JPH08155259A - Harmful gas removal method and agent - Google Patents
Harmful gas removal method and agentInfo
- Publication number
- JPH08155259A JPH08155259A JP6303711A JP30371194A JPH08155259A JP H08155259 A JPH08155259 A JP H08155259A JP 6303711 A JP6303711 A JP 6303711A JP 30371194 A JP30371194 A JP 30371194A JP H08155259 A JPH08155259 A JP H08155259A
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- agent
- harmful
- metal
- hydroxide
- copper hydroxide
- Prior art date
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Abstract
(57)【要約】
【目的】 有害成分に対する除害能力が高いという水酸
化銅の特性を活かしつつ、除害反応の速度を促進し、破
過前の有害成分の排出濃度を低下させることができる有
害ガスの除害方法及び除害剤を提供する。
【構成】 水酸化銅に、塩基性化合物及び/又は酸化剤
を添加した除害剤に、有害成分を含む排ガスを接触させ
る。(57) [Summary] [Purpose] While utilizing the property of copper hydroxide, which has a high ability to remove harmful components, it is possible to accelerate the rate of the abatement reaction and reduce the emission concentration of harmful components before breakthrough. To provide a harmful gas removing method and a harmful agent. [Structure] Exhaust gas containing a harmful component is brought into contact with a detoxifying agent obtained by adding a basic compound and / or an oxidizing agent to copper hydroxide.
Description
【0001】[0001]
【産業上の利用分野】本発明は、有害成分を含む排ガス
の除害方法及び除害剤に関し、詳しくは、半導体製造工
程等から排出される揮発性無機水素化物,揮発性無機ハ
ロゲン化物,有機金属化合物等の有害成分を含む排ガス
を除害する方法及び除害剤に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an abatement agent for removing exhaust gas containing harmful components. More specifically, the invention relates to a volatile inorganic hydride, a volatile inorganic halide, an organic compound discharged from a semiconductor manufacturing process or the like. The present invention relates to a method and an abatement agent for removing exhaust gas containing harmful components such as metal compounds.
【0002】[0002]
【従来の技術】半導体製造工程等では、シラン,アルシ
ン,ホスフィン等の揮発性無機水素化物や、クロロシラ
ン,フッ化ホウ素等の揮発性無機ハロゲン化物、そして
最近では、アルキル化合物やアルコキシド等の有機金属
化合物等が原料ガスとして使われている。これらのガス
は、そのほとんどが有害であるため、半導体製造工程等
から排出されるこれら有害成分を含む排ガスは、大気に
放出する前に無害化する必要がある。2. Description of the Related Art In semiconductor manufacturing processes, volatile inorganic hydrides such as silane, arsine and phosphine, volatile inorganic halides such as chlorosilane and boron fluoride, and recently, organic metals such as alkyl compounds and alkoxides. Compounds are used as source gas. Since most of these gases are harmful, the exhaust gas containing these harmful components discharged from the semiconductor manufacturing process or the like needs to be rendered harmless before being discharged to the atmosphere.
【0003】主として揮発性無機水素化物等を含む排ガ
スに対しては、従来から、酸化銅等の金属酸化物を主体
とした除害剤に排ガスを接触させて除害処理することが
行われている。With respect to exhaust gas containing mainly volatile inorganic hydrides, it has been conventionally practiced to bring the exhaust gas into contact with a harm-removing agent mainly composed of a metal oxide such as copper oxide to remove the harm. There is.
【0004】[0004]
【発明が解決しようとする課題】しかし、前記酸化銅等
の金属酸化物を主成分とした除害剤では、シラン系の有
害成分に対する除害能力が小さいため、他の有害成分よ
りも破過時間が短い。そのため、細粒化処理を行うとと
もに、アルミナ等の担体に担持させて比表面積を大きく
する必要があり、除害剤自体の製造も面倒であった。However, the harm-removing agent containing a metal oxide such as copper oxide as a main component has a smaller harm-removing ability with respect to silane-based harmful components, and therefore has a higher breakthrough than other harmful components. Time is short. Therefore, it is necessary to carry out a fine-graining treatment and to make the specific surface area larger by supporting it on a carrier such as alumina, and the production of the harmful agent itself has been troublesome.
【0005】さらに、最近の半導体製造技術では、CV
D法(化学気相成長法)による化合物半導体製造等に有
機金属化合物を使用することが増えてきているが、これ
らも有害であるため、除害する必要がある。このため、
シラン等に対する除害能力が大きく、有機金属化合物等
も除害できる除害剤の出現が望まれていた。Further, in recent semiconductor manufacturing technology, CV
Organometallic compounds are increasingly used in the production of compound semiconductors by the D method (chemical vapor deposition method), but these are also harmful and need to be removed. For this reason,
It has been desired to develop a detoxifying agent that has a large ability to remove silanes and the like and that can also remove organometallic compounds and the like.
【0006】このような状況に鑑み、本発明者らは、シ
ラン系の有害成分にも充分な除害能力を有する除害剤の
開発を目的として研究を重ねた結果、水酸化銅が、シラ
ン系の有害成分に対して従来の酸化銅に比べて約4倍の
除害能力があり、さらに、シラン以外の揮発性無機水素
化物にも、さらに有機金属化合物に対しても、優れた除
害能力を有していることを見出した。In view of such a situation, the inventors of the present invention have conducted extensive research for the purpose of developing a harm-removing agent having a sufficient harm-removing ability for silane-based harmful components. It has about 4 times the ability to remove harmful components from the system as compared to conventional copper oxide, and it is also excellent at removing volatile inorganic hydrides other than silane and organometallic compounds. It has been found to have the ability.
【0007】しかし、さらに詳細に検討した結果、シラ
ン等の有害成分を含む排ガスの除害処理に水酸化銅を単
独で用いると、除害剤が破過する前に、処理後の排ガス
中の有害成分の濃度が高くなることがしばしば起きた。
これは、水酸化銅の除害反応の速度が小さいためと考え
られる。However, as a result of further detailed examination, when copper hydroxide is used alone for the detoxification treatment of the exhaust gas containing harmful components such as silane, before the detoxifying agent breaks through, the exhaust gas after the treatment is treated. Higher concentrations of harmful components often occurred.
It is considered that this is because the rate of the copper hydroxide removal reaction is low.
【0008】そこで、水酸化銅の有害成分に対する除害
能力が高いという特性を活かしつつ、除害反応の速度を
促進し、破過前の有害成分の排出濃度を低下させること
ができる有害ガスの除害方法及び除害剤の開発を目的と
して鋭意研究を重ねた。Therefore, while taking advantage of the property that copper hydroxide has a high ability to remove harmful components, it is possible to accelerate the rate of the detoxifying reaction and reduce the emission concentration of harmful components before breakthrough. Intensive research was conducted for the purpose of developing detoxification methods and detoxifying agents.
【0009】[0009]
【課題を解決するための手段】その結果、水酸化銅に、
特定の添加物を添加することにより、上記課題を解決で
きることを知見した。本発明は、この知見に基づいて成
されたものであって、本発明の有害ガスの除害方法は、
有害成分を含む排ガスを、水酸化銅を主成分とし、塩基
性化合物及び/又は酸化剤を添加した除害剤に接触させ
ることを特徴としている。[Means for Solving the Problems] As a result, copper hydroxide
It was found that the above problems can be solved by adding a specific additive. The present invention was made based on this finding, and the harmful gas removing method of the present invention is
It is characterized in that the exhaust gas containing a harmful component is brought into contact with a detoxifying agent containing copper hydroxide as a main component and a basic compound and / or an oxidizing agent added.
【0010】また、本発明の有害ガスの除害剤は、有害
成分を含む排ガスの除害処理を行う除害剤であって、水
酸化銅を主成分とし、塩基性化合物及び/又は酸化剤を
添加したことを特徴とするもので、特に、前記塩基性化
合物が、金属水酸化物(水酸化銅を除く),金属炭酸
塩,金属アルミン酸塩又はアミン系化合物であること、
前記酸化剤が、金属硫酸塩,金属塩化物,金属酸化物,
金属酢酸塩,過マンガン酸塩,クロム酸塩,硝酸塩,過
酸化物,酸素酸塩又はペルオキソ酸塩であることを特徴
としている。Further, the harmful gas harm-removing agent of the present invention is a harm-removing agent for effecting the harm-removing treatment of exhaust gas containing harmful components, which contains copper hydroxide as a main component and a basic compound and / or an oxidizing agent. In particular, the basic compound is a metal hydroxide (excluding copper hydroxide), a metal carbonate, a metal aluminate or an amine compound,
The oxidizing agent is a metal sulfate, a metal chloride, a metal oxide,
It is characterized in that it is a metal acetate, permanganate, chromate, nitrate, peroxide, oxygenate or peroxoate.
【0011】本発明の除害対象となる主な有害成分は、
前述の半導体製造工程等で原料ガスとして使われている
揮発性無機水素化物,揮発性無機ハロゲン化物,有機金
属化合物等である。前記揮発性無機水素化物としては、
ジボラン,シラン,ジシラン,ゲルマン,アンモニア,
ホスフィン,アルシン,硫化水素,セレン化水素等を挙
げることができ、また、揮発性無機ハロゲン化物として
は、三フッ化ホウ素,三塩化ホウ素,四フッ化ケイ素,
ジクロルシラン,トリクロルシラン,四塩化ケイ素,ト
リクロルアルシン,六フッ化タングステン,フッ素,塩
素,フッ化水素,塩化水素,臭化水素等、ハロゲンガス
も含む各種ガスを挙げることができる。The main harmful components to be harmed by the present invention are:
Examples thereof include volatile inorganic hydrides, volatile inorganic halides, and organic metal compounds that are used as raw material gases in the semiconductor manufacturing process described above. As the volatile inorganic hydride,
Diborane, silane, disilane, germane, ammonia,
Examples thereof include phosphine, arsine, hydrogen sulfide, hydrogen selenide, and the like, and volatile inorganic halides include boron trifluoride, boron trichloride, silicon tetrafluoride,
Various gases including halogen gas such as dichlorosilane, trichlorosilane, silicon tetrachloride, trichloroarsine, tungsten hexafluoride, fluorine, chlorine, hydrogen fluoride, hydrogen chloride, hydrogen bromide and the like can be mentioned.
【0012】さらに、有機金属化合物としては、アルキ
ル基を含むものとして、ジメチル亜鉛,ジエチル亜鉛,
トリメチルアルミニウム,トリエチルアルミニウム,ト
リメチルガリウム,トリエチルガリウム,トリメチルイ
ンジウム,トリエチルインジウム,テトラメチル錫,テ
トラエチル錫,ターシャリーブチルホスフィン,トリメ
チルアルシン,トリエチルアルシン,ターシャリーブチ
ルアルシン等を、アルコキシド基を含むものとして、ジ
メトキシ亜鉛,トリブトキシガリウム,トリメトキシボ
ロン,トリエトキシボロン,テトラメトキシシラン,テ
トラエトキシシラン,テトラメトキシゲルマン,テトラ
エトキシゲルマン,テトラターシャリーブトキシ錫,ト
リメトキシホスフィン,トリエトキシホスフィン,トリ
メトキシアルシン,トリエトキシアルシン,テトラエト
キシセレン,テトラメトキシチタン,テトラエトキシチ
タン,テトライソプロポキシチタン,テトライソプロポ
キシジルコニウム,テトラターシャリーブトキシジルコ
ニウム,ペンタメトキシタンタル,ペンタエトキシタン
タル等をそれぞれ挙げることができる。Further, as the organometallic compound, those containing an alkyl group include dimethyl zinc, diethyl zinc,
Trimethylaluminum, triethylaluminum, trimethylgallium, triethylgallium, trimethylindium, triethylindium, tetramethyltin, tetraethyltin, tert-butylphosphine, trimethylarsine, triethylarsine, tert-butylarsine, etc., containing alkoxide groups, Dimethoxyzinc, tributoxygallium, trimethoxyboron, triethoxyboron, tetramethoxysilane, tetraethoxysilane, tetramethoxygermane, tetraethoxygermane, tetratert-butoxytin, trimethoxyphosphine, triethoxyphosphine, trimethoxyarsine, tri Ethoxyarsine, tetraethoxyselenium, tetramethoxytitanium, tetraethoxytitanium, tetraiso Ropokishichitan, tetraisopropoxy zirconium, tetra-tertiary-butoxy zirconium, pentamethoxy tantalum, pentaethoxytantalum etc. can be mentioned, respectively.
【0013】また、主成分となる水酸化銅は、主に水酸
化第二銅(Cu(OH)2 )を意味するが、水酸化第一
銅を含んでいてもよい。また、水酸化銅としては、結晶
性のものと非晶質のものの両方が使用できるが、結晶性
のものの方が非晶質のものより温度に対する安定性が高
いので、有害成分の濃度が高く、反応熱が高い場合に、
より安定的に使用できる。なお、本発明における反応は
発熱反応であるが、発熱量は従来の除去剤である前記酸
化銅とほぼ同等である。さらに、水酸化銅は、上記除去
対象ガスと接触して反応すると、青色から黒色に鮮明に
変色するので、除去筒に充填して使用する場合、上流側
から破過前線が進行して行くので、検知剤を使用する必
要がないばかりでなく、必要に応じて、該除去対象ガス
の検知剤としても使うことができる。The copper hydroxide as the main component mainly means cupric hydroxide (Cu (OH) 2 ), but it may contain cuprous hydroxide. As the copper hydroxide, both crystalline and amorphous ones can be used, but since the crystalline one is more stable against temperature than the amorphous one, the concentration of harmful components is high. , When the reaction heat is high,
It can be used more stably. Although the reaction in the present invention is an exothermic reaction, the calorific value is almost the same as that of the above-mentioned copper oxide which is a conventional removing agent. Furthermore, when copper hydroxide reacts in contact with the gas to be removed and changes its color from blue to black clearly, when it is used by filling the removal cylinder, the breakthrough front progresses from the upstream side. Not only is it unnecessary to use a detection agent, but it can also be used as a detection agent for the gas to be removed, if necessary.
【0014】一方、水酸化銅は、単独でも上記有害ガス
の除去剤として用いることができるが、従来の酸化銅と
本発明の水酸化銅とにおける同一条件でのシランに対す
る除害能力を比較すると、図1に示すように、処理後の
ガス中のシラン濃度が急激に上昇する破過現象を起こす
までの時間は、酸化銅に対して水酸化銅は長く、除害能
力が約4倍になることが判った。しかし、水酸化銅は、
破過する前の、処理後のガス中のシラン濃度が高いレベ
ルとなることがあるという欠点のあることも判った。On the other hand, although copper hydroxide can be used alone as a scavenger of the above-mentioned harmful gas, comparing the conventional copper oxide and the copper hydroxide of the present invention with respect to the ability to remove silane under the same conditions. As shown in FIG. 1, the time until the breakthrough phenomenon in which the silane concentration in the gas after the treatment rises sharply occurs is longer for copper hydroxide than copper oxide, and the detoxifying ability is about four times as high. It turned out to be. However, copper hydroxide
It has also been found that there is a drawback that the silane concentration in the gas after the treatment before the breakthrough may reach a high level.
【0015】その原因については、水酸化銅の方が酸化
銅よりも除害反応に寄与する成分の割合が高いためであ
ろうと考えられる。例えば、酸化銅の場合、微小な粉末
にして担体に担持させて比表面積を大きくしても、個々
の直径は、最小でも数ミクロン程度であり、反応は表面
の数オングストローム程度(直径に対して大きくても1
000分の1程度の厚み)で行われ、物質の表面だけが
反応に寄与し、内部の酸化銅は未反応のまま残るのに対
し、水酸化銅の場合は、反応が物質の内部まで進むため
であろうと推察される。実際に、水酸化銅の場合は、比
表面積が小さくても大量のシランを除害処理することが
できる。しかし他方では、反応が水酸化銅の内部に進行
すると、見掛けの反応速度が小さくなるために処理後の
有害成分のレベルが高くなるものと考えられる。It is considered that the cause is that copper hydroxide has a higher proportion of components contributing to the detoxification reaction than copper oxide. For example, in the case of copper oxide, even if it is made into a fine powder and supported on a carrier to increase the specific surface area, the individual diameter is at least about several microns, and the reaction is about several angstroms on the surface (relative to the diameter). At most 1
(Thickness of about 1/000), only the surface of the substance contributes to the reaction, and the copper oxide inside remains unreacted, whereas in the case of copper hydroxide, the reaction proceeds to the inside of the substance. It is presumed that it is because of this. In fact, in the case of copper hydroxide, a large amount of silane can be removed even if the specific surface area is small. On the other hand, however, it is considered that when the reaction proceeds inside the copper hydroxide, the apparent reaction rate decreases, and the level of harmful components after the treatment increases.
【0016】そこで本発明者らは、水酸化銅の除害挙動
を調べ、その反応速度増進を目的とした実験を種々試み
た。その結果、水酸化銅に水酸化ナトリウムやアルミン
酸ナトリウム等の塩基性化合物を添加すると、有害成分
の除害能力がやや向上するのみならず、剤が破過する前
の、処理後の有害成分の濃度が著しく低下する現象を知
見した。さらに研究を進めた結果、水酸化ナトリウムや
アルミン酸ナトリウムに限らず、塩基性化合物に共通の
効果のあることが判った。また、塩基性化合物に代え
て、酸化力のある物質を添加しても、同様の効果のある
ことも判った。さらにまた、塩基性化合物と酸化性の物
質とを適宜混合添加しても効果が損なわれることがない
ことも判明した。Therefore, the present inventors investigated the detoxification behavior of copper hydroxide and conducted various experiments aimed at enhancing the reaction rate thereof. As a result, when basic compounds such as sodium hydroxide and sodium aluminate are added to copper hydroxide, not only the detoxifying ability of harmful components is slightly improved, but also harmful components after treatment before the agent breaks through. It was found that the concentration of sucrose decreased remarkably. As a result of further research, it was found that not only sodium hydroxide and sodium aluminate but also basic compounds have common effects. It was also found that the same effect can be obtained by adding a substance having an oxidizing power instead of the basic compound. Furthermore, it has also been found that the effects are not impaired even if a basic compound and an oxidizing substance are appropriately mixed and added.
【0017】すなわち、水酸化銅に、塩基性化合物や酸
化剤を添加すると、何らかの理由によって水酸化銅の内
部での除害反応の速度が増進され、処理後の有害成分ガ
ス濃度のレベルが低下し、実用的な除害剤となることが
明らかとなった。That is, when a basic compound or an oxidizing agent is added to copper hydroxide, the rate of the detoxification reaction inside the copper hydroxide is enhanced for some reason, and the level of the harmful component gas concentration after the treatment is lowered. However, it became clear that it could be a practical harmful agent.
【0018】水酸化銅に添加する塩基性化合物あるいは
酸化剤は、それぞれ単独に添加してもよいし、それらの
複数種を混合添加してもよく、これらの添加量は、水酸
化銅100重量部に対して、0.001〜50.0重量
部、好ましくは、0.01〜20.0重量部が効果的で
ある。添加量が0.001重量部未満では殆ど効果がな
く、0.01重量部未満では充分な効果を発現しない。
また、添加量が20重量部を超えても添加効果は小さ
く、50重量部を超えると除害能力がむしろ低下する。The basic compound or oxidizing agent added to the copper hydroxide may be added individually or as a mixture of plural kinds thereof, and the addition amount thereof is 100 weight% of the copper hydroxide. 0.001 to 50.0 parts by weight, and preferably 0.01 to 20.0 parts by weight, are effective. If the addition amount is less than 0.001 part by weight, there is almost no effect, and if the addition amount is less than 0.01 part by weight, no sufficient effect is exhibited.
Also, if the addition amount exceeds 20 parts by weight, the effect of addition is small, and if it exceeds 50 parts by weight, the detoxifying ability is rather lowered.
【0019】ここで、本発明で添加剤として用いる塩基
性化合物としては、金属水酸化物,金属炭酸塩,金属ア
ルミン酸塩や、種々のアミン化合物を、また、酸化剤と
しては、金属硫酸塩,金属塩化物,金属酸化物,金属酢
酸塩,過マンガン酸塩,クロム酸塩,硝酸塩,過酸化
物,酸素酸塩,種々のペルオキソ酸塩等を挙げることが
でき、これらの1種又は複数種を添加することができ
る。Here, the basic compound used as an additive in the present invention is a metal hydroxide, a metal carbonate, a metal aluminate or various amine compounds, and the oxidizing agent is a metal sulfate. , Metal chlorides, metal oxides, metal acetates, permanganates, chromates, nitrates, peroxides, oxyacid salts, various peroxo acid salts, etc., and one or more of these may be mentioned. Seeds can be added.
【0020】具体的に、金属水酸化物としては、水酸化
リチウム(LiOH),水酸化ナトリウム(NaO
H),水酸化カリウム(KOH),水酸化マグネシウム
(Mg(OH)2 ),水酸化カルシウム(Ca(OH)
2 ),水酸化ストロンチウム(Sr(OH)2 ),水酸
化バリウム(Ba(OH)2 ),水酸化ニッケル(Ni
(OH)2 )等を挙げることができ、金属炭酸塩として
は、炭酸ナトリウム(Na2 CO3 ),炭酸カリウム
(K2 CO3 ),炭酸水素ナトリウム(NaHC
O3),炭酸水素カリウム(KHCO3 )等を挙げるこ
とができる。また、金属アルミン酸塩としては、アルミ
ン酸リチウム(Li(AlO2 )),アルミン酸ナトリ
ウム(Na(AlO2 )),アルミン酸カリウム(K
(AlO2 )),アルミン酸マグネシウム(Mg(Al
O2 )2 ),アルミン酸カルシウム(Ca(AlO2 )
2 ),アルミン酸ストロンチウム(Sr(Al
O2 )2 ),アルミン酸バリウム(Ba(Al
O2 )2 )等が挙げられ、さらに、アミン化合物として
は、1級アミン(RNH2 ),2級アミン(R2 N
H),3級アミン(R3 N),4級アミン(R4 NX)
を挙げることができる。なお、アミン化合物において、
Rはアルキル基であり、Xは陰イオン、例えば塩素イオ
ン等のハロゲンイオンを表す。Specifically, the metal hydroxides include lithium hydroxide (LiOH) and sodium hydroxide (NaO).
H), potassium hydroxide (KOH), magnesium hydroxide (Mg (OH) 2 ), calcium hydroxide (Ca (OH)
2 ), strontium hydroxide (Sr (OH) 2 ), barium hydroxide (Ba (OH) 2 ), nickel hydroxide (Ni
(OH) 2 ) and the like. Examples of the metal carbonate include sodium carbonate (Na 2 CO 3 ), potassium carbonate (K 2 CO 3 ), and sodium hydrogen carbonate (NaHC
O 3 ), potassium hydrogen carbonate (KHCO 3 ) and the like can be mentioned. The metal aluminate includes lithium aluminate (Li (AlO 2 )), sodium aluminate (Na (AlO 2 )), potassium aluminate (K
(AlO 2 )), magnesium aluminate (Mg (Al
O 2 ) 2 ), calcium aluminate (Ca (AlO 2 )
2 ), strontium aluminate (Sr (Al
O 2 ) 2 ), barium aluminate (Ba (Al
O 2 ) 2 ) and the like. Further, as the amine compound, primary amine (RNH 2 ) and secondary amine (R 2 N
H), tertiary amine (R 3 N), quaternary amine (R 4 NX)
Can be mentioned. In the amine compound,
R is an alkyl group, and X represents an anion, for example, a halogen ion such as a chlorine ion.
【0021】また、酸化剤としては、硫酸銅(CuSO
4 )の他、種々の金属硫酸塩、塩化鉄(FeCl3 )の
他、種々の金属塩化物、二酸化マンガン(MnO2 ),
酸化銅(CuO),五酸化二ヒ素(As2 O5 ),二酸
化セレン(SeO2 ),酸化ルテニウム(RuO2 ),
酸化銀(Ag2 O),酸化セリウム(CeO2 ),酸化
オスミウム(OsO4 ),酸化水銀(HgO),二酸化
鉛(PbO2 ),酸化ビスマス(Bi2 O3 )等の金属
酸化物、酢酸銅(Cu(CH3 COO)2 ),酢酸水銀
(Hg(CH3 COO)2 ),酢酸鉛(Pb(CH3 C
OO)4 ),酢酸ビスマス(Bi(CH3 COO)3 )
等の金属酢酸塩、過マンガン酸(HMnO4 ),過マン
ガン酸ナトリウム(NaMnO4 ),過マンガン酸カリ
ウム(KMnO4 )等の過マンガン酸塩、無水クロム酸
(CrO3 ),二塩化二酸化クロム(CrO2 C
l2 ),クロム酸ナトリウム(Na2 CrO4 ),重ク
ロム酸ナトリウム(Na2 Cr2 O7 ),塩化クロム酸
ナトリウム(Na2 CrO3 Cl)等のクロム酸塩、硝
酸アンモニウム(NH4 NO3 ),硝酸カリウム(KN
O3 ),硝酸銅(Cu(NO3 )2 )等の硝酸塩、過酸
化水素(H2 O2 ),過酸化ナトリウム(Na
2 O2 ),過酸化バリウム(BaO2 ),無水安息香酸
((C6 H5 CO)2 O)等の過酸化物、次亜塩素酸ナ
トリウム(NaClO),次亜臭素酸ナトリウム(Na
BrO),次亜ヨウ素酸ナトリウム(NaIO),塩素
酸ナトリウム(NaClO3 ),過ヨウ素酸(HI
O4 ),過ヨウ素酸カリウム(KIO4 ),過塩素酸ナ
トリウム(NaClO4 ),ヨウ素酸水素ナトリウム
(Na3 H2 IO6 )等の酸素酸塩、ペルオキソ二硫酸
ナトリウム(Na2 S2 O8 ),ペルオキソ二硫酸カリ
ウム(K2 S2 O8 ),ペルオキソ一硫酸ナトリウム
(Na2 SO5 ),ペルオキソ蟻酸(HCOOOH),
ペルオキソ酢酸(CH3COOOH),ペルオキソ安息
香酸(C6 H5 COOOH),ペルオキソフタル酸(C
6 H4 (COOH)COOOH),ペルオキソトリフル
オロ酢酸(CF3 COOOH)等のペルオキソ酸塩、さ
らには、ニトロベンゼン(C6 H5NO2 )やヨードソ
ベンゼン(C6 H5 IO)等を挙げることができる。As the oxidizer, copper sulfate (CuSO
4 ), various metal sulfates, iron chloride (FeCl 3 ), various metal chlorides, manganese dioxide (MnO 2 ),
Copper oxide (CuO), diarsenic pentoxide (As 2 O 5 ), selenium dioxide (SeO 2 ), ruthenium oxide (RuO 2 ),
Metal oxides such as silver oxide (Ag 2 O), cerium oxide (CeO 2 ), osmium oxide (OsO 4 ), mercury oxide (HgO), lead dioxide (PbO 2 ), bismuth oxide (Bi 2 O 3 ), acetic acid Copper (Cu (CH 3 COO) 2 ), mercury acetate (Hg (CH 3 COO) 2 ), lead acetate (Pb (CH 3 C 2
OO) 4 ), bismuth acetate (Bi (CH 3 COO) 3 )
Metal acetate such as permanganate (HMnO 4 ), sodium permanganate (NaMnO 4 ), permanganate such as potassium permanganate (KMnO 4 ), chromic anhydride (CrO 3 ), chromium dichloride chromium (CrO 2 C
l 2 ), sodium chromate (Na 2 CrO 4 ), sodium dichromate (Na 2 Cr 2 O 7 ), sodium chromate chromate (Na 2 CrO 3 Cl) and other chromates, ammonium nitrate (NH 4 NO 3 ), Potassium nitrate (KN
O 3 ), nitrates such as copper nitrate (Cu (NO 3 ) 2 ), hydrogen peroxide (H 2 O 2 ), sodium peroxide (Na
2 O 2 ), barium peroxide (BaO 2 ), benzoic anhydride ((C 6 H 5 CO) 2 O) and other peroxides, sodium hypochlorite (NaClO), sodium hypobromite (Na
BrO), sodium hypoiodite (NaIO), sodium chlorate (NaClO 3 ), periodate (HI)
O 4 ), potassium periodate (KIO 4 ), sodium perchlorate (NaClO 4 ), oxyacid salts such as sodium hydrogen iodate (Na 3 H 2 IO 6 ), sodium peroxodisulfate (Na 2 S 2 O) 8 ), potassium peroxodisulfate (K 2 S 2 O 8 ), sodium peroxomonosulfate (Na 2 SO 5 ), peroxoformic acid (HCOOOH),
Peroxo acid (CH3COOOH), peroxo acid (C 6 H 5 COOOH), peroxo phthalate (C
6 H 4 (COOH) COOOH) , peroxy acid salts such as peroxo trifluoroacetic acid (CF 3 COOOH), further include such nitrobenzene (C 6 H 5 NO 2) and iodosobenzene (C 6 H 5 IO) be able to.
【0022】上記のような添加剤を水酸化銅に添加する
ことにより、前記有害成分を効率よく除害処理すること
ができる。本発明方法においては、上記添加剤を含む除
害剤を適宜なカラムに充填し、該カラムに排ガスを流通
させて排ガスを除害剤に接触させるだけでよく、容易に
行うことができる。By adding the above-mentioned additives to copper hydroxide, the harmful components can be removed efficiently. In the method of the present invention, it is sufficient to fill the detoxifying agent containing the above-mentioned additive in an appropriate column, to flow the exhaust gas through the column, and to bring the exhaust gas into contact with the detoxifying agent, which can be easily carried out.
【0023】[0023]
【実施例】以下、本発明の実施例及び比較例を説明す
る。 実施例1及び比較例1 除害剤として下記除害剤A〜Dを作成した。 A(比較例):市販の粉末状酸化銅を打錠して直径3m
m,長さ3mmのペレットに成型したもの。また、周知
の手法により、酸化銅をアルミナ担体に担持させたも
の。 B(比較例):市販の粉末状水酸化銅をAと同様のペレ
ットに成型したもの。 C(実施例):Bと同じ水酸化銅100重量部に、市販
の水酸化ナトリウムを0.1重量部添加し、乳鉢で十分
に混合粉砕した後、打錠してAと同様のペレットに成型
したもの。 D(実施例):Cにおいて、水酸化ナトリウムをアルミ
ン酸ナトリウムに代え、同様にペレットに成型したも
の。EXAMPLES Examples and comparative examples of the present invention will be described below. Example 1 and Comparative Example 1 The following harmful agents A to D were prepared as harmful agents. A (comparative example): a commercially available powdered copper oxide is tableted to have a diameter of 3 m.
Molded into pellets of m and 3 mm in length. In addition, copper oxide is supported on an alumina carrier by a known method. B (Comparative Example): Commercially available powdered copper hydroxide molded into pellets similar to A. C (Example): To 100 parts by weight of the same copper hydroxide as in B, 0.1 part by weight of commercially available sodium hydroxide was added, thoroughly mixed and ground in a mortar, and then tableted to give pellets similar to A. Molded one. D (Example): In C, sodium hydroxide was replaced with sodium aluminate, and pellets were similarly molded.
【0024】上記各剤を、内径40mmの充填筒にそれ
ぞれ250gずつ充填し(充填高さ約200mm)、こ
こに、シランを1%含む水素ガスを、空筒速度1cm/
secで流した。充填筒出口のシラン濃度をモニター
(日本酸素製ADー10)で測定し、5ppmを破過点
(許容濃度)として終了までの時間から各剤のシランの
動的吸収量を計測するとともに、破過前の濃度を測定し
た。Each of the above agents was filled in a filling cylinder having an inner diameter of 40 mm in an amount of 250 g (filling height of about 200 mm), and hydrogen gas containing 1% of silane was filled therein with an empty space velocity of 1 cm / cm.
It was shed in sec. The silane concentration at the outlet of the filling cylinder was measured with a monitor (AD-10 made by Nippon Oxygen), and the dynamic absorption amount of silane of each agent was measured from the time until the end with 5 ppm as a breakthrough point (allowable concentration), and The previous concentration was measured.
【0025】その結果を下記に示す。 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] A 3 ND(注1) (25〜30(注2)) B 125 2.5 C 150 ND D 148 ND 注1)NDは、検出限界(1.0ppm)以下 注2)酸化銅をアルミナ担体に担持した場合The results are shown below. Agent Dynamic absorption [l / Kg] Concentration before breakthrough [ppm] A 3 ND (Note 1) (25 to 30 (Note 2)) B 125 2.5 C 150 ND D 148 ND Note 1) ND is , Detection limit (1.0ppm) or less Note 2) When copper oxide is supported on an alumina carrier
【0026】この結果から、酸化銅(A剤)の動的吸収
量は、単独では剤1Kgあたり3リットルであり、アル
ミナ担体に担持しても剤1Kgあたり25〜30リット
ル程度である。これに対し、水酸化銅(B剤)では、単
独で剤1Kgあたり125リットルとなり、酸化銅をア
ルミナ担体に担持した場合よりも4倍以上の動的吸収量
を示す。ただし、破過前の濃度については、B剤が破過
濃度(5ppm)には達してはいないが、2.5ppm
とやや高い濃度を示していた。次に、水酸化銅に水酸化
ナトリウムを添加したC剤及び水酸化銅にアルミン酸ナ
トリウムを添加したD剤では、B剤に比べて動的吸収量
がやや大きくなり、破過前の濃度がNDに低下している
ことが判る。From these results, the dynamic absorption amount of copper oxide (agent A) is 3 liters per 1 kg of the agent alone, and is about 25 to 30 liters per 1 kg of the agent when loaded on the alumina carrier. On the other hand, with copper hydroxide (agent B), the amount of 125 liters per 1 kg of the agent alone is four times or more that of the case where copper oxide is supported on the alumina carrier. However, regarding the concentration before breakthrough, agent B has not reached the breakthrough concentration (5 ppm), but 2.5 ppm
It showed a slightly higher concentration. Next, with the agent C in which sodium hydroxide was added to copper hydroxide and the agent D in which sodium aluminate was added to copper hydroxide, the amount of dynamic absorption was slightly larger than that of agent B, and the concentration before breakthrough was It can be seen that it has fallen to ND.
【0027】実施例2 塩基性化合物である各種金属水酸化物を水酸化銅に添加
して下記除害剤E〜Hを作成した。なお、以下の各添加
剤の重量部は、水酸化銅100重量部に対するものであ
る。 E:実施例1のBと同じ水酸化銅に、市販の水酸化カリ
ウムを0.1重量部添加し、乳鉢で十分に混合粉砕した
後、同様に打錠して直径3mm,長さ3mmのペレット
に成型したもの。 F:添加剤として市販の水酸化マグネシウムを10重量
部添加し、Eと同様にしてペレットに成型したもの。 G:添加剤として市販の水酸化カルシウムを1重量部添
加し、Eと同様にしてペレットに成型したもの。 H:添加剤として、市販の水酸化ニッケルを5重量部添
加し、Eと同様にしてペレットに成型したもの。Example 2 Various metal hydroxides, which are basic compounds, were added to copper hydroxide to prepare the following harmful agents E to H. The parts by weight of the following additives are based on 100 parts by weight of copper hydroxide. E: 0.1 part by weight of commercially available potassium hydroxide was added to the same copper hydroxide as in Example 1B, and the mixture was sufficiently mixed and pulverized in a mortar and then similarly tableted to give a diameter of 3 mm and a length of 3 mm. Molded into pellets. F: 10 parts by weight of commercially available magnesium hydroxide was added as an additive and molded into pellets in the same manner as in E. G: 1 part by weight of commercially available calcium hydroxide was added as an additive and molded into pellets in the same manner as in E. H: 5 parts by weight of commercially available nickel hydroxide was added as an additive and molded into pellets in the same manner as in E.
【0028】上記のE〜H剤を用いて実施例1と同様の
除害試験を行った結果を下記に示す。 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] E 150 ND F 149 ND G 149 ND H 147 ND この結果から、各水酸化物は、動的吸収量及び破過前の
濃度ともに、水酸化ナトリウムと同程度の添加効果であ
ることが判る。The results of the same abatement test as in Example 1 using the above E to H agents are shown below. Agent Dynamic absorption amount [l / Kg] Concentration before breakthrough [ppm] E 150 ND F 149 ND G 149 ND H 147 ND From these results, each hydroxide shows dynamic absorption amount and concentration before breakthrough. It can be seen that both have the same effect of addition as sodium hydroxide.
【0029】実施例3 塩基性化合物である各種金属炭酸塩を添加して下記除害
剤I,Jをそれぞれ作成した。 I:市販の水酸化銅に、市販の炭酸ナトリウムを1重量
部添加し、乳鉢で十分に混合粉砕した後、前記同様に打
錠して直径3mm,長さ3mmのペレットに成型したも
の。 J:市販の水酸化銅に、市販の炭酸カリウムを0.1%
重量部添加し、Iと同様にしてペレットに成型したも
の。Example 3 The following harmful agents I and J were prepared by adding various metal carbonates which are basic compounds. I: 1 part by weight of commercially available sodium carbonate was added to commercially available copper hydroxide, thoroughly mixed and ground in a mortar, and then tableted in the same manner as above to form pellets having a diameter of 3 mm and a length of 3 mm. J: Commercially available copper hydroxide, commercially available potassium carbonate 0.1%
Added in parts by weight and molded into pellets in the same manner as in I.
【0030】上記除害剤I,Jを用いて実施例1と同様
の除害試験を行った結果を下記に示す。 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] I 148 ND J 148 ND この結果から、塩基性化合物として金属炭酸塩を使用し
ても、動的吸収量及び破過前の濃度ともに、金属水酸化
物と同程度の添加効果であることが判る。The following shows the results of the same abatement test as in Example 1 using the aforesaid abatement agents I and J. Agent Dynamic absorption [l / Kg] Concentration before breakthrough [ppm] I 148 ND J 148 ND From these results, even if a metal carbonate was used as the basic compound, It can be seen that both the concentration and the addition effect are similar to those of the metal hydroxide.
【0031】実施例4 水酸化銅に添加する塩基性化合物として各種アルミン酸
塩を使用し、下記除害剤K〜Mを作成し、実験例1と同
様にして除害効果を調べた。 K:実施例3の除害剤Iにおいて、炭酸ナトリウムに代
えて市販のアルミン酸カリウム1重量部を添加剤として
添加した以外は、Iと同様にしてペレットに成型したも
の。 L:アルミン酸カリウムに代えて市販のアルミン酸カル
シウムを添加剤として使用した以外は、Kと同様にして
ペレットに成型したもの。 M:アルミン酸カリウムに代えて市販のアルミン酸バリ
ウムを添加剤として使用した以外は、Kと同様にしてペ
レットに成型したもの。Example 4 Using various aluminates as basic compounds to be added to copper hydroxide, the following harmful agents KM were prepared, and the harmful effect was examined in the same manner as in Experimental Example 1. K: Molded into pellets in the same manner as in I except that 1 part by weight of commercially available potassium aluminate was added as an additive instead of sodium carbonate in the harmful agent I of Example 3. L: molded into pellets in the same manner as K except that commercially available calcium aluminate was used as an additive instead of potassium aluminate. M: Molded into pellets in the same manner as K except that commercially available barium aluminate was used as an additive instead of potassium aluminate.
【0032】 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] K 147 ND L 146 ND M 147 ND この結果から、塩基性化合物としてアルミン酸塩を使用
しても、動的吸収量及び破過前の濃度ともに、金属水酸
化物と同程度の添加効果であることが判る。Agent Dynamic absorption amount [l / Kg] Concentration before breakthrough [ppm] K 147 ND L 146 ND M 147 ND From these results, the dynamic absorption was obtained even when an aluminate was used as the basic compound. It can be seen that both the amount and the concentration before breakthrough have the same effect of addition as the metal hydroxide.
【0033】実施例5 実施例4の塩基性化合物に代えて、トリフェニルアミン
(N(C6 H5 )3 )を1重量部添加し、同様にして除
害剤Nのペレットを作成し、動的吸収量及び破過前の濃
度を調べた。Example 5 In place of the basic compound of Example 4, 1 part by weight of triphenylamine (N (C 6 H 5 ) 3 ) was added, and pellets of the harmful agent N were prepared in the same manner. The amount of dynamic absorption and the concentration before breakthrough were examined.
【0034】 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] N 148 ND この結果から、アミン化合物についても、その添加効果
が判る。Agent Dynamic Absorption [l / Kg] Concentration before breakthrough [ppm] N 148 ND From these results, the addition effect of amine compounds can be seen.
【0035】実施例6 水酸化銅に、各種酸化剤を添加して下記の除害剤O〜S
を作成し、実施例1と同様にしてその有害成分に対する
除害能力を調べた。 O:市販の水酸化銅に、市販の過マンガン酸ナトリウム
を0.1重量部添加し、実施例1と同様のペレットに成
型したもの。 P:過マンガン酸ナトリウムに代えて過塩素酸カリウム
を0.5重量部添加し、Oと同様にしてペレットに成型
したもの。 Q:過マンガン酸ナトリウムに代えて硫酸銅を1重量部
添加し、Oと同様にしてペレットに成型したもの。 R:過マンガン酸ナトリウムに代えて塩化鉄を0.2重
量部添加し、Oと同様にしてペレットに成型したもの。 S:過マンガン酸ナトリウムに代えて二酸化マンガンを
5重量部添加し、Oと同様にしてペレットに成型したも
の。Example 6 Various oxidizing agents were added to copper hydroxide to remove the following harmful agents OS.
Was prepared, and the ability to remove harmful components was examined in the same manner as in Example 1. O: 0.1 parts by weight of commercially available sodium permanganate was added to commercially available copper hydroxide, and molded into pellets similar to those in Example 1. P: A product obtained by adding 0.5 parts by weight of potassium perchlorate in place of sodium permanganate and molding into pellets in the same manner as O. Q: A product obtained by adding 1 part by weight of copper sulfate in place of sodium permanganate and molding into pellets in the same manner as O. R: 0.2 parts by weight of iron chloride was added in place of sodium permanganate, and pelletized in the same manner as O. S: Manganese dioxide was added in an amount of 5 parts by weight in place of sodium permanganate, and pelletized in the same manner as O.
【0036】 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] O 150 ND P 150 ND Q 148 ND R 145 ND S 150 NDこれ
らの結果から、添加剤として各種酸化剤を添加した場合
も、同様の添加効果を示すことが判る。Agent Dynamic Absorption [l / Kg] Concentration before breakthrough [ppm] O 150 ND P 150 ND Q 148 ND R 145 ND S 150 ND From these results, various oxidizing agents were added as additives. Also in the case, it is understood that the same addition effect is exhibited.
【0037】実施例7 水酸化銅に、各種塩基性化合物及び各種酸化剤を混合添
加して、下記除害剤T〜Vを作成し、その除害能力を調
べた。 T:市販の水酸化銅に、水酸化マグネシウム15重量部
と過マンガン酸ナトリウム0.1重量部とを添加し、乳
鉢で十分混合粉砕した後、打錠して前記同様の直径3m
m,長さ3mmのペレットに成型したもの。 U:炭酸ナトリウム1重量部と過マンガン酸ナトリウム
0.2重量部とを添加し、Tと同様のペレットに成型し
たもの。 V:アルミン酸カルシウム0.5重量部と過マンガン酸
ナトリウム0.3重量部とを添加し、Tと同様のペレッ
トに成型したもの。Example 7 Various basic compounds and various oxidizing agents were mixed and added to copper hydroxide to prepare the following harmful agents T to V, and their harmful ability was examined. T: To a commercially available copper hydroxide, 15 parts by weight of magnesium hydroxide and 0.1 part by weight of sodium permanganate were added, thoroughly mixed and ground in a mortar, and then tableted to have a diameter of 3 m as described above.
Molded into pellets of m and 3 mm in length. U: 1 part by weight of sodium carbonate and 0.2 part by weight of sodium permanganate were added and molded into pellets similar to T. V: 0.5 parts by weight of calcium aluminate and 0.3 parts by weight of sodium permanganate were added and molded into pellets similar to T.
【0038】 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] T 155 ND U 154 ND V 155 ND このように、塩基性化合物と酸化剤とを混合して添加し
た場合でも、良好な添加効果が得られた。Agent Dynamic Absorption [l / Kg] Concentration before breakthrough [ppm] T 155 ND U 154 ND V 155 ND Thus, even when the basic compound and the oxidant are mixed and added, A good addition effect was obtained.
【0039】実施例8及び比較例2 実施例7の除害剤V及び比較例1における除害剤A,B
を使用し、有害成分をシランに代えてアルシンとした以
外は同様に操作を行った。その結果を下記に示す。 剤 動的吸収量[l/Kg] 破過前の濃度[ppm] A 70 ND B 120 0.04 V 150 NDExample 8 and Comparative Example 2 Detoxifying agent V of Example 7 and detoxifying agents A and B of Comparative Example 1
Was used, and the same operation was performed except that the harmful component was changed to silane and arsine was used. The results are shown below. Agent Dynamic absorption [l / Kg] Concentration before breakthrough [ppm] A 70 ND B 120 0.04 V 150 ND
【0040】実施例9及び比較例3 実施例1及び比較例1の除害剤A〜D及び実施例7の除
害剤Tにおいて、有害成分を含むガスとして無機ハロゲ
ン化物であるトリクロルシラン1%を含む窒素ガス(ガ
スX),金属アルキル化合物であるトリメチルアルミニ
ウム1%を含む水素ガス(ガスY),金属アルコキシド
であるテトラエトキシシラン1%を含む水素ガス(ガス
Z)の除害処理を、前記各実施例と同様にして行い、動
的吸収量[l/Kg]を測定した。その結果を下記に示
す。Example 9 and Comparative Example 3 In the harmful agents A to D of Example 1 and Comparative Example 1 and the harmful agent T of Example 7, 1% of trichlorsilane, which is an inorganic halide as a gas containing harmful components. Detoxification treatment of nitrogen gas (gas X) containing 1%, hydrogen gas containing 1% of metal alkyl compound trimethylaluminum (gas Y), and hydrogen gas containing 1% of metal alkoxide tetraethoxysilane (gas Z), The dynamic absorption amount [1 / Kg] was measured in the same manner as in each of the above-mentioned examples. The results are shown below.
【0041】動的吸収量[l/Kg] 剤 ガスX ガスY ガスZ A 4 5 5 B 110 100 90 C 160 130 135 D 155 125 140 T 160 140 145Dynamic Absorption [l / Kg] Agent Gas X Gas Y Gas Z A 455 B 110 100 90 C 160 130 135 135 D 155 125 140 T 160 160 140 145
【0042】[0042]
【発明の効果】以上説明したように、本発明によれば、
水酸化銅が有する有害成分の除害能力が向上するのみな
らず、剤が破過する前の処理後の有害成分の濃度が著し
く低下し、効果的な除害処理を行うことができる。As described above, according to the present invention,
Not only is the ability of copper hydroxide to remove harmful components improved, but the concentration of harmful components after the treatment before the agent breaks through is significantly reduced, and effective removal treatment can be performed.
【図1】 水酸化銅と酸化銅の除害能力を示す説明図で
ある。FIG. 1 is an explanatory diagram showing the detoxifying ability of copper hydroxide and copper oxide.
───────────────────────────────────────────────────── 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 B01D 53/68 B01D 53/34 120 D 134 Z ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location B01D 53/68 B01D 53/34 120 D 134 Z
Claims (4)
成分とし、塩基性化合物及び/又は酸化剤を添加した除
害剤に接触させることを特徴とする有害ガスの除害方
法。1. A method of removing harmful gases, which comprises contacting exhaust gas containing harmful components with a harmful compound containing copper hydroxide as a main component and containing a basic compound and / or an oxidizing agent.
除害剤であって、水酸化銅を主成分とし、塩基性化合物
及び/又は酸化剤を添加したことを特徴とする有害ガス
の除害剤。2. A detoxifying agent for detoxifying exhaust gas containing a detrimental component, characterized by containing copper hydroxide as a main component and adding a basic compound and / or an oxidizing agent. Harmful agent.
酸化銅を除く),金属炭酸塩,金属アルミン酸塩又はア
ミン系化合物であることを特徴とする請求項2記載の有
害成分の除害剤。3. The harmful component according to claim 2, wherein the basic compound is a metal hydroxide (excluding copper hydroxide), a metal carbonate, a metal aluminate or an amine compound. Harmful agent.
物,金属酸化物,金属酢酸塩,過マンガン酸塩,クロム
酸塩,硝酸塩,過酸化物,酸素酸塩又はペルオキソ酸塩
であることを特徴とする請求項2記載の有害成分の除害
剤。4. The oxidizing agent is a metal sulfate, a metal chloride, a metal oxide, a metal acetate, a permanganate, a chromate, a nitrate, a peroxide, an oxygenate or a peroxoate. The harm-removing agent for harmful components according to claim 2.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP30371194A JP3557539B2 (en) | 1994-12-07 | 1994-12-07 | Hazardous gas abatement method and abatement agent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP30371194A JP3557539B2 (en) | 1994-12-07 | 1994-12-07 | Hazardous gas abatement method and abatement agent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH08155259A true JPH08155259A (en) | 1996-06-18 |
| JP3557539B2 JP3557539B2 (en) | 2004-08-25 |
Family
ID=17924336
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP30371194A Expired - Lifetime JP3557539B2 (en) | 1994-12-07 | 1994-12-07 | Hazardous gas abatement method and abatement agent |
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| Country | Link |
|---|---|
| JP (1) | JP3557539B2 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2010092671A1 (en) * | 2009-02-10 | 2010-08-19 | ズードケミー触媒株式会社 | Agent and method for detoxifying metal hydride-containing exhaust gas |
| US8568672B2 (en) | 2009-03-27 | 2013-10-29 | Sued-Chemie Catalysts Japan Inc. | Agent for detoxifying discharge gas containing volatile inorganic hydride and method of detoxifying discharge gas containing volatile inorganic hydride |
| JP2013235869A (en) * | 2012-05-02 | 2013-11-21 | Ube Ind Ltd | Device for collecting organic metal compound exhausted from compound semiconductor manufacturing device |
| JP2015164724A (en) * | 2015-04-03 | 2015-09-17 | クラリアント触媒株式会社 | Agent and method for detoxifying metal hydride-containing exhaust gas |
-
1994
- 1994-12-07 JP JP30371194A patent/JP3557539B2/en not_active Expired - Lifetime
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2010092671A1 (en) * | 2009-02-10 | 2010-08-19 | ズードケミー触媒株式会社 | Agent and method for detoxifying metal hydride-containing exhaust gas |
| JP5833313B2 (en) * | 2009-02-10 | 2015-12-16 | クラリアント触媒株式会社 | Detoxifying agent and method for exhaust gas containing metal hydride |
| US8568672B2 (en) | 2009-03-27 | 2013-10-29 | Sued-Chemie Catalysts Japan Inc. | Agent for detoxifying discharge gas containing volatile inorganic hydride and method of detoxifying discharge gas containing volatile inorganic hydride |
| JP2013235869A (en) * | 2012-05-02 | 2013-11-21 | Ube Ind Ltd | Device for collecting organic metal compound exhausted from compound semiconductor manufacturing device |
| JP2015164724A (en) * | 2015-04-03 | 2015-09-17 | クラリアント触媒株式会社 | Agent and method for detoxifying metal hydride-containing exhaust gas |
Also Published As
| Publication number | Publication date |
|---|---|
| JP3557539B2 (en) | 2004-08-25 |
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