必要であることが判明した
However, since decabromidiphenyl ether produced by these methods or brominated diphenyl ether containing decabrominated diphenyl ether as a main component includes bromine in its crystals during crystallization, its removal has been a problem. If bromine is included in crystal 15, when decabrominated diphenyl ether or brominated diphenyl ether containing it as the main component is added to various plastics and molded,
The encapsulated bromine is liberated, which pollutes the working environment and also causes corrosion of the molding machine and mold. The present inventors conducted various studies on methods for removing bromine included in the crystals, and as a result, it was found that bromine included in these crystals cannot be removed only by washing with an organic solvent, a reducing agent, or an aqueous solution of an inorganic base. First, it was found that it was necessary to dissolve, recrystallize, or pulverize the crystals.

結晶を溶解して臭素を除去精製することは従来も、有機
溶媒による再結晶法として知られている。
Dissolving crystals and purifying them to remove bromine has been known as a recrystallization method using an organic solvent.

しかしこの方法では、再結晶に用いた有機溶媒の30回
収精製が必要であること、用いた有機溶媒の一部が結晶
中に包含されている臭素によつて臭素化されること、有
機溶媒中に溶解した臭素による装置の腐蝕が起る等のた
め好ましい方法ではない。結晶を粉砕して包含臭素を除
去する場合には微35粉砕することが必要である。しか
しながら、粉砕能力に限度があるため粉砕のみによる臭
素の完全除去は現実にはなかなか困難であり、また粉砕
時に遊離した臭素による装置腐蝕や排気ガス対策が必要
であつた。本発明者らは、これらの問題を解決するべく
鋭意検討を行つた結果の結晶の粉砕に際して還元剤およ
び/または無機塩基の水溶液中で湿式粉砕を行うことに
より、粉砕の際に遊離する臭素を直ちに臭化物に変えう
ること、さらに微粉砕せずとも、粉砕粒度をある一定値
以下にした場合に粉砕結晶中に臭素が残存しなくなるこ
とを見出し、本発明に達したものである。
However, in this method, it is necessary to collect and purify the organic solvent used for recrystallization 30 times, some of the organic solvent used is brominated by bromine contained in the crystals, and This is not a preferred method because the bromine dissolved in the water causes corrosion of the equipment. When the crystals are crushed to remove the included bromine, it is necessary to finely crush the crystals by 35 mm. However, due to the limited crushing capacity, it is actually quite difficult to completely remove bromine by crushing alone, and countermeasures against equipment corrosion and exhaust gas caused by bromine liberated during crushing are required. The present inventors have conducted intensive studies to solve these problems, and as a result, the present inventors have discovered that bromine liberated during pulverization can be removed by performing wet pulverization in an aqueous solution of a reducing agent and/or an inorganic base when pulverizing crystals. The present invention was achieved by discovering that bromine can be immediately converted to bromide, and that bromine does not remain in the pulverized crystals when the pulverized particle size is reduced to a certain value or less without pulverization.

而して本発明は、デカプロムジフエニルエーテルまたは
これを主成分とするブロム化ジフエニルエーテルの製造
に際して還元剤および/または無機塩基の水溶液中で粒
度が100ミクロン以下になるまで湿式粉砕することを
特徴とするブロム化ジフエニルエーテルの精製法に関す
るものである。デカプロムジフエニルエーテルまたはこ
れを主成分とするブロム化ジフエニルエーテルは各種プ
ラスチツクの成型時に添加し、これを難燃化するが、成
型品の物性の点からプラスチツク類との混合に際して均
一に分散、溶解させるために微細なデカプロムジフエニ
ルエーテルまたはこれを主成分とするブロム化ジフエニ
ルエーテルを用いる必要がある。
Therefore, the present invention involves wet grinding in an aqueous solution of a reducing agent and/or an inorganic base until the particle size becomes 100 microns or less when producing decaprom diphenyl ether or brominated diphenyl ether containing decaprom diphenyl ether as a main component. The present invention relates to a method for purifying brominated diphenyl ether characterized by the following. Decaprom diphenyl ether or brominated diphenyl ether containing it as the main component is added when molding various plastics to make them flame retardant, but from the viewpoint of the physical properties of the molded product, it is dispersed uniformly when mixed with plastics. , it is necessary to use finely divided decaprom diphenyl ether or brominated diphenyl ether containing it as a main component in order to dissolve it.

しかし各種の製造法により製造された、あるいは、再結
晶して得られたデカプロムジフエニルエーテルまたはこ
れを主成分とするブロム化ジフエニルエーテルは、粒度
200ミクロン以上であり、このままでは実用的でなく
、さらに微細化する必要があり、元来粉砕は不可欠の操
作である。又、各種の製造法により製造されたデカプロ
ムジフエニルエーテルまたはこれを主成分とするブロム
化ジフエニルエーテルは結晶中に臭素を包含しているだ
けでなく、その結晶表面にも臭素が付着している。この
結晶表面に付着している臭素は従来湿り結晶を、還元剤
水溶液で処理して除去していたが、本発明では、この前
処理も粉砕と同時に実施出来る。各種製造法で製造され
たデカプロムジフエニルエーテルまたはこれを主成分と
するブロム化ジフエニルエーテルは、製造時の反応液と
分離した後、還元剤および/または無機塩基の水溶液中
に懸濁させた後、粒度が100ミクロン以下になるまで
湿式粉砕される。粉砕後固液分離し、水洗乾燥して臭素
を含有しない製品を得る。本発明に用いる還元剤および
無機塩基としては通常知られている還元剤および無機塩
基は全て用いうるが、還元剤としては亜硫酸ナトリウム
、亜硫酸カリウム、亜硫酸水素ナトリウム等の亜硫酸塩
および亜硫酸水素塩、チオ硫酸ナトリウム等のチオ硫酸
塩、無機塩基としては、アルカリおよびアルカリ土類金
属の水酸化物が特に好ましい。結晶表面および結晶中に
包含されている臭素は、たとえば水酸化ナトリウム水溶
液中で湿式粉砕する場合は次の(1)、(2)式により
直ちに無害化される。亜硫酸ナトリウムと水酸化ナトリ
ウムを含有する水溶液中で湿式粉砕する場合の臭素の無
害化は恐らく次の(3)、(4)式によると考えられる
。又、還元剤はアルカリ性である場合が多いので、還元
剤の水溶液中で湿式粉砕する場合も(3)、(4)式に
準する反応により臭素の無害化が起つているものと考え
られる。還元剤および無機塩基の使用量は、除去すべき
臭素に対して理論反応量の1〜5倍量好ましくは1.5
〜3倍量である。
However, decaprom diphenyl ether produced by various production methods or obtained by recrystallization, or brominated diphenyl ether containing it as a main component, has a particle size of 200 microns or more, and is not practical as it is. However, it is necessary to further refine the particles, and pulverization is originally an essential operation. In addition, decaprom diphenyl ether produced by various production methods or brominated diphenyl ether containing this as the main component not only contains bromine in the crystal, but also has bromine attached to the crystal surface. ing. Conventionally, the bromine adhering to the surface of the crystal was removed by treating the wet crystal with an aqueous reducing agent solution, but in the present invention, this pretreatment can also be carried out at the same time as the crushing. Decaprom diphenyl ether produced by various production methods or brominated diphenyl ether containing it as a main component is separated from the reaction solution during production and then suspended in an aqueous solution of a reducing agent and/or an inorganic base. After that, it is wet milled until the particle size is less than 100 microns. After pulverization, solid-liquid separation is performed, followed by washing with water and drying to obtain a bromine-free product. As the reducing agent and inorganic base used in the present invention, all commonly known reducing agents and inorganic bases can be used, but as the reducing agent, sulfites and bisulfites such as sodium sulfite, potassium sulfite, and sodium hydrogen sulfite, thiosulfites, etc. As the thiosulfate such as sodium sulfate and the inorganic base, hydroxides of alkali and alkaline earth metals are particularly preferred. Bromine contained on the crystal surface and in the crystal is immediately rendered harmless by the following formulas (1) and (2), for example, when wet grinding is carried out in an aqueous sodium hydroxide solution. The detoxification of bromine during wet grinding in an aqueous solution containing sodium sulfite and sodium hydroxide is probably based on the following equations (3) and (4). Furthermore, since the reducing agent is often alkaline, it is thought that even when wet grinding is performed in an aqueous solution of the reducing agent, bromine is rendered harmless through reactions similar to equations (3) and (4). The amount of reducing agent and inorganic base to be used is 1 to 5 times the theoretical reaction amount, preferably 1.5 times the amount of bromine to be removed.
~3 times the amount.

理論量以下では遊離の臭素が残るため、本発明の効果が
なく5倍量以上では実用的でない。なお、還元剤および
無機塩基を反応当量以上に用いて、結晶を分離した溶液
を循環使用することも可能である。還元剤および無機塩
基の水溶液中の濃度は0,01〜5%好ましくは0.0
2〜3%である。
If the amount is less than the stoichiometric amount, free bromine remains, so the effect of the present invention is not achieved, and if the amount is 5 times or more, it is not practical. Note that it is also possible to use the reducing agent and the inorganic base in an amount greater than the reaction equivalent, and to recycle the solution from which the crystals have been separated. The concentration of the reducing agent and inorganic base in the aqueous solution is 0.01-5%, preferably 0.0
It is 2-3%.

還元剤および無機塩基の濃度が0.01%以下では使用
液量が多く、スラリー濃度が小さくなり粉砕効率が悪く
、5%以上では使用した薬品による装置腐蝕や廃水処理
問題が起ることもあり、実用的でない。湿式粉砕の際の
スラリー濃度は、10〜80%好ましくは20〜60%
である。
If the concentration of the reducing agent and inorganic base is less than 0.01%, the amount of liquid used will be large and the slurry concentration will be low, resulting in poor grinding efficiency, while if it is more than 5%, equipment corrosion and wastewater treatment problems may occur due to the chemicals used. , impractical. The slurry concentration during wet pulverization is 10 to 80%, preferably 20 to 60%.
It is.

濃度10%以下では粉砕効率が悪く、80%以上では粉
砕後のスラリー液の粘度が高く、流動性が低くなるため
実用的でない。本発明により結晶中の包含臭素を完全に
除去するためには、粉砕品の粒度を100ミクロン以下
にする必要があり、好ましくは50ミクロン以下とする
ことが望ましい。
If the concentration is less than 10%, the grinding efficiency is poor, and if it is more than 80%, the viscosity of the slurry liquid after grinding is high and the fluidity is low, which is not practical. In order to completely remove bromine included in the crystals according to the present invention, the particle size of the pulverized product must be 100 microns or less, preferably 50 microns or less.

粒度が100ミクロン以上では粉砕結晶中になお10p
pm前後の臭素が包含されている。本発明による粉砕の
際に粉砕効率をあげるために界面活性剤等の分散剤を併
用することも可能である。本発明による粉砕を行つた後
、沢過、水洗、乾燥して得られた100ミクロン以下の
デカプロムジフエニルエーテルまたはこれを主成分とす
るブロム化ジフエニルエーテルは全く臭素を含有してお
らず、しかも有機溶媒による再結晶で得られた製品に比
べ何ら遜色がない。
If the particle size is 100 microns or more, there will still be 10p in the crushed crystal.
Bromine around pm is included. During the pulverization according to the present invention, it is also possible to use a dispersant such as a surfactant in order to increase the pulverization efficiency. After pulverization according to the present invention, decaprom diphenyl ether of 100 microns or less obtained by filtering, washing with water, and drying, or brominated diphenyl ether containing this as a main component, does not contain any bromine. Moreover, it is in no way inferior to products obtained by recrystallization using organic solvents.

尚、比較例2に示した様に、単に水の中で湿式粉砕した
場合は、たとえ粒度が50ミクロン以下になるまで粉砕
しても、なお臭素が残存しており、これにくらべれば本
発明のすぐれた効果が理解出来よう。
As shown in Comparative Example 2, when simply wet-pulverizing in water, bromine still remains even if the particle size is reduced to 50 microns or less, and compared to this, the present invention You can understand the excellent effects of

以下に例をあげて説明する。This will be explained below using an example.

実施例 1 臭素730ppmを包含しているデカプロムジフエニル
エーテルを主成分とするブロム化ジフエニルエーテルの
乾燥結晶100yを乳鉢に入れ、これに亜硫酸ナトリウ
ム90m9、水酸化ナトリウム74ηを溶解した水溶液
1007を入れた。
Example 1 100y of dry crystals of brominated diphenyl ether containing decaprom diphenyl ether as the main component containing 730ppm of bromine were placed in a mortar, and an aqueous solution 1007 containing 90m9 of sodium sulfite and 74η of sodium hydroxide dissolved therein was added. I put it in.

この乳鉢を塩化ビニールのシートで覆つた箱の中に入れ
よく粉砕した。粉砕中にこの箱の中の空気中の臭素を測
定したが全く検出されなかつた。得られた粉末を沢過、
水洗乾燥して99.5Vの粉末を得た。
This mortar was placed in a box covered with a vinyl chloride sheet and thoroughly ground. Bromine in the air inside this box was measured during crushing, but no bromine was detected. Pour the obtained powder,
After washing with water and drying, a powder with a voltage of 99.5V was obtained.

この粉末をTyler標準篩で篩分し、325メツシユ
篩下92.0yを得た。▲液中および325メツシユ篩
下の粉末中には臭素は全く検出されなかつた。比較例
1 実施例1に用いたと同じ結晶1007を塩化ビニールシ
ートで覆つた箱の中でそのまま乳鉢で粉砕した。
This powder was sieved using a Tyler standard sieve to obtain a 325 mesh sieve size of 92.0y. ▲ No bromine was detected in the liquid or in the powder under the 325 mesh sieve. Comparative example
1 The same crystal 1007 used in Example 1 was crushed in a mortar in a box covered with a vinyl chloride sheet.

この際箱の中の空気中の臭素を測定した結果10ppm
以上の濃度の臭素が検出された。得られた粉末のうち3
25メツシユ篩下のものについては100ppmの臭素
が検出された。比較例 2 実施例1で用いたと同じ結晶100yに水200yを加
えて乳鉢に入れ、塩化ビニールシートで覆つた箱の中で
粉砕した。
At this time, the bromine in the air inside the box was measured and found to be 10 ppm.
Bromine was detected at concentrations above. 3 of the powders obtained
100 ppm of bromine was detected under the 25 mesh sieve. Comparative Example 2 200 y of water was added to 100 y of the same crystals used in Example 1, placed in a mortar, and crushed in a box covered with a vinyl chloride sheet.

粉砕中箱の中の空気中には臭素は殆んど検出されなかつ
た。得られた粉末を沢過、水洗乾燥した。沢液中には1
30ppmの臭素が検出され、325メツシユ篩下乾燥
粉末中には90ppmの臭素が検出された。実施例 2
〜8臭素2760ppmを含むデカプロムジフエニルエ
ーテルを主成分とするブロム化ジフエニルエーテルの湿
り結晶1007について実施例1と同様操作で還元剤、
無機塩基の種類、量を変えて粉砕した結果、表−1の結
果を得た。
Almost no bromine was detected in the air inside the box during crushing. The obtained powder was filtered, washed with water and dried. 1 in the sap
30 ppm of bromine was detected, and 90 ppm of bromine was detected in the dry powder under the 325 mesh sieve. Example 2
~8 Wet crystals of brominated diphenyl ether containing 2760 ppm of bromine as a main component 1007 were treated with a reducing agent,
As a result of pulverization with different types and amounts of inorganic bases, the results shown in Table 1 were obtained.

なお箱の中の空気中および沢液中にはいづれの場合も臭
素は検出されなかつた。実施例2の場合は200メツシ
ユ ドについて残存臭素をしらべた。
In any case, no bromine was detected in the air inside the box or in the slough. In the case of Example 2, residual bromine was examined for 200 meshes.

Claims (1)

【特許請求の範囲】[Claims] 1 デカブロムジフェニルエーテルまたはこれを主成分
とするブロム化ジフェニルエーテルを還元剤および/ま
たは無機塩基の水溶液中で粒度が100ミクロン以下に
なるまで湿式粉砕することを特徴とするブロム化ジフェ
ニルエーテルの精製法。
1. A method for purifying brominated diphenyl ether, which comprises wet-pulverizing decabrominated diphenyl ether or a brominated diphenyl ether containing it as a main component in an aqueous solution of a reducing agent and/or an inorganic base until the particle size becomes 100 microns or less.
JP12776976A 1976-10-26 1976-10-26 Purification method of prominated diphenyl ether Expired JPS5914013B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12776976A JPS5914013B2 (en) 1976-10-26 1976-10-26 Purification method of prominated diphenyl ether

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12776976A JPS5914013B2 (en) 1976-10-26 1976-10-26 Purification method of prominated diphenyl ether

Publications (2)

Publication Number Publication Date
JPS5353629A JPS5353629A (en) 1978-05-16
JPS5914013B2 true JPS5914013B2 (en) 1984-04-02

Family

ID=14968229

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12776976A Expired JPS5914013B2 (en) 1976-10-26 1976-10-26 Purification method of prominated diphenyl ether

Country Status (1)

Country Link
JP (1) JPS5914013B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02110818U (en) * 1989-02-22 1990-09-05

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4214103A (en) * 1978-11-30 1980-07-22 Great Lakes Chemical Corporation Purification of brominated organic products
GB2081253B (en) * 1980-07-23 1985-05-30 Great Lakes Chemical Corp Process for producing purified brominated aromatic compounds
JP2009500500A (en) * 2005-07-05 2009-01-08 アルベマール・コーポレーシヨン Method for improving dielectric constant and / or dissipation factor of flame retardant composition
WO2008057644A1 (en) 2006-11-09 2008-05-15 Albemarle Corporation Processing of solid brominated aromatic organic compounds containing occluded bromine
US7408088B1 (en) 2007-02-08 2008-08-05 Albemarle Corporation Process for separation of bromine from gaseous hydrogen bromide and use of such process in production of decabromodiphenylethane
EP2132158B1 (en) 2007-03-16 2014-08-13 Albemarle Corporation Preparation and provision of high assay decabromodiphenylethane
CA2680010C (en) 2007-03-16 2015-05-05 Albemarle Corporation Preparation and provision of high assay decabromodiphenylethane
CA2767394A1 (en) 2009-07-27 2011-02-10 Albemarle Corporation Preparation of high assay decabromodiphenylalkane product with low occluded free bromine content

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02110818U (en) * 1989-02-22 1990-09-05

Also Published As

Publication number Publication date
JPS5353629A (en) 1978-05-16

Similar Documents

Publication Publication Date Title
JPS5914013B2 (en) Purification method of prominated diphenyl ether
CA1197043A (en) Process for regenerating resin
WO2017121343A1 (en) Process for recovering lithium from industrial wastewater
RU2650147C2 (en) Method for processing expired solid rocket propellant
CN102390832A (en) Method for treating waste silicon powder produced in trichlorosilane synthesis process
GB1443876A (en) Purification of wet-processed phosphoric acid
JPS5499173A (en) Regeneration of polyamide
US3923689A (en) Removal of iron contaminants from porous materials
US3839463A (en) Purification of organic compounds
US2055763A (en) Process fob sulphahon of olefines
US1311232A (en) Process for the separation of cyanid compounds from other substances
CN106629779B (en) A kind of method for recycling sodium bromide and sodium sulfocyanate
DE2625690C2 (en) Process for precoat filtration of liquefied coal
WO2006080324A1 (en) Method of screening out cellulosic polymer and apparatus therefor
SU1551241A3 (en) Method of purifying liquid from hydrogen sulfide
US3017245A (en) Removal of sodium sulfate from caustic salt
JPH07107007B2 (en) Method for purifying tetrabromobisphenol A
JPS6365602B2 (en)
JP4118495B2 (en) How to reuse mud
JP2003212901A (en) Carboxymethyl cellulose and salt thereof, excellent in dispersion to water
JPS6325116B2 (en)
JP2002179833A (en) Method for separating recovered flame retardant components
RU2120407C1 (en) Method of production of potassium chloride from the spent electrolyte of magnesium production
SU1133267A1 (en) Process for purifying n-carbomethoxysulfanyl chloride
JP2001179006A (en) Regeneration treatment agent for paint-containing thinner