JPS6033072B2 - Deodorizing device - Google Patents
Deodorizing deviceInfo
- Publication number
- JPS6033072B2 JPS6033072B2 JP56052759A JP5275981A JPS6033072B2 JP S6033072 B2 JPS6033072 B2 JP S6033072B2 JP 56052759 A JP56052759 A JP 56052759A JP 5275981 A JP5275981 A JP 5275981A JP S6033072 B2 JPS6033072 B2 JP S6033072B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- bromide
- filler
- deodorizing device
- ozone
- 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
Links
Landscapes
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Separation Of Gases By Adsorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【発明の詳細な説明】
この発明は着臭したガスを、オゾンと固体充填剤を併用
して無臭化する脱臭装置に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a deodorizing device that deodorizes odorized gas by using ozone and a solid filler in combination.
従来この種の脱臭装置としては活性炭による吸着脱臭装
置があった。Conventionally, as this type of deodorizing device, there has been an adsorption deodorizing device using activated carbon.
しかし活性炭による吸着により、下水やし尿処理場の排
ガスを脱臭しようとする場合、排ガス中の硫化メチルや
二硫化メチル等の酸塩基度が中性の悪臭成分が除去され
難く、活性炭の悪臭除去館が早く劣化するという欠点が
あった。また近年開発された活性炭に特殊な加工を施し
た添着活性炭による悪臭の吸着脱臭装置は、多種類の悪
臭成分を含有する下水やし尿処理場の排ガスの臭気処理
に際して、酸性ガス用、塩基性ガス用、硫化物用および
一般ガス用の少くとも4種類の活性炭を直列に使用しな
ければ所期の総合的脱臭性能を発揮することができない
うえ、比較的高価な添着活性炭を多量に使用するので、
ガス処理費用が割高になるという欠点があった。この発
明は上記のような従来のものの欠点を除去するためにな
されたもので、被処理ガス中の特定成分を除去する前処
理およびオゾンと臭化物添着剤による処理を併用するこ
とによって、下水やし尿処理場で発生する臭気を総合的
にかつ安価に脱臭することを可能にした脱臭装置を提供
することを目的としている。以下、この発明の一実施例
を図について説明する。However, when trying to deodorize exhaust gas from sewage and human waste treatment plants by adsorption with activated carbon, it is difficult to remove malodorous components with neutral acidity and basicity, such as methyl sulfide and methyl disulfide, from the exhaust gas. The disadvantage was that it deteriorated quickly. In addition, recently developed malodor adsorption and deodorization equipment using impregnated activated carbon, which has been specially processed, is used for acid gas, basic gas The desired overall deodorizing performance cannot be achieved unless at least four types of activated carbon, one for gas, one for sulfides, and one for general gas, are used in series, and a large amount of relatively expensive impregnated activated carbon is used. ,
The disadvantage was that the gas processing costs were relatively high. This invention was made in order to eliminate the drawbacks of the conventional methods as described above, and by using a combination of pre-treatment to remove specific components in the gas to be treated and treatment with ozone and bromide impregnants, it is possible to treat sewage and human waste. The purpose of the present invention is to provide a deodorizing device that can comprehensively and inexpensively deodorize odors generated in a treatment plant. An embodiment of the present invention will be described below with reference to the drawings.
図において、1は脱臭塔であり、内部に硫化水素除去用
充填剤2、アンモニア除去用充填剤3、反応剤4、オゾ
ン分解剤5が上記順序で被処理ガス(白い矢印)と接触
するように配列されている。6はオゾナイザであり、こ
こで発生したオゾン化空気(黒い矢印)は拡散器7を経
て、アンモニア除去用充填剤3と接触した後の彼処理ガ
ス中に混合されるように、脱臭塔1に接続している。In the figure, 1 is a deodorizing tower, inside of which a hydrogen sulfide removal filler 2, an ammonia removal filler 3, a reactant 4, and an ozone decomposer 5 are placed in contact with the gas to be treated (white arrow) in the above order. are arranged in 6 is an ozonizer, and the ozonized air (black arrow) generated here passes through a diffuser 7 and is sent to the deodorizing tower 1 so that it is mixed into the treated gas after contacting the ammonia removal filler 3. Connected.
8は隔壁「 9は彼処理ガスの入口側ダクト、10‘ま
出口側ダクトである。8 is a bulkhead; 9 is a duct on the inlet side of the processing gas; and 10' is a duct on the outlet side.
硫化水素除去用充填剤2としてはべレットないし破砕状
の酸化鉄「水酸化鉄または活性炭にョウ化カリウムを添
着させたものが好ましい。As the filler 2 for removing hydrogen sulfide, pellets or crushed iron oxide (iron hydroxide) or activated carbon impregnated with potassium iodide are preferable.
アンモニア除去用充填剤3としてはべレットないし破砕
状の活性炭に塩酸または硫酸を含浸させたものが好まし
い。反応剤4としては臭化水素や臭化ナトリウム、臭化
カリウム等の水溶性臭化物を比表面積の大きな、化学的
に安定な担体、例えば活性炭に数%添着させたものが好
ましい。オゾン分解剤5としてはャシ殻活性炭または酸
化鉄、二酸化マンガン等の重金属酸化物を添着した活性
炭が好ましい。次に動作について説明する。As the filler 3 for removing ammonia, it is preferable to use pellets or crushed activated carbon impregnated with hydrochloric acid or sulfuric acid. As the reactant 4, it is preferable to use a chemically stable carrier having a large specific surface area, such as activated carbon, impregnated with several percent of a water-soluble bromide such as hydrogen bromide, sodium bromide, or potassium bromide. The ozone decomposer 5 is preferably chassis shell activated carbon or activated carbon impregnated with heavy metal oxides such as iron oxide or manganese dioxide. Next, the operation will be explained.
入口側ダクト9から脱臭塔1に導入された彼処理ガス(
白い矢印)は、まず硫化水素除去用充填剤2およびアン
モニア除去用充填剤3と順次接触し、被処理ガス中の主
要悪臭成分である硫化水素とアンモニアの大部分を除去
される。次いで被処理ガスは拡散器7から放出されたオ
ゾン化空気を混合された後、反応剤4を接触し、彼処理
ガス中の悪臭物質はオゾンと上記反応剤4との反応によ
って生成する臭素(Br2)や次頭臭素酸(HBの)と
反応し、異種物質に転換される。例えば硫化メチル〔(
CH3)2S〕は、臭化水素を添着した添着剤を反応剤
4として用いた場合、下記化学反応式のごとくオゾンに
よって間接的に酸化分解され、ジメチルスルホキシドに
なる。The treated gas (
The white arrow) first comes into contact with the hydrogen sulfide removal filler 2 and the ammonia removal filler 3 in order, and most of hydrogen sulfide and ammonia, which are the main malodorous components in the gas to be treated, are removed. Next, the gas to be treated is mixed with the ozonized air released from the diffuser 7, and then brought into contact with the reactant 4. The malodorous substances in the gas to be treated are bromine (produced by the reaction between ozone and the reactant 4). It reacts with Br2) and hypobromic acid (HB) and is converted into a different substance. For example, methyl sulfide [(
CH3)2S] is indirectly oxidized and decomposed by ozone to become dimethyl sulfoxide when an impregnating agent impregnated with hydrogen bromide is used as the reactant 4, as shown in the chemical reaction formula below.
HBr+03→HBr○十02 ……(1
)HBの十(CH3)2S→HBr十(CH3)2SO
.・…‐(ロ)またメチルメルカプタン(CH3SH)
は次式によりメタンスルホン酸に酸化される。HBr+03→HBr○102...(1
) HB 10 (CH3) 2S → HBr 10 (CH3) 2SO
..・…-(b) Also methyl mercaptan (CH3SH)
is oxidized to methanesulfonic acid according to the following formula.
父8の十CH3SH→知日Br十CH3S03日.・・
.・・(m)さらに二硫化メチル((CH3)2S2)
は次式によりメタンスルホン酸に酸化される。Father 8 no 10 CH3SH → Chihito Br10 CH3S03 day.・・・
.. ...(m) Furthermore, methyl disulfide ((CH3)2S2)
is oxidized to methanesulfonic acid according to the following formula.
丸mの十(CH3)ぶ2十日20
一8mr+次QS03日 ・・・・・・(N
)以上により生成したジメチルスルホキシドやメタンス
ルホン酸は無臭の物質であり、脱臭の目的が達成されて
いる。Maru m no 10 (CH3) 20 days 20 18 mr + next QS 03 days ...... (N
) The dimethyl sulfoxide and methanesulfonic acid produced above are odorless substances, and the purpose of deodorization has been achieved.
上記、イ乙学反応式(1)は効率よく進行してオゾンは
完全に消費されるが、上記脱臭反応生成物が反応剤4表
面に蓄積してくると添加オゾンが一部未反応のまま反応
剤4を通過してくる。The above reaction equation (1) progresses efficiently and ozone is completely consumed, but as the deodorizing reaction product accumulates on the surface of the reactant 4, some of the added ozone remains unreacted. It passes through reactant 4.
しかし未反応オゾンは次のオゾン分解剤5と接触し0.
01桝以下に除去され、処理ガスは出口側ダクト10か
ら排出される。被処理ガスに対するオゾンの添加割合は
、硫化水素除去用充填剤2およびアンモニア除去用充填
剤3と接触した後の被処理ガスに含まれた主要悪臭物質
の濃度の3〜5倍以上であればよく、通常3〜5跡程度
でよい。However, the unreacted ozone comes into contact with the next ozone decomposer 5 and the ozone is removed.
The processing gas is removed to less than 0.01 square meters, and the processing gas is discharged from the outlet side duct 10. The ratio of ozone added to the gas to be treated is 3 to 5 times or more the concentration of the main malodorous substances contained in the gas to be treated after contact with the hydrogen sulfide removal filler 2 and the ammonia removal filler 3. Generally, 3 to 5 marks are sufficient.
次にこの発明の脱臭装置の優れた性能を確認するために
実施したテスト結果について述べる。Next, the results of tests conducted to confirm the excellent performance of the deodorizing device of the present invention will be described.
臭気の処理条件は表1に示す通りであり、このような操
作条件のもとで約370斑時間にわたって臭気を処理し
た結果を表2に示す。表−1
表− 2 脱臭前/脱臭後の悪臭成分の濃度(ppm)
なお、通常のヤシ殻活性炭だけを表1の4種の充填剤と
同容量(約8夕,3.6k9)だけ充填した装置では、
硫化メチルと二硫化メチルが稼動時間100餌時間未満
で破遇し始めた。The odor treatment conditions are as shown in Table 1, and Table 2 shows the results of odor treatment for about 370 hours under these operating conditions. Table-1 Table-2 Concentration of malodorous components before/after deodorization (ppm)
In addition, in a device filled with only ordinary coconut shell activated carbon in the same volume as the four types of fillers in Table 1 (approximately 8 yen, 3.6 k9),
Methyl sulfide and methyl disulfide started to fail after less than 100 feeding hours.
また表1の条件設定で、オゾン添加をしない場合には、
活性炭だけを充填した場合と同様に硫化メチルと二硫化
メチルの破週が観測され、性能的に不満足であった。な
お図の構成の装置で、通常のャシ殻活性炭だけを全ての
充填剤充填個所に充填した場合には、オゾン混合物の被
処理ガスと接触する活性炭が経時的に灰化して消耗する
とともに、二硫化メチルが部分的に増大することもあり
、脱臭性能としては不充分であった。なお、上記実施例
では、隔壁8により脱臭塔1を2分し、ガス流が折返し
流となるように構成したが、ガス流が直線流となるよう
に各充填剤を配置してもよく、脱臭塔1の構造は適宜変
更可能である。また各充填剤も前記例示のものに限定さ
れず、その機能を有する範囲において任意のものが選択
可能である。以上のように、この発明によれば、硫化水
素とアンモニアを高濃度に含み、かつその他の悪臭成分
も含む肴臭した排ガスを硫化水素およびアンモニア除去
用の充填剤と接触させた後、オゾンを添加し、さらに臭
化水素を添着した充填剤と接触させるようにしたので、
高性能の脱臭が可能となり、実用上の価値が高い。Also, if ozone is not added under the conditions set in Table 1,
Similar to the case when only activated carbon was filled, rupture of methyl sulfide and methyl disulfide was observed, and the performance was unsatisfactory. In addition, in the case where only ordinary chassis shell activated carbon is filled into all filler filling points in the apparatus configured as shown in the figure, the activated carbon that comes into contact with the gas to be treated of the ozone mixture will ash and be consumed over time. Methyl disulfide was partially increased, and the deodorizing performance was insufficient. In the above embodiment, the deodorizing tower 1 is divided into two parts by the partition wall 8 so that the gas flow is turned back, but each filler may be arranged so that the gas flow is a straight flow. The structure of the deodorizing tower 1 can be changed as appropriate. Further, each filler is not limited to those exemplified above, and any filler can be selected as long as it has the function. As described above, according to the present invention, ozone is removed from the ozone-containing exhaust gas, which contains a high concentration of hydrogen sulfide and ammonia and also contains other malodorous components, after bringing it into contact with a filler for removing hydrogen sulfide and ammonia. Since the hydrogen bromide was added and brought into contact with the filler impregnated with hydrogen bromide,
It enables high-performance deodorization and has high practical value.
また硫化水素およびアンモニアが予め除去されるので、
オゾンを有効に使用でき、処理コストを低くできるなど
の効果がある。Also, since hydrogen sulfide and ammonia are removed in advance,
Ozone can be used effectively and processing costs can be reduced.
図はこの発明の一実施例を示す脱臭装置の垂直断面図で
あり、1は脱臭塔、2は硫化水素除去用充填剤、3はア
ンモニア除去用充填剤、4は反応剤、5はオゾン分解剤
、6はオゾナィザ、7は拡散器である。The figure is a vertical sectional view of a deodorizing apparatus showing an embodiment of the present invention, in which 1 is a deodorizing tower, 2 is a packing material for removing hydrogen sulfide, 3 is a packing material for removing ammonia, 4 is a reactant, and 5 is an ozonolytic 6 is an ozonizer, and 7 is a diffuser.
Claims (1)
的に分離する2種類の充填剤、これらの充填剤と接触し
た後のガスにオゾンを混合する拡散器および臭化物を添
着した充填剤を備え、上記順序で被処理ガスを充填剤と
接触させるようにしたことを特徴とする脱臭装置。 2 臭化物は臭化水素、またはアルカリ臭化物であるこ
とを特徴とする特許請求の範囲第1項記載の脱臭装置。 3 臭化物を添着する担体は活性炭であることを特徴と
する特許請求の範囲第1項または第2項記載の脱臭装置
。4 臭化物を添着した充填剤の後にオゾン分解剤を備
えたことを特徴とする特許請求の範囲第1項ないし第3
項のいずれかに記載の脱臭装置。[Claims] 1. Two types of fillers that selectively separate hydrogen sulfide and ammonia in odorized gas, a diffuser that mixes ozone into the gas after contact with these fillers, and impregnation with bromide. 1. A deodorizing device comprising: a filler, and a gas to be treated is brought into contact with the filler in the above order. 2. The deodorizing device according to claim 1, wherein the bromide is hydrogen bromide or an alkali bromide. 3. The deodorizing device according to claim 1 or 2, wherein the carrier to which bromide is impregnated is activated carbon. 4 Claims 1 to 3, characterized in that an ozonolytic agent is provided after the bromide-impregnated filler.
The deodorizing device according to any one of paragraphs.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56052759A JPS6033072B2 (en) | 1981-04-08 | 1981-04-08 | Deodorizing device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56052759A JPS6033072B2 (en) | 1981-04-08 | 1981-04-08 | Deodorizing device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57168669A JPS57168669A (en) | 1982-10-18 |
| JPS6033072B2 true JPS6033072B2 (en) | 1985-07-31 |
Family
ID=12923805
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56052759A Expired JPS6033072B2 (en) | 1981-04-08 | 1981-04-08 | Deodorizing device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6033072B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63181765A (en) * | 1987-01-23 | 1988-07-26 | 東海興業株式会社 | Simple deodorizer |
| JP2516656B2 (en) * | 1988-03-09 | 1996-07-24 | 三菱重工業株式会社 | Denitration reactor |
-
1981
- 1981-04-08 JP JP56052759A patent/JPS6033072B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57168669A (en) | 1982-10-18 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4370301A (en) | Dry deodorizing apparatus | |
| CA1090259A (en) | Amyl alcohol and acetic acid to reduce odor of sewage sludge | |
| CN102000484B (en) | Rubber-mixing waste gas deodorizing and purifying device and method through dry oxidation | |
| JPS6033072B2 (en) | Deodorizing device | |
| JPS6034892B2 (en) | Dry deodorization equipment | |
| JPS62163726A (en) | Simple deodorizer | |
| JPS5730531A (en) | Dry type deodorizer | |
| JPS6341612B2 (en) | ||
| JP4222607B2 (en) | Deodorizing method and deodorizing liquid | |
| JP2731124B2 (en) | Deodorization method | |
| KR101133548B1 (en) | Apparatus and method for removing hydrogen sulfide odor using micro bubble ozone | |
| JPH0224539B2 (en) | ||
| KR0145198B1 (en) | Oxidation deodorization device of waste gas | |
| JP4138289B2 (en) | Method for removing malodorous substances generated from composting equipment | |
| JPS57174122A (en) | Deodorizing device for gas | |
| JPS58131121A (en) | Deodorizing method | |
| JPS6034893B2 (en) | Deodorizing device | |
| JPS5821528B2 (en) | Deodorizing method | |
| JPS5594622A (en) | Deodorizing apparatus for ozone | |
| JPH02258015A (en) | Deodorization method and apparatus | |
| JPS56115619A (en) | Ozone decoloration and deodorization method | |
| JPS5730530A (en) | Dry type deodorizer | |
| JP3278337B2 (en) | Deodorization method | |
| JPS5922571B2 (en) | ozone | |
| JPH07308696A (en) | Method for preventing malodor from being generated in waste water treatment |