JPH0521585B2 - - Google Patents
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- Publication number
- JPH0521585B2 JPH0521585B2 JP63248421A JP24842188A JPH0521585B2 JP H0521585 B2 JPH0521585 B2 JP H0521585B2 JP 63248421 A JP63248421 A JP 63248421A JP 24842188 A JP24842188 A JP 24842188A JP H0521585 B2 JPH0521585 B2 JP H0521585B2
- Authority
- JP
- Japan
- Prior art keywords
- microorganisms
- carbon
- pores
- producing
- ability
- 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 - Lifetime
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- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
Description
[産業上の利用分野]
本発明は一般家庭の廃棄物、産業廃棄物、農畜
産廃棄物等から発生するすべての種類の悪臭を対
象とする脱臭剤の製造方法に関するものである。
[従来の技術]
脱臭剤として従来使用されて来ているものは、
活性炭等に見られるように、悪臭を吸着する能力
は強い。
[発明が解決しようとする課題]
従来の技術で述べたものにあつては、下記のよ
うな問題点を有していた。
脱臭剤としての活性炭等は、吸着した悪臭を脱
着して脱臭剤を再使用するのに難点があり、通
常、高温での加熱再生を行うか、もしくは使い捨
てにしなければならない。
本発明は、吸着剤の再生を悪臭成分の分解能を
有した微生物に行わせることにより、長寿命の再
生不要な脱臭剤を開発するものであるが、このよ
うな、微生物を利用した脱臭剤には、悪臭を吸着
する能力を有すると同時に、微生物を安定に存在
させうる能力も併せ持つことが必要である。
このような脱臭剤は微生物の存在する微生物用
細孔と悪臭成分を吸着する細孔のサイズの異なる
両細孔が機能的に隣接していなければならない。
本発明は、この様な機能を有する炭素多孔体を
使用した脱臭剤を製造する目的でなされたもので
ある。
[課題を解決するための手段]
上記目的を達成するために、本発明のものは下
記のようになるものである。
炭素多孔体に、悪臭成分分解能を有する微生物
を固定した脱臭剤の製造方法である。
この場合、上記炭素多孔体の骨格炭素として、
粉砕後一定粒度範囲に整粒した石炭を用い、これ
をバインダー油により造粒することができ、ま
た、上記炭素多孔体の骨格炭素として、上記石炭
の代わりにプラスチツク等、各種有機高分子化合
物の炭化物やコークスを用いることができると共
に、上記炭素多孔体は、石炭などを粉砕後所定寸
法の粒子を数種に篩分けした骨格炭素を、バイン
ダー油としてコールタールを用いて造粒した造粒
物を、還元雰囲気下で所定の昇温速度で加温し
て、所定温度で所定時間保持することにより炭化
したのち、この炭化物を所定温度で水蒸気流通下
賦活して構成することができる。
この場合、上記炭素多孔体に、悪臭成分を分解
する能力を持つ微生物を付着させるには当該微生
物を含む培養液に所定時間浸せきすることにより
行つてもよく、また、上記炭素多孔体を骨格炭素
の粒子の大きさにより微生物用細孔の大きさを制
御することもできる。
[作用]
本発明の脱臭剤について、以下のような吸着試
験装置3により行つた性能確認試験結果を報告す
る。
図中、3Aはキヤリヤーガス、3Bはガス流量
調整弁、3Cはガス流量計、3Dは悪臭ガス発生
部、3Eは悪臭ガス吸着部、3Fは吸着剤試料、
3Gはサンプラー、3Hは悪臭ガス検出部、3I
はテープヒーターをそれぞれ示す。
第3図に示す吸着試験装置3に炭素多孔体を装
填して、当該炭素多孔体の吸着サイトが飽和する
まで悪臭を吸着させた。
なお、悪臭は一定温度に保持した発生装置を通
じて連続的に吸着層に供給した。
悪臭吸着能を消失した炭素多孔体を48時間、一
定温度で保持したのち、再び吸着試験装置により
悪臭の吸着を行わせて吸着能の回復割合を調べ
た。
同様の操作を微生物の付着していない炭素多孔
体に対しても行い、両者の差から微生物の作用の
みによる回復吸着量を算出した。
回復吸着量の例を第1表に示す。
[Industrial Application Field] The present invention relates to a method for producing a deodorizing agent for all kinds of bad odors generated from household waste, industrial waste, agricultural and livestock waste, etc. [Prior art] The deodorizers that have been conventionally used are:
As seen in activated carbon, etc., it has a strong ability to adsorb bad odors. [Problems to be Solved by the Invention] The conventional techniques described above had the following problems. Activated carbon and the like as a deodorizing agent have the disadvantage of desorbing the adsorbed bad odor and reusing the deodorizing agent, and usually must be regenerated by heating at a high temperature or be disposed of. The present invention aims to develop a long-life deodorizer that does not require regeneration by regenerating the adsorbent using microorganisms that have the ability to decompose malodorous components. It is necessary to have the ability to adsorb bad odors and at the same time to have the ability to allow microorganisms to exist stably. In such a deodorizing agent, pores for microorganisms where microorganisms exist and pores for adsorbing malodorous components, which have different sizes, must be functionally adjacent to each other. The present invention was made for the purpose of producing a deodorizing agent using a porous carbon material having such a function. [Means for Solving the Problems] In order to achieve the above object, the present invention is as follows. This is a method for producing a deodorizer in which microorganisms capable of decomposing malodorous components are immobilized on a porous carbon material. In this case, as the skeleton carbon of the carbon porous body,
Using coal that has been sized to a certain particle size range after pulverization, it can be granulated with binder oil.In addition, as the skeleton carbon of the above-mentioned carbon porous body, various organic polymer compounds such as plastics can be used instead of the above-mentioned coal. Carbide or coke can be used, and the carbon porous body may be a granulated material obtained by granulating skeleton carbon obtained by pulverizing coal or the like and sifting particles of a predetermined size into several types, using coal tar as a binder oil. is heated at a predetermined temperature increase rate in a reducing atmosphere, held at a predetermined temperature for a predetermined period of time to carbonize, and then this carbide is activated at a predetermined temperature while flowing steam. In this case, microorganisms capable of decomposing malodorous components may be attached to the carbon porous material by immersing the carbon porous material in a culture solution containing the microorganisms for a predetermined period of time. The size of the pores for microorganisms can also be controlled by the size of the particles. [Function] The results of a performance confirmation test conducted on the deodorizer of the present invention using an adsorption test device 3 as described below will be reported. In the figure, 3A is a carrier gas, 3B is a gas flow rate adjustment valve, 3C is a gas flow meter, 3D is a malodorous gas generation part, 3E is a malodorous gas adsorption part, 3F is an adsorbent sample,
3G is a sampler, 3H is a malodorous gas detection unit, 3I
indicate tape heaters, respectively. A carbon porous body was loaded into the adsorption test apparatus 3 shown in FIG. 3, and a malodor was adsorbed until the adsorption sites of the carbon porous body were saturated. Incidentally, the bad odor was continuously supplied to the adsorption layer through a generator maintained at a constant temperature. After the porous carbon material, which had lost its ability to adsorb bad odors, was held at a constant temperature for 48 hours, it was allowed to adsorb bad odors again using an adsorption test device to examine the rate of recovery of its adsorption ability. The same operation was performed on a carbon porous material to which no microorganisms were attached, and the amount of adsorption recovered only by the action of microorganisms was calculated from the difference between the two. Examples of recovered adsorption amounts are shown in Table 1.
【表】
第1表の説明(第2図より)
A−1:細孔は比較的多いが、微生物が活躍しや
すいと考えられる8ミクロン程度の細孔がA−
2、A−3〜に比べて少ない。
A−2、A−3:全体的に細孔が多いが、他に比
べて特に8ミクロン以上の細孔が多い。
A−4:細孔が全体的に少ない。
なお、ここで用いた微生物は鶏糞から採取した
放線菌のうちの一つである。
市販活性炭を含め、微生物の付着能の乏しい炭
素多孔体では吸着能をほとんど回復していない
が、微生物を安定に存在させうる細孔を有した、
微生物付着能の高い炭素多孔体では吸着量のかな
りの回復が見られた。
[発明の実施例]
実施例について図面を参照して説明する。
1は本発明で得た脱臭剤で、炭素多孔体2と、
この炭素多孔体2に固定した悪臭成分分解能を有
する微生物(図示略)とから構成されている。
そこで、上記炭素多孔体2は、石炭、コークス
等の粉砕物を篩分けて整粒した骨格炭素2Aを原
料として、これにバインダーピツチ2Bを加えて
造粒することにより、微生物用細孔2Cを生じさ
せている。
すなわち、第1図に示すように悪臭の吸着に適
した細孔2A1を石炭、コークス等の骨格炭素に
発現させ、微生物の存在に必要な微生物用細孔2
Cを整粒された骨格炭素粒子間〓に発現させるこ
とにより目的とする炭素多孔体2を得る。
なお、石炭として赤平炭を、バインダーピツチ
として市販コールタールを用いて造粒した。
この場合、石炭は粉砕後0.5mm以下の粒子を数
種に篩分けして用いた。
このようにして得た造粒物を、還元雰囲気下で
昇温速度1から10℃/minで加温して500℃から
900℃で1から5時間保持することにより炭化し
た。
この炭化物を600℃から900℃で水蒸気流通下
(0.5から3.2ml/min/g−sample)賦活し、多
孔体を製造した。
生成炭素多孔体のBET法による比表面積とメ
チレンブルー吸着量を第2表に、また水銀圧入法
による微生物用細孔の分布を第2図に示した。
この場合、上記炭素多孔体の製造に際して、原
料の粒子の大きさにより微生物用細孔の大きさを
制御することができる。[Table] Explanation of Table 1 (from Figure 2) A-1: There are relatively many pores, but there are pores of about 8 microns that are considered to be easy for microorganisms to play an active role.
2. Less than A-3~. A-2, A-3: There are many pores overall, but there are especially many pores of 8 microns or more compared to the others. A-4: There are fewer pores overall. The microorganism used here was one of the actinomycetes collected from chicken manure. Porous carbon materials, including commercially available activated carbon, which have poor adhesion ability for microorganisms, have hardly recovered their adsorption ability, but they have pores that allow microorganisms to exist stably.
A significant recovery in the amount of adsorption was observed on the carbon porous material, which has a high ability to attach microorganisms. [Embodiments of the Invention] Examples will be described with reference to the drawings. 1 is a deodorizing agent obtained according to the present invention, and a carbon porous body 2;
It is composed of microorganisms (not shown) fixed to the carbon porous body 2 and having the ability to decompose malodorous components. Therefore, the above-mentioned carbon porous body 2 is made by using as raw material skeletal carbon 2A obtained by sieving and sifting crushed coal, coke, etc., and adding binder pitch 2B to it and granulating it to form pores 2C for microorganisms. is causing it. That is, as shown in FIG. 1, pores 2A1 suitable for adsorbing bad odors are developed in the skeleton carbon of coal, coke, etc., and pores 2A1 for microorganisms necessary for the presence of microorganisms are created.
By expressing C between the sized skeletal carbon particles, the desired carbon porous body 2 is obtained. Incidentally, Akahira charcoal was used as the coal and commercially available coal tar was used as the binder pitch. In this case, the coal was pulverized and then sieved into several types of particles with a size of 0.5 mm or less. The granules thus obtained were heated at a temperature increase rate of 1 to 10°C/min in a reducing atmosphere to 500°C.
Carbonization was achieved by holding at 900°C for 1 to 5 hours. This carbide was activated at 600° C. to 900° C. under steam flow (0.5 to 3.2 ml/min/g-sample) to produce a porous body. Table 2 shows the specific surface area and methylene blue adsorption amount of the produced carbon porous material by the BET method, and Figure 2 shows the distribution of microbial pores by the mercury intrusion method. In this case, when producing the carbon porous body, the size of the pores for microorganisms can be controlled by the size of the particles of the raw material.
【表】
このようにして製造した炭素多孔体に悪臭成分
を分解する能力を持つ微生物を含む培養液に1か
ら5時間浸せきすることにより微生物を炭素多孔
体に付着させた。
この悪臭除去剤は、悪臭を吸着し、さらに吸着
した悪臭を付着微生物により分解、脱着して悪臭
の再吸着が可能なものとなる長寿命の悪臭除去能
力の高い処理剤として使用できる。
なお、悪臭成分分解能を有する微生物の採取お
よび純粋培養は次のようにして行つた。
排出後12時間以内の新鮮な豚糞を採取してこれ
を微生物(放線菌)の培養用培地の原料とした。
培地は豚糞(20wt%)の蒸留水への懸濁溶液
をガーゼで濾過した豚糞抽出エキスに硝安0.2wt
%と硝酸ナトリウム0.2wt%とを添加後、カ性ソ
ーダにより溶液のPHを7.6として、120℃で30分間
殺菌することにより調製した。
この培地に約10wt%の豚糞、鶏糞、牛糞のう
ちの一つを添加して、空気流通下室温で2〜3日
間放線菌の培養を行つた。
培養液の一白金耳を1.5wt%の寒天を含むワツ
クスマン培地(グルコース1.0wt%、ペプトン
0.5wt%、肉エキス0.5wt%、食塩0.5wt%、PH
7.0)により培養した。
数日後、培地上に生じたコロニーの各々につい
てワツクスマン培地上で更に培養を繰り返すこと
により純粋な放線菌を採取した。
採取した放線菌の一つ一つについて悪臭の除去
能を調べるとともに除去能を有する放線菌を保管
して悪臭除去用とした。
[発明の効果]
本発明は、上述の通り構成されているので次に
記載する効果を奏する。
このように、悪臭を吸着する細孔と微生物を安
定に存在させる微生物用細孔の両者を併せ持つ炭
素多孔体の利用により自己再生のできる、寿命の
長い、また吸着能の高い悪臭除去剤の製造が可能
となつた。
さらに、ここで微生物の大きさに合せて第1図
の微生物用細孔2Cの大きさを変化させる、すな
わち、原料炭素の粒径を変化させることにより
種々の微生物の固定が可能となり、また悪臭の種
類により細孔2A1の大きさを変化させる。
すなわち、炭素多孔体の炭化条件および賦活条
件を変化させることにより種々の悪臭の吸着が可
能になる。
このように各種微生物と炭素多孔体との組合せ
によりあらゆる種類の悪臭除去剤として使用しう
るようになる。[Table] The carbon porous bodies thus produced were immersed in a culture solution containing microorganisms capable of decomposing malodorous components for 1 to 5 hours to allow microorganisms to adhere to the carbon porous bodies. This malodor remover can be used as a long-life treatment agent with high malodor removal ability that adsorbs malodors, decomposes and desorbs the adsorbed malodors by attached microorganisms, and makes it possible to re-adsorb the malodors. The collection and pure culture of microorganisms capable of decomposing malodorous components were carried out as follows. Fresh pig feces was collected within 12 hours after excretion and was used as a raw material for a culture medium for microorganisms (actinomycetes). The culture medium is a suspension of pig manure (20wt%) in distilled water, filtered through gauze, a pig manure extract, and 0.2wt ammonium nitrate.
% and 0.2 wt % of sodium nitrate, the pH of the solution was adjusted to 7.6 with caustic soda, and the solution was sterilized at 120° C. for 30 minutes. Approximately 10 wt% of one of pig manure, chicken manure, and cow manure was added to this medium, and actinomycetes were cultured for 2 to 3 days at room temperature under air circulation. Transfer one loopful of the culture solution to Waxmann medium containing 1.5 wt% agar (glucose 1.0 wt%, peptone
0.5wt%, meat extract 0.5wt%, salt 0.5wt%, PH
7.0). After several days, each of the colonies formed on the medium was further cultured on Waxmann's medium to collect pure actinomycetes. Each of the collected actinomycetes was examined for its ability to remove bad odors, and the actinomycetes that had the ability to remove them were stored for use in removing bad odors. [Effects of the Invention] Since the present invention is configured as described above, it produces the following effects. In this way, by using a carbon porous material that has both pores that absorb bad odors and pores for microorganisms that allow microorganisms to stably exist, we are able to produce a malodor remover that can self-regenerate, has a long life, and has a high adsorption capacity. became possible. Furthermore, by changing the size of the microorganism pores 2C shown in FIG. 1 according to the size of the microorganisms, that is, by changing the particle size of the raw carbon, it is possible to immobilize various microorganisms, and also to eliminate bad odors. The size of the pore 2A1 is changed depending on the type. That is, by changing the carbonization conditions and activation conditions of the porous carbon material, it becomes possible to adsorb various bad odors. In this way, the combination of various microorganisms and porous carbon materials makes it possible to use them as all kinds of odor removers.
第1図は脱臭剤の要部拡大図、第2図は炭素多
孔体における細孔の分布状態を示すグラフ、第3
図は悪臭吸着試験装置である。
1……脱臭剤、2……炭素多孔体、2A……骨
格炭素、2A1……細孔、2B……バインダーピ
ツチ、2C……微生物用細孔。
Figure 1 is an enlarged view of the main parts of the deodorizer, Figure 2 is a graph showing the distribution of pores in the carbon porous material, and Figure 3 is a graph showing the distribution of pores in the carbon porous material.
The figure shows a malodor adsorption test device. DESCRIPTION OF SYMBOLS 1... Deodorizer, 2... Porous carbon material, 2A... Skeleton carbon, 2A1... Pore, 2B... Binder pitch, 2C... Pore for microorganisms.
Claims (1)
を有する粒状炭化物を骨格炭素としてバインダー
油で造粒し粒子間に微生物用細孔を形成し、この
微生物用細孔に悪臭成分分解能を有する微生物を
固定したことを特徴とする脱臭剤の製造方法。 2 上記炭素多孔体の骨格炭素として、上記石炭
の代わりにプラスチツク等、各種有機高分子化合
物の炭化物やコークスを用いた請求項1記載の脱
臭剤の製造方法。 3 上記炭素多孔体に、悪臭成分を分解する能力
を持つ微生物を含む培養液に所定時間浸せきする
ことにより微生物を炭素多孔体に付着させた請求
項1記載の脱臭剤の製造方法。 4 上記炭素多孔体を骨格炭素の粒子の大きさに
より微生物用細孔の大きさを制御するようにした
請求項1記載の脱臭剤の製造方法。[Scope of Claims] 1 Granular carbide made from coal and having pores on the surface that adsorbs bad odors is granulated with binder oil as skeleton carbon, and pores for microorganisms are formed between the particles, and pores for microorganisms are formed between the particles. A method for producing a deodorizer, characterized in that microorganisms having the ability to decompose malodorous components are immobilized. 2. The method for producing a deodorizing agent according to claim 1, wherein carbonized materials of various organic polymer compounds such as plastics or coke are used instead of the coal as the skeleton carbon of the carbon porous body. 3. The method for producing a deodorizing agent according to claim 1, wherein microorganisms are attached to the carbon porous material by immersing the carbon porous material in a culture solution containing microorganisms having the ability to decompose malodorous components for a predetermined period of time. 4. The method for producing a deodorizing agent according to claim 1, wherein the size of the pores for microorganisms in the carbon porous body is controlled by the size of the skeletal carbon particles.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63248421A JPH0295376A (en) | 1988-09-30 | 1988-09-30 | Manufacture of deodorant |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63248421A JPH0295376A (en) | 1988-09-30 | 1988-09-30 | Manufacture of deodorant |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0295376A JPH0295376A (en) | 1990-04-06 |
| JPH0521585B2 true JPH0521585B2 (en) | 1993-03-24 |
Family
ID=17177873
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63248421A Granted JPH0295376A (en) | 1988-09-30 | 1988-09-30 | Manufacture of deodorant |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0295376A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002095730A (en) * | 2000-07-21 | 2002-04-02 | Midori Anzen Co Ltd | Deodorizing material and method for producing the same |
| KR100798221B1 (en) * | 2002-03-05 | 2008-01-24 | 주식회사 엘지생활건강 | Deodorant comprising carbon material of core-shell structure |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6046803B2 (en) * | 1980-07-11 | 1985-10-18 | 鐘通工業株式会社 | Switchable permanent magnet holding device |
| JPS5922555A (en) * | 1982-07-30 | 1984-02-04 | 門馬 義芳 | Deodorant utilizing microorganism |
| JPS62298364A (en) * | 1986-06-18 | 1987-12-25 | 岡部株式会社 | Deodorant |
-
1988
- 1988-09-30 JP JP63248421A patent/JPH0295376A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0295376A (en) | 1990-04-06 |
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