JP2003210930A - Deodorization method - Google Patents

Deodorization method

Info

Publication number
JP2003210930A
JP2003210930A JP2002012330A JP2002012330A JP2003210930A JP 2003210930 A JP2003210930 A JP 2003210930A JP 2002012330 A JP2002012330 A JP 2002012330A JP 2002012330 A JP2002012330 A JP 2002012330A JP 2003210930 A JP2003210930 A JP 2003210930A
Authority
JP
Japan
Prior art keywords
honeycomb
activated carbon
acid
deodorizing
shaped activated
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
Application number
JP2002012330A
Other languages
Japanese (ja)
Inventor
Seiichi Amano
成一 天野
Norio Aibe
紀夫 相部
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.)
NIKKO PLANT KK
Original Assignee
NIKKO PLANT KK
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 NIKKO PLANT KK filed Critical NIKKO PLANT KK
Priority to JP2002012330A priority Critical patent/JP2003210930A/en
Publication of JP2003210930A publication Critical patent/JP2003210930A/en
Pending legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for efficiently deodorizing the exhaust gas from a garbage treatment machine over a long period of time at a low running cost using a compact device. <P>SOLUTION: The exhaust gas from the garbage treatment machine is brought into contact with honeycomb activated carbon, especially chemicals supported honeycomb activated carbon at 50-150°C at a gas spatial velocity of 15,000/hr or more. <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、生ゴミ処理機から
の排ガスを低ランニングコストで長期に亘り効率よく脱
臭する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for efficiently deodorizing exhaust gas from a garbage processor at a low running cost for a long period of time.

【0002】[0002]

【従来の技術】生ゴミ処理機からの排ガスには、硫化水
素、メチルメルカプタンなどの硫黄系化合物、アンモニ
ア、アミン類などの窒素含有化合物、ホルマリン、アセ
トアルデヒドなどのアルデヒド類など各種の臭気成分が
含まれており、しかも臭気成分濃度、温度、湿度など
は、経時的に大きく変化するので脱臭が難しい。この生
ゴミ処理機からの排ガスを脱臭処理する方法として、こ
れまでにも種々の方法、例えば、触媒燃焼法、オゾン脱
臭法、薬液洗浄法、粒状活性炭吸着法などが提案されて
いる。触媒燃焼法は、排ガスを触媒の存在下に約300
℃に加熱する方法であるが、触媒が劣化するのでランニ
ングコストが高くなる。オゾン脱臭法は、排ガスに含ま
れる臭気成分の種類および濃度に対応してオゾン量を調
整したり、未反応オゾンを分解したりする必要がある。
薬液洗浄法は、所定量の薬液を常時供給しなければなら
ず、また洗浄後の薬液の処理が必要である。粒状活性炭
吸着法は、吸着効率が低いので多量の活性炭を使用しな
ければならず、また圧力損失が大きく、ガスの偏流が起
こりやすい。しかも生ゴミ処理機の排ガスのように高湿
度ガスでは、脱臭効率がさらに低くなり、高温ガスの接
触で発熱、発火の危険性もある。これらいずれの方法も
脱臭装置が大型なものとなり、かつ維持管理が大変であ
る。
2. Description of the Related Art Exhaust gas from garbage processing equipment contains various odorous components such as hydrogen sulfide, sulfur-based compounds such as methyl mercaptan, nitrogen-containing compounds such as ammonia and amines, and aldehydes such as formalin and acetaldehyde. In addition, the concentration of odorous components, temperature, humidity, etc. change significantly over time, making deodorization difficult. Various methods such as a catalytic combustion method, an ozone deodorizing method, a chemical cleaning method, and a granular activated carbon adsorption method have been proposed as methods for deodorizing the exhaust gas from the garbage treatment machine. The catalytic combustion method uses exhaust gas in the presence of a catalyst of about 300
Although this is a method of heating to ℃, the running cost becomes high because the catalyst deteriorates. In the ozone deodorization method, it is necessary to adjust the amount of ozone in accordance with the type and concentration of odorous components contained in exhaust gas and to decompose unreacted ozone.
In the chemical cleaning method, a predetermined amount of chemical solution must be constantly supplied, and the chemical solution after cleaning must be treated. Since the granular activated carbon adsorption method has a low adsorption efficiency, a large amount of activated carbon must be used, the pressure loss is large, and gas drift is likely to occur. Moreover, dehumidification efficiency is further reduced with high-humidity gas such as exhaust gas from a garbage treatment machine, and there is a risk of heat generation and ignition due to contact with high-temperature gas. Both of these methods require a large deodorizing device and are difficult to maintain.

【0003】[0003]

【発明が解決しようとする課題】本発明の目的は、生ゴ
ミ処理機からの排ガスの脱臭方法として、コンパクトな
装置を用い、維持管理が容易で、ランニングコストが安
く、かつ長期に亘って良好な脱臭効率が発揮される方法
を提供することにある。
SUMMARY OF THE INVENTION An object of the present invention is to use a compact device as a method for deodorizing exhaust gas from a garbage treatment machine, easy to maintain and maintain, low running cost, and good for a long period of time. The object of the present invention is to provide a method of exhibiting excellent deodorizing efficiency.

【0004】[0004]

【課題を解決するための手段】本発明者らは、生ゴミ処
理機排ガスの脱臭方法について種々検討した結果、生ゴ
ミ処理機排ガスを、ハニカム状活性炭層に適度の高温
下、高ガス空間速度で接触させることによって効率よく
脱臭できることを見出し本発明を完成した。すなわち本
発明は、(1)生ゴミ処理機からの排ガスを温度50〜
150℃、ガス空間速度15,000/時以上でハニカ
ム状活性炭に接触させる脱臭方法、(2)ハニカム状活
性炭のセル数が、10〜1,500個/inch2であ
る(1)記載の脱臭方法、(3)ハニカム状活性炭のB
ET比表面積が、200m2/g以上である(1)記載
の脱臭方法、(4)ガス空間速度が15,000〜50
0,000/時である(1)記載の脱臭方法、(5)ハ
ニカム状活性炭が、薬品担持ハニカム状活性炭である脱
臭方法、(6)ハニカム状活性炭に担持する薬品が、ヨ
ウ素、無機ヨウ化物、臭素、無機臭化物、酸、白金族化
合物、Ti、V、Cr、Mn、Fe、Co、Ni、CuおよびAgの化合
物から選ばれた少なくとも1種類である(5)記載の脱
臭方法、(7)使用により脱臭性能が低下したハニカム
状活性炭に散水して、再び生ゴミ処理機からの排ガスの
脱臭処理を行う(1)記載の脱臭方法、である。
Means for Solving the Problems As a result of various studies on the deodorizing method of the exhaust gas of the raw garbage treating machine, the present inventors have found that the exhaust gas of the raw garbage treating machine is applied to the honeycomb-like activated carbon layer at a high temperature and a high gas space velocity. The present invention has been completed by discovering that deodorization can be efficiently performed by contacting with. That is, the present invention provides (1) the exhaust gas from the garbage treatment device at a temperature of 50 to
Deodorizing method of contacting with honeycomb-shaped activated carbon at 150 ° C. and gas space velocity of 15,000 / hour or more, (2) Deodorization according to (1), wherein the number of cells of honeycomb-shaped activated carbon is 10 to 1,500 cells / inch 2. Method (3) Honeycomb-shaped activated carbon B
(1) The deodorizing method according to (1), wherein the ET specific surface area is 200 m 2 / g or more, and (4) the gas space velocity is 15,000 to 50.
The deodorizing method according to (1), which is 10,000 / hour, (5) the deodorizing method in which the honeycomb-shaped activated carbon is a chemical-supporting honeycomb-shaped activated carbon, and (6) the chemical supported on the honeycomb-shaped activated carbon is iodine or an inorganic iodide. , Bromine, inorganic bromide, acid, platinum group compound, Ti, V, Cr, Mn, Fe, Co, Ni, Cu and Ag compounds (5). ) The deodorizing method according to (1), wherein the honeycomb-like activated carbon whose deodorizing performance has deteriorated due to use is sprinkled with water, and the deodorizing treatment of the exhaust gas from the garbage treatment machine is performed again.

【0005】[0005]

【発明の実施の形態】本発明では、生ゴミ処理機からの
排ガスを温度50〜150℃、好ましくは60〜150
℃、ガス空間速度15,000/時以上、好ましくは1
5,000〜500,000/時でハニカム状活性炭に
接触させて脱臭する。ハニカム状活性炭に対する排ガス
の線流速は通常0.3〜10m/sec.好ましくは
0.5〜7m/sec.である。このような条件でハニ
カム状活性炭を使用することによって比較的高い温度、
高い湿度、高いガス空間速度、高い線流速でも効率よく
脱臭できる。
BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, exhaust gas from a garbage treatment machine is heated at a temperature of 50 to 150 ° C., preferably 60 to 150.
℃, gas space velocity 15,000 / hour or more, preferably 1
The honeycomb-like activated carbon is contacted at 5,000 to 500,000 / hour for deodorization. The linear velocity of the exhaust gas with respect to the honeycomb-shaped activated carbon is usually 0.3 to 10 m / sec. Preferably 0.5 to 7 m / sec. Is. Relatively high temperature by using honeycomb activated carbon under such conditions,
It can deodorize efficiently even at high humidity, high gas space velocity, and high linear flow velocity.

【0006】本発明におけるハニカム状活性炭として
は、たとえば特公昭57−95816号公報に記載され
ているような公知のハニカム状活性炭が使用でき、たと
えば、以下のような方法で製造される。第一の製法で
は、微粉末である木炭、石炭、コークス、オガクズ、樹
脂などの原料にピッチ、粘土鉱物などの結合剤アルカリ
金属塩などの賦活剤を加え、水と共に練合し、ハニカム
状に成型する。この後、通常の方法で炭化し、賦活する
と本発明に使用するハニカム状活性炭が得られる。
As the honeycomb-like activated carbon in the present invention, a known honeycomb-like activated carbon as described in, for example, Japanese Patent Publication No. 57-95816 can be used, and it is produced by the following method. In the first method, charcoal, which is a fine powder, coal, coke, sawdust, resin, and other raw materials are added with activators such as pitch, clay minerals and other binder alkali metal salts, and kneaded with water to form a honeycomb shape. Mold. After that, the honeycomb-like activated carbon used in the present invention is obtained by carbonizing and activating by a usual method.

【0007】第二の製法は、上記の第一の製法で得られ
たハニカム状活性炭を必要に応じて、酸、水などで洗浄
処理することにより得られる。
The second manufacturing method is obtained by washing the honeycomb-shaped activated carbon obtained by the above-mentioned first manufacturing method with acid, water or the like, if necessary.

【0008】第三の製法では、木炭、石炭、コークス、
ヤシガラ、オガクズなどの原料(必要に応じて結合剤、
賦活剤を添加し、円柱状、破砕状に成型する。)を通常
の方法で炭化し、賦活して必要に応じて酸、水などで洗
浄し、微粉砕した後、ピッチ、粘土鉱物などの結合剤を
加え水と共に練合し、ハニカム状に成型し、必要に応じ
て加熱処理することにより得られる。これらの方法によ
り本発明に使用するハニカム状活性炭が得られる。これ
らはいずれも活性炭が繊維状ではなく微粒子で構成され
ており、かつハニカム状の構造であるため、非常に緻密
な構造をしており、本発明の実施に最適である。本発明
に使用されるハニカム状活性炭は、活性炭含量が、30
%以上、好ましくは40%以上のもので、種々の結合剤
や多孔質粘度鉱物などを含有してもよい。
In the third method, charcoal, coal, coke,
Raw materials such as coconut husks and sawdust (if necessary, binder,
Add an activator and mold into a cylindrical or crushed shape. ) Is carbonized by a normal method, activated, washed with acid, water, etc. as needed, pulverized, and then a binder such as pitch and clay mineral is added and kneaded with water to form a honeycomb shape. It can be obtained by heat treatment if necessary. The honeycomb-like activated carbon used in the present invention can be obtained by these methods. In all of these, since the activated carbon is composed of fine particles instead of fibrous and has a honeycomb structure, it has a very dense structure and is most suitable for carrying out the present invention. The honeycomb-like activated carbon used in the present invention has an activated carbon content of 30.
% Or more, preferably 40% or more, and may contain various binders and porous clay minerals.

【0009】本発明に用いられるハニカム状活性炭のセ
ル数は、10〜1,500個/inch2、好ましく
は、50〜1,000個/inch2、より好ましくは
100〜750個/inch2である。ハニカムの開口
率は、50〜80%、好ましくは55〜75%程度であ
る。また、ハニカム状活性炭の比表面積は、200m2
/g以上、好ましくは、300〜3,500m2/g、
より好ましくは、400〜2,000m2/gである。
生ゴミ処理機から発生する臭気成分には例えば、硫黄含
有化合物(硫化水素、メチルメルカプタンなどのメルカ
プタン類、流化メチルなどのスルフィド類、二硫化メチ
ルなどのジスルフィド類など)、窒素含有化合物(アン
モニア、ジメチルアミン、トリメチルアミン、トリエチ
ルアミン等のアミン類など)、アルデヒド類(ホルムア
ルデヒド、アセトアルデヒドなど)、有機酸(ギ酸、酢
酸、プロピオン酸、酪酸、吉草酸など)などが含まれて
いる。被処理ガスは、通常、これらの臭気成分のうち少
なくとも一種の成分を含んでいる。臭気成分の濃度は特
に限定されず、例えば、0.1〜1,000ppm(容
量基準)程度であってもよい。
The number of cells of the honeycomb activated carbon used in the present invention is 10 to 1,500 cells / inch 2 , preferably 50 to 1,000 cells / inch 2 , and more preferably 100 to 750 cells / inch 2 . is there. The opening ratio of the honeycomb is 50 to 80%, preferably 55 to 75%. The specific surface area of the honeycomb-shaped activated carbon is 200 m 2
/ G or more, preferably 300 to 3,500 m 2 / g,
More preferably, it is 400 to 2,000 m 2 / g.
Examples of odorous components generated from garbage processing equipment include sulfur-containing compounds (hydrogen sulfide, mercaptans such as methyl mercaptan, sulfides such as methyl chloride, disulfides such as methyl disulfide), and nitrogen-containing compounds (ammonia. , Dimethylamine, trimethylamine, triethylamine, etc.), aldehydes (formaldehyde, acetaldehyde, etc.), organic acids (formic acid, acetic acid, propionic acid, butyric acid, valeric acid, etc.) and the like. The gas to be treated usually contains at least one of these odorous components. The concentration of the odorous component is not particularly limited and may be, for example, about 0.1 to 1,000 ppm (volume basis).

【0010】本発明では、ハニカム状活性炭に生ゴミ処
理機からの排ガスを温度50〜150℃で接触させて脱
臭するのが特徴の一つである。通常、排ガスの温度は常
温から徐々に昇温され、最終的には50〜150℃、好
ましくは60〜150℃、より好ましくは80〜130
℃とする。この変化に伴って、湿度も大きく変化する
が、本ハニカム状活性炭を用いることによって、ガス性
状の大幅な変動に対しても、脱臭性能は充分に追従でき
る。
One of the features of the present invention is that the exhaust gas from the garbage treatment machine is brought into contact with the honeycomb-shaped activated carbon at a temperature of 50 to 150 ° C. to deodorize. Usually, the temperature of the exhaust gas is gradually raised from room temperature, and finally 50 to 150 ° C, preferably 60 to 150 ° C, more preferably 80 to 130 ° C.
℃. With this change, the humidity also changes greatly, but by using the honeycomb-shaped activated carbon, the deodorizing performance can sufficiently follow even a large change in the gas properties.

【0011】本発明では、薬品無担持のハニカム状活性
炭でも、脱臭性能を十分発揮することができるが、処理
される生ゴミの種類や、生ゴミ処理の方式によっては生
ゴミ処理機からの排ガス中の臭気成分、温度、湿度など
が変動するので、薬品を担持したハニカム状活性炭を用
いることにより、これらの処理によりよく対応すること
ができる。
In the present invention, the deodorizing performance can be sufficiently exerted even with the honeycomb-like activated carbon which does not carry chemicals, but the exhaust gas from the garbage disposer depending on the kind of garbage to be treated and the method of garbage disposal. Since the odorous components, temperature, humidity and the like in the inside fluctuate, it is possible to better cope with these treatments by using a honeycomb-shaped activated carbon carrying a chemical.

【0012】薬品担持ハニカム状活性炭のうち、ヨウ素
及び無機ヨウ化物の担持ハニカム状活性炭は、ハニカム
状活性炭にヨウ素又は/及び無機ヨウ化物を担持するこ
とにより得られる。無機ヨウ化物には、I2O5、NH4I、金
属ヨウ化物などが含まれる。前記金属ヨウ化物として
は、例えば、LiI、NaI、NaIO3、KI、KI3、KIO3、RbI、C
sIなどのヨウ化アルカリ金属;CaI2、SrI2、BaI2、MgI2
などのヨウ化アルカリ土類金属;CuI、CuI2、AgIなどの
元素周期表Ib族金属のヨウ化物;ZnI2などの元素周期表
IIb族金属のヨウ化物;AlI3などの元素周期表III族金属
のヨウ化物CrI3などの元素周期表VI族金属のヨウ化物;
MnI2などの元素周期表VII族金属のヨウ化物;CoI2、NiI
2などの元素周期表VIII族金属のヨウ化物などが挙げら
れる。好ましい無機ヨウ化物には、I2O5、NH4I、KIO3
ヨウ化アルカリ金属、CoI2、NiI2、ZnI2などが含まれ
る。特に好ましい無機ヨウ化物には、ヨウ化アルカリ金
属、なかでもヨウ化カリウムが好ましい。ヨウ素、無機
ヨウ化物は一種または二種以上で使用できる。
Among the chemical-supporting honeycomb-shaped activated carbons, the honeycomb-shaped activated carbons supporting iodine and inorganic iodide are obtained by supporting iodine or / and inorganic iodide on the honeycomb-shaped activated carbon. Inorganic iodides include I 2 O 5 , NH 4 I, metal iodides, and the like. Examples of the metal iodide include LiI, NaI, NaIO 3 , KI, KI 3 , KIO 3 , RbI and C.
alkali metal iodide such as sI; CaI 2, SrI 2, BaI 2, MgI 2
Alkaline earth metal iodides; CuI, CuI 2 , AgI, etc. Periodic table Ib group metal iodides; ZnI 2, etc. Periodic table
Group IIb metal iodides; AlI 3 and other periodic tables Group III metal iodides such as CrI 3 Periodic Table VI and group metal iodides;
MnI 2 and other elements Periodic Table Group VII metal iodides; CoI 2 , NiI
The periodic table of elements such as 2 includes iodide of Group VIII metal. Preferred inorganic iodides include I 2 O 5 , NH 4 I, KIO 3 ,
Alkali metal iodides, CoI 2 , NiI 2 , ZnI 2 and the like are included. Particularly preferable inorganic iodides are alkali metal iodides, and potassium iodide is particularly preferable. One type or two or more types of iodine and inorganic iodide can be used.

【0013】ハニカム状活性炭へのヨウ素又は/及び無
機ヨウ化物の担持は慣用の方法で行なうことができる。
例えば、ヨウ素又は/及び無機ヨウ化物を、水、アルコ
ール類などの有機溶媒に溶解又は分散し、前記ハニカム
状活性炭に散布、含浸又は浸漬することにより担持して
もよく、活性炭を製造する際に、ヨウ素又は/及び無機
ヨウ化物を溶液や微粉末の形で原料として練合して成形
し、担持させてもよい。また、ヨウ素の場合にはKI、NH
4Iなどの水溶液に溶解して、散布、含浸又は浸漬するこ
とにより担持させてもよい。さらに、必要に応じて、ヨ
ウ素又は/及び無機ヨウ化物をハニカム状活性炭に担持
させた後、乾燥又は焼成してもよい。
The loading of iodine or / and inorganic iodide on the honeycomb-shaped activated carbon can be carried out by a conventional method.
For example, iodine or / and inorganic iodide may be dissolved or dispersed in an organic solvent such as water or alcohol, and may be carried by being sprayed, impregnated or dipped in the above honeycomb-like activated carbon. Alternatively, iodine or / and an inorganic iodide may be kneaded as a raw material in the form of a solution or a fine powder, shaped, and supported. In the case of iodine, KI, NH
It may be supported by being dissolved in an aqueous solution of 4 I or the like and then sprayed, impregnated or dipped. Further, if necessary, iodine or / and inorganic iodide may be supported on the honeycomb-shaped activated carbon, and then dried or fired.

【0014】ハニカム状活性炭に対するヨウ素又は/及
び無機ヨウ化物の担持量は、臭気成分の除去が損なわれ
ない範囲で選択でき、ヨウ素換算で、例えば、0.1〜
40重量%、好ましくは0.2〜20重量%、さらに好
ましくは0.4〜10重量%程度である。
The amount of iodine or / and inorganic iodide supported on the honeycomb-like activated carbon can be selected within a range that does not impair the removal of odorous components.
It is 40% by weight, preferably 0.2 to 20% by weight, more preferably 0.4 to 10% by weight.

【0015】臭素担持ハニカム状活性炭は、ハニカム状
活性炭に液体状の臭素、臭素を含有する臭化物の溶媒溶
液を散布、含浸、浸漬するか、気体状の臭素をハニカム
状活性炭に接触させることによって得られる。臭化物と
しては、例えば、臭化水素、臭化アンモニウム、アルカ
リ金属の臭化物(例えば、臭化カリウム)などが挙げら
れる。また、溶媒としては、水、アルコール類(例え
ば、メタノール、エタノールなど)、ケトン類(例え
ば、アセトンなど)、エーテル類(例えば、ジエチルエ
ーテルなど)、ハロゲン化炭化水素類(例えば、クロロ
ホルム、四塩化炭素、エチレンクロライドなど)やこれ
らの混合溶媒が例示される。ハニカム状活性炭に対する
臭素の担持量は1〜30重量%、好ましくは2〜20重
量%、特に好ましくは5〜15重量%である。
The bromine-supporting honeycomb-like activated carbon is obtained by spraying, impregnating or immersing liquid bromine or a solvent solution of bromide containing bromine on the honeycomb-like activated carbon, or by bringing gaseous bromine into contact with the honeycomb-like activated carbon. To be Examples of the bromide include hydrogen bromide, ammonium bromide, alkali metal bromide (eg, potassium bromide), and the like. As the solvent, water, alcohols (eg methanol, ethanol etc.), ketones (eg acetone etc.), ethers (eg diethyl ether etc.), halogenated hydrocarbons (eg chloroform, tetrachloride etc.) Carbon, ethylene chloride, etc.) and mixed solvents thereof are exemplified. The amount of bromine supported on the honeycomb-shaped activated carbon is 1 to 30% by weight, preferably 2 to 20% by weight, and particularly preferably 5 to 15% by weight.

【0016】酸担持ハニカム状活性炭は、前記ハニカム
状活性炭に酸を担持することにより得られる。酸として
は、例えば、リン酸、硫酸、硝酸などの無機酸、シュウ
酸、マロン酸、酒石酸、コハク酸、クエン酸、リンゴ
酸、グルタル酸などの有機酸が挙げられる。これらの酸
は一種又は二種以上使用できる。好ましい酸には、例え
ば、リン酸、シュウ酸、リンゴ酸などが含まれる。さら
に好ましい酸にはリン酸が含まれる。リン酸としては、
例えば、オルトリン酸、メタリン酸、ポリリン酸(ピロ
リン酸などの鎖状ポリリン酸、三メタリン酸、四メタリ
ン酸などの環状ポリリン酸、無限鎖状メタリン酸など)
などが挙げられる。特に好ましいリン酸にはオルトリン
酸が含まれる。リン酸は一種又は二種以上使用できる。
The acid-supporting honeycomb-shaped activated carbon is obtained by supporting an acid on the honeycomb-shaped activated carbon. Examples of the acid include inorganic acids such as phosphoric acid, sulfuric acid and nitric acid, and organic acids such as oxalic acid, malonic acid, tartaric acid, succinic acid, citric acid, malic acid and glutaric acid. These acids can be used alone or in combination of two or more. Preferred acids include, for example, phosphoric acid, oxalic acid, malic acid and the like. More preferred acids include phosphoric acid. As phosphoric acid,
For example, orthophosphoric acid, metaphosphoric acid, polyphosphoric acid (chain polyphosphoric acid such as pyrophosphoric acid, cyclic polyphosphoric acid such as trimetaphosphoric acid and tetrametaphosphoric acid, infinite chain metaphosphoric acid, etc.)
And so on. Particularly preferred phosphoric acid includes orthophosphoric acid. Phosphoric acid may be used alone or in combination of two or more.

【0017】ハニカム状活性炭への酸の担持も慣用の方
法により行うことができる。例えば、酸を水溶液又は分
散液の形態で前記ハニカム状活性炭に散布、含浸または
浸漬して担持させてもよく、ハニカム状活性炭を製造す
る際に、酸単独で又は酸水溶液、分散液を原料として練
合して成形し、担持させてもよい。また、必要に応じて
ハニカム状活性炭に酸を担持させた後、乾燥又は焼成し
てもよい。ハニカム状活性炭に対する酸の担持量は、例
えば、0.1〜60重量%、好ましくは0.2〜50重
量%、さらに好ましく5〜40重量%程度である。
The supporting of the acid on the honeycomb-shaped activated carbon can also be carried out by a conventional method. For example, an acid may be dispersed, impregnated or immersed in the honeycomb-shaped activated carbon in the form of an aqueous solution or a dispersion to carry the acid. When manufacturing the honeycomb-shaped activated carbon, the acid alone or the aqueous acid solution, the dispersion is used as a raw material. It may be kneaded, molded, and supported. If necessary, the honeycomb-shaped activated carbon may be loaded with an acid and then dried or fired. The amount of acid supported on the honeycomb-like activated carbon is, for example, 0.1 to 60% by weight, preferably 0.2 to 50% by weight, and more preferably 5 to 40% by weight.

【0018】白金族元素としては、例えば、白金、イリ
ジウム、オスミウム、パラジウム、ロジウム、ルテニウ
ムが挙げられ、これら白金族元素化合物のハニカム状活
性炭に対する担持量は、白金族元素として0.01〜2
0重量%、好ましくは0.025〜15重量%、特に好
ましくは0.05〜10重量%である。
Examples of the platinum group element include platinum, iridium, osmium, palladium, rhodium and ruthenium. The loading amount of these platinum group element compounds on the honeycomb-shaped activated carbon is 0.01 to 2 as the platinum group element.
It is 0% by weight, preferably 0.025 to 15% by weight, particularly preferably 0.05 to 10% by weight.

【0019】白金族元素化合物担持ハニカム状活性炭は
ハニカム状活性炭に白金族元素化合物の塩酸、ヨウ化水
素、臭化水素、フッ酸、硝酸、硫酸、リン酸などの水溶
液を散布、含浸、浸漬することによって得られ、またハ
ニカム状活性炭を製造する際に、これらの白金族元素化
合物の酸水溶液の形で原料と練合して成形することによ
っても得られる。必要に応じて乾燥又は焼成してもよ
い。その際の温度は、40〜500℃、好ましくは50
〜400℃、特に好ましくは60〜350℃であり、そ
の際の雰囲気は減圧下、常圧下、加圧下のいずれでもよ
く、空気、窒素、炭酸ガス、燃焼ガスなどの存在下で行
なうことができる。Ti、V、Cr、Mn、Fe、Co、Ni、Cuま
たはAgの金属の化合物としては、それらの金属の水溶性
無機塩、たとえば硝酸塩、硫酸塩、アンモニウム塩など
が挙げられる。これらの金属化合物担持ハニカム状活性
炭は、白金族元素化合物を担持した薬品担持ハニカム状
活性炭と同様の方法で製造できる。この場合、金属化合
物の添加比率は、金属として、0.5〜15重量%、好
ましくは1.0〜10重量%である。得られた金属化合
物は必要に応じて乾燥又は焼成してもよい。その場合の
温度は、40〜500℃、好ましくは50〜400℃、
特に好ましくは60〜350℃であり、その際の雰囲気
は減圧下、常圧下、加圧下のいずれでもよく、空気、窒
素、炭酸ガス、燃焼ガスなどの存在下で行うことができ
る。
The platinum-group element compound-supporting honeycomb-shaped activated carbon is sprayed, impregnated, and dipped into the honeycomb-shaped activated carbon with an aqueous solution of a platinum-group element compound such as hydrochloric acid, hydrogen iodide, hydrogen bromide, hydrofluoric acid, nitric acid, sulfuric acid, and phosphoric acid. It can also be obtained by kneading with a raw material in the form of an aqueous acid solution of these platinum group element compounds when manufacturing a honeycomb-shaped activated carbon. You may dry or bake as needed. The temperature at that time is 40 to 500 ° C., preferably 50.
To 400 ° C., particularly preferably 60 to 350 ° C., and the atmosphere at that time may be any of reduced pressure, normal pressure and increased pressure, and it can be carried out in the presence of air, nitrogen, carbon dioxide gas, combustion gas and the like. . Examples of the metal compound of Ti, V, Cr, Mn, Fe, Co, Ni, Cu or Ag include water-soluble inorganic salts of these metals, such as nitrates, sulfates and ammonium salts. These metal compound-supporting honeycomb-shaped activated carbons can be manufactured by the same method as the chemical-supporting honeycomb-shaped activated carbons supporting the platinum group element compound. In this case, the addition ratio of the metal compound is 0.5 to 15% by weight, preferably 1.0 to 10% by weight, as metal. The obtained metal compound may be dried or calcined if necessary. The temperature in that case is 40 to 500 ° C., preferably 50 to 400 ° C.,
The temperature is particularly preferably 60 to 350 ° C., and the atmosphere at that time may be any of reduced pressure, normal pressure, and increased pressure, and it can be performed in the presence of air, nitrogen, carbon dioxide gas, combustion gas, or the like.

【0020】本発明の実施に際し、ハニカム状活性炭
は、脱臭塔などの通気可能な脱臭装置内に積層(充填)
して使用できる。ハニカム状活性炭は、ガスの流通方向
とハニカム状活性炭の通気孔(開孔部)とが同じ方向に
なるように積層される。ハニカムは1個のハニカムで形
成してもよく、複数個のハニカムで形成してもよい。複
数個のハニカムは、必要に応じて厚み方向とともに、縦
及び/又は横方法に廃してもよい。また、厚み方向に複
数のハニカムを配設する場合、隣接するハニカムのセル
は互いに位置をずらしてもよい。本発明の方法は従って
脱臭処理を続けるうち、ハニカム状活性炭の悪臭成分の
吸着能は次第に低下してくるが、その場合、ハニカム状
活性炭に散水することにより、活性炭の吸着力を再生さ
せることができる。すなわち、たとえば被処理ガスの入
り口および処理ガスの出口を備えた脱臭装置の充填層に
水(水及び/又は薬品を含む水など)を間欠的に散布し
ながら、臭気成分含有被処理ガス(特に臭気成分を含有
する空気)を通気し、臭気成分をハニカム状活性炭に接
触させることにより、長期に亘り効率よく脱臭すること
ができる。散布する水の量は、散水の頻度にもよるが、
通常ハニカム状活性炭の体積の1/2〜5倍量程度であ
る。本発明に使用されるハニカム状活性炭、特に薬品担
持ハニカム状活性炭は、単位体積当たりのガス吸着能が
高いので、装置としてコンパクトなものを使用すること
ができる。
In carrying out the present invention, the honeycomb-shaped activated carbon is laminated (filled) in a ventilated deodorizing device such as a deodorizing tower.
Can be used. The honeycomb-like activated carbon is laminated so that the gas flow direction and the ventilation holes (opening portions) of the honeycomb-like activated carbon are in the same direction. The honeycomb may be formed of one honeycomb or plural honeycombs. The plurality of honeycombs may be disposed in a longitudinal and / or lateral method along with the thickness direction as necessary. When a plurality of honeycombs are arranged in the thickness direction, the cells of adjacent honeycombs may be displaced from each other. According to the method of the present invention, therefore, while the deodorizing treatment is continued, the adsorption ability of the malodorous component of the honeycomb-like activated carbon gradually decreases. In that case, the adsorbing power of the activated carbon can be regenerated by sprinkling water on the honeycomb-like activated carbon. it can. That is, for example, while intermittently spraying water (water containing water and / or chemicals, etc.) on a packed bed of a deodorizing device equipped with an inlet for a treated gas and an outlet for a treated gas, the treated gas containing an odorous component (particularly, By aerating the air containing the odor component) and bringing the odor component into contact with the honeycomb-shaped activated carbon, it is possible to efficiently deodorize for a long period of time. The amount of water sprayed depends on the frequency of watering,
It is usually about 1/2 to 5 times the volume of the honeycomb-like activated carbon. Since the honeycomb-shaped activated carbon used in the present invention, particularly the chemical-supporting honeycomb-shaped activated carbon has a high gas adsorption capacity per unit volume, a compact device can be used.

【0021】[0021]

【実施例】以下に実施例をあげて本発明を具体的に説明
する。 実施例1 残飯、野菜クズ、肉類、魚類などを含む生ゴミ約10k
gを生ゴミ処理機に入れ、送風・攪拌しながら電気ヒー
ターで加熱した。処理機からの排ガス量は、約2.5〜
3.0m3/分(25℃ 1気圧換算)であった。この排
ガスをBET比表面積900m2/g、セル数300個
/inch2、厚み30mmのハニカム状活性炭に流通
し、脱臭した。この際のハニカム状活性炭層に対するガ
ス空間速度は、100,000〜120,000/時
(25℃1気圧換算)であった。生ゴミ処理機の運転に
伴って、排ガスの温度は7時間で20℃から100℃ま
で上昇した。その間、ハニカム状活性炭層の出入口ガス
を臭気濃度で評価した結果、カラム入口ガスの臭気濃度
は100〜1,000まで変化したが、出口ガスの臭気
濃度は50以下であった。テスト終了後、生ゴミ処理機
から、約3Kgの無臭の粉末状の乾燥物が得られた。
EXAMPLES The present invention will be specifically described with reference to the following examples. Example 1 Approximately 10 k of raw garbage including leftover food, scraps of vegetables, meat, fish, etc.
g was put in a garbage disposal and heated with an electric heater while blowing and stirring. The amount of exhaust gas from the processor is about 2.5-
It was 3.0 m 3 / min (converted at 25 ° C. and 1 atm). This exhaust gas was passed through a honeycomb activated carbon having a BET specific surface area of 900 m 2 / g, a number of cells of 300 cells / inch 2 , and a thickness of 30 mm to deodorize. At this time, the gas hourly space velocity for the honeycomb-shaped activated carbon layer was 100,000 to 120,000 / hour (calculated at 25 ° C. and 1 atmosphere). The temperature of the exhaust gas increased from 20 ° C. to 100 ° C. in 7 hours with the operation of the garbage processing machine. Meanwhile, as a result of evaluating the odor concentration of the inlet / outlet gas of the honeycomb-shaped activated carbon layer, the odor concentration of the column inlet gas changed from 100 to 1,000, but the odor concentration of the outlet gas was 50 or less. After the test was completed, about 3 kg of an odorless powdery dried product was obtained from the garbage processing machine.

【0022】実施例2 (1)ハニカム状活性炭の調製 BET比表面積810m2/g、セル数300個/in
ch2、開口率67%、直径27mm、厚さ30mmの
ハニカム状活性炭を活性炭Aとした。塩化パラジウム
3.5gを4%硝酸水溶液100mlに溶解した。この
溶液の所定量を、前記ハニカム状活性炭AにPd−20
mg/g、HNO−40mgとなる量を均一に散布し
て添着させた。このハニカム状活性炭を空気中、140
℃で5時間乾燥した。乾燥中、HNOの大部分は分解
してハニカム状活性炭から脱離し、Pd−20mg/g
担持ハニカム状活性炭Bが得られた。塩化パラジウム
3.5g、硝酸銅6水塩14.8g、リン酸1.1gを
4%硝酸水溶液100mlに溶解した。この溶液の所定
量を前記ハニカム状活性炭Aに均一に散布して、Pd−
20mg/g、Cu−30mg/g、HNO−40m
g/g、HPO−10mg/gを添着させた。この
活性炭を空気中、140℃で5時間乾燥することにより
Pd−20mg/g、Cu−30mg/g、HPO
−10mg/g担持ハニカム状活性炭Cが得られた。 (2)脱臭実験 レストランからの食品残渣30Kgを生ゴミ処理機に入
れ、送風、攪拌しながら処理した。処理機の運転に伴っ
て、処理機からの排ガスの温度は、9時間で25℃から
130℃まで上昇した。内径27mmのカラムを4本用
意し、(1)で調製したハニカム状活性炭A,Bおよび
Cのそれぞれを別々のカラムに90mm積層し、1本は
ハニカム状活性炭を収容しなかった。前記生ゴミ処理機
からの排ガスを前記A、BおよびCのハニカム状活性炭
積層カラムおよび活性炭を収容しなかったカラムのそれ
ぞれに、50リットル/分(25℃、1気圧換算、線流
速約1.5m/秒、空間速度約60,000/時)流通
し、脱臭効果をみた。 (3)脱臭試験結果 各カラムにおける出口ガスを臭気濃度で評価し、その結
果を表1に示した。
Example 2 (1) Preparation of honeycomb-like activated carbon BET specific surface area 810 m 2 / g, cell number 300 cells / in
A honeycomb-shaped activated carbon having a ch 2 , an aperture ratio of 67%, a diameter of 27 mm and a thickness of 30 mm was designated as activated carbon A. 3.5 g of palladium chloride was dissolved in 100 ml of 4% nitric acid aqueous solution. A predetermined amount of this solution was added to the above-mentioned honeycomb-shaped activated carbon A with Pd-20.
The amounts of mg / g and HNO 3 -40 mg were evenly dispersed and attached. This honeycomb-shaped activated carbon was heated to 140
It dried at 5 degreeC for 5 hours. During drying, most of HNO 3 is decomposed and desorbed from the honeycomb-like activated carbon, and Pd-20 mg / g
A supported honeycomb activated carbon B was obtained. 3.5 g of palladium chloride, 14.8 g of copper nitrate hexahydrate and 1.1 g of phosphoric acid were dissolved in 100 ml of a 4% aqueous nitric acid solution. A predetermined amount of this solution was evenly dispersed on the above-mentioned honeycomb-shaped activated carbon A, and Pd-
20 mg / g, Cu-30 mg / g, HNO 3 -40 m
g / g, the H 3 PO 4 -10mg / g were impregnated. This activated carbon was dried in air at 140 ° C. for 5 hours to obtain Pd-20 mg / g, Cu-30 mg / g, H 3 PO 4
-10 mg / g-supported honeycomb-like activated carbon C was obtained. (2) Deodorization Experiment 30 Kg of food residue from the restaurant was put in a garbage disposal and treated while blowing and stirring. With the operation of the processor, the temperature of the exhaust gas from the processor increased from 25 ° C to 130 ° C in 9 hours. Four columns having an inner diameter of 27 mm were prepared, and each of the honeycomb-shaped activated carbons A, B, and C prepared in (1) was laminated on a separate column for 90 mm, and one column did not contain the honeycomb-shaped activated carbon. The exhaust gas from the garbage treatment machine was supplied to the honeycomb-shaped activated carbon laminated columns A, B and C and the column not containing activated carbon at 50 liter / min (25 ° C., 1 atmospheric pressure conversion, linear flow rate of about 1. 5 m / sec, space velocity of about 60,000 / hour), and the deodorizing effect was observed. (3) Deodorization test result The outlet gas in each column was evaluated by the odor concentration, and the results are shown in Table 1.

【0023】[0023]

【表1】 表1から明らかなとおり、ハニカム状活性炭Aでも十分
な脱臭効果があるが、Pdを担持させることにより脱臭
性能は向上し、Pd−Cu−HPOを担持させるこ
とにより脱臭性能はさらに向上した。
[Table 1] As apparent from Table 1, although there is sufficient deodorizing effect can honeycomb activated carbon A, deodorization performance by deodorization performance is improved by carrying Pd, supporting the Pd-Cu-H 3 PO 4 is further enhanced did.

【0024】[0024]

【発明の効果】本発明は、生ゴミ処理機からの脱臭方法
としてコンパクトな装置を用い、維持管理が容易で、ラ
ンニングコストが低く、高い脱臭効果が長期に亘り持続
するので生ゴミ処理場のみならず、一般家庭でも便宜に
使用しうる。
INDUSTRIAL APPLICABILITY The present invention uses a compact device as a deodorizing method from a garbage disposer, is easy to maintain and manage, has a low running cost, and has a high deodorizing effect for a long time. Not to mention, it can be conveniently used in general households.

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D002 AB02 BA03 CA07 DA41 GA01 GB01 GB03 GB12 4G066 AA05B BA07 BA24 BA26 CA02 DA02 4G146 AA06 AA15 AA16 AC07A AC08A AC08B AC09A AC10A AD32 BA01 BA11 BA38 BD08 BD13    ─────────────────────────────────────────────────── ─── Continued front page    F-term (reference) 4D002 AB02 BA03 CA07 DA41 GA01                       GB01 GB03 GB12                 4G066 AA05B BA07 BA24 BA26                       CA02 DA02                 4G146 AA06 AA15 AA16 AC07A                       AC08A AC08B AC09A AC10A                       AD32 BA01 BA11 BA38 BD08                       BD13

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】生ゴミ処理機からの排ガスを温度50〜1
50℃、ガス空間速度15,000/時以上でハニカム
状活性炭に接触させる脱臭方法。
1. The temperature of the exhaust gas from the garbage disposal is 50 to 1
A deodorizing method of contacting with honeycomb-like activated carbon at 50 ° C. and a gas space velocity of 15,000 / hour or more.
【請求項2】ハニカム状活性炭のセル数が、10〜1,
500個/inch2である請求項1記載の脱臭方法。
2. The number of cells of honeycomb-shaped activated carbon is 10 to 1,
The deodorizing method according to claim 1, wherein the number is 500 / inch 2 .
【請求項3】ハニカム状活性炭の比表面積が、200m
2/g以上である請求項1記載の脱臭方法。
3. The specific surface area of the honeycomb-shaped activated carbon is 200 m.
The deodorizing method according to claim 1, which is 2 / g or more.
【請求項4】ガス空間速度が15,000〜500,0
00/時である請求項1記載の脱臭方法。
4. A gas space velocity of 15,000 to 500,0.
The deodorizing method according to claim 1, which is 00 / hour.
【請求項5】ハニカム状活性炭が薬品担持ハニカム状活
性炭である請求項1の脱臭方法。
5. The deodorizing method according to claim 1, wherein the honeycomb-shaped activated carbon is a chemical-supporting honeycomb-shaped activated carbon.
【請求項6】ハニカム状活性炭に担持する薬品が、ヨウ
素、無機ヨウ化物、臭素、無機臭化物、酸、白金族化合
物、Ti、 V、 Cr、 Mn、 Fe、 Co、 Ni、 CuおよびAgの
化合物から選ばれた少なくとも1種類である請求項5記
載の脱臭方法。
6. The chemical supported on the honeycomb-shaped activated carbon is a compound of iodine, inorganic iodide, bromine, inorganic bromide, acid, platinum group compound, Ti, V, Cr, Mn, Fe, Co, Ni, Cu and Ag. The deodorizing method according to claim 5, wherein the deodorizing method is at least one selected from the group consisting of:
【請求項7】使用により脱臭性能が低下したハニカム状
活性炭に散水して、再び生ゴミ処理機からの排ガスの脱
臭処理を行う請求項1記載の脱臭方法。
7. The deodorizing method according to claim 1, wherein the honeycomb-like activated carbon whose deodorizing performance has deteriorated due to use is sprinkled with water, and the deodorizing treatment of the exhaust gas from the garbage treating machine is carried out again.
JP2002012330A 2002-01-22 2002-01-22 Deodorization method Pending JP2003210930A (en)

Priority Applications (1)

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Applications Claiming Priority (1)

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Publications (1)

Publication Number Publication Date
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Family

ID=27649562

Family Applications (1)

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Country Status (1)

Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006088023A (en) * 2004-09-22 2006-04-06 Cataler Corp Deodorizing/adsorbing agent

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006088023A (en) * 2004-09-22 2006-04-06 Cataler Corp Deodorizing/adsorbing agent

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