JPS5910329A - Method for removing fluorinated hydrocarbon - Google Patents

Method for removing fluorinated hydrocarbon

Info

Publication number
JPS5910329A
JPS5910329A JP57118107A JP11810782A JPS5910329A JP S5910329 A JPS5910329 A JP S5910329A JP 57118107 A JP57118107 A JP 57118107A JP 11810782 A JP11810782 A JP 11810782A JP S5910329 A JPS5910329 A JP S5910329A
Authority
JP
Japan
Prior art keywords
liquid
gas
alkali metal
fluorinated hydrocarbon
ammonia
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.)
Pending
Application number
JP57118107A
Other languages
Japanese (ja)
Inventor
Takashi Oshiba
大柴 孝
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.)
Resonac Holdings Corp
Original Assignee
Showa Denko 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 Showa Denko KK filed Critical Showa Denko KK
Priority to JP57118107A priority Critical patent/JPS5910329A/en
Publication of JPS5910329A publication Critical patent/JPS5910329A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

Abstract

PURPOSE:To remove fluorinated hydrocarbon contained in a gas or liquid easily and almost quantitatively, by bringing it into contact with a liquid ammonia soln. of an alkali metal. CONSTITUTION:To remove the fluorinated hydrocarbon from a gas, the gas to be treated freed of O2, CO2, H2O, etc. in advance is passed through a liquid ammonia dissolving a metallic sodium or the like alkali metal, and to bring them into gas-liquid contact. To remove fluorinated hydrocarbon dissolved in the liquid, a liquid ammonia soln. of the alkali metal and the liquid freed of water, alcohols, organic acids, etc. in advance are brought into liquid-liquid contact. The ammonia remaining in the gas and the liquid after the treatment is removed by cooling or the like.

Description

【発明の詳細な説明】 本発明は弗素化炭化水素を含有する気体又は液体より弗
素化炭化水素を除去する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing fluorinated hydrocarbons from gases or liquids containing them.

周知のように70ン11(cal@F)、フロン12(
OOJ*h)、フロン13 (OOJ?s )、フロン
14(OF4)、フロン21 (0HOJ、F)、フロ
ン22 (oHo11!I* )、フロン113(OO
1mFOOJI?、)、70ン114(OOJIF雪o
alh、)等のような弗素化炭化水素は、通常化学的に
安定で200℃以下の温度では大部分の金属および酸、
とは反応しない。
As is well known, 70 ton 11 (cal@F), Freon 12 (
OOJ*h), Freon 13 (OOJ?s), Freon 14 (OF4), Freon 21 (0HOJ,F), Freon 22 (oHo11!I*), Freon 113 (OO
1mFOOJI? ), 70n114 (OOJIF snow o
Fluorinated hydrocarbons such as alh, ) are usually chemically stable and are resistant to most metals and acids at temperatures below 200°C.
It doesn't react.

また上記弗素化炭化水素は200℃以上の温度、例えば
火炎の中においても完全に分解するととはないが分解し
九生成物は烈しい屑食性がある。ま友邦素化炭化水素は
、固体(例えばポリテトラフルオロエチレン、黒鉛等)
に吸着させることも出来るが、その吸着量は極めて低く
、弗素化炭化水素を効率よく定量的に除去する方法は知
られていない。
Further, the above-mentioned fluorinated hydrocarbons decompose at temperatures above 200° C., for example in flames, although they do not decompose completely, and the resulting products are highly erodible. The hydrogenated hydrocarbons are solids (e.g. polytetrafluoroethylene, graphite, etc.)
Although it is possible to adsorb fluorinated hydrocarbons, the amount of adsorption is extremely low, and there is no known method for efficiently and quantitatively removing fluorinated hydrocarbons.

しかるに近年弗素化炭化水素が成層圏に蓄積され、成層
圏に存在するオゾン層を破壊するとの説が出され、地球
上の生物への影響が懸念されている。そのため弗素化炭
化水素をエアゾールに使用することが問題に々シ始めた
。また上記弗素化炭化水素は半導体の製造、その他にも
使用され、今後の消費量は増大することが予想されてい
る。このため弗素化炭化水素を大気中に放散させること
は、極力抑制しなければならない。本発明はこの様な状
況に基く社会の要求に応するべく行なわれたものである
However, in recent years, it has been proposed that fluorinated hydrocarbons accumulate in the stratosphere and destroy the ozone layer that exists in the stratosphere, raising concerns about their impact on living things on Earth. As a result, the use of fluorinated hydrocarbons in aerosols has become problematic. Furthermore, the above-mentioned fluorinated hydrocarbons are used for semiconductor manufacturing and other purposes, and consumption is expected to increase in the future. Therefore, the release of fluorinated hydrocarbons into the atmosphere must be suppressed as much as possible. The present invention has been made to meet the demands of society based on such circumstances.

周知のように週期率表第1族Aのアルカリ土属(例えば
リチウム、ナトリウム、カリウム等)は、液体アンモニ
ア(以下液安と云う)に溶解する。
As is well known, alkaline earth metals (for example, lithium, sodium, potassium, etc.) in Group 1 A of the weekly rate table are dissolved in liquid ammonia (hereinafter referred to as liquid ammonium).

これらの溶液は(1)式に示すようにアルカリ金属;M
がアルカリ金属陽イオンと電子に解離する。
These solutions contain alkali metal; M
dissociates into alkali metal cations and electrons.

M−M+十e−(NH8):c・・・・・・・・・(1
)上記#5液は、アルカリ金属の種類にかかわらず青色
であり、アルカリ金属の濃度が高い場合赤褐〜金色を早
する。これは上記解離した電子とアンモニア分子の会合
したものf!(NH,)、Zjの色のためであると言わ
れている。父上配溶液は高い電気伝導度を示す。それと
ともに化学的には電子を与える、すなわち電子ドナーと
して極めて高い還元力を有することが知られている。
M−M+10e−(NH8):c・・・・・・・・・(1
) The above #5 liquid is blue regardless of the type of alkali metal, and when the concentration of alkali metal is high, the color changes from reddish brown to gold quickly. This is a combination of the above-mentioned dissociated electrons and ammonia molecules f! It is said that this is due to the color of (NH,), Zj. The father solution exhibits high electrical conductivity. At the same time, chemically, it is known to have an extremely high reducing power as an electron donor.

本発明者は、上記の見地よシ、従来化学的に安定なため
その除去が極めて困難とされてきた弗素化炭化水素をア
ルカリ金属の液安溶液と接触させることによp極めて速
やかに反応が行なわれ、アルカリ金属の弗素化物を生成
することを知見した。
From the above viewpoint, the present inventors have discovered that by bringing fluorinated hydrocarbons, which have conventionally been considered extremely difficult to remove due to their chemical stability, into contact with a liquid solution of an alkali metal, a reaction can be achieved extremely rapidly. It was discovered that fluorides of alkali metals were produced.

例えば OF4+4na(液体NHs 浴U)=e + 41J
alF ・・・+2)のように弗素化炭化水素分子中の
すべての弗素原子はアルカリ金属の弗素化物となる。
For example, OF4+4na (liquid NHs bath U) = e + 41J
alF...+2), all the fluorine atoms in the fluorinated hydrocarbon molecule become alkali metal fluorides.

壕だ、 aaA、F+4Na(1体NH,溶1) =c+3Na
Cl+NaF・・・・・・・・・ (3) のように他のハロゲン原子の存在する弗素化炭化水素は
すべてのノ・ロゲン原子がアルカリ金属のノ・ロゲン化
物となる。但しく2)および(3)式中の右辺の0は必
ずしも炭素のみとは限らない。
It's a trench, aaA, F+4Na (1 body NH, 1 melt) = c+3Na
In a fluorinated hydrocarbon in which other halogen atoms are present, such as Cl+NaF (3), all the halogen atoms become halogenides of alkali metals. However, 0 on the right side in formulas 2) and (3) does not necessarily represent only carbon.

上記反応条件は%に厳しいものでない。各々のアルカリ
金属の液安溶液は、常温(加圧)或いは低温(常圧)で
も、それぞれの溶解度に大差がなく、又それらの弗素化
炭化水素の除去能力は変らないので、目的に応じて圧、
温度条件を選択出来る。
The above reaction conditions are not critical. There is no major difference in the solubility of liquid solutions of each alkali metal at room temperature (under pressure) or at low temperatures (at normal pressure), and their ability to remove fluorinated hydrocarbons remains the same, so it can be used depending on the purpose. pressure,
Temperature conditions can be selected.

特に金属ナトリウムは安価で使い易く、さらにこれの液
安溶液は安定性に優れている。また金属ナトリウムを液
安に直接溶解する代りに、塩化ナトリウム、臭化ナトリ
ウムのような液安によく溶解するナトリウム塩の液安清
液をつくり、これを隔膜を有する電解槽の中で電解し、
陰極室に生成するアルカリ金属の液安溶液を使用するこ
とも出来る。
In particular, metallic sodium is cheap and easy to use, and its liquid solution has excellent stability. In addition, instead of directly dissolving metallic sodium in liquid ammonium, a liquid ammonium solution of a sodium salt such as sodium chloride or sodium bromide that dissolves well in liquid ammonium is prepared, and this is electrolyzed in an electrolytic cell with a diaphragm. ,
It is also possible to use a liquid solution of an alkali metal formed in the cathode chamber.

ガス中に含有する弗素化炭化水素を除去する場合には、
ガス中に含有するO@ 、00鴬、1110等は、金属
ナトリウムの液安溶液と反応するので齢もって除去しな
ければならない。これら有害不純物を除去したガスを上
記アルカリ金属を溶解した液安溶液中に通す。この際気
液の接触に有効な攪拌装置或いは分散器(例えば硝子、
カーボン等の多孔吹込板等)或いは吸収塔を通して上記
ガスを液安清液中に微粒子として分散して、気液接触面
積を大きくする必要がある。なお水素、窒素等は上記溶
液に対し不活性で、存在しても何ら差支えない。
When removing fluorinated hydrocarbons contained in gas,
O@, 00, 1110, etc. contained in the gas react with the liquid ammonium solution of metallic sodium, so they must be removed as the gas ages. The gas from which these harmful impurities have been removed is passed through a liquid ammonium solution in which the alkali metal is dissolved. At this time, a stirring device or a disperser (e.g. glass,
It is necessary to increase the gas-liquid contact area by dispersing the above-mentioned gas as fine particles in the liquid washing liquid through a porous blowing plate made of carbon, etc.) or an absorption tower. Note that hydrogen, nitrogen, etc. are inert to the above solution, and there is no problem even if they are present.

また液中に含有する弗素化炭化水素を除去する場合には
、液中に含有する水、アルコール類、有機酸、含酸素化
合物等アルカリ金属の液安清液と反応するものは前もっ
て除去しておく必要がある。
In addition, when removing fluorinated hydrocarbons contained in the liquid, water, alcohols, organic acids, oxygen-containing compounds, and other substances that react with the alkali metal liquid must be removed in advance. It is necessary to keep it.

一般に液安は石油系炭化水素或いは飽和芳香族炭化水素
に溶解しガいか又は/h量しか溶解しないので二層分離
して存在するアルカリ金属の液安溶液と弗素化炭化水素
を含有する石油系炭化水素或いは飽和芳香族炭化水素を
激しく攪拌し、比重の小さい液安清液を上記弗素化炭化
水素を含有する炭化水素中に導入してエマルジョン状態
とし液−液接触させ、上記弗素化炭化水素を除去するこ
とが出来る。
In general, liquid ammonium dissolves in petroleum-based hydrocarbons or saturated aromatic hydrocarbons in only a small amount, so it exists in two separate layers: a liquid ammonium solution of an alkali metal and a petroleum-based solution containing fluorinated hydrocarbons. Hydrocarbons or saturated aromatic hydrocarbons are vigorously stirred, and a liquid solution having a low specific gravity is introduced into the hydrocarbon containing the fluorinated hydrocarbon to form an emulsion and liquid-liquid contact is carried out to produce the fluorinated hydrocarbon. can be removed.

上記のように気体又は液体に含有される弗素化炭化水素
をアルカリ金属の液安溶液で処理した後、該気体又は液
体中にはその処理温度および圧力に応じた濃度のアンモ
ニアを含有するが、これは公知の方法、例えは冷却又は
圧縮と冷却その他物理的な吸着、化学的中和、酸による
洗浄、水洗等によって容易に除去することが出来る。
After the fluorinated hydrocarbon contained in the gas or liquid is treated with a liquid alkali metal solution as described above, the gas or liquid contains ammonia at a concentration depending on the treatment temperature and pressure. This can be easily removed by known methods such as cooling, compression and cooling, other physical adsorption, chemical neutralization, washing with acid, washing with water, etc.

以上述べたように、本発明にかかる弗素化炭化水素の除
去方法は、弗素化炭化水素を含有したガス又は液をアル
カリ金属を溶解した液安溶液を用いて洗浄することによ
って殆どすべての弗素化炭化水素を容易に除去すること
が出来るものである。
As described above, the method for removing fluorinated hydrocarbons according to the present invention removes almost all fluorinated hydrocarbons by washing the gas or liquid containing the fluorinated hydrocarbons with a liquid solution containing an alkali metal. Hydrocarbons can be easily removed.

次に実施例を示し本発明の方法を具体的に説明する。Next, the method of the present invention will be specifically explained with reference to Examples.

〔実施例−1〕 金属ナトリウム509を溶解した液安溶9460ccを
容器に入れ、−33℃に保持し毎分3000回転の攪拌
機で攪拌しながら、四弗化炭素(OF4)を2.5%含
有する窒素ガスを毎分lO1の流速で通した。排出ガス
は一70℃の還流冷却器により同伴するアンモニアガス
を凝−させ上記吸収瓶に戻した。排ガス中の四弗化炭素
はQ、lpp以下であった。
[Example-1] 9460 cc of a liquid solution containing metallic sodium 509 was put into a container, and while being kept at -33°C and stirred with a stirrer at 3000 revolutions per minute, 2.5% carbon tetrafluoride (OF4) was added. Containing nitrogen gas was passed through at a flow rate of 1O1 per minute. The exhaust gas was returned to the absorption bottle after condensing the accompanying ammonia gas using a reflux condenser at -70°C. Carbon tetrafluoride in the exhaust gas was below Q, lpp.

〔実施例−2〕 円筒縦形の吸収塔に金属ナトリウム23gを含む液安浴
液223 ccを入れ、この液安M液中にロータリーア
トマイザを配置し、このロータリーアトマイザの回転子
を3000191で回転するとともにこの回転子の下方
よ如、ジクロロジフロロメタン(acl、y、)  o
、a俤を含有する輩素な1077g1rの速度で30分
通した。液安の温度は常温(25℃)で蒸気圧は9 k
y/iである。排ガスは一33℃に冷却した冷却器によ
シ同伴アンモニアを上記吸収塔に還流した。排出ガス中
にool、F!は検出されなかった。
[Example-2] Put 223 cc of liquid ammonium bath liquid containing 23 g of metallic sodium into a cylindrical vertical absorption tower, place a rotary atomizer in this liquid ammonium liquid, and rotate the rotor of this rotary atomizer at 3000191. At the same time, below this rotor, dichlorodifluoromethane (acl, y,) o
, 30 minutes at a speed of 1077g1r containing a ton of water. The temperature of the liquid is room temperature (25℃) and the vapor pressure is 9K.
It is y/i. The exhaust gas was cooled to -33° C. through a condenser, and the entrained ammonia was refluxed to the absorption tower. ool, F in the exhaust gas! was not detected.

〔実施例−3〕 吸収液として金属カリウム150gを含有した液安溶W
i、600gを実施例−2と同じロータリーアトマイザ
を配置した吸収塔に入れ一33℃に保持し、クロロジフ
ルオロメタン(aaolFt)を5%含有する水素ガス
を1017分の流速で回転子下方より導入した。排出ガ
スは一70℃の還流冷却器を通して排出したところ、排
出ガス中の0HOA’F’!濃度は0.1pIm以下で
あった。
[Example-3] Liquid weak solution W containing 150 g of metallic potassium as an absorption liquid
i, 600 g was placed in an absorption tower equipped with the same rotary atomizer as in Example-2 and maintained at -33°C, and hydrogen gas containing 5% chlorodifluoromethane (aaolFt) was introduced from below the rotor at a flow rate of 1017 min. did. When the exhaust gas was discharged through a reflux condenser at -70°C, 0HOA'F' was found in the exhaust gas! The concentration was below 0.1 pIm.

実施例 吸収液の容器として攪拌羽根を取付けた耐圧の電解槽の
陰極室を用いた。電解槽には隔膜として硝子微粒子を焼
結した多孔板が設けられ、この隔膜を隔てて金属アルミ
ニラ板よシなる陰極、および黒鉛よりなる陽極が設けら
れている。
Example A cathode chamber of a pressure-resistant electrolytic cell equipped with a stirring blade was used as a container for the absorption liquid. The electrolytic cell is provided with a porous plate made of sintered glass particles as a diaphragm, and a cathode made of a metal aluminum plate and an anode made of graphite are provided across the diaphragm.

上記電解槽には、予め乾燥した臭化ナトIJウム100
0gを液安35009に溶解した電解液を入れ、これを
30℃ 11kg/、lの下で直流7V、190AHを
通して電解した。通電開始15分後より、トリクロロフ
ルオロメタン(OFOlm )0.5チ、ジクロロジフ
ルオロメタン(OF、 cl、 ) 2.OqA、クロ
ロトリフルオロメタン(oFs CI )1.2 %を
含有する窒素ガスを毎分101の速度で陰極室に激しく
攪拌しながら30分間吹込んだ。陰極室から排出された
ガスは一33℃の冷却トラップを通し同伴するアンモニ
アを除去した。
In the above electrolytic cell, pre-dried sodium bromide IJum 100
An electrolytic solution containing 0 g dissolved in liquid ammonium 35009 was added, and this was electrolyzed by passing DC 7 V and 190 AH at 30° C. and 11 kg/l. 15 minutes after the start of current application, 0.5 t of trichlorofluoromethane (OFOlm), 0.5 t of dichlorodifluoromethane (OF, cl, ) 2. Nitrogen gas containing 1.2% OqA, chlorotrifluoromethane (oFs CI ) was blown into the cathode chamber at a rate of 101/min for 30 minutes with vigorous stirring. The gas discharged from the cathode chamber was passed through a cold trap at -33°C to remove entrained ammonia.

排出ガス中の弗素化炭化水素の総量は、0.13−であ
った。
The total amount of fluorinated hydrocarbons in the exhaust gas was 0.13-.

〔実施例−5〕 トリクロロフルオロメタン(oval、)t、5 qA
を含有する鉱油100ccと金属ナトリウム2IIを液
安10gに溶解した処理液を攪拌機を有する加圧溜器に
入れ、常温下3000rl)lで攪拌して反応さ虻た。
[Example-5] Trichlorofluoromethane (oval,) t, 5 qA
A treatment solution prepared by dissolving 100 cc of mineral oil containing 100 cc of sodium metal 2II in 10 g of liquid ammonium was placed in a pressurized distillation vessel equipped with a stirrer and stirred at room temperature at 3000 ml to react.

反応後、反応生成物を液安の存在下水で洗浄し、アンモ
ニアおよび生成した塩類(弗化ナトリウム、塩化ナトリ
ウム等)を除去した。
After the reaction, the reaction product was washed with water in the presence of liquid sodium chloride to remove ammonia and generated salts (sodium fluoride, sodium chloride, etc.).

二I−分離した鉱油からは弗素化弗化水素は検出されな
かった。
2I - No fluorinated hydrogen fluoride was detected in the separated mineral oil.

出願人昭和電工株式会社Applicant Showa Denko Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] アルカリ金属の液体アンモニア#!液と弗素化炭化水素
を含有するガス又は液とを接触せしめることを特徴とす
る弗素化炭化水素の除去法。
Alkali metal liquid ammonia #! A method for removing fluorinated hydrocarbons, which comprises bringing a liquid into contact with a gas or liquid containing a fluorinated hydrocarbon.
JP57118107A 1982-07-07 1982-07-07 Method for removing fluorinated hydrocarbon Pending JPS5910329A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57118107A JPS5910329A (en) 1982-07-07 1982-07-07 Method for removing fluorinated hydrocarbon

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57118107A JPS5910329A (en) 1982-07-07 1982-07-07 Method for removing fluorinated hydrocarbon

Publications (1)

Publication Number Publication Date
JPS5910329A true JPS5910329A (en) 1984-01-19

Family

ID=14728185

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57118107A Pending JPS5910329A (en) 1982-07-07 1982-07-07 Method for removing fluorinated hydrocarbon

Country Status (1)

Country Link
JP (1) JPS5910329A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5110364A (en) * 1987-03-30 1992-05-05 A.L. Sandpiper Corporation Processes for decontaminating polluted substrates
US5414200A (en) * 1994-03-07 1995-05-09 A.L. Sandpiper Corporation Non-metallized and subtoichiometric metallized reactions with ammonia and other weak bases in the dehalogenation of refrigerants
US5602295A (en) * 1994-03-07 1997-02-11 Commodore Laboratories, Inc. Methods for the elimination of cyanides in the dehalogenation of halofluorocarbons

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5110364A (en) * 1987-03-30 1992-05-05 A.L. Sandpiper Corporation Processes for decontaminating polluted substrates
US5414200A (en) * 1994-03-07 1995-05-09 A.L. Sandpiper Corporation Non-metallized and subtoichiometric metallized reactions with ammonia and other weak bases in the dehalogenation of refrigerants
US5559278A (en) * 1994-03-07 1996-09-24 Commodore Laboratories, Inc. Methods for the destruction of ozone depleting substances
US5602295A (en) * 1994-03-07 1997-02-11 Commodore Laboratories, Inc. Methods for the elimination of cyanides in the dehalogenation of halofluorocarbons

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