JPS58124524A - Removal of malodorous component - Google Patents
Removal of malodorous componentInfo
- Publication number
- JPS58124524A JPS58124524A JP57006746A JP674682A JPS58124524A JP S58124524 A JPS58124524 A JP S58124524A JP 57006746 A JP57006746 A JP 57006746A JP 674682 A JP674682 A JP 674682A JP S58124524 A JPS58124524 A JP S58124524A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- malodorous
- catalyst
- ozone
- 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.)
- Pending
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は、オゾンを用いる悪臭除去方法に関するもので
ある。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing bad odors using ozone.
下水処理施設や、し尿処理施設から発生する悪臭を除去
する方法の一つとして、オゾンの酸化力と触媒を介在さ
せた言わばオゾン−触媒法■(%開昭54−11957
1号参照)がある。One of the methods for removing bad odors generated from sewage treatment facilities and human waste treatment facilities is the so-called ozone-catalyst method (% 11957-11957), which uses the oxidizing power of ozone and a catalyst.
(See No. 1).
更に悪臭除去効果を高めるために、前処理として乾式ア
ンモニア除去装置を設けた方法■(特開昭56−150
209号公報)および前処理として炭化水素類を吸着除
去するために活性炭フィルターを設けた方法■(特願昭
56−91490号)がある。In order to further enhance the odor removal effect, a method (Japanese Patent Application Laid-open No. 56-150
209 (Japanese Patent Application No. 56-91490) and method 2 (Japanese Patent Application No. 56-91490) in which an activated carbon filter is provided to adsorb and remove hydrocarbons as a pretreatment.
上記処理施設から発生する排ガス中vcFi、悪臭成分
、例えばアンモニア、硫化水素、メチルメルカプタン、
硫化メチル、二硫化メチルなどの他に臭いとは関係のな
い炭化水素類(炭素数で08〜C1,の化合物]があっ
て、上記出願方法によって各々除去しているが、昨今の
環境行政の強化に対応するには、悪臭除去効果の向−ト
を更に図る必要があり、従来の悪臭除去方法の改善が必
要である。vcFi in the exhaust gas generated from the above treatment facility, malodorous components such as ammonia, hydrogen sulfide, methyl mercaptan,
In addition to methyl sulfide and methyl disulfide, there are hydrocarbons (compounds with a carbon number of 08 to C1) that are unrelated to odor, and each of them is removed using the above application method, but due to recent environmental administration. In order to cope with the enhancement, it is necessary to further improve the malodor removal effect, and it is necessary to improve the conventional malodor removal method.
本発明者等は悪臭成分のうち、硫化水素、メチルメルカ
プタン、硫化メチルなどはオゾン−触媒法で除去すると
同時に、アンモニアおよび炭化水素類が除去できれば、
悪臭除去効果は向上するばかりでなく、触媒寿命も延び
て全体様能の向上が図れると考えた。そこで、(1)対
象処理ガス中のうち、触媒活性の低下および触媒寿命を
早める原因となる炭化水素類は活性炭フィルターにより
触媒層の前で除去し、(2)オゾンとの反応性に乏しい
アンモニアは、固体酸吸着剤層により触媒層の前で除去
すると共に、13+ k化水素、メチルメルカプタン、
硫化メチルなどの悪臭成分は、オゾンを注入してオゾン
の酸化力と触媒の作用により除去することとし、これら
(11〜(3)の方法を一つのシステムとしたのが本発
明の特徴である。The present inventors believe that among malodorous components, hydrogen sulfide, methyl mercaptan, methyl sulfide, etc. can be removed by the ozone-catalyst method, and at the same time ammonia and hydrocarbons can be removed.
We believe that not only will the odor removal effect be improved, but the life of the catalyst will also be extended and the overall performance improved. Therefore, (1) hydrocarbons in the target gas to be treated, which cause a decrease in catalyst activity and shorten the catalyst life, are removed in front of the catalyst layer using an activated carbon filter, and (2) ammonia, which has poor reactivity with ozone, is is removed before the catalyst layer by a solid acid adsorbent layer, and 13+ hydrogen k hydride, methyl mercaptan,
Odor components such as methyl sulfide are removed by injecting ozone and using the oxidizing power of ozone and the action of a catalyst, and it is a feature of the present invention that these methods (11 to (3)) are combined into one system. .
第1図に本発明からなる悪臭除去装置フロー図を示す。FIG. 1 shows a flow diagram of the malodor removal apparatus according to the present invention.
ここで、悪臭を含む原ガスGは炭化水素除去用活性炭フ
ィルタ一層1を通過したのち、オゾン発生機2からオゾ
ン化空気分岐コック3を経て送られてくるオゾン化空気
0.− Aと共に、固体酸吸着剤を充填した塔4を通過
し、オゾン化空気分岐コック3を経て送られてくるオゾ
ン化空気と共に、ガス調湿器5から送られてくる水分H
,Oと混合して、ガス混合槽6に入る。つぎに、触媒反
応器7に送られて悪臭成分、 〕λ1 :1気L1を
通過し−(人気内 ム1〜ガスとして放出される。Here, the raw gas G containing a bad odor passes through the activated carbon filter layer 1 for removing hydrocarbons, and then the ozonized air is sent from the ozone generator 2 through the ozonized air branch cock 3. - Moisture H sent from the gas humidifier 5 together with the ozonized air that passes through the column 4 filled with solid acid adsorbent and is sent via the ozonized air branch cock 3 together with A.
, O and enters the gas mixing tank 6. Next, the malodorous components are sent to the catalytic reactor 7, pass through L1, and are released as a gas.
排風機8により誘引された悪臭ガスは、炭化水素除去用
活性炭フィルタ一層1を通過する際、ガス中の含まれる
悪臭成分とは無関係の炭化水素、例えばn−ヘキサン、
ヘプタン、オクタン、デカンなどが吸着・除去される。When the malodorous gas induced by the exhaust fan 8 passes through the activated carbon filter layer 1 for removing hydrocarbons, it removes hydrocarbons unrelated to the malodorous components contained in the gas, such as n-hexane,
Heptane, octane, decane, etc. are adsorbed and removed.
活性炭フィルタ一層1には、粒状もしくは破砕活性炭(
原材料としては、やしから、石炭、木炭、石油ピッチな
どがあげられる]が薄層(〜100m1m)に充填され
、パッケージ方式になって交換が容易な形式となってい
る。この活性炭フィルタ一層1では、80〜90チ以上
の06〜CI5からなる炭化水素類が除去されて、ガス
後流へ溢流することはない。Activated carbon filter layer 1 contains granular or crushed activated carbon (
Raw materials include palm, coal, charcoal, petroleum pitch, etc.] are filled in a thin layer (~100m1m) and packaged for easy replacement. In this activated carbon filter layer 1, 80 to 90 or more hydrocarbons consisting of 06 to CI5 are removed and do not overflow into the gas downstream.
つぎに、活性炭フィルタ一層1を通過した悪臭ガス中に
オゾン発生機2からオゾンを注入し、悪臭成分のうち、
硫化水素などのオゾンと反応性の高い成分とオゾンの気
相反応を促進させながら、固体酸吸着剤を充填した塔4
へ送る。Next, ozone is injected from an ozone generator 2 into the malodorous gas that has passed through the activated carbon filter layer 1, and among the malodorous components,
Column 4 packed with solid acid adsorbent while promoting gas phase reaction between ozone and components highly reactive with ozone such as hydrogen sulfide.
send to
固体酸吸着剤を充填した塔4には天然ゼオライト、合成
ゼオライト、アルミナ、シリカ−アルミナ、その他の多
孔質担体にリン酸、硫酸、kM酷等の無機酸類を5〜5
0重量%含浸した吸着剤が充填され、悪臭成分のうちの
アンモニアが吸着除去される。またこの塔4では、上記
オゾンと硫化水素などの成分が効果的に接触され、両者
の気相反応が進む。In the column 4 filled with a solid acid adsorbent, 5 to 5% of inorganic acids such as phosphoric acid, sulfuric acid, and KM chloride are added to a porous carrier such as natural zeolite, synthetic zeolite, alumina, silica-alumina, or other porous carrier.
It is filled with an adsorbent impregnated with 0% by weight, and ammonia among the malodorous components is adsorbed and removed. Further, in this column 4, the ozone and components such as hydrogen sulfide are brought into effective contact, and a gas phase reaction between the two proceeds.
ガス混合槽では、ガス調湿器で湿分調整された悪臭成分
とオゾンの混合が進み、悪臭成分の気相反応が更に促進
される。In the gas mixing tank, the malodorous components whose moisture content has been adjusted by the gas humidifier are mixed with ozone, and the gas phase reaction of the malodorous components is further promoted.
触媒反応器7には、例えば炭素質材料(例えば、粒状、
破砕状あるいは粉末状の活性炭、グラファイト、炭素繊
維等)からなる触媒担体上にバナジウム、クロム、マン
ガン、鉄、コバルト、ニッケル、銅、銀、亜鉛等の金属
酸化物の一種または二種以上を担持させたもの、必要に
応じてこれら金属酸化物と共に白金、パラジウム、ロジ
ウム、ルテニウム等を助触媒として担持させたもの等が
触媒として充填されている。The catalytic reactor 7 may contain, for example, a carbonaceous material (e.g. granular,
One or more metal oxides such as vanadium, chromium, manganese, iron, cobalt, nickel, copper, silver, zinc, etc. are supported on a catalyst carrier made of crushed or powdered activated carbon, graphite, carbon fiber, etc. The catalyst is filled with a catalyst in which platinum, palladium, rhodium, ruthenium, etc. are supported as a co-catalyst along with these metal oxides as necessary.
ガス混合槽6を通過したガスが触媒反応器7を通過する
とき、未反応悪臭成分とオゾンとの反応が完結され、同
時に余剰オゾンの自己分解が完結される。When the gas that has passed through the gas mixing tank 6 passes through the catalytic reactor 7, the reaction between the unreacted malodorous components and ozone is completed, and at the same time, the self-decomposition of excess ozone is completed.
本発明方法により次のような効果が奏される。The method of the present invention provides the following effects.
■ 悪臭ガス中に含まれる炭化水素類は、悪臭成分とは
ならず臭気問題とはならないが、前記触媒表面に吸着し
て蓄積しやすく、触媒氷面上を被覆して触媒の活性を著
しく低下する(触媒寿命を短くする)傾向にある。本発
明における炭化水素除去用フィルターは、この炭化水素
類を触媒反応器以前で予め除去し、触媒表面への吸着を
僅少社に抑えて、触媒活性の低下を防止し、かつ触媒寿
命を擾くする効果がある。■ Hydrocarbons contained in malodorous gas do not become malodorous components and do not pose an odor problem, but they tend to adsorb and accumulate on the catalyst surface, coating the catalyst ice surface and significantly reducing catalyst activity. (shorten catalyst life). The hydrocarbon removal filter of the present invention removes these hydrocarbons in advance before the catalyst reactor, suppresses adsorption to the catalyst surface to a minimum, prevents a decrease in catalyst activity, and shortens the catalyst life. It has the effect of
■ 悪臭ガス中の塵埃もこの炭化水素除去フィルターで
除去されるため、後流側の触媒反応器が塵埃によって汚
染されることもなくなる。■ Since dust in the foul-smelling gas is also removed by this hydrocarbon removal filter, the catalytic reactor on the downstream side will not be contaminated by dust.
■ 原ガス中のアンモニアは固体酸吸着剤表面に吸着固
定されるため、水洗もしくは薬洗によるアンモニア吸収
除去と同じ効果が得られるばかりでなく、原ガス中の塵
埃もこの固体酸吸着剤層で史vc除去されるため、後流
側の触媒反応器が塵挨によって汚染されることもなくな
るという効果を奏する。■ Since ammonia in the raw gas is adsorbed and fixed on the surface of the solid acid adsorbent, not only can the same effect as ammonia absorption and removal by washing with water or chemical cleaning be obtained, but also dust in the raw gas can be removed by this solid acid adsorbent layer. Since the dust is removed, the catalytic reactor on the downstream side is not contaminated by dust.
■ 悪臭成分を含む原ガスを水洗もしくは薬液洗浄する
ことなく、オゾン−触媒法によって、無臭になるまで処
理でき(悪臭除去効果の向上)かつ、触媒寿命を廷ばす
ことによって運転費の低減を図ることができる。■ Raw gas containing malodorous components can be treated until it becomes odorless using the ozone-catalyst method without washing with water or chemicals (improving the odor removal effect), and reducing operating costs by extending the life of the catalyst. be able to.
例1
下水処理場のうちの沈砂池、最初沈殿池、暖気槽および
汚泥処理室から発生する悪臭ガス中に含まれる炭化水素
類のうち08以上の成分について濃度測定した結果、メ
チルへブタン、n−オクタン、メチルオクタン、トリメ
チルシクロヘキサン、n−ノナン、n−デカン、ジメチ
ルシクロオクタン、5メチル/ナン、n−ブチルシクロ
ヘキサノンおよびC11以上の未同定成分が、0、00
1〜1 ppmの濃度で検出された。Example 1 As a result of measuring the concentration of 08 or more components of hydrocarbons contained in the foul-smelling gas generated from the settling tank, primary settling tank, warming tank, and sludge treatment room in a sewage treatment plant, methyl hebutane, n -Octane, methyloctane, trimethylcyclohexane, n-nonane, n-decane, dimethylcyclooctane, 5-methyl/nan, n-butylcyclohexanone, and unidentified components of C11 or higher are 0,00
It was detected at a concentration of 1-1 ppm.
このガスを粒状(4〜6メツシユ)ヤシガラ活性炭を充
填したioowm厚さの炭化水素除去用フィルターに通
したところ、フィルター後流ガス中の上記成分濃度は0
.0001 ppm以下まで低減され、炭化水素除去用
フィルターに効率よく吸着された。When this gas was passed through an ioowm thick hydrocarbon removal filter filled with granular (4 to 6 mesh) coconut shell activated carbon, the concentration of the above components in the gas downstream of the filter was 0.
.. The amount was reduced to 0,001 ppm or less, and was efficiently adsorbed on the hydrocarbon removal filter.
例2
6〜10關φに成形したペレット状ケイソウ土に硫酸を
0.5.10及び20重量%担持させた固体酸吸着剤に
100 ppmのアンモニアガスを通した。Example 2 100 ppm of ammonia gas was passed through a solid acid adsorbent in which 0.5.10% and 20% by weight of sulfuric acid was supported on pellets of diatomaceous earth formed to a diameter of 6 to 10 mm.
結果は第2図に示す通りであった。The results were as shown in Figure 2.
第2図から明らかなように、5重量%以りで効果がある
が、余り多駒ぎても不経済であるため、酸の含浸量は5
〜50加置チとすればよいことが判る。As is clear from Figure 2, the amount of acid impregnated is 5% by weight or more, which is effective, but it is uneconomical to use too many pieces.
It turns out that it is sufficient to add 50 points.
例5
下水処理施設のうち、沈砂池、最初沈殿池、曝気槽およ
び汚泥処理室から発生する悪臭を排風機(500Nm3
/min )で吸引し、第1図に示すフローシートに沿
って脱臭した。Example 5 In a sewage treatment facility, a ventilation fan (500Nm3
/min) and deodorized according to the flow sheet shown in FIG.
炭化水素除去用活性炭フィルターには、粒状やしがら活
性炭(4〜6メツシユ)を1001充填し、0.4 m
/secの流速でガスを流した。The activated carbon filter for removing hydrocarbons is filled with 1,001 pieces of granular coconut shell activated carbon (4 to 6 meshes) and is 0.4 m thick.
The gas was flowed at a flow rate of /sec.
アンモニア除去用固体酸吸着剤には、10重置−硫酸担
持ケイソウ土を6〜1011jlφに成形したペレット
を150111111充填し、0.4 Ill / S
eeの流速でガスを流した。触媒としては、酸化マンガ
ン担持活性炭を使用した。オゾンは、炭化水素除去用活
性炭フィルタ一層1後流直後に2ppm、固体酸g&着
剤充填塔4直後に1 ppm注入した。The solid acid adsorbent for ammonia removal was filled with 150111111 pellets formed from 10-layered diatomaceous earth supported on sulfuric acid to a size of 6 to 1011 jlφ, and 0.4 Ill/S.
Gas was flowed at a flow rate of ee. Activated carbon supporting manganese oxide was used as a catalyst. Ozone was injected at 2 ppm immediately after the layer 1 of the activated carbon filter for removing hydrocarbons, and 1 ppm was injected immediately after the column 4 packed with solid acid and adhesive.
結果は下表に示すとおりであった。The results were as shown in the table below.
また運転開始後8000時間における悪臭成分除去効果
は例えば、硫化水素については、となり、高い脱臭効果
の維持されていることが確認された。Furthermore, the effect of removing malodorous components, for example, hydrogen sulfide, after 8000 hours from the start of operation was as follows, confirming that a high deodorizing effect was maintained.
第1図は本発明方法の一実IN態様を示すフローシート
であり、第2図は本発明方法で用いられる固体酸g&着
剤充填塔における酸担持量とアンモニア除去量との関係
を示すグラフである。
復代理人 内 1) 明
復代理人 萩 原 亮 −Figure 1 is a flow sheet showing an actual IN mode of the method of the present invention, and Figure 2 is a graph showing the relationship between the amount of acid supported and the amount of ammonia removed in the solid acid g & adhesive packed column used in the method of the present invention. It is. Sub-agents 1) Meifuku agent Ryo Hagiwara -
Claims (1)
性炭フィルタ一層および固体酸吸着剤充填塔を設置して
、悪臭成分を含訃原ガス中に含まれる炭化水素類および
アンモニアを除去したのち、オゾン−触媒法により悪臭
除去することを特徴とする悪臭除去方法。When removing bad odors using ozone, a single layer of activated carbon filter and a column packed with solid acid adsorbent are installed in front of the catalytic reactor to remove hydrocarbons and ammonia contained in the raw gas containing bad odor components, and then ozone is removed. - A method for removing a bad odor, characterized by removing the bad odor by a catalytic method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57006746A JPS58124524A (en) | 1982-01-21 | 1982-01-21 | Removal of malodorous component |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57006746A JPS58124524A (en) | 1982-01-21 | 1982-01-21 | Removal of malodorous component |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS58124524A true JPS58124524A (en) | 1983-07-25 |
Family
ID=11646759
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP57006746A Pending JPS58124524A (en) | 1982-01-21 | 1982-01-21 | Removal of malodorous component |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS58124524A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4806032A (en) * | 1987-05-11 | 1989-02-21 | Hewlett-Packard Company | Conical vent containing capillary bore |
JPH04313320A (en) * | 1991-01-31 | 1992-11-05 | Daikin Ind Ltd | Deodorizing device |
-
1982
- 1982-01-21 JP JP57006746A patent/JPS58124524A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4806032A (en) * | 1987-05-11 | 1989-02-21 | Hewlett-Packard Company | Conical vent containing capillary bore |
JPH04313320A (en) * | 1991-01-31 | 1992-11-05 | Daikin Ind Ltd | Deodorizing device |
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