JPS5934412B2 - Ozone deodorization method - Google Patents
Ozone deodorization methodInfo
- Publication number
- JPS5934412B2 JPS5934412B2 JP53050741A JP5074178A JPS5934412B2 JP S5934412 B2 JPS5934412 B2 JP S5934412B2 JP 53050741 A JP53050741 A JP 53050741A JP 5074178 A JP5074178 A JP 5074178A JP S5934412 B2 JPS5934412 B2 JP S5934412B2
- Authority
- JP
- Japan
- Prior art keywords
- ozone
- malodorous
- hydrogen sulfide
- injected
- exhaust gas
- 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)
- Treating Waste Gases (AREA)
Description
【発明の詳細な説明】
本発明は悪臭排ガスをオゾンにより脱臭する方法の改良
に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a method for deodorizing malodorous exhaust gas using ozone.
従来、悪臭排ガスにオゾンを気相混合させて脱臭する方
法においては、反応率が低く、例えば、該排ガス中の悪
臭物質量lに対し30割合でオゾンを注入混合させると
、硫化水素においては50係程度の分解率しか得られず
、しかもオゾン注入割合を3以上としても硫化水素の分
解率50%は変わらなかった。Conventionally, in the deodorizing method by mixing ozone in the vapor phase with malodorous exhaust gas, the reaction rate is low. For example, if ozone is injected and mixed at a ratio of 30% to the amount of malodorous substances in the exhaust gas, 50% Moreover, even when the ozone injection ratio was increased to 3 or higher, the hydrogen sulfide decomposition rate of 50% did not change.
そこで本発明等は、悪臭排ガス中の各種悪臭物質とオゾ
ンとの反応性を検討したところ、該排ガス流路の広い範
囲にわたって反応率とモル比(悪臭物質とオゾンとのモ
ル比)との関係は一定であるという知見を得た。Therefore, the present invention investigated the reactivity of various malodorous substances in malodorous exhaust gas with ozone, and found that the relationship between reaction rate and molar ratio (molar ratio between malodorous substances and ozone) over a wide range of the exhaust gas flow path was investigated. We obtained the knowledge that is constant.
従って、悪臭排ガスの流れに沿って次々にオゾンを補給
して行けば、総オゾン注入割合は一定でも全体の反応率
は上がるという結論に達し、本発明方法を完成するに至
った。Therefore, they came to the conclusion that if ozone is replenished one after another along the flow of malodorous exhaust gas, the overall reaction rate will increase even if the total ozone injection ratio remains constant, and the method of the present invention was completed.
すなわち本発明は、悪臭排ガスの流路に複数個のオゾン
注入装置を設け、オゾン注入点における上記悪臭排ガス
中での残存悪臭物質の量とオゾン量との比が一定になる
ように、上記オゾン注入装置からオゾンを注入して悪臭
ガスを脱臭することを特徴とするオゾン脱臭方法を要旨
とするものである。That is, the present invention provides a plurality of ozone injection devices in the flow path of the malodorous exhaust gas, and injects the ozone so that the ratio between the amount of malodorous substances remaining in the malodorous exhaust gas and the amount of ozone at the ozone injection point is constant. The gist of the present invention is an ozone deodorizing method characterized by injecting ozone from an injection device to deodorize malodorous gas.
以下、添付図面を用いて本発明方法を更に詳細に説明す
る。Hereinafter, the method of the present invention will be explained in more detail using the accompanying drawings.
添付図面は本発明方法の一実施態様例を示す概略説明図
である。The accompanying drawings are schematic illustrations showing one embodiment of the method of the present invention.
図中、1はオゾン接触槽、2はバッフル、31〜33は
オゾン注入ラインである。In the figure, 1 is an ozone contact tank, 2 is a baffle, and 31 to 33 are ozone injection lines.
ライン4かも導入される悪臭排ガスは、先ず、ライン3
1からオゾンが注入され、悪臭成分の一部が分解されつ
つオゾン接触槽1内を進む。The foul-smelling exhaust gas that is also introduced into line 4 is first introduced into line 3.
Ozone is injected from 1 and advances through the ozone contact tank 1 while some of the malodorous components are decomposed.
次いで、ライン3□から新たなオゾンが注入され、残存
オゾンと新たなオゾンとの合量が残存悪臭成分と一定の
比率になるようにする。Next, new ozone is injected from line 3□ so that the total amount of remaining ozone and new ozone becomes a constant ratio with the remaining malodorous components.
これにより悪臭成分は更に分解を続け、オゾン接触槽1
内を進む。As a result, the malodorous components continue to decompose, and the ozone contact tank 1
Go inside.
最後に、ライン33から上記ライン3□と同じ条件で新
たなオゾンが注入され、大部分の悪臭成分が分解されて
、ライン5かも脱臭排ガスとして系外へ抜き出される。Finally, new ozone is injected from line 33 under the same conditions as line 3□, most of the malodorous components are decomposed, and line 5 is also discharged out of the system as deodorized exhaust gas.
悪臭物質として硫化水素を例にとり、更に具体的に説明
する。A more specific explanation will be given using hydrogen sulfide as an example of a malodorous substance.
硫化水素1に対して30割合でオゾンを注入すると、従
来法では、前記したように硫化水素は50%、オゾンは
60%が分解し、オゾンの注入害拾を3以上としてもこ
の分解率は変わらない。When ozone is injected at a ratio of 30 parts to 1 part of hydrogen sulfide, in the conventional method, 50% of the hydrogen sulfide and 60% of the ozone are decomposed as described above, and even if the ozone injection damage is 3 or more, this decomposition rate remains low. does not change.
しかし、本発明法の場合、第1段(図中、ライン3□
)で硫化水素1に対し30割合でオゾンを注入すると、
前記したように硫化水素とオゾンの分解率は一定である
から、残存硫化水素は(1−I Xo、5=) 0.5
、残存オゾンは(L−3X0.6=)1.2となる。However, in the case of the method of the present invention, the first stage (line 3□ in the figure)
), when ozone is injected at a ratio of 30 parts to 1 part hydrogen sulfide,
As mentioned above, since the decomposition rate of hydrogen sulfide and ozone is constant, the residual hydrogen sulfide is (1-I Xo, 5=) 0.5
, the residual ozone is (L-3X0.6=)1.2.
次いで、第2段(図中、ライン3□ )で新たなオゾン
を残存オゾン1.2トの合量が残存硫化水素0.5に対
して3の割合となるように、すなわち0.3の新たなオ
ゾンを注入すると、ここでも硫化水素とオゾンの分解率
は一定であるから、残存硫化水素は(0,5−0,5X
O,5=)0.25、残存オゾンは(1,5−1,5
X 0.6=〕0.6となる。Next, in the second stage (line 3□ in the figure), new ozone is added so that the total amount of residual ozone (1.2 tons) is at a ratio of 3 to 0.5 of residual hydrogen sulfide, that is, 0.3 When new ozone is injected, the decomposition rate of hydrogen sulfide and ozone remains constant, so the remaining hydrogen sulfide is (0,5-0,5X
O,5=)0.25, residual ozone is (1,5-1,5
X0.6=]0.6.
更に、第3段(図中、ライン33 )で新たなオゾンを
第2段と同じ条件で0.15注入すると、ここでも硫化
水素とオゾンの分解率は一定であるから、残存硫化水素
は0.125、残存オゾンは0.3となる。Furthermore, if 0.15% of new ozone is injected in the third stage (line 33 in the figure) under the same conditions as the second stage, the decomposition rate of hydrogen sulfide and ozone is also constant, so the residual hydrogen sulfide will be 0. .125, and the residual ozone is 0.3.
すなわち本発明法によれば、硫化水素1に対し合計3.
45の割合でオゾンを注入すると、オゾン分解率は87
.5%になるわけである。That is, according to the method of the present invention, a total of 3.
When ozone is injected at a rate of 45%, the ozone decomposition rate is 87%.
.. This amounts to 5%.
この操作を続ければ、効果はいくらでも上がるが、実用
上は3段程度が限度であろう。If you continue this operation, the effect will increase as much as you want, but in practical terms, the limit is about 3 stages.
以上のことは、他の悪臭物質、例えばアンモニア、メチ
ルメルカプタン、硫化メチル、トリメチルアミン等につ
いても言える。The above also applies to other malodorous substances such as ammonia, methyl mercaptan, methyl sulfide, and trimethylamine.
これら悪臭物質に対するオゾン注入割合は、いずれも硫
化水素の場合と同様l二3の害拾で充分であるが、アン
モニアについてはオゾンとの反応性が低いため、基本的
には前処理で除去するようにする。As for the ozone injection rate for these malodorous substances, it is sufficient to remove 123 harmful substances as in the case of hydrogen sulfide, but since ammonia has low reactivity with ozone, it is basically removed by pretreatment. Do it like this.
従って、悪臭物質と残存オゾン量を各段毎に検出して常
に一定割合のオゾン量を注入すれば効果が更に上ること
は言うまでもない。Therefore, it goes without saying that the effect will be further improved if the malodorous substance and the amount of residual ozone are detected at each stage and a constant amount of ozone is always injected.
また、本発明方法は、室温(20℃、latm)で充分
に分解が進行するが、30°C以上の温度では更に分解
速度が促進される。Further, in the method of the present invention, decomposition proceeds sufficiently at room temperature (20°C, latm), but the decomposition rate is further accelerated at temperatures of 30°C or higher.
なお、従来法において、硫化水素1に対し3.45の割
合でオゾンを注入したところ、接触時間2〜5秒で硫化
水素の分解率は50%、オゾンの分解率は60%と変わ
らず、残存硫化水素は0.5、残存オゾンは1.49で
あった。In addition, in the conventional method, when ozone was injected at a ratio of 3.45 to 1 hydrogen sulfide, the decomposition rate of hydrogen sulfide remained unchanged at 50% and ozone at 60% at a contact time of 2 to 5 seconds. Residual hydrogen sulfide was 0.5, and residual ozone was 1.49.
以上より、本発明方法によればオゾン注入量は従来法と
同じであっても悪臭物質の分解が格段に上り、本発明方
法が優れたオゾン脱臭方法であることが明らかであろう
。From the above, it is clear that according to the method of the present invention, the decomposition of malodorous substances is markedly improved even when the amount of ozone injected is the same as in the conventional method, and that the method of the present invention is an excellent ozone deodorizing method.
添付図面は本発明方法の一実施態様例を示す概略説明図
である。The accompanying drawings are schematic illustrations showing one embodiment of the method of the present invention.
Claims (1)
、オゾン注入点における上記悪臭排ガス中での残存悪臭
物質の量とオゾン量との比が一定になるように、上記オ
ゾン注入装置からオゾンを注入して悪臭ガスを脱臭する
ことを特徴とするオゾン脱臭方法。1 A plurality of ozone injection devices are installed in the flow path of the malodorous exhaust gas, and ozone is injected from the ozone injection device so that the ratio between the amount of odor substances remaining in the malodorous exhaust gas and the amount of ozone at the ozone injection point is constant. An ozone deodorizing method characterized by deodorizing malodorous gas by injecting it.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53050741A JPS5934412B2 (en) | 1978-05-01 | 1978-05-01 | Ozone deodorization method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53050741A JPS5934412B2 (en) | 1978-05-01 | 1978-05-01 | Ozone deodorization method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54143765A JPS54143765A (en) | 1979-11-09 |
| JPS5934412B2 true JPS5934412B2 (en) | 1984-08-22 |
Family
ID=12867254
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53050741A Expired JPS5934412B2 (en) | 1978-05-01 | 1978-05-01 | Ozone deodorization method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5934412B2 (en) |
-
1978
- 1978-05-01 JP JP53050741A patent/JPS5934412B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54143765A (en) | 1979-11-09 |
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