JPS6034892B2 - Dry deodorization equipment - Google Patents

Dry deodorization equipment

Info

Publication number
JPS6034892B2
JPS6034892B2 JP55105794A JP10579480A JPS6034892B2 JP S6034892 B2 JPS6034892 B2 JP S6034892B2 JP 55105794 A JP55105794 A JP 55105794A JP 10579480 A JP10579480 A JP 10579480A JP S6034892 B2 JPS6034892 B2 JP S6034892B2
Authority
JP
Japan
Prior art keywords
impregnated
packed bed
bromide
hbr
activated carbon
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP55105794A
Other languages
Japanese (ja)
Other versions
JPS5730532A (en
Inventor
邦宏 土居
哲 竹山
健国 吾妻
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.)
Mitsubishi Electric Corp
Original Assignee
Mitsubishi Electric Corp
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 Mitsubishi Electric Corp filed Critical Mitsubishi Electric Corp
Priority to JP55105794A priority Critical patent/JPS6034892B2/en
Priority to US06/211,286 priority patent/US4370301A/en
Publication of JPS5730532A publication Critical patent/JPS5730532A/en
Publication of JPS6034892B2 publication Critical patent/JPS6034892B2/en
Expired legal-status Critical Current

Links

Description

【発明の詳細な説明】 この発明はオゾン、臭化水素または臭化水素酸の添着体
およびアルカリまたはアルカリ士類金属の臭化物の添着
体を用いた乾式脱臭装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a dry deodorizing apparatus using an impregnated body of ozone, hydrogen bromide or hydrobromic acid, and an impregnated body of an alkali or alkali metal bromide.

従来、この種の乾式脱臭装置としては第1図に示す様な
臭化水素添着炭と活性炭の充填層を備えた脱臭装置があ
った。
Conventionally, as a dry deodorizing apparatus of this type, there has been a deodorizing apparatus equipped with a packed bed of hydrogen bromide-impregnated carbon and activated carbon as shown in FIG.

図において、1はブロア、2はコンブレツサ、3はオゾ
ナイザ、4はブロア1で吸引された被処理空気にオゾナ
ィザ3より送給されるオゾン化空気を混合する混合槽、
5は反応塔、6は臭化水素または臭化水素酸を活性炭に
添着した添着炭(以下HBr添着炭という。)充填層、
7は活性炭充填層である。悪臭を帯びた彼処理空気Aは
、ブロア1‘こより吸引され、オゾナィザ3より送給さ
れたオゾン化空気と混合槽4において均一混合された後
、反応塔5に導入される。
In the figure, 1 is a blower, 2 is a compressor, 3 is an ozonizer, 4 is a mixing tank that mixes the ozonized air sent from the ozonizer 3 with the air to be treated sucked by the blower 1;
5 is a reaction tower, 6 is a packed bed of impregnated carbon (hereinafter referred to as HBr-impregnated carbon) in which activated carbon is impregnated with hydrogen bromide or hydrobromic acid;
7 is an activated carbon packed bed. The foul-smelling treated air A is sucked through the blower 1', uniformly mixed with ozonized air fed from the ozonizer 3 in the mixing tank 4, and then introduced into the reaction tower 5.

反応塔5では、まずHBr添着炭充填層6において、次
の反応式{1に従ってオゾンとHBrから臭素(Br2
)が生成される。2HBr十03→Br2十日20十0
2 ・・・【1}HBr添着炭充填層
6内では、この生成されたBr2によって悪臭成分(主
として硫化メチル、メチルメルカプタン等)の接触酸化
分解が行なわれ、ついで活性炭充填層7において、余剰
のオゾンの分解あるいは臭素や生成物である亜硫酸ガス
の吸着除去がなされた後、処理空気Bとして放出されて
いた。
In the reaction tower 5, first, in the HBr-impregnated carbon packed bed 6, bromine (Br2
) is generated. 2HBr 1003 → Br2 10th 2010
2...[1] In the HBr-impregnated carbon packed bed 6, the generated Br2 causes catalytic oxidative decomposition of malodorous components (mainly methyl sulfide, methyl mercaptan, etc.), and then in the activated carbon packed bed 7, excess After ozone was decomposed or bromine and the product sulfur dioxide gas were adsorbed and removed, it was released as treated air B.

この様な装置では、HBn添着炭が酸性であるため、硫
化水素等の酸性ガスは吸着されにくく、臭素との反応で
除去する必要があるので、オゾン添加量を増すか、処理
しされない硫化水素を吸着するために後段の活性炭層7
の活性炭充填量を増大させる必要があった。
In such equipment, since the HBn-impregnated carbon is acidic, acidic gases such as hydrogen sulfide are difficult to adsorb and must be removed by reaction with bromine. activated carbon layer 7 in the latter stage to adsorb
It was necessary to increase the amount of activated carbon loaded.

また、被処理ガスA中に含まれている硫化水素がHBr
添着炭層6で酸化されると最終的には硫酸になるため、
硫酸より弱い酸であるHBrはこの硫酸で置換されて彼
処理ガスAの流入側から流出側に順次移行し、遂には気
中に放散されるため、臭素添着量の減少速度が早く、寿
命が短かくなるという欠点があった。この発明は上記の
様な欠点を除去するためになされたもので、HBh添着
炭充填層の下流側にアルカリまたはアルカリ士類金属の
臭化物を活性炭等の担体に添着させた添着体(以下KB
r添着炭という)の充填層を設け、この充填層で、HB
r添着炭充填層から気中に放散されたHBrを補促する
とともに、この充填層においてもBr2の酸化作用によ
り悪臭成分の酸化分解を行なわせるようにしたものであ
る。
In addition, hydrogen sulfide contained in the gas to be treated A is HBr.
When it is oxidized in the impregnated carbon layer 6, it eventually becomes sulfuric acid, so
HBr, which is a weaker acid than sulfuric acid, is replaced by this sulfuric acid and sequentially moves from the inflow side to the outflow side of the processing gas A, and is finally dissipated into the air, so the amount of bromine impregnated decreases quickly and the service life is shortened. It had the disadvantage of being shorter. This invention was made in order to eliminate the above-mentioned drawbacks, and is provided with an impregnated body (hereinafter referred to as KB) in which an alkali or alkali metal bromide is impregnated on a carrier such as activated carbon on the downstream side of the HBh-impregnated carbon packed bed.
A packed bed of impregnated coal is provided, and in this packed bed, HB
The HBr diffused into the air from the r-impregnated carbon packed bed is supplemented, and malodorous components are also oxidized and decomposed in this packed bed by the oxidizing action of Br2.

第2図はこの発明の一実施例を示すフロー図で、8はK
Br添着炭の充填層(以下KBr添着炭充填層という)
である。
FIG. 2 is a flow diagram showing an embodiment of the present invention, and 8 is a flowchart showing an embodiment of the present invention.
Packed bed of Br-impregnated coal (hereinafter referred to as KBr-impregnated coal packed bed)
It is.

次に動作について説明する。ブロアーで吸引された悪臭
ガスを含有する被処理空気Aはオゾナィザ3より送給さ
れたオゾン化空気と混合槽4を通る間に均一混合された
後、反応塔5に導入される。反応塔5でHBr添着炭充
填層6において、従来と同様の酸化反応により大部分の
悪臭成分が除去される。硫化水素はオゾンや反応式{1
}で生成したBr2と反応式‘2},‘3}に示す酸化
反応によって分解され、その一部は反応式■,(即こよ
って最終的に硫酸に酸化される。日2S+03→日20
十S02 ・・・t2}日2S
+Br2→2HBr+S ・・
・{31S02十日20十03→日2S04十02
・・・‘4}S04十日20十1/202
→日2S04 ・・・‘5}生成した硫酸
の蓄積によってHBr添着炭充填層6の彼処理空気入口
側より、しだいに強酸性を呈する様になり弱酸であるH
Brが日2S04に置換されて出口側に移動し、HBn
添着体充填層6からしだし、にもれ出す様になる。この
状態ではオゾンのもれ出しも著しくなる。つぎにHBr
添着炭充填層6を通った彼処理ガスはKBn添着炭充填
層8を通過すると、まず、余剰のオゾンと反応式(6}
‘こ従って、水酸化2KBr+03→日20→2KOH
+Br2十02 ・・・{6ーカリウムと臭素を生
成する。
Next, the operation will be explained. The air to be treated A containing the malodorous gas sucked in by the blower is uniformly mixed with the ozonized air fed from the ozonizer 3 while passing through the mixing tank 4, and then introduced into the reaction tower 5. In the reaction tower 5, in the HBr-impregnated carbon packed bed 6, most of the malodorous components are removed by an oxidation reaction similar to the conventional method. Hydrogen sulfide is reacted with ozone and reaction formula {1
} is decomposed by the oxidation reaction shown in the reaction formula '2}, '3}, and a part of it is decomposed by the reaction formula ■, (Thus, it is finally oxidized to sulfuric acid. Day 2S + 03 → Day 20
10S02...t2}Day 2S
+Br2→2HBr+S...
・{31S02 10th 20103 → 2S04 1002
...'4}S04 10th 2011/202
→Sun 2S04...'5} Due to the accumulation of the generated sulfuric acid, the HBr-impregnated carbon packed bed 6 gradually becomes strongly acidic from the air inlet side, and H, which is a weak acid, becomes
Br is replaced with day 2S04 and moved to the exit side, and HBn
It begins to seep out from the adhesive filling layer 6 and leak out. In this state, ozone leaks out significantly. Next, HBr
When the treated gas that has passed through the impregnated coal packed bed 6 passes through the KBn impregnated coal packed bed 8, it first reacts with excess ozone according to equation (6).
'Therefore, 2KBr hydroxide + 03 → day 20 → 2KOH
+Br202...{Produces 6-potassium and bromine.

水酸化カリウムは中和反応式{九脚により、HBrや公
○を捕捉する。KOH+HBr→KBr十日20
・・・{7}KOH+日2S→KHS+
日20 …【8)水酸化カリウムは
さらに臭素と反応して硫黄をなって脱臭される。
Potassium hydroxide captures HBr and public ○ by the neutralization reaction formula {nine legs. KOH + HBr → KBr Toka 20
...{7}KOH+Japanese 2S→KHS+
Day 20...[8] Potassium hydroxide further reacts with bromine to form sulfur and is deodorized.

〔反応式{9}〕KHS+Br2→KBr+HBr十S
・・・【9}この様にKBn添着炭充
填層を設けると、もれ出したHBrを捕捉するので、オ
ゾンとHBrの反応による酸化脱臭能力の寿命を伸ばす
と同時に、硫化水素の酸化能力も向上する。
[Reaction formula {9}] KHS+Br2→KBr+HBr1S
...[9} Providing a KBn-impregnated carbon packed bed in this way captures leaked HBr, extending the life of the oxidative deodorizing ability due to the reaction between ozone and HBr, and at the same time increasing the oxidizing ability of hydrogen sulfide. improves.

この場合、HBr添着炭充填層6を設けずに、KBr添
着炭充填層8のみにすると、反応式(1}に従がう容易
なBr2生成反応がないので初期の脱臭性能の低下がま
ぬがれない。彼処理ガスは最後に、活性炭充填層を通っ
て、余剰酸化剤および亜硫酸ガス等の反応生成物を吸着
除去した後、処理空気Bとなって系外に放出される。
In this case, if the HBr-impregnated carbon packed bed 6 is not provided and only the KBr-impregnated carbon packed bed 8 is provided, there is no easy Br2 production reaction according to reaction formula (1}, so the initial deodorizing performance will inevitably deteriorate. Finally, the processing gas passes through an activated carbon packed bed to adsorb and remove reaction products such as excess oxidizing agent and sulfur dioxide gas, and is then released as processing air B to the outside of the system.

この発明の構成の概略は以上のようであるが以下に悪臭
成分との反応および効果について詳細に説明する。
Although the outline of the structure of this invention is as above, the reaction with malodorous components and effects will be explained in detail below.

オゾンと反応してBr2を生成する臭化物としては、H
Brのほか、臭化カリウム、臭化ナトリウム、臭化アン
モニウム、臭化マグネシウム、臭化カルシウムなどがあ
るが、オゾンとの反応で特に効率よく臭素を生成するの
はHBrであること、HBc添着炭と臭化カリゥム添着
炭あるいは臭化力ルシウム添着炭を組合わせて用いると
、臭素の付着量の減少が抑えられ、長時間酸化能力を維
持できること等の知見に基づいてこの発明は完成した。
第3図は、代表的な悪臭成分である硫化水素を処理した
場合の除去効果を示す特性図で、反応管径26◇の反応
管2本を用いて、一方には8〜10〆ッシュのHBn添
着炭を4cm充填し、他方には、同粒径のHBr添着炭
をまず2cの充填し、その上に同粒径のKBr添着炭を
2cm計4肌充填し、硫化水素30ppm、オゾン30
ppmを含有する被処理空気を10そ/minで5加持
間通気処理した場合の硫化水素の除去率の経時変化を示
す特性図で、特性曲線AはHBG添着炭のみを充填した
場合、特性曲線BはHBr添着炭とKBr添着炭を充填
した場合を示した。
Bromides that react with ozone to produce Br2 include H
In addition to Br, there are potassium bromide, sodium bromide, ammonium bromide, magnesium bromide, calcium bromide, etc., but it is HBr that produces bromine particularly efficiently when reacting with ozone, and HBc-impregnated carbon. This invention was completed based on the knowledge that when bromine is used in combination with potassium bromide-impregnated carbon or lucium bromide-impregnated carbon, the reduction in the amount of bromine attached can be suppressed and the oxidizing ability can be maintained for a long time.
Figure 3 is a characteristic diagram showing the removal effect when hydrogen sulfide, a typical malodorous component, is treated. 4 cm of HBn-impregnated coal was filled, and on the other side, 2 c of HBr-impregnated coal of the same particle size was first filled, and on top of that, a total of 4 skins of 2 cm of KBr-impregnated coal of the same particle size were filled, hydrogen sulfide was 30 ppm, ozone was 30
This is a characteristic diagram showing the change over time in the removal rate of hydrogen sulfide when the air to be treated containing ppm is aerated at 10 so/min for 5 times.Characteristic curve A is the characteristic curve when only HBG-impregnated coal is charged. B shows the case where HBr-impregnated coal and KBr-impregnated coal were filled.

HBr添着炭とKBr添着炭を組み合わせた場合がより
効果的であった、さらに上記試験を行ったのち、それぞ
れの充填層に、3ppmの硫化メチルと30ppmのオ
ゾンを含有した空気を1時間通気して硫化メチルの除去
効率を調べた結果、いずれの場合も99%以上の除去率
を示し★本来の除去能力は低下していないことを確認し
た。第4図には、これらの実験に使用した添着炭の彼処
理ガス入口側からの充填層厚と臭素添着率の関係を調べ
た結果を示した。HBr添着炭には臭素換算で約0.8
4%のHBr,KBr添着炭には0.755%のKBr
を添着した添着炭を用いた。図中実線で示した特性曲線
Cはf柏r添着炭を充填した場合、破線で示した特性曲
線DはHBr添着炭2cm充填した上にKBr添着炭を
2cm充填した場合の結果である。前者の場合、臭素添
着率は0.84%から0.8〜0.81%に低下したが
、後者の場合、HBG添着炭部では同様に低下したが、
KBr添着炭入口部の臭素添着率は0.85%に上昇し
、pHは低下していた。これは反応式(6},‘7}に
よってHBr添着炭充填層から放散されてきたHBrが
KBr添着炭部に吸着され、保持されるためと考えられ
る。すなわち、HBrの移動がみかけ上せき止められ、
HBr添着炭単独の場合よりHBrがゆっくりと移動す
るためであると考えれる。この実施例では担体として活
性炭を用いた場合について説明したが、活性白土、シリ
カ、アルミナ、アルミナなどの担体でもよい。なおこれ
らの実施例において使用したHBr添着体は、各担体を
10%臭化水素酸水溶液に1時間浸潰したのち窒素ガス
雰囲気中で乾燥させて調整した。
The combination of HBr-impregnated coal and KBr-impregnated coal was more effective.After conducting the above test, air containing 3 ppm methyl sulfide and 30 ppm ozone was vented into each packed bed for 1 hour. As a result of investigating the removal efficiency of methyl sulfide, the removal rate was 99% or more in all cases, and it was confirmed that the original removal ability was not decreased. Figure 4 shows the results of investigating the relationship between the packed bed thickness from the treated gas inlet side of the impregnated coal used in these experiments and the bromine impregnation rate. HBr-impregnated carbon contains approximately 0.8 in terms of bromine.
4% HBr, 0.755% KBr for KBr impregnated coal
Impregnated charcoal was used. The characteristic curve C shown by the solid line in the figure is the result when the carbon is filled with f-bar impregnated coal, and the characteristic curve D shown by the broken line is the result when the carbon is filled with 2 cm of HBr-impregnated coal and then 2 cm of KBr-impregnated coal. In the former case, the bromine impregnation rate decreased from 0.84% to 0.8-0.81%, but in the latter case, it decreased similarly in the HBG-impregnated coal part.
The bromine impregnation rate at the inlet of the KBr-impregnated coal increased to 0.85%, and the pH decreased. This is thought to be because HBr released from the HBr-impregnated coal packed bed is adsorbed and retained in the KBr-impregnated coal layer according to reaction equations (6}, '7}. In other words, the movement of HBr is apparently blocked. ,
This is thought to be because HBr moves more slowly than in the case of HBr-impregnated coal alone. In this example, the case where activated carbon was used as the carrier was explained, but carriers such as activated clay, silica, alumina, alumina, etc. may also be used. The HBr-impregnated bodies used in these Examples were prepared by soaking each carrier in a 10% hydrobromic acid aqueous solution for 1 hour and then drying it in a nitrogen gas atmosphere.

10%臭化水素酸の蒸気圧は4×10‐4側Hgと低く
、刺激臭はほとんどないため、取扱いが容易であり、窒
素ガスによる乾燥時における臭化水素の放散も少ない。
The vapor pressure of 10% hydrobromic acid is as low as 4 x 10-4 Hg, and there is almost no irritating odor, so it is easy to handle, and less hydrogen bromide is released during drying with nitrogen gas.

しかし、30%以上の水溶液を用いて臭化水素酸添着体
を調整する場合には乾燥の結果、臭化水素の放散が著し
く大きくなり、経済的ではない。10%臭化水素酸水溶
液を用いた場合の各種担体への添着量は各担体の単位重
量あたりの重量%として、臭素換算で表わすと、活性炭
0.8〜1.5%、活性白土4.8〜5%、アルミナ2
.5〜3%であった。
However, when a hydrobromic acid impregnated body is prepared using an aqueous solution of 30% or more, hydrogen bromide is significantly released as a result of drying, which is not economical. When using a 10% aqueous solution of hydrobromic acid, the amount of impregnated onto various carriers is expressed as weight % per unit weight of each carrier and expressed in terms of bromine: activated carbon 0.8 to 1.5%, activated clay 4. 8-5%, alumina 2
.. It was 5-3%.

。このように、臭化水素酸水溶液は10%溶液を用いて
添着炭を調整するのが好ましいが2%溶液を用いても実
用上支障はない。
. As described above, it is preferable to use a 10% hydrobromic acid aqueous solution to prepare the impregnated carbon, but there is no practical problem even if a 2% solution is used.

なお、このようにして調整した添着体には臭化水素酸と
臭化水素も添着されており、臭化水素酸水溶液を使う代
わりに臭化水素を含むガスを通気しても同様な添着体が
得られた。
Note that the impregnated body prepared in this way is also impregnated with hydrobromic acid and hydrogen bromide, and even if a gas containing hydrogen bromide is passed through the impregnated body instead of using an aqueous solution of hydrobromic acid, the same impregnated body will not be produced. was gotten.

また、KBr添着炭は、経済的理由から1.5%以下(
2〜15%)のKBr水溶液を用いて、HBG添着炭と
同様の処理により調整した。
In addition, KBr-impregnated coal should be 1.5% or less (
It was prepared by the same treatment as the HBG-impregnated carbon using a KBr aqueous solution (2% to 15%).

KBr添着量は臭素換算で0.5%〜5%が適当であっ
た。ここでKBr添着炭の場合を示したが、NaBr、
CaBr2,MgBr2などのアルカリ金属、アルカリ
土類金属の臭化物でも同様の効果を発揮する。また脱臭
装置の一実施例として反応塔の最終充填層に活性炭を用
いた場合について説明したが、アルカリ金属あるいはア
ルカリ士類金属の水酸化物、炭酸塩を活性炭、ゼオラィ
ト、アルミナ等の担体に添着したアルカリ添着体あるい
は経済的に許される場合はKI添着炭などの余剰酸化剤
や反応生成物である亜硫酸ガスを除去できる添着体とし
てもよい。
The appropriate amount of KBr impregnated was 0.5% to 5% in terms of bromine. Here, the case of KBr-impregnated coal was shown, but NaBr,
Similar effects are also exhibited by bromides of alkali metals and alkaline earth metals such as CaBr2 and MgBr2. In addition, as an example of the deodorizing device, we have explained the case where activated carbon is used in the final packed bed of the reaction tower, but hydroxides or carbonates of alkali metals or alkali metals are impregnated with a carrier such as activated carbon, zeolite, or alumina. An impregnated body capable of removing excess oxidizing agent and reaction product sulfur dioxide gas such as KI-impregnated carbon may be used if economically permitted.

この発明は以上詳細に説明したように、オゾナィザとこ
のオゾナィザから送給されるオゾン化空気を悪臭成分を
含む被処理空気中に散気させる装置と、臭化水素または
臭化水素酸を担体に添着せる添着体の充填層と、アルカ
リ金属またはアルカリ士類金属の臭化物を担体に添着せ
る添着体の充填層と、活性炭またはアルカリ添着体の充
填層と、上記オゾンを添加された被処理空気を上記HB
r添着体層、KBr添着体層、活性炭充填層の順に通過
させる送気装置とを備えたもので、オゾンと臭化水素ま
たは臭化水素酸の反応により生成される臭素により悪臭
成分を酸化するので、活性炭では吸着除去が困難なアン
モニア、硫化メチル、二硫化メチル等の成分を効率よく
除去することができるまた、KBh添着体層を通すこと
により、HBr添着体層からもれ出すHBrを捕捉し、
これを有効利用するため、上記オゾンとHBrによる酸
化反応の寿命を伸ばすと共に硫化水素の除去効率を高め
る。
As explained in detail above, the present invention comprises an ozonizer, a device for aerating ozonized air supplied from the ozonizer into air to be treated containing malodorous components, and hydrogen bromide or hydrobromic acid as a carrier. A packed bed of an impregnating body to be impregnated, a packed bed of an impregnating body to impregnate a carrier with an alkali metal or alkali metal bromide, a packed bed of activated carbon or an alkali impregnating body, and a packed bed of an impregnating body to impregnate the carrier, and a packed bed of an impregnating body to impregnate the support with the ozone-added air. Above HB
It is equipped with an air supply device that passes through the r impregnator layer, the KBr impregnator layer, and the activated carbon packed bed in this order, and oxidizes malodorous components with bromine produced by the reaction of ozone and hydrogen bromide or hydrobromic acid. Therefore, components such as ammonia, methyl sulfide, and methyl disulfide, which are difficult to adsorb and remove with activated carbon, can be efficiently removed.Also, by passing through the KBh impregnator layer, HBr leaking from the HBr impregnate layer is captured. death,
In order to effectively utilize this, the life of the oxidation reaction using ozone and HBr will be extended, and the efficiency of removing hydrogen sulfide will be increased.

さらに、余剰酸化剤、反応生成物を活性炭またはアルカ
リ添着体の充填層で吸着除去するようにしたので2次公
害の発生もない。図面の簡単な説明第1図はオゾンを用
いた従来の乾式脱臭装置のフロー図、第2図はこの発明
の一実施例を示すフロー図、第3図はHBr添着炭とK
Br添着炭とを組合せた充填層における硫化水素の除去
効果を示す特性図、第4図はこの発明による臭素添着率
の層厚依存性を示す特性図である。
Furthermore, since excess oxidizing agent and reaction products are adsorbed and removed by the packed bed of activated carbon or alkali impregnated material, no secondary pollution occurs. Brief Description of the Drawings Fig. 1 is a flow diagram of a conventional dry deodorizing device using ozone, Fig. 2 is a flow diagram showing an embodiment of the present invention, and Fig. 3 is a flow diagram of a conventional dry deodorizing device using ozone.
FIG. 4 is a characteristic diagram showing the hydrogen sulfide removal effect in a packed bed combined with Br-impregnated carbon, and FIG. 4 is a characteristic diagram showing the layer thickness dependence of the bromine impregnation rate according to the present invention.

図において、1はブロア、3はオゾナィザ、4は混合層
、6は反応塔、6はHB増添着炭充填層、7は活性炭充
填層、8はKBr添着炭充填層である。なお、図中同一
符号はそれぞれ同一または相当部分を示す。第1図 第2図 第3図 第4図
In the figure, 1 is a blower, 3 is an ozonizer, 4 is a mixed layer, 6 is a reaction column, 6 is an HB-enhanced carbon packed bed, 7 is an activated carbon packed bed, and 8 is a KBr-impregnated carbon packed bed. Note that the same reference numerals in the figures indicate the same or corresponding parts. Figure 1 Figure 2 Figure 3 Figure 4

Claims (1)

【特許請求の範囲】 1 オゾナイザと、このオゾナイザから送給されるオゾ
ン化ガスと悪臭成分を含む被処理空気に混合する手段と
、臭化水素または臭化水素酸を担体に添着せる添着体の
充填層と、アルカリ金属またはアルカリ土類金属の臭化
物を担体に添着せる添着体の充填層と、活性炭またはア
ルカリ添着体の充填層と、上記オゾンが添加された被処
理空気を上記臭化水素または臭化水素酸添着体層、臭化
物添着体層、活性炭充填層の順に通過させる送気装置と
を備えた乾式脱臭装置。 2 担体が活性炭、ゼオライト、シリカ、アルミナまた
はアルミナである特許請求の範囲第1項記載の乾式脱臭
装置。 3 臭化水素または臭化水素酸添着体の添着量が臭素換
算値で0.1〜10重量%の範囲内である特許請求の範
囲第1項記載の乾式脱臭装置。 4 臭化水素または臭化水素酸添着体の添着量が臭素換
算値で0.5〜5重量%の範囲内である特許請求の範囲
第3項記載の乾式脱臭装置。 5 アルカリ金属あるいはアルカリ土類金属の臭化物添
着量が0.1〜10重量%の範囲内である特許請求の範
囲第1項記載の乾式脱臭装置。 6 アルカリ金属あるいはアルカリ土類金属の臭化物添
着体の添着量が0.5〜5重量%の範囲内である特許請
求の範囲第5項記載の乾式脱臭装置。
[Claims] 1. An ozonizer, a means for mixing the ozonized gas supplied from the ozonizer with the air to be treated containing malodorous components, and an impregnator for impregnating hydrogen bromide or hydrobromic acid onto a carrier. a packed bed of an impregnator for impregnating an alkali metal or alkaline earth metal bromide onto a carrier; a packed bed of activated carbon or an alkali impregnator; A dry deodorizing device comprising an air supply device that passes through a hydrobromic acid impregnated layer, a bromide impregnated layer, and an activated carbon packed bed in this order. 2. The dry deodorizing device according to claim 1, wherein the carrier is activated carbon, zeolite, silica, alumina, or alumina. 3. The dry deodorizing apparatus according to claim 1, wherein the amount of hydrogen bromide or hydrobromic acid impregnated is within the range of 0.1 to 10% by weight in terms of bromine. 4. The dry deodorizing device according to claim 3, wherein the amount of hydrogen bromide or hydrobromic acid impregnated is within the range of 0.5 to 5% by weight in terms of bromine. 5. The dry deodorizing device according to claim 1, wherein the amount of alkali metal or alkaline earth metal bromide impregnated is within the range of 0.1 to 10% by weight. 6. The dry deodorizing device according to claim 5, wherein the amount of the alkali metal or alkaline earth metal bromide impregnated body is within the range of 0.5 to 5% by weight.
JP55105794A 1979-11-28 1980-07-31 Dry deodorization equipment Expired JPS6034892B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP55105794A JPS6034892B2 (en) 1980-07-31 1980-07-31 Dry deodorization equipment
US06/211,286 US4370301A (en) 1979-11-28 1980-11-28 Dry deodorizing apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55105794A JPS6034892B2 (en) 1980-07-31 1980-07-31 Dry deodorization equipment

Publications (2)

Publication Number Publication Date
JPS5730532A JPS5730532A (en) 1982-02-18
JPS6034892B2 true JPS6034892B2 (en) 1985-08-12

Family

ID=14417028

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55105794A Expired JPS6034892B2 (en) 1979-11-28 1980-07-31 Dry deodorization equipment

Country Status (1)

Country Link
JP (1) JPS6034892B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH035192B2 (en) * 1984-02-01 1991-01-24 Bandai Co

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH064126B2 (en) * 1985-06-10 1994-01-19 株式会社日本触媒 Exhaust gas purification method
JPS62171739A (en) * 1986-01-24 1987-07-28 Nippon Shokubai Kagaku Kogyo Co Ltd High denitration method
JP2583912B2 (en) * 1987-10-26 1997-02-19 バブコツク日立株式会社 Nitrogen oxide removal catalyst
JP2542290B2 (en) * 1991-02-18 1996-10-09 正勝 平岡 Exhaust gas purification method
WO1992019366A1 (en) * 1991-04-30 1992-11-12 Nippon Shokubai Co., Ltd. Method of oxidative decomposition of organic halogen compound
JP2609393B2 (en) * 1992-03-04 1997-05-14 東京都 Exhaust gas treatment method
US6638486B2 (en) 2000-03-08 2003-10-28 Nippon Shokubai Co., Ltd. Catalyst for purification of exhaust gases, production process therefor, and process for purification of exhaust gases
JP6443679B2 (en) * 2015-03-27 2018-12-26 Jfeエンジニアリング株式会社 Exhaust gas treatment method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH035192B2 (en) * 1984-02-01 1991-01-24 Bandai Co

Also Published As

Publication number Publication date
JPS5730532A (en) 1982-02-18

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