JPH0692249B2 - Treatment method for polychlorosilanes - Google Patents

Treatment method for polychlorosilanes

Info

Publication number
JPH0692249B2
JPH0692249B2 JP8235688A JP8235688A JPH0692249B2 JP H0692249 B2 JPH0692249 B2 JP H0692249B2 JP 8235688 A JP8235688 A JP 8235688A JP 8235688 A JP8235688 A JP 8235688A JP H0692249 B2 JPH0692249 B2 JP H0692249B2
Authority
JP
Japan
Prior art keywords
polychlorosilanes
reaction
impact
solid particles
silicon
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
JP8235688A
Other languages
Japanese (ja)
Other versions
JPH01257119A (en
Inventor
達也 吉井
辰男 浅野
徹也 和田
秀樹 松村
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.)
Denka Co Ltd
Original Assignee
Denki Kagaku Kogyo KK
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 Denki Kagaku Kogyo KK filed Critical Denki Kagaku Kogyo KK
Priority to JP8235688A priority Critical patent/JPH0692249B2/en
Publication of JPH01257119A publication Critical patent/JPH01257119A/en
Publication of JPH0692249B2 publication Critical patent/JPH0692249B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B33/00Silicon; Compounds thereof
    • C01B33/02Silicon
    • C01B33/021Preparation
    • C01B33/027Preparation by decomposition or reduction of gaseous or vaporised silicon compounds other than silica or silica-containing material
    • C01B33/03Preparation by decomposition or reduction of gaseous or vaporised silicon compounds other than silica or silica-containing material by decomposition of silicon halides or halosilanes or reduction thereof with hydrogen as the only reducing agent

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Silicon Compounds (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は水素と塩化珪素を金属珪素存在下または不存在
下反応させ、該塩化珪素を還元する際に副生するポリク
ロロシラン類を処理する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention treats hydrogen and silicon chloride in the presence or absence of metallic silicon to treat polychlorosilanes produced as a by-product when the silicon chloride is reduced. Regarding the method.

該塩化珪素としては、トリクロロシランや四塩化珪素が
ある。四塩化珪素が還元された状態としてはトリクロロ
シランが、又トリクロロシランがジーメンス法により還
元された状態としては、多結晶シリコンがある。これら
は半導体や太陽電池等の素子を製造する原料として使用
される。
Examples of the silicon chloride include trichlorosilane and silicon tetrachloride. Trichlorosilane is present in the state where silicon tetrachloride is reduced, and polycrystalline silicon is present in the state where trichlorosilane is reduced by the Siemens method. These are used as raw materials for manufacturing elements such as semiconductors and solar cells.

〔従来の技術〕[Conventional technology]

該ポリクロロシラン類は次の一般式(1)(2)(3)
および(4)で表される化合物よりなる混合物である。
The polychlorosilanes are represented by the following general formulas (1) (2) (3)
And a mixture of the compounds represented by (4).

SinCl2n+2 n≧2 (1) SinHmCl2n+2-m n≧2,m≧1,2n+2−m≧1 (2) SinCl2n+2Ol n≧2,n−l≧1 (3) SinHmCl2n+2-mOl n≧2,m≧1,2n+2−m≧1,n−l≧
1 (4) 該ポリクロロシラン類は、特開昭60−81010号公報や特
開昭58−217422号公報に示されるように水素と四塩化珪
素を金属珪素存在下または不存在下反応させ、トリクロ
ロシランを製造する際に副生するポリクロロシラン類で
ある。
SinCl 2 n +2 n ≧ 2 (1) SinHmCl 2 n + 2- m n ≧ 2, m ≧ 1,2 n + 2-m ≧ 1 (2) SinCl 2 n +2 Ol n ≧ 2, n−1 ≧ 1 ( 3) SinHmCl 2 n + 2- mOl n ≧ 2, m ≧ 1,2n + 2-m ≧ 1, n−1 ≧
1 (4) As described in JP-A-60-81010 and JP-A-58-217422, the polychlorosilanes are reacted with hydrogen and silicon tetrachloride in the presence or absence of metallic silicon to obtain trichlorosilane. It is a polychlorosilane that is a by-product when producing chlorosilane.

特開昭60−81010号公報では、水素と四塩化珪素とを高
温で平衡にさせ次に急冷することによつてトリクロロシ
ランを製造する方法が示されている。特開昭58−217422
号公報では、水素と金属珪素と四塩化珪素とを高温で反
応させることによつてトリクロロシランを製造する方法
が示されている。該ポリクロロシラン類の形状は、褐色
の液体であり、ときには粘稠な液体である。該ポリクロ
ロシランは、水または空気中の水に接触し、灰白色の衝
撃によつて発火爆発する物質に変化する。
JP-A-60-81010 discloses a method for producing trichlorosilane by equilibrating hydrogen and silicon tetrachloride at high temperature and then quenching. JP 58-217422
The publication discloses a method for producing trichlorosilane by reacting hydrogen, metallic silicon and silicon tetrachloride at high temperature. The polychlorosilanes are in the form of brown liquids, sometimes viscous liquids. The polychlorosilane comes into contact with water or water in the air, and changes into a substance that ignites and explodes due to an off-white impact.

従来は、該ポリクロロシランを水酸化ナトリウムの水溶
液と撹拌し中和処理していたが、処理反応により生成し
た固体粒子は衝撃発火性を示し、処理を中断しなければ
ならなかつた。
In the past, the polychlorosilane was neutralized by stirring it with an aqueous solution of sodium hydroxide, but the solid particles produced by the treatment reaction had an impact ignitability and the treatment had to be interrupted.

特開昭58−180494号公報において、珪素金属と塩化水素
の反応によるトリクロロシランの製造の際副生するクロ
ロシラン化合物を、濃塩化水素水溶液又は塩化カルシウ
ム水溶液を用い処理する方法が提案されている。
Japanese Unexamined Patent Publication (Kokai) No. 58-180494 proposes a method of treating a chlorosilane compound, which is a by-product during the production of trichlorosilane by the reaction of silicon metal and hydrogen chloride, with a concentrated aqueous hydrogen chloride solution or an aqueous calcium chloride solution.

しかしながら従来の技術では、該ポリクロロシラン類を
処理しようとした場合、処理中での発火や処理反応によ
つて生成した固体粒子の衝撃による発火がともない、安
全な処理方法が望まれていた。
However, in the prior art, when attempting to treat the polychlorosilanes, a safe treatment method has been demanded because ignition occurs during the treatment and solid particles generated by the treatment reaction cause impact.

〔発明が解決しようとする課題〕[Problems to be Solved by the Invention]

本発明は、該ポリクロロシランの処理中での発火や処理
反応によつて生成した固体粒子の発火の問題点を解決す
るものである。
The present invention solves the problems of ignition during the treatment of the polychlorosilane and ignition of solid particles generated by the treatment reaction.

〔課題を解決するための手段〕[Means for Solving the Problems]

本発明者は、該ポリクロロシラン類の処理方法について
鋭意研究を重ねた結果、アルカリ土類金属の水酸化物、
アルカリ土類金属の酸化物、またはアンモニアをもちい
れば安全に処理できることを見出した。
The present inventor has conducted extensive studies on a treatment method for the polychlorosilanes, and as a result, a hydroxide of an alkaline earth metal,
It was found that the alkaline earth metal oxide or ammonia can be safely used.

即ち、本発明は水素と塩化珪素を金属珪素存在下または
不存在下反応させ、該塩化珪素を還元する際に、副生す
るポリクロロシラン類をアルカリ土類金属の水酸化物、
アルカリ土類金属の酸化物またはアンモニアで処理する
事を特徴とする、副生ポリクロロシラン類の処理方法で
ある。
That is, in the present invention, hydrogen and silicon chloride are reacted in the presence or absence of metallic silicon, and when the silicon chloride is reduced, polychlorosilanes produced as a by-product are alkaline earth metal hydroxides,
A method for treating by-produced polychlorosilanes, which comprises treating with an oxide of an alkaline earth metal or ammonia.

本発明で使用するアルカリ土類金属の水酸化物として
は、水酸化カルシウム、水酸化マグネシウムが、アルカ
リ土類金属の酸化物としては、酸化カルシウム、酸化マ
グネシウムが入手しやすい。アルカリ土類金属の水酸化
物または酸化物は、あらかじめ飽和水溶液またはスラリ
ーに調製して使用したほうが操作しやすい。本発明で使
用するアルカリ土類金属の水酸化物または酸化物の形状
としては粉末状が、スラリーを調製するのに好ましい。
アンモニアは水溶液として使用したほうが操作しやす
く、飽和水溶液としても稀釈して用いても良い。該ポリ
クロロシラン類はそのままでもよいし、四塩化珪素で希
釈して処理してもよい。本発明の処理は、加熱または冷
却の必要が無く、温度0〜50℃で行なうのが効果的であ
る。50℃を越える温度で行なう事も可能であるが、高温
で行なうと発火性の固体粒子が生成し易くなる。処理
は、処理液のpHを、7.0〜14.0に保ち行なうのが効果的
である。pHが7.0未満の場合、発火性の固体粒子が生成
し易くなる。処理に用いる装置は何等制限されないが、
撹拌槽型が操作しやすい。処理方法はバツチ式でも連続
式でもよい。
As the alkaline earth metal hydroxide used in the present invention, calcium hydroxide and magnesium hydroxide are easily available, and as the alkaline earth metal oxide, calcium oxide and magnesium oxide are easily available. It is easier to operate the alkaline earth metal hydroxide or oxide prepared in advance as a saturated aqueous solution or slurry. The alkaline earth metal hydroxide or oxide used in the present invention is preferably in powder form for preparing a slurry.
Ammonia is easier to operate when used as an aqueous solution, and may be used as a saturated aqueous solution after diluting. The polychlorosilanes may be used as they are or may be diluted with silicon tetrachloride and treated. The treatment of the present invention does not require heating or cooling and is effectively carried out at a temperature of 0 to 50 ° C. It is possible to carry out at a temperature exceeding 50 ° C, but if it is carried out at a high temperature, ignitable solid particles are easily generated. The treatment is effectively performed by keeping the pH of the treatment liquid at 7.0 to 14.0. When the pH is less than 7.0, ignitable solid particles are easily generated. The device used for processing is not limited,
The stirring tank type is easy to operate. The treatment method may be a batch method or a continuous method.

〔実施例〕〔Example〕

以下実施例により、本発明をさらに具体的に説明する
が、これらはあくまで例示であり、これらに限定される
ものではない。
Hereinafter, the present invention will be described in more detail with reference to Examples, but these are merely examples and the present invention is not limited thereto.

実施例1 500mlのガラス製丸底フラスコに、15重量%水酸化カル
シウムスラリーを280g仕込み、300回転/分で撹拌しな
がら20℃に保つた。四塩化珪素を265モル/h、水素を530
モル/hの割合で、1250℃に保たれた黒鉛製反応器に供給
し、次に急冷して得られた反応液から蒸留によつて副生
ポリクロロシラン類を得た。この副生ポリクロロシラン
類36.7gを30分間で滴下した。さらに30分間撹拌を続け
たがこの間フラスコ内での発火は無かつた。反応後の液
のpHは、7.9であつた。その後反応で生成した固体粒子
を濾過で分離し、水洗後窒素雰囲気下で乾燥した。乾燥
した固体粒子の衝撃発火性を測定するのに落つい式衝撃
試験機(上島製作所(株)製)を用いた。与えた衝撃の
量は、落下させた分銅の重量(kg重)と分銅を落下させ
た高さ(m)の積で表示される。測定の結果、1.0kg重.
mの衝撃を与えても発火しなかつた。
Example 1 A 500 ml round-bottom glass flask was charged with 280 g of a 15 wt% calcium hydroxide slurry, and the mixture was kept at 20 ° C. with stirring at 300 rpm. 265 mol / h of silicon tetrachloride, 530 of hydrogen
The by-product polychlorosilanes were obtained by distillation from the reaction solution obtained by supplying the reaction solution at a rate of mol / h to a graphite reactor kept at 1250 ° C. and then rapidly cooling it. 36.7 g of this by-product polychlorosilane was added dropwise over 30 minutes. Stirring was continued for another 30 minutes, but during this period, no ignition occurred in the flask. The pH of the liquid after the reaction was 7.9. Thereafter, solid particles generated by the reaction were separated by filtration, washed with water, and dried under a nitrogen atmosphere. A drop-type impact tester (manufactured by Kamijima Seisakusho Co., Ltd.) was used to measure the impact ignition properties of the dried solid particles. The amount of impact given is displayed as the product of the weight (kg weight) of the weight dropped and the height (m) of the weight dropped. As a result of the measurement, it weighs 1.0 kg.
It did not ignite even when given a shock of m.

実施例2 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリー280gにかえて、15重量%水酸化マグネシウ
ムスラリー220gを用いて実施した。撹拌の間、フラスコ
内での発火は無かつた。反応後のpHは7.6であつた。衝
撃試験機で1.0kg重・mの衝撃を与えても発火しなかつ
た。
Example 2 Under the same conditions as in Example 1, 220 g of 15 wt% magnesium hydroxide slurry was used instead of 280 g of 15 wt% calcium hydroxide slurry. There was no ignition in the flask during stirring. The pH after the reaction was 7.6. It did not ignite even when given an impact of 1.0 kg weight / m with an impact tester.

実施例3 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリー280gにかえて、15重量%酸化カルシウムス
ラリー212gを用いて同様に実施した。撹拌の間フラスコ
内での発火は無かつた。反応後のpHは11.9であつた。衝
撃試験機で1.0kg重・mの衝撃を与えても発火しなかつ
た。
Example 3 Under the same conditions as in Example 1, the same procedure was performed using 212 g of 15 wt% calcium oxide slurry instead of 280 g of 15 wt% calcium hydroxide slurry. There was no ignition in the flask during stirring. The pH after the reaction was 11.9. It did not ignite even when given an impact of 1.0 kg weight / m with an impact tester.

実施例4 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリー280gかえて、15重量%酸化マグネシウムス
ラリー152gを用いて同様に実施した。撹拌の間フラスコ
内での発火は無かつた。反応後のpHは9.1であつた。衝
撃試験機で1.0kg重・mの衝撃を与えても発火しなかつ
た。
Example 4 Under the same conditions as in Example 1, 280 g of the 15 wt% calcium hydroxide slurry was replaced with 152 g of the 15 wt% magnesium oxide slurry, and the same procedure was carried out. There was no ignition in the flask during stirring. The pH after the reaction was 9.1. It did not ignite even when given an impact of 1.0 kg weight / m with an impact tester.

実施例5 500mlのガラス製丸底フラスコに、15重量%水酸化カル
シウムスラリーを9.3g/分の速度で、実施例1で処理に
用いたものと同じポリクロロシラン類を1.2g/分の速度
でおのおの滴下し、300回転/分で撹拌しながら供給し
た。滴下開始30分後から、10.5g/分の速度でスラリー状
の反応液を抜出し、連続的に処理を行なつた。3時間連
続的に処理を行なつたが、フラスコ内での発火は無かつ
た。反応で生成した固体粒子を濾過で分離し、水洗後窒
素雰囲気下乾燥し、衝撃試験機で測定した。1.0kg重・
mの衝撃を与えても発火しなかつた。
Example 5 A 500 ml glass round bottom flask was charged with 15 wt% calcium hydroxide slurry at a rate of 9.3 g / min and the same polychlorosilanes used in the treatment of Example 1 at a rate of 1.2 g / min. Each was dripped and supplied with stirring at 300 rpm. Thirty minutes after the start of dropping, the slurry-like reaction liquid was extracted at a rate of 10.5 g / min and continuously treated. The treatment was continuously carried out for 3 hours, but there was no ignition in the flask. The solid particles generated by the reaction were separated by filtration, washed with water, dried under a nitrogen atmosphere, and measured by an impact tester. 1.0 kg weight
It did not ignite even when given a shock of m.

実施例6 1000mlのガラス製丸底フラスコに、25重量%アンモニア
水溶液を2.4g/分の速度で、実施例1で処理に用いたも
のと同じポリクロロシラン類を1.2g/分の速度で各々滴
下し、300回転/分で撹拌しながら供給した。滴下開始3
0分後から、3.6g/分の速度でスラリー状の反応液を抜出
し連続的に処理を行なつたが、フラスコ内での発火は無
かつた。反応で生成した固体粒子を濾過で分離し、水洗
後窒素雰囲気下乾燥し、衝撃試験機で測定した。1.0kg
重・mの衝撃を与えても発火しなかつた。
Example 6 To a 1000 ml glass round bottom flask, 25 wt% aqueous ammonia solution was added dropwise at a rate of 2.4 g / min, and the same polychlorosilanes used in the treatment in Example 1 were added dropwise at a rate of 1.2 g / min. Then, it was fed at 300 rpm with stirring. Start dripping 3
After 0 minutes, the slurry-like reaction liquid was extracted at a rate of 3.6 g / min and continuously treated, but no ignition occurred in the flask. The solid particles generated by the reaction were separated by filtration, washed with water, dried under a nitrogen atmosphere, and measured by an impact tester. 1.0 kg
It did not ignite even when given a heavy m impact.

実施例7 500mlのガラス製丸底フラスコに、15重量%水酸化カル
シウムスラリーを280g仕込み、300回転/分で撹拌しな
がら20℃に保つた。四塩化珪素:水素のモル比を3:2の
割合で、450℃に保たれた金属シリコンの流動床反応器
(内径10cm)に供給し得られた反応液から蒸留によつて
副生ポリクロロシラン類を得た。このポリクロロシラン
類36.7gを30分間で滴下した。さらに30分間撹拌を続け
たがこの間フラスコ内での発火は無かつた。その後反応
で生成した固体粒子を濾過で分離し、水洗後窒素雰囲気
下で乾燥後、衝撃試験機で測定した結果、1.0kg重・m
の衝撃を与えても発火しなかつた。
Example 7 A 500 ml round-bottom glass flask was charged with 280 g of a 15 wt% calcium hydroxide slurry, and the mixture was kept at 20 ° C. with stirring at 300 rpm. A silicon tetrachloride: hydrogen molar ratio of 3: 2 was supplied to a metallic silicon fluidized bed reactor (inside diameter 10 cm) kept at 450 ° C., and the reaction liquid obtained was distilled as a by-product to produce polychlorosilane. I got a kind. 36.7 g of these polychlorosilanes were added dropwise over 30 minutes. Stirring was continued for another 30 minutes, but during this period, no ignition occurred in the flask. After that, the solid particles generated by the reaction are separated by filtration, washed with water, dried under a nitrogen atmosphere, and then measured by an impact tester to find that the weight is 1.0 kg / m.
It did not ignite even when given a shock.

比較例1 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリーにかえて、15重量%水酸化ナトリウム水溶
液151gを用いて同様に実施した。撹拌中にフラスコ内で
発火があつた。反応で生成した固体粒子を濾過分離し、
水洗後、窒素雰囲気下で乾燥し、固体粒子の衝撃発火性
を測定したところ0.02kg重・mで発火した。
Comparative Example 1 Under the same conditions as in Example 1, the same procedure as in Example 1 was repeated except that 151 g of a 15 wt% sodium hydroxide aqueous solution was used instead of the 15 wt% calcium hydroxide slurry. Ignition occurred in the flask during stirring. The solid particles produced in the reaction are separated by filtration,
After washing with water, it was dried in a nitrogen atmosphere, and the impact ignitability of the solid particles was measured.

比較例2 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリー水にかえて35重量%塩化水素水溶液59gを
用いて同様に実施した。撹拌中にフラスコ内で発火があ
つた。反応で生成した固体粒子を濾過分離し、水洗後、
窒素雰囲気下で乾燥し、固体粒子の衝撃発火性を測定し
たところ、0.04kg重・mで発火した。
Comparative Example 2 Under the same conditions as in Example 1, the same procedure was carried out by using 59 g of 35 wt% hydrogen chloride aqueous solution instead of 15 wt% calcium hydroxide slurry water. Ignition occurred in the flask during stirring. Solid particles generated in the reaction are separated by filtration, washed with water,
When the solid particles were dried under a nitrogen atmosphere and the impact ignitability of the solid particles was measured, it was ignited at 0.04 kg weight · m.

比較例3 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリーにかえて15重量%塩化カルシウム水溶液41
6gを用いて同様に実施した。撹拌の間フラスコ内での発
火は無かつた。反応で生成した固体粒子を濾過分離し、
水洗しないで窒素雰囲気下で乾燥し、衝撃発火性を測定
したところ、1.0kg重・mで発火しなかつた。
Comparative Example 3 Under the same conditions as in Example 1, a 15 wt% calcium hydroxide slurry was used instead of the 15 wt% calcium hydroxide slurry.
It carried out similarly using 6g. There was no ignition in the flask during stirring. The solid particles produced in the reaction are separated by filtration,
It was dried in a nitrogen atmosphere without washing with water, and the impact ignitability was measured to find that it did not ignite at 1.0 kgf / m.

しかしながら反応で生成した固体粒子を濾過分離し、水
洗後、窒素雰囲気下で乾燥し、固体粒子の衝撃発火性を
測定したところ0.04kg重・mで発火した。
However, the solid particles produced by the reaction were separated by filtration, washed with water, dried under a nitrogen atmosphere, and the impact ignitability of the solid particles was measured.

比較例4 実施例1と同様の条件において、15重量%水酸化カルシ
ウムスラリー280gにかえて、15重量%水酸化カルシウム
スラリー水溶液100gを用いて同様に実施した。撹拌の間
フラスコ内での発火は無かつた。反応後のpHは1.1であ
つた。水洗後、窒素雰囲気下で乾燥し、固体粒子の衝撃
発火性を測定したところ衝撃試験機で0.03kg重・mの衝
撃で発火した。
Comparative Example 4 Under the same conditions as in Example 1, 280 g of the 15 wt% calcium hydroxide slurry was replaced with 100 g of the 15 wt% calcium hydroxide slurry aqueous solution, and the same procedure was performed. There was no ignition in the flask during stirring. The pH after the reaction was 1.1. After washing with water, it was dried in a nitrogen atmosphere, and the impact ignitability of the solid particles was measured. As a result, it was ignited with an impact tester at an impact of 0.03 kg weight · m.

〔発明の効果〕〔The invention's effect〕

本発明は上述のように、該ポリクロロシラン類を安全に
処理できる。
The present invention can safely treat the polychlorosilanes as described above.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】水素と塩化珪素を金属珪素存在下または不
存在下反応させ、該塩化珪素を還元する際に、副生する
ポリクロロシラン類をアルカリ土類金属の水酸化物、ア
ルカリ土類金属の酸化物またはアンモニアで処理する事
を特徴とする、副生ポリクロロシラン類の処理方法。
1. A polychlorosilane produced as a by-product during the reaction of hydrogen with silicon chloride in the presence or absence of metallic silicon to reduce the silicon chloride is a hydroxide of an alkaline earth metal or an alkaline earth metal. A method for treating by-produced polychlorosilanes, which comprises treating with an oxide of the above or ammonia.
JP8235688A 1988-04-05 1988-04-05 Treatment method for polychlorosilanes Expired - Lifetime JPH0692249B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8235688A JPH0692249B2 (en) 1988-04-05 1988-04-05 Treatment method for polychlorosilanes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8235688A JPH0692249B2 (en) 1988-04-05 1988-04-05 Treatment method for polychlorosilanes

Publications (2)

Publication Number Publication Date
JPH01257119A JPH01257119A (en) 1989-10-13
JPH0692249B2 true JPH0692249B2 (en) 1994-11-16

Family

ID=13772301

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8235688A Expired - Lifetime JPH0692249B2 (en) 1988-04-05 1988-04-05 Treatment method for polychlorosilanes

Country Status (1)

Country Link
JP (1) JPH0692249B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2019181044A1 (en) * 2018-03-23 2019-09-26 株式会社 東芝 Treatment solution and treatment method
JP7156605B2 (en) * 2019-01-25 2022-10-19 株式会社東芝 Processing equipment and processing method

Also Published As

Publication number Publication date
JPH01257119A (en) 1989-10-13

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