Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH07100130B2 - Gas purification method - Google Patents
[go: Go Back, main page]

JPH07100130B2 - Gas purification method - Google Patents

Gas purification method

Info

Publication number
JPH07100130B2
JPH07100130B2 JP63144643A JP14464388A JPH07100130B2 JP H07100130 B2 JPH07100130 B2 JP H07100130B2 JP 63144643 A JP63144643 A JP 63144643A JP 14464388 A JP14464388 A JP 14464388A JP H07100130 B2 JPH07100130 B2 JP H07100130B2
Authority
JP
Japan
Prior art keywords
silver
gas
oxide
purifying
purifying agent
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
JP63144643A
Other languages
Japanese (ja)
Other versions
JPH01315318A (en
Inventor
宏一 北原
昇 秋田
孝 島田
幸平 佐々木
忠 平本
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.)
Japan Pionics Ltd
Original Assignee
Japan Pionics 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 Japan Pionics Ltd filed Critical Japan Pionics Ltd
Priority to JP63144643A priority Critical patent/JPH07100130B2/en
Priority to EP88307918A priority patent/EP0309099B1/en
Priority to DE8888307918T priority patent/DE3869301D1/en
Priority to KR1019880010970A priority patent/KR960004610B1/en
Priority to US07/238,068 priority patent/US4910001A/en
Publication of JPH01315318A publication Critical patent/JPH01315318A/en
Publication of JPH07100130B2 publication Critical patent/JPH07100130B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Catalysts (AREA)
  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明はガスの浄化方法に関し、さらに詳細には有害ガ
スボンベなどから高濃度の有害ガスが急激に漏洩したよ
うな場合にこれを効率よく除去するためのガスの浄化方
法に関する。
Description: TECHNICAL FIELD The present invention relates to a method for purifying gas, and more specifically, to efficiently remove a high concentration of harmful gas from a harmful gas cylinder or the like when such gas leaks rapidly. The present invention relates to a method for purifying gas for cleaning.

近年半導体工業の発展と共にアルシン、ホスフィン、シ
ランおよびジボランなどの極めて毒性の強い水素化物系
ガスの使用量が増加している。これらの有害ガスはシリ
コン半導体や化合物半導体の製造プロセスにおいて、原
料ガスあるいはドーピングガスとして不可欠なものであ
るが、いずれも極めて毒性が高く、それぞれの許容濃度
はアルシン(AsH3)で0.05ppm、ホスフィン(PH3)で0.
3ppm、シラン(SiH4)で5ppm、ジボラン(B2H6)で0.1p
pm、セレン化水素(SeH2)で0.05ppmとされている。こ
れらの有害ガスは通常は例えば下表に示したように0.1
〜50程度のガスボンベに充填して市販されている。
With the development of the semiconductor industry in recent years, the use amount of extremely toxic hydride gases such as arsine, phosphine, silane and diborane has been increasing. These harmful gases are indispensable as a source gas or a doping gas in the manufacturing process of silicon semiconductors and compound semiconductors, but both are extremely toxic, and the permissible concentration of each is 0.05 ppm for arsine (A s H 3 ). , With phosphine (PH 3 ) 0.
3 ppm, silane (SiH 4 ) 5 ppm, diborane (B 2 H 6 ) 0.1 p
pm, hydrogen selenide (SeH 2 ) 0.05 ppm. These noxious gases are usually 0.1% as shown in the table below.
It is marketed by filling a gas cylinder of about 50.

これらのボンベはガスが漏洩した場合に直接外部の空気
を汚染することを防止するため、通常はボンベボックス
と呼ばれる換気ダクトに接続されたボンベ収納容器内に
収納された状態で半導体プロセスなどへのガスの供給配
管に接続して使用される。このようなボンベボックス内
に収納されていても思わぬ事故などにより、例えば5〜
10分程度の短時間でボンベが空になるような急激なガス
の漏洩が発生する危険性が皆無といえず、このような事
故に対処しうる安全対策が強く要望されている。
In order to prevent the air from directly contaminating the outside air when gas leaks, these cylinders are normally stored in a cylinder storage container connected to a ventilation duct called a cylinder box, and are used for semiconductor processes. Used by connecting to gas supply pipe. Even if it is stored in such a cylinder box, due to an unexpected accident, for example,
There is absolutely no risk of sudden gas leaks that will empty the cylinder in a short time of about 10 minutes, and there is a strong demand for safety measures that can deal with such accidents.

〔従来の技術〕[Conventional technology]

ガス中に含有されるアルシン、ホスフィンなどを除去す
る方法としては、スクラバーで吸収分解させる湿式法
と、吸着剤または酸化剤を充填した充填筒内にガスを流
して除去する乾式法とが知られている。一般的には湿式
法は、吸収液による腐食や後処理などに困難性があり、
装置の保守に費用を要するという欠点がある。
Known methods for removing arsine, phosphine, etc. contained in the gas are a wet method of absorbing and decomposing with a scrubber and a dry method of flowing a gas into a filling cylinder filled with an adsorbent or an oxidant to remove the gas. ing. Generally, the wet method has difficulty in corrosion by the absorbing liquid and post-treatment.
The disadvantage is that maintenance of the device is expensive.

乾式法としては、空気中のアルシン、ホスフィンなどの
有害ガスを除去するために、化学戦争において活性炭を
充填したガスマスクが知られており、また、この活性炭
の吸着力を利用し、さらに種々の物質を添着して、除去
能力の向上を企てる試みも行われている。例えば、活性
炭を担体とし、これに銅化合物、アルカリ金属化合物、
Al,Ti,V,Cr,Mn,Feなどの金属化合物の一種以上を含有さ
せたアルシン、ホスフインなどの吸着剤(特開昭59−16
0535号、60−71039号公報)およびヨウ素またはヨウ素
化合物と金属硫酸塩などを活性炭に含浸させたアルシ
ン、ホスフィンなどの吸着剤(特開昭60−71040号公
報)などがある。
As a dry method, in order to remove harmful gases such as arsine and phosphine in the air, a gas mask filled with activated carbon in chemical warfare is known. Attempts have also been made to attach substances and attempt to improve their removal ability. For example, using activated carbon as a carrier, a copper compound, an alkali metal compound,
Adsorbents such as arsine and phosphine containing one or more metal compounds such as Al, Ti, V, Cr, Mn and Fe (Japanese Patent Laid-Open No. 59-16
No. 0535, 60-71039) and an adsorbent such as arsine and phosphine in which activated carbon is impregnated with iodine or an iodine compound and a metal sulfate (JP-A-60-71040).

また、活性炭を担体とするもの以外では本発明者らによ
る(1)酸化第二銅、および(2)酸化珪素、酸化アル
ミニウムおよび酸化亜鉛からなる群から選ばれる少なく
とも1種の金属酸化物を配合し、成型した浄化剤を用い
る方法(特開昭61−209030号公報)がある。
In addition to those using activated carbon as a carrier, the present inventors have blended (1) cupric oxide and (2) at least one metal oxide selected from the group consisting of silicon oxide, aluminum oxide and zinc oxide. However, there is a method of using a molded purifying agent (JP-A-61-209030).

〔発明が解決しようとする問題点〕[Problems to be solved by the invention]

しかしながら、前記のような活性炭を担体とする吸着剤
は比較的濃度のアルシン、ホスフィンなどの有害ガスを
除去することは可能であるが、高濃度で流速の大きいガ
ス中の有害ガスに対しては活性が低く過ぎ、また、これ
らの水素化物系ガスによって還元されたヨウ素が飛散し
易いという問題点がある。
However, although the adsorbent having activated carbon as a carrier as described above can remove harmful gases such as arsine and phosphine in a relatively high concentration, it does not remove harmful gases in a gas having a high concentration and a high flow rate. There is a problem that the activity is too low and the iodine reduced by these hydride-based gases is easily scattered.

一方、本発明者らによる特開昭61−209030号公報におけ
る浄化剤は従来の浄化剤に比べ、単位重量および単位容
積に対する有害ガスの除去容量が格段に大きく、大量の
有害ガスを除去することができる。
On the other hand, the cleaning agent disclosed in Japanese Patent Laid-Open No. 61-209030 by the present inventors has a remarkably large removal capacity of harmful gas per unit weight and unit volume as compared with the conventional cleaning agent, and is capable of removing a large amount of harmful gas. You can

しかしながらこの浄化剤は、条件によっては除去速度が
必ずしも十分とはいえないため、前記したようにボンベ
などから有害ガスが急激に漏洩したような緊急時に対し
ては十分迅速に処理することができないという問題点が
ある。
However, this purifying agent cannot be said to have a sufficient removal rate depending on the conditions, and as described above, it cannot be treated sufficiently swiftly in an emergency where harmful gas is suddenly leaked from a cylinder or the like. There is a problem.

従って大量の有害ガスが漏洩するような緊急時などにお
いては従来の除害方法では対処することが出来ないた
め、さらに除去性能の優れた浄化方法の出現が望まれて
きた。
Therefore, in the case of an emergency where a large amount of harmful gas leaks, the conventional removal method cannot be dealt with, and therefore, the advent of a purification method having further excellent removal performance has been desired.

〔問題点を解決するための手段、作用〕[Means and actions for solving problems]

本発明者らはこれらの問題点を解決するべく鋭意検討を
重ねた結果、二酸化マンガン、酸化銅および酸化コバル
トの三成分を主成分とする組成物に、さらに銀化合物を
含有させた浄化剤を用いることによって空気中などに漏
洩した高濃度の有害ガスを極めて効率よく除去しうるこ
とを見出し本発明に到達した。
As a result of repeated intensive studies to solve these problems, the present inventors have found that a composition containing three components of manganese dioxide, copper oxide and cobalt oxide as a main component, and a purifying agent further containing a silver compound are used. The present invention has been found to be capable of extremely efficiently removing a high-concentration harmful gas that has leaked into the air, etc., by using it, and arrived at the present invention.

すなわち、本発明は有害ガスとしてアルシン、ホスフィ
ン、シラン、ジボランおよびセレン化水素の一種以上を
含有するガスと、浄化剤とを接触させて当該ガスから有
害ガスを除去するガスの浄化方法において、浄化剤とし
て(1)二酸化マンガン、酸化銅および酸化コバルトを
主成分とする組成物に(2)銀化合物を含有せしめてな
る成型体を用いることを特徴とする排ガスの浄化方法で
ある。
That is, the present invention is a method for purifying a gas in which a gas containing one or more of arsine, phosphine, silane, diborane and hydrogen selenide as a harmful gas is brought into contact with a purifying agent to remove the harmful gas from the gas. The method for purifying exhaust gas is characterized in that a molded body obtained by incorporating (2) a silver compound into a composition containing (1) manganese dioxide, copper oxide and cobalt oxide as main components is used as an agent.

本発明の浄化方法は空気、窒素および水素中など、主に
空気中に含有されるアルシン、ホスフィンなどの有害ガ
スを効率よく除去することができる。
The purification method of the present invention can efficiently remove harmful gases such as arsine and phosphine contained mainly in the air such as air, nitrogen and hydrogen.

特に、本発明の浄化方法は多量で比較的濃度の高い有害
ガスを迅速に、しかも常温で除去することができる。例
えば、前記したようにボンベから急激に漏洩するなどで
有害ガスによって汚染されたガスの迅速な浄化などに優
れた効果が得られる。
In particular, the purification method of the present invention can remove a large amount of harmful gas having a relatively high concentration quickly and at room temperature. For example, as described above, it is possible to obtain an excellent effect such as rapid purification of a gas contaminated by a harmful gas such as a sudden leak from the cylinder.

本発明において二酸化マンガン、酸化銅および酸化コバ
ルトの三成分を主成分とする組成物(以下Mn−Cu−Co系
組成物と記す)に銀化合物を含有せしめてなる成型体が
浄化剤として使用される。
In the present invention, a molded body obtained by containing a silver compound in a composition mainly containing three components of manganese dioxide, copper oxide and cobalt oxide (hereinafter referred to as Mn-Cu-Co composition) is used as a purifying agent. It

Mn−Cu−Co系組成物中の二酸化マンガンおよび酸化銅の
含有量は通常、両者を合わせて60wt%以上、好ましくは
70wt%以上であり、このうち二酸化マンガンに対する酸
化銅の割合は重量比で通常は1:0.2〜1.2、好ましくは1:
0.3〜0.8程度とされる。
The content of manganese dioxide and copper oxide in the Mn-Cu-Co-based composition is usually 60 wt% or more in total, preferably
70 wt% or more, of which the ratio of copper oxide to manganese dioxide is usually 1: 0.2 to 1.2 by weight, preferably 1 :.
It is set to about 0.3 to 0.8.

また、Mn−Cu−Co系組成物中の酸化コバルトの含有量は
上記二酸化マンガンと酸化銅の含有量にもよるが、通常
は5〜40wt%、好ましくは10〜30wt%とされる。
The content of cobalt oxide in the Mn-Cu-Co composition depends on the contents of manganese dioxide and copper oxide, but is usually 5 to 40 wt%, preferably 10 to 30 wt%.

さらに、Mn−Cu−Co系組成物には所望により例えば、ア
ルミニウム、珪素、鉄、ニッケルおよびカリウムの酸化
物などを含有させてもよい。
Further, if desired, the Mn-Cu-Co-based composition may contain, for example, oxides of aluminum, silicon, iron, nickel and potassium.

これらのMn−Cu−Co系組成物を得るには種々な方法があ
り、例えば それぞれの成分である酸化物を同時に混合する方法、 二酸化マンガンと酸化銅を混合するか、あるいは混合
物の市販品(ホプカライト)もあるので、これらの二成
分系の組成物に、さらに酸化コバルトを混合する方法、 これらの金属の塩、水酸化物などの中間物の段階で混
合し、これらを焼成するなどで酸化物の組成物とする方
法などがある。
There are various methods for obtaining these Mn-Cu-Co-based compositions, for example, a method of simultaneously mixing oxides as respective components, a mixture of manganese dioxide and copper oxide, or a commercially available mixture ( Hopcalite) is also available, so a method of further mixing cobalt oxide with these two-component compositions, mixing at the stage of intermediates such as salts of these metals, hydroxides, etc., and oxidizing them by firing etc. And the like.

このようなMn−Cu−Co系組成物を成型体とし、そのまま
アルシン、ホスフィンなどの水素化物系ガスの除去に用
いてもよいが、その場合には乾燥ガス中ではこれらの有
害成分は或程度除去できても、通常の大気中のような相
対湿度30〜100%の範囲の空気中など水分を含むガスに
ついては浄化能力が著しく低下する。
Such Mn-Cu-Co-based composition may be used as a molded body and may be used as it is for removal of hydride-based gas such as arsine and phosphine, but in that case, these harmful components are contained to some extent in the dry gas. Even if it can be removed, the purification capacity of the gas containing water such as the air in the relative humidity range of 30 to 100%, which is the same as in the normal atmosphere, is significantly lowered.

これらの欠点を解消すると共に浄化能力をさらに高める
ために、本発明においてはMn−Cu−Co系組成物に、さら
に銀化合物を加えたものを浄化剤として用いる。
In order to eliminate these drawbacks and further improve the purifying ability, in the present invention, a Mn-Cu-Co based composition to which a silver compound is further added is used as a purifying agent.

銀化合物としては、酸化銀(I)、酸化銀(II)ならび
に無機酸銀、有機酸銀およびハロゲン化銀などの銀塩
(I)が挙げられる。無機酸銀としては例えば炭酸銀、
硝酸銀、亜硝酸銀、硫酸銀、亜硫酸銀、塩素酸銀、過塩
素酸銀、臭素酸銀、ヨウ素酸銀、過ヨウ素酸銀、燐酸水
素二銀、燐酸銀、ピロリン酸銀、メタリン酸銀、テトラ
フルオロホウ酸銀、ヘキサルフルオロ燐酸銀など、ハロ
ゲン化銀としては例えば弗化銀、塩化銀、臭化銀、ヨウ
化銀、有機酸銀としては例えば酢酸銀、シュウ酸銀など
がある。これらのうちでも酸化銀(I)および酸化銀
(II)が好ましく、また、各種銀塩(I)のうちでは水
に難溶ないし不溶性の塩が一般的に好ましく、例えば炭
酸銀、硫酸銀、燐酸銀、亜硫酸銀、塩化銀、臭化銀、ヨ
ウ化銀、ヨウ素酸銀、ピロリドン酸銀、メタリン酸銀お
よびシュウ酸銀などが挙げられる。このうち酸化銀(I
I)が特に好ましく、次いで炭酸銀(I)、酸化銀
(I)およびこれらの混合物が好ましい。
Examples of the silver compound include silver (I) oxide, silver (II) oxide, and silver salts (I) such as inorganic acid silver, organic acid silver and silver halide. Examples of the inorganic acid silver include silver carbonate,
Silver nitrate, silver nitrite, silver sulfate, silver sulfite, silver chlorate, silver perchlorate, silver bromate, silver iodate, silver periodate, dihydrogen phosphate, silver phosphate, silver pyrophosphate, silver metaphosphate, tetra Examples of silver halides such as silver fluoroborate and silver hexalfluorophosphate include silver fluoride, silver chloride, silver bromide and silver iodide, and examples of organic silver salts include silver acetate and silver oxalate. Of these, silver oxide (I) and silver oxide (II) are preferable, and among various silver salts (I), salts that are sparingly soluble or insoluble in water are generally preferable, and examples thereof include silver carbonate and silver sulfate. Examples thereof include silver phosphate, silver sulfite, silver chloride, silver bromide, silver iodide, silver iodate, silver pyrrolide acid, silver metaphosphate and silver oxalate. Of these, silver oxide (I
I) is particularly preferred, followed by silver (I) carbonate, silver (I) oxide and mixtures thereof.

浄化剤に含有せしめられる銀化合物の量は、通常は0.01
〜10.0wt%とされ好ましくは0.2〜5wt%とされる。含有
量が0.01wt%以下ではガスの浄化効率が低下し、一方10
wt%以上では経済的負担が大きくなる。
The amount of silver compound contained in the purifying agent is usually 0.01.
〜10.0wt% and preferably 0.2〜5wt%. If the content is 0.01 wt% or less, the gas purification efficiency decreases, while 10
If it is more than wt%, the economic burden will increase.

浄化剤の形態としてはMn−Cu−Co系組成物と銀化合物と
の混合物の成型体であってもよく、また、Mn−Cu−Co系
組成物の成型体の銀化合物を添着させたものであっても
よいが、比較的高価な銀化合物を少量で効果的に作用さ
せるなどの目的から、後者のようにMn−Cu−Co系組成物
の成型体に銀化合物を添着させる形態が好ましい。
The form of the purifying agent may be a molded product of a mixture of an Mn-Cu-Co-based composition and a silver compound, or a molded product of the Mn-Cu-Co-based composition to which a silver compound is attached. However, for the purpose of effectively acting a relatively expensive silver compound in a small amount, it is preferable to attach the silver compound to the molded body of the Mn-Cu-Co composition like the latter. .

銀化合物を添着させる場合のMn−Cu−Co系組成物として
は破砕品、押出成形品、打錠成型品などの種々の形状の
ものを用いることができる。そのサイズは破砕品であれ
ば4〜20メッシュ程度、押出成型品であれば1.5〜4mmφ
×3〜20mm程度、打錠成型品であれば通常は円筒状で3
〜6mmφ×3〜6mm程度の大きさのものが好ましい。しか
し、装置の設計条件などによってその他の寸法としても
何ら支障はない。
As the Mn-Cu-Co-based composition to which the silver compound is attached, various shapes such as a crushed product, an extrusion molded product, and a tablet molded product can be used. The size is about 4 to 20 mesh for crushed products, and 1.5 to 4 mmφ for extruded products.
× 3 to 20 mm, usually 3 mm in the case of tablet molding
A size of about 6 mmφ × 3 to 6 mm is preferable. However, there is no problem with other dimensions depending on the design conditions of the device.

銀化合物をMn−Cu−Co系組成物に添着させる方法として
は種々のやりかたが可能であり、湿式法を用いてもよ
く、また、乾式法を用いてもよい。簡便な方法としては
Mn−Cu−Co系組成物の成型体に粉末状の銀化合物をまぶ
しつける方法、または銀化合物を水性スラリーとして添
着する方法、あるいは水溶性の銀化合物を水溶液として
含浸させる方法などがある。
Various methods can be used to attach the silver compound to the Mn-Cu-Co-based composition, and a wet method or a dry method may be used. As a simple method
There are a method of sprinkling a powdered silver compound on a molded body of the Mn-Cu-Co composition, a method of impregnating the silver compound as an aqueous slurry, a method of impregnating a water-soluble silver compound as an aqueous solution, and the like.

本発明において浄化剤の粒の密度は、通常は0.62〜1.88
g/ml、好ましくは0.78〜1.56g/mlであり、また、浄化剤
を浄化筒などに充填したときの充填密度は、通常は0.4
〜1.2g/ml程度、好ましくは0.5〜1.0g/ml程度とされ
る。
In the present invention, the particle density of the purifying agent is usually 0.62 to 1.88.
g / ml, preferably 0.78 to 1.56 g / ml, and the packing density when the cleaning agent is packed in a cleaning column is usually 0.4
The amount is about 1.2 g / ml, preferably about 0.5 to 1.0 g / ml.

本発明において、粒の密度とは、成型体(粒)の重さを
幾何学的体積で割ったもの、また、充填密度とは、筒に
充填された浄化剤の重さを浄化剤の充填容積で割ったも
のとしてそれぞれ定義される。
In the present invention, the density of particles is the weight of the molded body (particles) divided by the geometric volume, and the packing density is the weight of the cleaning agent filled in the cylinder. Each is defined as divided by volume.

浄化剤によって除去可能なアルシンおよびホスフィンな
ど水素化物系ガスの濃度は通常は1%以下とされる。こ
れよりも高濃度では反応熱が大きくなり冷却装置などが
必要となることがある。
The concentration of hydride-based gas such as arsine and phosphine that can be removed by the purifying agent is usually 1% or less. If the concentration is higher than this, the reaction heat becomes large and a cooling device or the like may be required.

浄化剤と接触させるガスの温度は通常は0〜90℃、好ま
しくは室温の10〜50℃で操作され、特に加熱や冷却を必
要としない。勿論、接触開始後は反応熱のため、水素化
物系ガスの濃度に応じた温度上昇を示す。
The temperature of the gas to be brought into contact with the purifying agent is usually 0 to 90 ° C., preferably 10 to 50 ° C. at room temperature, and heating or cooling is not particularly required. Of course, after the contact is started, the temperature rises in accordance with the concentration of the hydride-based gas due to the heat of reaction.

接触時の圧力は、通常は常圧であるが、減圧ないし1Kg/
cm2Gのような加圧下で操作することも可能である。
The pressure at the time of contact is usually atmospheric pressure, but reduced pressure or 1 Kg /
It is also possible to operate under pressure such as cm 2 G.

また、接触時間は通常は0.01秒以上でよいが、好ましく
は0.025秒以上である。0.01秒よりも短い接触時間では
充分な浄化能力が得られないことがある。
The contact time is usually 0.01 seconds or longer, preferably 0.025 seconds or longer. If the contact time is shorter than 0.01 seconds, sufficient cleaning performance may not be obtained.

本発明が適用される空気、窒素および水素などのガスの
湿度には特に制限はなく乾燥状態のみならず湿った状態
でもよい。一般的には通常の大気に相当する30〜100%
の相対湿度で使用されることが多く、このような場合に
は浄化剤の含水量はガスの相対湿度に応じて変化し、5
〜30wt%程度に保たれる。また、浄化剤は空気中などの
炭酸ガスなどによって悪影響を受けることはなく、これ
らの存在は状況によっては却って浄化能力を若干高める
こともある。
The humidity of gas such as air, nitrogen and hydrogen to which the present invention is applied is not particularly limited and may be not only a dry state but also a wet state. Generally, 30-100% equivalent to normal atmosphere
Often used at a relative humidity of less than 5%, in which case the water content of the purifier will vary depending on the relative humidity of the gas.
It is kept at about 30wt%. In addition, the purifying agent is not adversely affected by carbon dioxide gas in the air or the like, and the presence of these may rather slightly increase the purifying ability depending on the situation.

本発明において水分を含有するガスの浄化に際しては、
浄化剤はあらかじめ同程度の湿度の雰囲気ガスと接触さ
せることによりその湿度に応じた含水状態に保っておく
ことが好ましい。
In purifying the gas containing water in the present invention,
It is preferable that the purifying agent is kept in a water-containing state corresponding to the humidity by being brought into contact with an atmospheric gas having a similar humidity in advance.

浄化剤は通常は有害ガスの浄化筒に充填され固定床とし
て用いられるが、移動床、流動床として用いることも可
能である。
The purifying agent is usually packed in a purifying column for harmful gas and used as a fixed bed, but it can also be used as a moving bed or a fluidized bed.

浄化剤は例えば第1図のフローシートで示されたような
浄化筒1に充填され、浄化筒1はガスボンベ2が収納さ
れた前記のボンベボックス3内の空気を連続的に吸引換
気するためのブロアー4に接続された換気ダクト5に介
在させて使用される。
For example, the purifying agent is filled in a purifying cylinder 1 as shown in the flow sheet of FIG. 1, and the purifying cylinder 1 is for continuously sucking and ventilating the air in the cylinder box 3 in which the gas cylinder 2 is housed. It is used by interposing it in a ventilation duct 5 connected to the blower 4.

浄化剤をこのような状態で使用する場合には、有害ガス
の濃度が1%を越えるような高濃度では発熱が大きくな
るため、除熱手段が必要となる。しかしながらこのよう
な設備では有害ガスの急激な漏洩が生じても空気との混
合によってその濃度が1%以下に稀釈されるに充分な容
量のブロアーが設けられているのが通常である。具体的
には換気容量が5〜200m3/min程度のブロアーが多く設
置され、例えば前記の表で示されたような市販のガスボ
ンベが5〜10分で空になるような大量の漏洩が生じた場
合の空気中などの有害ガスの含有量は50〜1000ppm程度
であると想定される。
When the purifying agent is used in such a state, the heat generation becomes large at a high concentration of the harmful gas exceeding 1%, and a heat removing means is required. However, in such equipment, it is usual to provide a blower having a sufficient capacity so that the concentration of the harmful gas is diluted to 1% or less by mixing with air even if the harmful gas is suddenly leaked. Specifically, many blowers with a ventilation capacity of about 5 to 200 m 3 / min are installed, and for example, a large amount of leakage occurs such that a commercial gas cylinder shown in the above table becomes empty in 5 to 10 minutes. In such a case, the content of harmful gas such as in the air is assumed to be about 50 to 1000 ppm.

浄化筒内の浄化剤の充填長はガスの流量および有害ガス
の濃度などによって異なり、一概に特定はできないが実
用上通常は50〜500mm程度とされ、浄化筒の内径は筒内
を流れるガスの空筒線速度(LV)が0.3〜1.5m/sec程度
となる大きさとされる。一般的にはこれらは充填層の圧
力損失、空気との接触効率および有害ガスの量などによ
って定められる。
The filling length of the purifying agent in the purification column depends on the flow rate of the gas and the concentration of harmful gas, etc. and cannot be specified unconditionally, but in practice it is usually about 50 to 500 mm, and the inner diameter of the purification column is the inner diameter of the gas flowing in the column. The empty cylinder linear velocity (LV) is about 0.3 to 1.5 m / sec. Generally, these are determined by the pressure loss of the packed bed, the contact efficiency with air and the amount of harmful gas.

〔発明の効果〕〔The invention's effect〕

本発明のガスの浄化方法によれば、ガス中に含有される
有害ガスとしてアルシン、ホスフィン、ジボラン、シラ
ンおよびセレン化水素、特に大量で比較的高濃度の有害
ガスを効率良く、しかも極めて迅速に除去することがで
きるので、例えば、ガスボンベから有害ガスが急激に漏
洩するなどの緊急時の除害処理に対して優れた効果が得
られる。
According to the gas purification method of the present invention, a harmful gas contained in the gas is arsine, phosphine, diborane, silane and hydrogen selenide, particularly a large amount of a relatively high-concentration harmful gas, efficiently and extremely quickly. Since it can be removed, an excellent effect can be obtained for the detoxification process in an emergency, for example, when a harmful gas is suddenly leaked from the gas cylinder.

以下、本発明を実施例によってさらに具体的に示す。Hereinafter, the present invention will be described more specifically by way of examples.

〔実施例〕〔Example〕

実施例1〜5 (Mn−Cu−Co系組成物の調製) 活性二酸化マンガン100g、水酸化銅(II)を酸化銅(I
I)換算で40gおよび水酸化コバルト(III)を酸化コバ
ルト(Co2O3)換算で40gをそれぞれ計量し、これらを粉
末状態で混合したものにアルミナゾル(Al2O3)15gおよ
び少量の水を加えて混練して得られた組成物を押出成形
し、300℃で3時間焼成して、1.5φ×5〜20mmのMn−Cu
−Co系組成物の成型体を調製した。
Examples 1 to 5 (Preparation of Mn-Cu-Co-based composition) 100 g of active manganese dioxide and copper (II) hydroxide were mixed with copper oxide (I
40 g in terms of I) and 40 g in terms of cobalt (III) hydroxide in terms of cobalt oxide (Co 2 O 3 ) were weighed and mixed in powder form, and 15 g of alumina sol (Al 2 O 3 ) and a small amount of water were added. Was added and kneaded to obtain a composition, which was extruded and baked at 300 ° C. for 3 hours to obtain 1.5 φ × 5 to 20 mm Mn-Cu.
A molding of the Co-based composition was prepared.

(酸化銀(II)の調製) 102gの硝酸銀を200mlの水に溶解した。別に90gの苛性ソ
ーダと150gの過硫酸カリウムを85℃に温めたイオン交換
水200mlにかきまぜながら溶解した。後者をそのまま加
熱しながらかきまぜを続けているところへ上記の硝酸銀
水溶液を滴下して沈殿物を析出させた。このものをデカ
ンテーションと水洗を繰り返して洗浄した後、100℃で
3時間真空乾燥して74gの酸化銀(II)の粉末を得た。
(Preparation of silver (II) oxide) 102 g of silver nitrate was dissolved in 200 ml of water. Separately, 90 g of caustic soda and 150 g of potassium persulfate were dissolved in 200 ml of ion-exchanged water heated to 85 ° C while stirring. The above silver nitrate aqueous solution was added dropwise to a place where stirring was continued while heating the latter as it was to deposit a precipitate. This was washed by repeating decantation and washing with water, and then vacuum dried at 100 ° C. for 3 hours to obtain 74 g of silver (II) oxide powder.

(浄化剤の調製) 酸化銀(II)7.2gを水100mlにけん濁させたけん濁液を
激しくかきまぜながら、バット中にあるMn−Cu−Co系組
成物に散布して酸化銀(II)の粉末を添着させ、次いで
80℃×2時間の条件で乾燥させ、酸化銀(II)が3.85wt
%添着した浄化剤(粒の密度1.08g/ml)を得た。その後
室内に放置して10wt%程度の含水率まで大気中の湿分を
吸収させた。
(Preparation of Purifying Agent) Silver (II) oxide (7.2 g) was suspended in water (100 ml) with vigorous stirring, and the mixture was sprayed on the Mn-Cu-Co-based composition in the vat to remove silver (II) oxide. Impregnate the powder, then
Drying at 80 ℃ x 2 hours, silver (II) oxide 3.85wt
% Purifying agent (particle density 1.08 g / ml) was obtained. Then, it was left indoors to absorb moisture in the atmosphere to a water content of about 10 wt%.

(活性テスト) 内径19mmφの石英製の浄化筒に充填長が100mm(充填量2
8.3ml、25.0g)になるように浄化剤を充填し、これにア
ルシンまたはホスフィンを200〜2000ppm含有させた相対
湿度60%、温度25℃の空気を、11.4〜20.4/min(空筒
線速度LV67〜120cm/sec)の流量で通流させた。浄化剤
の出口ガスの一部をサンプリングし、冷原子吸光法によ
り、出口ガス中のアルシンまたはホスフィンの濃度が25
ppbまで上昇する時間(有効処理時間)を測定した。
(Activity test) Filling length is 100mm (filling amount 2
8.3ml, 25.0g) filled with a purifying agent and containing 200 to 2000ppm of arsine or phosphine in air at 60% relative humidity and 25 ° C for 11.4 to 20.4 / min (vacuum linear velocity LV67-120 cm / sec). A portion of the outlet gas of the purifying agent was sampled, and the concentration of arsine or phosphine in the outlet gas was measured by cold atomic absorption spectrometry.
The time to rise to ppb (effective treatment time) was measured.

結果を第1表に示す。The results are shown in Table 1.

実施例 6〜8 アルシン、ホスフィンの代わりに、ジボラン、シラン、
セレン化水素を含有する空気について実施例1〜5と同
様にして、有効処理時間を測定した。
Examples 6 to 8 Instead of arsine and phosphine, diborane, silane,
Effective treatment time was measured in the same manner as in Examples 1 to 5 for air containing hydrogen selenide.

但し浄化筒の出口ガス濃度は、ジボランおよびセレン化
水素については検知管を用いて測定し、これらのガスが
検知されるに至るまでの時間(有効処理時間)を求め
た。検知管はジボランについてはドレーゲル社製のもの
で、検知下限は0.05ppmであり、セレン化水素について
は光明理化学製で検知下限は1ppmである。
However, the gas concentration at the outlet of the purifying column was measured for diborane and hydrogen selenide using a detector tube, and the time until effective detection of these gases (effective treatment time) was determined. The detection tube was manufactured by Dräger for diborane, and the lower limit of detection was 0.05 ppm. For hydrogen selenide, the lower limit of detection was 1 ppm.

また、シランについては塩基性炭酸銅をアルミナに担持
させた変色試薬を用いたが、このものの検知下限は10pp
mである。
For silane, a color-changing reagent in which basic copper carbonate was supported on alumina was used, but the lower limit of detection for this was 10 pp.
m.

結果を第2表に示す。The results are shown in Table 2.

実施例 9、10 空気の代わりにアルシンまたはホスフィンを1000ppmを
含有する窒素および水素を用いた他は実施例1と同様に
して有効処理時間を測定した。
Examples 9 and 10 The effective treatment time was measured in the same manner as in Example 1 except that nitrogen and hydrogen containing 1000 ppm of arsine or phosphine were used instead of air.

結果を第3表に示す。The results are shown in Table 3.

実施例 11、12 実施例1で用いたと同じMn−Cu−Co系組成物に酸化銀
(II)が0.5および2.0wt%になるように添着量を変化さ
せたものについて有効処理時間をそれぞれ測定した。
Examples 11 and 12 Effective treatment time was measured for each of the same Mn-Cu-Co-based compositions used in Example 1 except that the amount of silver (II) oxide was changed to 0.5 and 2.0 wt%. did.

結果を第4表に示す。The results are shown in Table 4.

比較例 1、2 実施例1で使用したと同じMn−Cu−Co系組成物の成型体
を酸化銀(II)を添着させずに乾燥後、室内に放置して
含水率を約10%とし、これを浄化剤として用い、実施例
1と同様にしてアルシンおよびホスフィンについて有効
処理時間を測定した。
Comparative Examples 1 and 2 A molded body of the same Mn-Cu-Co-based composition used in Example 1 was dried without silver (II) oxide being attached, and then left indoors to have a water content of about 10%. Using this as a purifying agent, the effective treatment time was measured for arsine and phosphine in the same manner as in Example 1.

結果を第5表に示す。The results are shown in Table 5.

比較例 3〜5 Mn−Cu−Co系組成物の代わりに担体に粒度が6〜10メッ
シュの活性炭、α−アルミナ、モレキュラーシーブ5Aを
用い、これに酸化銀(II)を4.25wt%添着したものにつ
いて実施例1と同様にして有効処理時間を測定した。
Comparative Example 3-5 In place of the Mn-Cu-Co composition, activated carbon having a particle size of 6-10 mesh, α-alumina, and molecular sieve 5A were used as a carrier, and 4.25 wt% of silver (II) oxide was impregnated on the carrier. The effective treatment time was measured for each of the products in the same manner as in Example 1.

結果を第6表に示す。The results are shown in Table 6.

実施例13〜15 水酸化コバルト(III)の混合量を酸化コバルト(Co
2O3)換算でそれぞれ20g、30g、50gと変化させた他は実
施例1と同様にして3種類のMn−Cu−Co系組成物の成型
体を調整した。
Examples 13 to 15 The amount of cobalt (III) hydroxide mixed was changed to cobalt oxide (Co
Molded bodies of three types of Mn-Cu-Co based compositions were prepared in the same manner as in Example 1 except that the amounts were changed to 20 g, 30 g, and 50 g in terms of 2 O 3 ).

この成型体のそれぞれに酸化銀(II)のけん濁液を散布
してそれぞれ酸化銀(II)が3.85wt%添着した浄化剤を
得た。このものを室内に放置して10%程度の含水率まで
大気中の水分を吸収させた後、実施例1と同様に浄化筒
に充填し、アルシンを含有する空気を流して有効処理時
間を測定した。
A suspension of silver (II) oxide was sprayed on each of the molded bodies to obtain a purifying agent in which 3.85 wt% of silver (II) oxide was impregnated. After leaving this in a room to absorb moisture in the atmosphere to a water content of about 10%, the same is filled in a purifying cylinder as in Example 1 and air containing arsine is flowed to measure the effective treatment time. did.

結果を第7表に示す。The results are shown in Table 7.

参考例 1〜2 Mn−Cu−Co組成物の代わりに二酸化マンガン100g、酸化
銅40gおよび酸化アルミニウム15gを混合した組成物であ
って、酸化コバルトを含有しない組成物の成型体を用
い、実施例1におけると同様にして酸化銀(II)が3.85
wt%添着した浄化剤を調製した。この浄化剤に空気中の
湿分を含水率が10%程度になるまで吸湿させた後、実施
例1および5におけると同様にしてアルシンおよびホス
フィンを含有するガスについて有効処理時間を測定し
た。
Reference Example 1-2 A composition obtained by mixing 100 g of manganese dioxide, 40 g of copper oxide and 15 g of aluminum oxide in place of the Mn-Cu-Co composition, and using a molded body of a composition containing no cobalt oxide. Silver oxide (II) is 3.85 as in 1.
A cleaning agent impregnated with wt% was prepared. The purifying agent was allowed to absorb moisture in the air until the water content became about 10%, and then the effective treatment time was measured for the gas containing arsine and phosphine in the same manner as in Examples 1 and 5.

結果を第8表に示す。The results are shown in Table 8.

実施例16〜20 (酸化銀(I)の調製) 102gの硝酸銀を200mlの水に溶解した。別に90gの苛性ソ
ーダを85℃に温めたイオン交換水200mlにかきまぜなが
ら溶解した。後者をそのまま加熱しながらかきまぜを続
けているところへ上記の硝酸銀水溶液を滴下して沈殿物
を析出させた。このものをデカンテーションと水洗を繰
り返して洗浄した後、100℃で3時間真空乾燥して69gの
酸化銀(I)の粉末を得た。
Examples 16 to 20 (Preparation of silver (I) oxide) 102 g of silver nitrate was dissolved in 200 ml of water. Separately, 90 g of caustic soda was dissolved in 200 ml of ion-exchanged water warmed to 85 ° C while stirring. The above silver nitrate aqueous solution was added dropwise to a place where stirring was continued while heating the latter as it was to deposit a precipitate. This product was washed by repeating decantation and washing with water, and then vacuum dried at 100 ° C. for 3 hours to obtain 69 g of silver (I) oxide powder.

(Mn−Cu−Co系組成物) 実施例1で用いたと同じものを使用した。(Mn-Cu-Co composition) The same composition as used in Example 1 was used.

(浄化剤の調製) 酸化銀(I)7.2gを水100mlにけん濁させたけん濁液を
激しくかきまぜながら、バット中にあるMn−Cu−Co系組
成物に散布して酸化銀(I)の粉末を添着させ、次いで
80℃×2時間の条件で乾燥させ、酸化銀(I)を3.85wt
%添着した浄化剤を得た。その後室内に放置して10wt%
程度の含水率まで大気中の湿分を吸収させた。
(Preparation of Purifying Agent) Silver (I) oxide (7.2 g) was suspended in water (100 ml) with vigorous stirring, and the mixture was sprayed on the Mn-Cu-Co-based composition in the vat to remove silver (I) oxide. Impregnate the powder, then
Dry under the condition of 80 ℃ x 2 hours, and add silver oxide (I) 3.85wt
% Purifying agent was obtained. Then leave it indoors and 10wt%
Moisture in the atmosphere was absorbed up to a water content of a certain degree.

(活性テスト) 実施例1と同様にしておこなった。(Activity test) It carried out like Example 1.

結果を第9表に示す。The results are shown in Table 9.

実施例 21〜23 実施例16〜20と同種の浄化剤を用い、アルシン、ホスフ
ィンの代わりにジボラン、シラン、セレン化水素を含有
する空気につい実施例1〜5と同様にして有効処理時間
を測定した。
Examples 21 to 23 Using the same type of purifying agent as in Examples 16 to 20, effective treatment time was measured in the same manner as in Examples 1 to 5 for air containing diborane, silane, hydrogen selenide instead of arsine and phosphine. did.

結果を第10表に示す。The results are shown in Table 10.

実施例 24〜28 (Mn−Cu−Co系組成物) 実施例1で用いたと同じものを用いた。 Examples 24 to 28 (Mn-Cu-Co-based composition) The same composition as that used in Example 1 was used.

(浄化剤の調製) 炭酸銀(I)7.2gを水100mlにけん濁させたけん濁液を
激しくかきまぜながら、バット中にあるMn−Cu−Co系組
成物に散布して炭酸銀(I)の粉末を添着させ、次いで
80℃×2時間の条件で乾燥させ、炭酸銀(I)が3.85wt
%添着した浄化剤312gを得た。その後室内に放置して10
wt%程度の含水率まで大気中の湿分を吸収させた。
(Preparation of Purifying Agent) Silver (I) carbonate (7.2 g) was suspended in water (100 ml) with vigorous stirring, and the mixture was sprayed on the Mn-Cu-Co-based composition in the vat to prepare silver (I) carbonate. Impregnate the powder, then
Silver (I) carbonate 3.85wt% after drying at 80 ℃ x 2 hours
% Of the impregnated purifying agent was obtained. Then leave it indoors 10
Absorbed moisture in the atmosphere to a water content of about wt%.

(活性テスト) 実施例1と同様にして有効処理時間を測定した。(Activity test) The effective treatment time was measured in the same manner as in Example 1.

結果を第11表に示す。The results are shown in Table 11.

実施例 29〜31 実施例24〜28と同種の浄化剤を用い、アルシン、ホスフ
ィンの代わりに、ジボラン、シラン、セレン化水素を含
有する空気について実施例1〜5と同様にして、有効処
理時間を測定した。
Examples 29 to 31 Using the same type of purifying agent as in Examples 24 to 28, and using diborane, silane, hydrogen selenide instead of arsine and phosphine in the same manner as in Examples 1 to 5, effective treatment time Was measured.

結果を第12表に示す。The results are shown in Table 12.

実施例 32 銀化合物として炭酸銀(I)又は酸化銀(II)をそれぞ
れ単独で使用する代わりに両者を1:1で混合して水にけ
ん濁させたものを実施例1で用いたと同じMn−Cu−Co系
組成物に散布し、3.85wt%の銀化合物を添着した浄化剤
を用いた他は実施例1と同様にして有効処理時間を測定
した。
Example 32 The same Mn as used in Example 1 was prepared by mixing silver carbonate (I) and silver oxide (II) as a silver compound alone and mixing them in a ratio of 1: 1 and suspending them in water. Effective treatment time was measured in the same manner as in Example 1 except that a purifying agent was sprayed on the -Cu-Co composition and a 3.85 wt% silver compound was used.

結果を第13表に示す。The results are shown in Table 13.

実施例 33、34 (浄化剤の調製) 実施例1で用いたと同じMn−Cu−Co系組成物200gに、水
100mlに硝酸銀20gを溶解した硝酸銀水溶液を霧吹で48g
だけ吹きかけた。この硝酸銀を添着させたMn−Cu−Co系
組成物を80℃で10時間乾燥させて、3.85wt%の硝酸銀が
添着した浄化剤208gを得た。
Examples 33, 34 (Preparation of Purifying Agent) To 200 g of the same Mn-Cu-Co composition as used in Example 1, water was added.
48 g of a silver nitrate aqueous solution prepared by dissolving 20 g of silver nitrate in 100 ml by spraying
Just sprayed. This Mn-Cu-Co-based composition impregnated with silver nitrate was dried at 80 ° C for 10 hours to obtain 208 g of a cleaning agent impregnated with 3.85 wt% silver nitrate.

このものを空気中に放置して約8wt%の含水品としてか
ら実施例1、5と同様にして有効処理時間を測定した。
This was left to stand in the air to give a product containing about 8 wt% of water, and the effective treatment time was measured in the same manner as in Examples 1 and 5.

結果を第14表に示す。The results are shown in Table 14.

比較例 6〜8 Mn−Cu−Co系組成物の代わりに担体に粒度が6〜10メッ
シュの活性炭、α−アルミナ、モレキュラーシーブ5Aを
用い、これに炭酸銀(I)を4.25wt%になるように添着
したものについて実施例1と同様にして有効処理時間を
測定した。
Comparative Example 6-8 Activated carbon having a particle size of 6-10 mesh, α-alumina, and molecular sieve 5A were used as a carrier instead of the Mn-Cu-Co composition, and silver carbonate (I) was added at 4.25 wt%. The effective treatment time was measured in the same manner as in Example 1 for the thus adhered product.

結果を第15表に示す。The results are shown in Table 15.

実施例 35,36 実施例1で用いたと同じMn−Cu−Co系組成物に炭酸銀
(I)が0.5および2.0wt%になるように添着量を変化さ
せたものについて有効処理時間をそれぞれ測定した。
Examples 35 and 36 Effective treatment times were measured for the same Mn-Cu-Co-based composition as used in Example 1 with different amounts of impregnated silver (I) carbonate to 0.5 and 2.0 wt%, respectively. did.

結果を第16表に示す。The results are shown in Table 16.

実施例 37〜42 実施例24で用いた炭酸銀(I)の代わりに硫酸銀、塩化
銀、臭化銀、ヨウ化銀、燐酸銀、ヨウ素酸銀を3.85wt%
になるように添着させ、乾燥後8%程度の含水率まで大
気中の湿分を吸収させてから実施例1と同様にして有効
処理時間を測定した。
Examples 37 to 42 Instead of the silver (I) carbonate used in Example 24, silver sulfate, silver chloride, silver bromide, silver iodide, silver phosphate, and silver iodate were added at 3.85 wt%.
Then, the effective treatment time was measured in the same manner as in Example 1 after the moisture content in the atmosphere was absorbed to a water content of about 8% after drying.

結果を第17表に示す。The results are shown in Table 17.

実施例 43,44 実施例33、34における硝酸銀の代わりに過塩素酸銀、酢
酸銀を3.85wt%になるように添着させ、乾燥させた後
に、再び大気中の水分を8wt%吸収させたものについて
実施例1と同様にして有効処理時間を測定した。
Examples 43 and 44 Instead of silver nitrate in Examples 33 and 34, silver perchlorate and silver acetate were impregnated so as to be 3.85 wt% and dried, and then 8 wt% of moisture in the atmosphere was again absorbed. The effective treatment time was measured in the same manner as in Example 1.

結果を第18表に示す。The results are shown in Table 18.

実施例45 活性二酸化マンガン80g、水酸化銅(II)を酸化銅(I
I)換算で40g、水酸化コバルト(III)を酸化コバルト
(Co2O3)換算で20g、アルミナゾル(Al2O3)20gおよび
酸化銀(I)10gを同時に混合し、これに少量の加えて
混練し、次いで成型板の中で乾燥させた後、200℃で3
時間焼成して4mmφ×4mmのペレット状で酸化銀(I)を
5.88wt%含有する浄化剤を調整した。この浄化剤をさら
に破砕して4〜20meshとしたものを用い、実施例1と同
様にして有効処理時間の測定を行った。
Example 45 80 g of active manganese dioxide and copper (II) hydroxide were mixed with copper oxide (I
I) 40 g, cobalt (III) hydroxide 20 g in terms of cobalt oxide (Co 2 O 3 ), alumina sol (Al 2 O 3 ) 20 g and silver oxide (I) 10 g are mixed at the same time, and a small amount of this is added. After kneading and drying in a forming plate,
Sintered for 4 hours to obtain silver (I) oxide in the form of 4mmφ x 4mm pellets.
A cleaning agent containing 5.88 wt% was prepared. This purifying agent was further crushed to obtain 4 to 20 mesh, and the effective treatment time was measured in the same manner as in Example 1.

結果を第19表に示す。The results are shown in Table 19.

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

第1図は有害ガスの浄化剤が浄化筒に充填され、ガスの
流路に介在させられた例を示すフローシートである。 図面の各番号は以下のごとくである。 1……浄化剤、2……ガスボンベ 3……ボンベボックス、4……ブロアー および 5……換気ダクト
FIG. 1 is a flow sheet showing an example in which a purifying agent for harmful gas is filled in a purifying cylinder and is interposed in a gas passage. The numbers in the drawings are as follows. 1 ... Purifying agent, 2 ... Gas cylinder 3, ... Cylinder box, 4 ... Blower and 5 ... Ventilation duct

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01J 23/89 A B01D 53/34 ZAB (72)発明者 平本 忠 神奈川県平塚市田村5181番地 日本パイオ ニクス株式会社平塚工場内 審査官 野田 直人Continuation of front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical indication location B01J 23/89 A B01D 53/34 ZAB (72) Inventor Tadashi Hiramoto 5181 Tamura, Hiratsuka-shi, Kanagawa Japan Pionics Naoto Noda, Examiner, Hiratsuka Factory, Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】有害ガスとしてアルシン、ホスフィン、シ
ラン、ジボランおよびセレン化水素の一種以上を含有す
るガスと、浄化剤とを接触させて当該ガスから有害ガス
を除去するガスの浄化方法において、浄化剤として
(1)二酸化マンガン、酸化銅および酸化コバルトを主
成分とする組成物に(2)銀化合物を含有せしめてなる
成型体を用いることを特徴とするガスの浄化方法。
1. A method for purifying a gas, wherein a gas containing one or more of arsine, phosphine, silane, diborane and hydrogen selenide as a harmful gas is brought into contact with a purifying agent to remove the harmful gas from the gas. A method for purifying a gas, which comprises using a molded body comprising (1) a composition containing manganese dioxide, copper oxide and cobalt oxide as a main component and (2) a silver compound as an agent.
JP63144643A 1987-08-31 1988-06-14 Gas purification method Expired - Lifetime JPH07100130B2 (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP63144643A JPH07100130B2 (en) 1988-06-14 1988-06-14 Gas purification method
EP88307918A EP0309099B1 (en) 1987-08-31 1988-08-26 Method for cleaning gas containing toxic component
DE8888307918T DE3869301D1 (en) 1987-08-31 1988-08-26 METHOD FOR PURIFYING GAS CONTAINING TOXIC COMPONENTS.
KR1019880010970A KR960004610B1 (en) 1987-08-31 1988-08-29 Toxic Ingredients-Containing Gases
US07/238,068 US4910001A (en) 1987-08-31 1988-08-30 Method for cleaning gas containing toxic component

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63144643A JPH07100130B2 (en) 1988-06-14 1988-06-14 Gas purification method

Publications (2)

Publication Number Publication Date
JPH01315318A JPH01315318A (en) 1989-12-20
JPH07100130B2 true JPH07100130B2 (en) 1995-11-01

Family

ID=15366838

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63144643A Expired - Lifetime JPH07100130B2 (en) 1987-08-31 1988-06-14 Gas purification method

Country Status (1)

Country Link
JP (1) JPH07100130B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US12161971B2 (en) * 2019-10-31 2024-12-10 Toyota Motor Engineering And Manufacturing North America, Inc. Catalyst for direct NOx decomposition and a method for making and using the catalyst

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4929508B2 (en) * 2007-05-16 2012-05-09 クラレケミカル株式会社 Silver impregnated activated carbon, method for producing the same, and water purifier

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US12161971B2 (en) * 2019-10-31 2024-12-10 Toyota Motor Engineering And Manufacturing North America, Inc. Catalyst for direct NOx decomposition and a method for making and using the catalyst

Also Published As

Publication number Publication date
JPH01315318A (en) 1989-12-20

Similar Documents

Publication Publication Date Title
US4910001A (en) Method for cleaning gas containing toxic component
EP0194366B1 (en) Method of cleaning exhaust gases
JPH07308538A (en) Hazardous gas purifier
KR100320372B1 (en) Hazardous Gas Purification Method
JP3716030B2 (en) How to clean harmful gases
JP3073321B2 (en) How to purify harmful gases
JPH05161841A (en) Air purifying agent and method for producing the same
JP3340510B2 (en) Hazardous gas purification method
JPH07100130B2 (en) Gas purification method
KR100488091B1 (en) Hazardous Gas Purifiers and Methods
JPH07100128B2 (en) Gas purification method
JPH09234336A (en) Hazardous gas purification method
JP2633511B2 (en) Exhaust gas purification method
JPS62286520A (en) Method for purifying exhaust gas
JPH02144125A (en) Method for purifying exhaust gas
JPH08281063A (en) Hazardous gas purification method
JPS62286521A (en) Method for purifying exhaust gas
JP3131480B2 (en) Air purifier and method for producing the same
JPH10249144A (en) How to purify harmful gases
JPH067637A (en) Hazardous gas purification method
JPS62286525A (en) Method for purifying exhaust gas
JPS62286522A (en) Method for purifying exhaust gas
JPS62286524A (en) Method for purifying exhaust gas
JPH06154535A (en) Method for purifying harmful gas
JPS62286523A (en) Method for purifying exhaust gas

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20081101

Year of fee payment: 13

EXPY Cancellation because of completion of term
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20081101

Year of fee payment: 13