JPH0295376A - Manufacture of deodorant - Google Patents

Manufacture of deodorant

Info

Publication number
JPH0295376A
JPH0295376A JP63248421A JP24842188A JPH0295376A JP H0295376 A JPH0295376 A JP H0295376A JP 63248421 A JP63248421 A JP 63248421A JP 24842188 A JP24842188 A JP 24842188A JP H0295376 A JPH0295376 A JP H0295376A
Authority
JP
Japan
Prior art keywords
carbon
porous body
carbon porous
microorganisms
coal
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.)
Granted
Application number
JP63248421A
Other languages
Japanese (ja)
Other versions
JPH0521585B2 (en
Inventor
Kiyotaka Matsuo
清隆 松尾
Akihiko Hirai
平井 明彦
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.)
Sumitomo Coal Mining Co Ltd
Original Assignee
Sumitomo Coal Mining Co Ltd
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 Sumitomo Coal Mining Co Ltd filed Critical Sumitomo Coal Mining Co Ltd
Priority to JP63248421A priority Critical patent/JPH0295376A/en
Publication of JPH0295376A publication Critical patent/JPH0295376A/en
Publication of JPH0521585B2 publication Critical patent/JPH0521585B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)

Abstract

PURPOSE:To manufacture an offensive odor remover whose self-reproduction is possible, whose service life is long and whose adsorptivity is high by fixing a microorganism having capacity for decomposing an offensive component to a carbon porous body. CONSTITUTION:A carbon porous body 2 is pelletized by using skeleton carbon 2A sized by sieving a pulverized matter of coal, coke, etc., as a raw material and adding a binder pitch 2B thereto. This pelletized matter is carbonized by heating at 1 to 10 deg.C/min temperature rise speed under a reducing atmosphere and holding it for 1 to 5 hours at 500 to 900 deg.C, activated under a flow of water vapor at 600 to 900 deg.C, by which a porous body is manufactured. This carbon porous body 2 is immersed into a culture solution containing a microorganism having capacity for decomposing an offensive odor component for 1-5 hours and the microorganism is allowed to adhere to the carbon porous body. This offensive odor remover adsorbs an offensive odor, and also, decomposes and desorbs the adsorbed offensive odor by the adhered microorganism and can be used as a processing agent which can readsorb an offensive odor, has a long service life and has a high offensive odor removing capacity.

Description

【発明の詳細な説明】 [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。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for producing a deodorizer that targets all types of bad odors generated from household waste, industrial waste, agricultural and livestock waste, etc. It is something.

[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。
[Prior Art] Deodorizers that have been conventionally used have a strong ability to adsorb bad odors, such as activated carbon.

[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フては、下記のような問題
点を有していた。
[Problems to be Solved by the Invention] The conventional techniques described above have the following problems.

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
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.

本発明は、このような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、現状では悪臭成分
の吸着能を有し、かつ悪臭成分分解能を持つ微生物を安
定に担持しつるような本目的に適合した炭素系多孔体は
開発されていない。
The present invention aims to develop a long-life deodorizing agent that does not require regeneration by regenerating such an adsorbent using microorganisms that have the ability to decompose malodorous components. A carbon-based porous material suitable for this purpose that stably supports microorganisms having the ability to decompose malodorous components has not been developed.

本発明は、従来の技術の有するこのような問題点に鑑み
なされたものであり、その目的とするところは、次のよ
うな事のできるものを提供しようとするものである。
The present invention has been devised in view of the above-mentioned problems of the prior art, and its purpose is to provide a device that can do the following.

上述のように、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
つる能力も併せ持つことが必要である。
As mentioned above, a deodorizing agent using microorganisms must have the ability to adsorb bad odors and at the same time have the ability to maintain the stable presence of microorganisms.

このような脱臭剤は微生物の存在する細孔と悪臭成分を
吸着する細孔のサイズの異なる両線孔が機能的に隣接し
ていなければならない。
In such a deodorizing agent, pores in which microorganisms exist and pores in which malodorous components are adsorbed must be functionally adjacent to each other.

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。
The present invention was made for the purpose of producing a deodorizing agent using a porous carbon material having such a function.

[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。
[Means for Solving the Problems] In order to achieve the above object, the present invention is as follows.

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。
This is a method for producing a deodorizer in which microorganisms capable of decomposing malodorous components are immobilized on a porous carbon material.

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ック等、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。
In this case, as the skeleton carbon of the carbon porous body, coal that has been pulverized and sized to a certain particle size range can be used and granulated with binder oil, and as the skeleton carbon of the carbon porous body, the coal Instead of plastic, carbide of various organic polymer compounds or coke can be used, and the above-mentioned porous carbon material can be made of skeletal carbon obtained by pulverizing coal or the like and then sieving into several types of particles of a certain size. The granulated material is granulated using coal tar as the binder oil.
It can be constructed by carbonizing by heating at a predetermined temperature increase rate in a reducing atmosphere and holding at a predetermined temperature for a predetermined time, and then activating this carbide at a predetermined temperature while flowing water vapor.

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ってもよく、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。
In this case, microorganisms capable of decomposing malodorous components may be attached to the carbon porous material by immersing it in a culture solution containing the microorganisms for a predetermined period of time, and
The size of the pores for microorganisms in the carbon porous body can also be controlled by the size of the skeleton carbon particles.

[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
により行った性能確認試験結果を報告する。
[Operation] Regarding the deodorizing agent of the present invention, the following adsorption test device 3 was used.
We report the results of performance confirmation tests conducted by

図中、3Aはキャリヤーガス、3Bはガス流i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、3
Hは悪臭ガス検出部、3Iはテープヒーターをそれぞれ
示す。
In the figure, 3A is a carrier gas, 3B is a gas flow 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, 3
H indicates a malodorous gas detection unit, and 3I indicates a tape heater.

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。
Loading the carbon porous body into the adsorption test device 3 shown in FIG.
The odor was adsorbed until the adsorption sites of the carbon porous material were saturated.

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。
Incidentally, the bad odor was continuously supplied to the adsorption layer through a generator maintained at a constant temperature.

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。
After the porous carbon material that 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.

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。
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.

回復吸着量の例を第1表に示す。Examples of recovered adsorption amounts are shown in Table 1.

第1表 悪臭除去試験結果 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。
Table 1 Results of malodor removal test The microorganism used here is one of the actinomycetes collected from chicken manure.

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。
Porous carbon materials, including commercially available activated carbon, that have poor adhesion ability for microorganisms have hardly recovered their adsorption ability, but porous carbon materials that have pores that allow microorganisms to stably exist and have a high ability to adhere to microorganisms can reduce the amount of adsorption. Significant recovery was observed.

[発明の実施例] 実施例について図面を参照して説明する。[Embodiments of the invention] Examples will be described with reference to the drawings.

1は本発明で得た脱臭剖で、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
示路)とから構成されている。
1 is a deodorizing tissue obtained according to the present invention, which is composed of a carbon porous body 2 and a microorganism fixed to the carbon porous body 2 and having the ability to decompose malodorous components (as shown in the diagram).

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
にバインダーピッチ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。
Therefore, the above-mentioned carbon porous body 2 is made by using skeleton carbon 2A obtained by sieving and sifting pulverized materials such as coal or coke as a raw material, and adding binder pitch 2B to it and granulating it.
Pores 2C for microorganisms are generated.

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2Cを整粒された骨格炭
素粒子間隙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。
That is, as shown in FIG. 1, pores 2A1 suitable for adsorption of bad odors are developed in the skeleton carbon of coal, coke, etc., and pores 2C for microorganisms necessary for the presence of microorganisms are formed in the gaps between the sized skeleton carbon particles. The desired carbon porous body 2 is obtained by causing the carbon to develop.

なお、石炭として赤平炭を、バインダーピッチとして市
販コールタールを用いて造粒した。
Incidentally, Akahira charcoal was used as the coal and commercially available coal tar was used as the binder pitch.

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。
In this case, the coal was pulverized and then sieved into several types of particles with a size of 0.5 mm or less.

このようにして得た造粒物を、還元雰囲気下で昇温速度
lか610℃/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。
The granules thus obtained were heated at a temperature increase rate of l or 610°C/min in a reducing atmosphere to a temperature of 500°C to 900°C.
Carbonization was achieved by holding at for 1 to 5 hours.

この炭化物を600℃から900℃で水蒸気流通下(0
,5から3.2ml/1Ilin/g−sample)
賦活し、多孔体を製造した。
This carbide was heated at 600°C to 900°C under steam flow (0
, 5 to 3.2 ml/1 Ilin/g-sample)
Activation was performed to produce a porous body.

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。
Table 2 shows the specific surface area and methylene blue adsorption amount of the produced carbon porous material measured by the BET method, and FIG. 2 shows the distribution of microbial pores measured by the mercury intrusion method.

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。
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.

第2表 炭素多孔体物性値 kl−B:メチレンブルー吸着量 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。
Table 2 Physical properties of carbon porous material kl-B: Methylene blue adsorption amount The carbon porous material produced in this manner is immersed for 1 to 5 hours in a culture solution containing microorganisms capable of decomposing malodorous components. It was attached to a porous body.

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。
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.

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った。
The collection and pure culture of microorganisms capable of decomposing malodorous components were performed as follows.

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。
Fresh pig feces within 12 hours after excretion were collected and used as a raw material for a culture medium for microorganisms (actinomycetes).

培地は豚i (20wt″4)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0.2wtkと
硝酸ナトリウム0.2wt零とを添加後、力性ソーダに
より溶ン夜の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。
The culture medium was prepared by adding 0.2 wtk of ammonium nitrate and 0.2 wt of sodium nitrate to a pig feces extract obtained by filtering a suspension of pig I (20wt''4) in distilled water through gauze, and then dissolving it with diluted sodium chloride. The pH was adjusted to 7.6 and the mixture was sterilized at 120°C for 30 minutes.

この培地に約10wtX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
養を行った。
Approximately 10 wtX 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.

培養液の一白金耳を1.5wlの寒天を含むワックスマ
ン培地(グルコース1.0wt1.ペプトン0.5+r
tk、肉エキス0.5wt%i、食塩Q、5wt!1゜
11117.0 )により培養した。
Transfer one loopful of the culture solution to Waxman medium containing 1.5 wl of agar (glucose 1.0 wt 1, peptone 0.5 + r
tk, meat extract 0.5wt%i, salt Q, 5wt! 1°11117.0).

数日後、培地上に生じたコロニーの各々についてワック
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。
After several days, each colony that had formed on the medium was further cultured on Waxman's medium to collect pure actinomycetes.

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。
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.

[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。
[Effects of the Invention] Since the present invention is configured as described above, it produces the following effects.

このように、悪臭を吸着する微生物用細孔と微生物を安
定に存在させる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った。
In this way, by using a carbon porous material that has both pores for microorganisms that adsorb bad odors and pores that allow microorganisms to stably exist, we can produce a bad odor remover that can self-regenerate, has a long life, and has a high adsorption capacity. became possible.

さらに、ここで微生物の大ぎさに合せて第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。
Furthermore, by changing the size of the microorganism pores 2C in Figure 1 according to the size of the microorganisms, that is, by changing the particle size of the raw material 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.

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。
That is, by changing the carbonization conditions and activation conditions of the porous carbon material, it becomes possible to adsorb various bad odors.

このように各ff1l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つるように
なる。
In this way, the combination of each ff1l microorganism and the porous carbon material allows it to be used as a bad odor remover of all kinds.

【図面の簡単な説明】[Brief explanation of drawings]

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。 199.脱臭剤、 211.炭素多孔体、  A 、骨格炭素、  B バインダーピッチ、 2C,、、微生物用細孔。 特許出願人   住友石炭鉱業株式会社−代理人 弁理
士   川  成  端  夫第 ] 図 第 図 細孔半1(A)
Figure 1 is an enlarged view of the main parts of the deodorizer, Figure 2 is a graph showing the distribution of pores in a carbon porous body, and Figure 3 is a malodor adsorption test device. 199. Deodorizer, 211. Porous carbon material, A. Skeletal carbon, B. Binder pitch, 2C, Pore for microorganisms. Patent Applicant Sumitomo Coal Mining Co., Ltd. - Agent Patent Attorney Kawa Naruta Fudai] Figure Diagram Pore Half 1 (A)

Claims (1)

【特許請求の範囲】 1、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、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
造粒した請求項1記載の脱臭剤の製造方法。 3、上記炭素多孔体の骨格炭素として、上記石炭の代わ
りにプラスチック等、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2記載の脱臭剤の製造方法。 4、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なる請求項1記載の脱臭剤の製造
方法。 5、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。6、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. A method for producing a deodorizing agent, characterized in that microorganisms capable of decomposing malodorous components are immobilized on a carbon porous material. 2. The method for producing a deodorizing agent according to claim 1, wherein coal that has been pulverized and sized to a certain particle size range is used as the skeleton carbon of the carbon porous body, and the coal is granulated with binder oil. 3. The method for producing a deodorizing agent according to claim 2, 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. 4. The above-mentioned carbon porous body is made by pulverizing coal, etc. and sieving it into several types of particles of a predetermined size, and then granulating the skeletal carbon using coal tar as a binder oil. 2. The method for producing a deodorizing agent according to claim 1, wherein the deodorizing agent is carbonized by heating at a temperature increasing rate and held at a predetermined temperature for a predetermined time, and then activated under steam flow at a predetermined temperature. 5. 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. 6. The method for producing a deodorizer 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.
JP63248421A 1988-09-30 1988-09-30 Manufacture of deodorant Granted JPH0295376A (en)

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 true JPH0295376A (en) 1990-04-06
JPH0521585B2 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)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002007790A1 (en) * 2000-07-21 2002-01-31 Midori Anzen Co.,Ltd. Deodorant material and method for preparation thereof
KR100798221B1 (en) * 2002-03-05 2008-01-24 주식회사 엘지생활건강 Deodorant comprising carbon materials having core-shell structure

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5626417A (en) * 1980-07-11 1981-03-14 Kanetsuu Kogyo Kk Permanent-magnet holding device that can be switched
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

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5626417A (en) * 1980-07-11 1981-03-14 Kanetsuu Kogyo Kk Permanent-magnet holding device that can be switched
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

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002007790A1 (en) * 2000-07-21 2002-01-31 Midori Anzen Co.,Ltd. Deodorant material and method for preparation thereof
KR100798221B1 (en) * 2002-03-05 2008-01-24 주식회사 엘지생활건강 Deodorant comprising carbon materials having core-shell structure

Also Published As

Publication number Publication date
JPH0521585B2 (en) 1993-03-24

Similar Documents

Publication Publication Date Title
US3216905A (en) Purification of gas with soil microorganisms
US7524795B1 (en) Activated carbons from animal manure
CN111135790A (en) Dephosphorization composite adsorbent, preparation method thereof and application thereof in sewage treatment
US6030922A (en) Synthesizing carbon from sludge
JPH0549921A (en) Porous carbon material for treatment of waste water
KR102314371B1 (en) Alginate beads having buckwheat hull biochar and radionuclide removal method using the same
JPH0295376A (en) Manufacture of deodorant
JP2004024996A (en) Carrier for carrying living body, biological deodorizing apparatus using the same and deodorization method
US20120039757A1 (en) Filtering device for food waste treatment apparatus
KR102168615B1 (en) Nano-porous mineral activated carbon and its using method
CN109382073B (en) Preparation method and application of alkali fusion fly ash modified pig manure biochar
JP3066145B2 (en) Activated carbon and its manufacturing method
JP2007308325A (en) Earthworm cast carbide and adsorbent
JP2000288386A (en) Filter medium for removing environmental pollutant and recovering useful substance
Piekarski et al. Effect of bed height on efficiency of adsorption of odors from sewage sludge using modified biochars from organic waste materials as an adsorbent
KR0139559B1 (en) Activated Carbon Fibers and Nonwovens
JP2000107555A (en) Method for deodorization
JP3250773B2 (en) Aliphatic aldehyde adsorbent
JPH1199194A (en) Deodorizing composition, deodorizing device and deodorizing method with it
WO2002007790A1 (en) Deodorant material and method for preparation thereof
JP3985081B2 (en) Microbial carrier
JP2009240889A (en) Gas adsorbent and gas adsorbing filter using the same
JPS6048183B2 (en) Air purification method and device
JP2931633B2 (en) Biological deodorizing filter
JP3948902B2 (en) Seeding agent and production method