JPH04200634A - Active carbon for deodorization - Google Patents

Active carbon for deodorization

Info

Publication number
JPH04200634A
JPH04200634A JP2329884A JP32988490A JPH04200634A JP H04200634 A JPH04200634 A JP H04200634A JP 2329884 A JP2329884 A JP 2329884A JP 32988490 A JP32988490 A JP 32988490A JP H04200634 A JPH04200634 A JP H04200634A
Authority
JP
Japan
Prior art keywords
activated carbon
sulfuric acid
sulfonic acid
active carbon
ammonia
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
JP2329884A
Other languages
Japanese (ja)
Other versions
JP2965347B2 (en
Inventor
Atsushi Kosaka
淳 小坂
Kenji Takigawa
賢司 瀧川
Satoru Kadowaki
覚 門脇
Makoto Suzuki
誠 鈴木
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.)
Denso Corp
Soken Inc
Original Assignee
Nippon Soken Inc
NipponDenso 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 Nippon Soken Inc, NipponDenso Co Ltd filed Critical Nippon Soken Inc
Priority to JP2329884A priority Critical patent/JP2965347B2/en
Publication of JPH04200634A publication Critical patent/JPH04200634A/en
Application granted granted Critical
Publication of JP2965347B2 publication Critical patent/JP2965347B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)

Abstract

PURPOSE:To obtain a deodorant having excellent in particular removing ability of basic gas by allowing a raw active carbon to react with sulfuric acid in the presence of acetic anhydride and fixedly and chemically combining with surface part of the active carbon. CONSTITUTION:The raw active carbon is allowed to react with sulfuric acid in the presence of acetic anhydride. At this time, sulfonic group as a functional group fixedly and chemically combines with end of active carbon molecule and the structure having the surface part of active carbon surrounded with sulfonic group is obtained. Then the sulfonic group does not eliminate in the use and does not fall out in the case of wet molding. The deodorant obtained in such a way has excellent removing ability of basic gas.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は脱臭用活性炭に関し、さらに詳しく述べると、
官能基としてのスルホン酸基が表面部位に固定的に結合
せしめられてなる脱臭用活性炭に関する。本発明の脱臭
用活性炭は、特に塩基性悪臭成分(例えばアンモニア臭
)に対してすぐれた脱臭性能を有しておりかつその性能
を長期的に持続することができ、したがって、各種の分
野で脱臭目的に有利に利用することができる。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to deodorizing activated carbon, and more specifically,
The present invention relates to deodorizing activated carbon in which a sulfonic acid group as a functional group is fixedly bonded to a surface site. The activated carbon for deodorization of the present invention has excellent deodorizing performance, especially against basic malodorous components (for example, ammonia odor), and can maintain this performance for a long period of time. It can be used advantageously for the purpose.

〔従来の技術〕[Conventional technology]

脱臭法としては、薬液洗浄法、直接燃焼法、触媒酸化法
、生物脱臭法、吸着脱臭法等の各種方法があるが、−船
釣に最も多く利用されているのは活性炭を用いた吸着脱
臭法である。これは活性炭が幅広く悪臭成分を吸着除去
するためである。しかし、残念ながら、この吸着脱臭法
はアセトアルデヒド、アンモニアといった極性成分(酸
性・塩基性悪臭成分)については吸着能力が低くこの点
を改善する必要がある。そのため、最近では、極性成分
に対する吸着能力が低いという欠点を補うために添着活
性炭が用いられるようになってきた。
There are various deodorization methods such as chemical cleaning method, direct combustion method, catalytic oxidation method, biological deodorization method, and adsorption deodorization method, but the most commonly used method for boat fishing is adsorption deodorization using activated carbon. It is the law. This is because activated carbon adsorbs and removes a wide range of malodorous components. Unfortunately, however, this adsorption deodorization method has a low adsorption capacity for polar components (acidic/basic malodorous components) such as acetaldehyde and ammonia, and this point needs to be improved. Therefore, recently, impregnated activated carbon has come to be used to compensate for the drawback of low adsorption capacity for polar components.

添着活性炭は、周知の通り、例えば銅、亜鉛、銀、銅等
の金属の塩又は例えばフタル酸、硫酸等の酸(有機酸、
無機酸)からなる添着剤を物理的手段によって活性炭の
表面に添着したものであり、極性成分に対する吸着能力
も良好である。しかし、これらの添着活性炭は、上記し
たように添着剤を物理吸着で活性炭表面に付着している
ため、使用中に脱離したり、また湿式成形で加工した際
添着剤が脱落し性能が著しく低下するという問題点があ
る。
As is well known, impregnated activated carbon is a salt of a metal such as copper, zinc, silver, or copper, or an acid (organic acid, etc.) such as phthalic acid or sulfuric acid.
An impregnant consisting of an inorganic acid is attached to the surface of activated carbon by physical means, and it has good adsorption ability for polar components. However, as mentioned above, these impregnated activated carbons have the impregnant attached to the surface of the activated carbon through physical adsorption, so they may come off during use, or the impregnant may fall off during wet molding, resulting in a significant drop in performance. There is a problem with that.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

本発明の目的は、したがって、特に例えばアンモニア臭
などのような塩基性悪臭成分に対してすぐれた脱臭性能
を有し、しかもその性能が長時間にわたって安定的に持
続し得るような改良された脱臭用活性炭を桿供すること
にある。
Therefore, an object of the present invention is to provide an improved deodorizing system that has excellent deodorizing performance, particularly against basic malodorous components such as ammonia odor, and that can stably maintain this performance over a long period of time. The purpose is to provide activated charcoal for use.

〔課題を解決するための手段〕[Means to solve the problem]

本発明者らは、上記した目的を達成すべく鋭意研究の結
果、活性炭の有する分子構造(芳香環が蜂の巣のように
連結した芳香族多環化合物に相当すると考えられている
)に着目し、その芳香環に塩基性臭気成分吸着用のスル
ホン酸基を直接化学結合により固定化するのが有効であ
るという知見を得、以下に詳述する本発明を完成した。
As a result of intensive research to achieve the above object, the present inventors focused on the molecular structure of activated carbon (which is thought to correspond to an aromatic polycyclic compound in which aromatic rings are connected like a honeycomb), We found that it is effective to directly immobilize a sulfonic acid group for adsorbing basic odor components to the aromatic ring by chemical bonding, and completed the present invention as detailed below.

本発明は、原料活性炭と硫酸を無水酢酸の存在下におい
て反応させることによって得られるものであり、かつそ
の表面部位に固定的に化学結合せしめられたスルホン酸
基を有してなることを特徴とする脱臭用活性炭にある。
The present invention is characterized in that it is obtained by reacting raw material activated carbon and sulfuric acid in the presence of acetic anhydride, and has a sulfonic acid group fixedly chemically bonded to its surface site. There is activated carbon for deodorization.

[作 用] 本発明の脱臭用活性炭は、前記した通り、原料活性炭と
硫酸を無水酢酸の存在下において反応させることによっ
て得られるものである。このようにしてスルホン化を実
施すると、官能基としてのスルホン酸基が活性炭分子の
末端に固定的に化学結合せしめられ、よって、活性炭の
表面部位をスルホン酸基が取り囲んだ構造となる。これ
を反応式で示すと、例えば次の通りである(活性炭はそ
の考えられる分子構造の一部が示される):活性炭  
      固定化スルホン酸基含有活性炭 このようにして活性炭の表面部位に固定化されたスルホ
ン酸基(−5O3M)は、使用中に脱離したり、湿式成
形中に脱落したりすることがない。また、一般の塩基性
臭気用の硫酸添着活性炭が水洗や高温放置で硫酸が脱離
して性能が低下するのに対し、上記のようにして合成し
たスルホン化活性炭は、スルホン酸基が活性炭に化学結
合で固定化されているため、吸着性能の低下は全く見ら
れない。さらにまた、硫酸添着活性炭の場合、硫酸が凝
集してしまい有効に作用しないのに対し、本性ではスル
ホン酸基が活性炭表面に均一に固定化されているため、
塩基性ガスの除去性能は格段に優れている。さらにまた
、吸着性能の持続性に関しては、初期の吸着性能がすで
に従来品と比して格段に向上しているため、従来品と同
レベルの吸着性能に敗る期間は長くなり、従ってこの面
からも持続性は向上する(第2図参照)。
[Function] As described above, the deodorizing activated carbon of the present invention is obtained by reacting raw material activated carbon and sulfuric acid in the presence of acetic anhydride. When sulfonation is carried out in this manner, the sulfonic acid group as a functional group is fixedly chemically bonded to the terminal end of the activated carbon molecule, resulting in a structure in which the surface portion of the activated carbon is surrounded by sulfonic acid groups. For example, this reaction formula is as follows (a part of the possible molecular structure of activated carbon is shown):Activated carbon
Activated Carbon Containing Immobilized Sulfonic Acid Groups The sulfonic acid groups (-5O3M) immobilized on the surface of activated carbon in this way do not come off during use or fall off during wet molding. In addition, while sulfuric acid-impregnated activated carbon for general basic odors loses its performance due to sulfuric acid being released when washed with water or left at high temperatures, the sulfonated activated carbon synthesized as described above has sulfonic acid groups chemically bonded to the activated carbon. Since it is immobilized by bonding, no deterioration in adsorption performance is observed at all. Furthermore, in the case of sulfuric acid-impregnated activated carbon, the sulfuric acid aggregates and does not work effectively, whereas in the case of sulfuric acid groups, the sulfonic acid groups are uniformly immobilized on the activated carbon surface.
The basic gas removal performance is extremely excellent. Furthermore, regarding the sustainability of adsorption performance, since the initial adsorption performance has already been significantly improved compared to conventional products, the period during which the adsorption performance loses the same level as conventional products will be longer. Sustainability also improves (see Figure 2).

さらにまた、従来の技術では硫酸のみの処理で活性炭に
スルホン酸基を導入しているが、この方法で導入される
スルホン酸基の量は少なく、従って脱臭効果も少ない。
Furthermore, in the conventional technique, sulfonic acid groups are introduced into activated carbon by treatment with only sulfuric acid, but the amount of sulfonic acid groups introduced by this method is small, and therefore the deodorizing effect is also small.

これとは対称的に、本発明では、無水酢酸の存在下で硫
酸を滴下し、最適温度条件下で反応を行なうため、活性
炭表面に固定化されるスルホン酸基の量は格段に増加し
、従って脱臭効率も極めて高くなる。ここで、無水酢酸
が存在することによってスルホン化の反応効率が向上し
た理由として、一つは反応中間体としてカチオン中間体
が生成した際に溶媒としての無水酢酸がそのカチオン中
間体の安定化に寄与し、反応を促進させたこと、そして
二つ目の理由として、無水酢酸が生成してくる水の分子
と反応してその水の分子を除去しスルホン化を促進させ
たことが、考えられる。
In contrast, in the present invention, sulfuric acid is added dropwise in the presence of acetic anhydride and the reaction is carried out under optimal temperature conditions, so the amount of sulfonic acid groups immobilized on the activated carbon surface is significantly increased. Therefore, the deodorizing efficiency is also extremely high. Here, one of the reasons why the reaction efficiency of sulfonation was improved by the presence of acetic anhydride is that when a cation intermediate is generated as a reaction intermediate, acetic anhydride as a solvent stabilizes the cation intermediate. The second reason is that acetic anhydride reacts with the generated water molecules, removes the water molecules, and promotes sulfonation. .

ちなみに、本発明による固定化スルホン酸基含有活性炭
、硫酸添着活性炭、そして無添着活性炭のそれぞれにつ
いてアンモニア吸着特性をグラフで示すと、第1図に示
す通りである。なお、アンモニア初期濃度は200pp
mに設定した。この図から、本発明の活性炭のすぐれた
アンモニア吸着特性が理解できる。
Incidentally, the ammonia adsorption characteristics of the immobilized sulfonic acid group-containing activated carbon, the sulfuric acid impregnated activated carbon, and the non-impregnated activated carbon according to the present invention are shown in graphs as shown in FIG. The initial concentration of ammonia is 200pp.
It was set to m. From this figure, the excellent ammonia adsorption properties of the activated carbon of the present invention can be understood.

〔実施例] 本発明の脱臭用活性炭は、無水酢酸の存在下、原料活性
炭を硫酸処理して調製することができる。
[Example] The deodorizing activated carbon of the present invention can be prepared by treating raw material activated carbon with sulfuric acid in the presence of acetic anhydride.

原料活性炭としては、工業的に一般に入手可能な活性炭
、例えば活性炭素繊維、粉末状又は粒状の活性炭、その
他を任意に選択して使用することができる。使用する原
料活性炭の形態、粉末度、粒度等の条件も使用目的に応
じて任意に変更可能である。
As the raw material activated carbon, commercially available activated carbon such as activated carbon fibers, powdered or granular activated carbon, and others can be arbitrarily selected and used. Conditions such as the form, powder size, and particle size of the raw material activated carbon to be used can also be changed arbitrarily depending on the purpose of use.

原料活性炭の硫酸処理はいろいろな手法に従って行うこ
とができるが、原料活性炭と無水酢酸を混合した後、得
られた混合物に対して硫酸を徐々に滴下して行くのが好
ましい。硫酸としては濃硫酸(濃度98%程度)が好ま
しく、これよりも希薄な希硫酸や水の含有量の多い硫酸
等の使用は、スルホン化が十分に進行しないので、避け
なければならない。すなわち、スルホン化の反応系に水
の分子が存在すると、反応が非常におこりにくくなるか
らである。硫酸の滴下量は広い範囲で変更し得るという
ものの、好ましくは、原料活性炭100に対して約60
重量%以上である。約60重量%を下廻る硫酸滴下量で
は、90%以上の悪臭成分(例えばアンモニア)除去率
を達成するのが困難となるであろう。また、この硫酸処
理の処理温度は、好ましくは約50〜90°C1さらに
好ましくは約60〜70°Cである。
Although the raw activated carbon can be treated with sulfuric acid according to various methods, it is preferable to mix the raw activated carbon and acetic anhydride and then gradually drop sulfuric acid into the resulting mixture. Concentrated sulfuric acid (concentration of about 98%) is preferable as the sulfuric acid, and use of dilute sulfuric acid diluted or sulfuric acid containing a large amount of water should be avoided since sulfonation will not proceed sufficiently. That is, the presence of water molecules in the sulfonation reaction system makes it extremely difficult for the reaction to occur. Although the amount of sulfuric acid added can be varied within a wide range, it is preferably about 60 sulfuric acid per 100 s of raw activated carbon.
% by weight or more. If the amount of sulfuric acid added is less than about 60% by weight, it will be difficult to achieve a removal rate of malodorous components (eg ammonia) of 90% or more. The temperature of this sulfuric acid treatment is preferably about 50 to 90°C, more preferably about 60 to 70°C.

本発明の脱臭用活性炭の調製は、その好ましいプロセス
の一例を順を追って示すと、次の通りである: (1)原料活性炭の反応器への充填 (2)無水酢酸の添加 (3)反応器内容物の昇温(60〜70°C)及び撹拌
(4)濃硫酸の滴下(撹拌下) (5)撹拌 (6)冷却 (7)濾過 (8)アルコール洗浄 (9)水洗(pHを中性に調節) (10)乾燥 このようにして、本発明による固定化スルホン酸基含有
活性炭が得られる。
An example of a preferred process for preparing the deodorizing activated carbon of the present invention is as follows: (1) Filling the raw material activated carbon into a reactor (2) Adding acetic anhydride (3) Reaction Raising the temperature of the contents of the vessel (60 to 70°C) and stirring (4) Adding concentrated sulfuric acid dropwise (with stirring) (5) Stirring (6) Cooling (7) Filtration (8) Washing with alcohol (9) Washing with water (to adjust the pH) Adjustment to neutrality) (10) Drying In this way, the activated carbon containing immobilized sulfonic acid groups according to the present invention is obtained.

本発明による固定化スルホン酸基含有活性炭は、脱臭目
的及びその他の目的で使用するため、いろいろな形態に
加工して使用することができる。例えば、本発明の活性
炭をペーパー状に抄紙し、エアピュリファイアのエレメ
ントや、脱臭紙(障子紙、襖紙、包装紙等)として使用
することができる。また、粒状活性炭は容器にそのま一
充填して、例えば冷蔵庫、下駄箱等の脱臭剤として使用
できる。
The immobilized sulfonic acid group-containing activated carbon according to the present invention can be processed into various forms and used for deodorizing purposes and other purposes. For example, the activated carbon of the present invention can be made into paper and used as an element of an air purifier or deodorizing paper (shoji paper, sliding door paper, wrapping paper, etc.). Furthermore, the granular activated carbon can be used as a deodorizing agent for refrigerators, shoe cabinets, etc. by filling the container as is.

以下、本発明による固定化スルホン酸基含有活性炭の調
製とそのすぐれた脱臭性能を具体例を参照しながら詳細
に説明する。なお、アンモニアの吸着性能に関しての評
価はバッチ式で、容積15fのガラス容器中に200p
p−のアンモニアガスを充満させ、その中へ試料0.5
gを加え、容器内のアンモニア検知管によりアンモニア
濃度を測定することによって行った。アンモニア濃度の
測定値から吸着開始30分後のアンモニア残存率をもと
め、このアンモニア残存率よりアンモニア除去率を算出
した。
Hereinafter, the preparation of the immobilized sulfonic acid group-containing activated carbon according to the present invention and its excellent deodorizing performance will be explained in detail with reference to specific examples. The evaluation of ammonia adsorption performance was conducted using a batch method.
Fill with p- ammonia gas and place 0.5 of the sample into it.
g was added thereto, and the ammonia concentration was measured using an ammonia detection tube inside the container. The ammonia residual rate 30 minutes after the start of adsorption was determined from the measured ammonia concentration, and the ammonia removal rate was calculated from this ammonia residual rate.

ス1」ロー 活性炭素繊維200gを無水酢酸1000II11に均
一に分散させ、濃硫酸(98%)90−を、3d/分の
滴下速度で処理温度60〜70°Cで30分間にわたっ
て滴下した。その後、撹拌下に1時間にわたって反応処
理を行い、スルホン化を完了させた。反応終了後、ガラ
スフィルタを用いてスルホン化活性炭繊維を濾別分離し
、アルコールで洗浄し、そしてptt値が中性になるま
で水洗をくり返した。得られた固定化スルホン酸基含有
活性炭繊維を120°Cで乾燥した後、アンモニアの吸
着性能に関して評価した。得られた結果を下記の第1表
及び添付の第3図に示す。
200 g of activated carbon fibers were uniformly dispersed in acetic anhydride 1000 II 11, and concentrated sulfuric acid (98%) 90 was added dropwise at a rate of 3 d/min over a period of 30 minutes at a treatment temperature of 60-70°C. Thereafter, reaction treatment was carried out for 1 hour while stirring to complete the sulfonation. After the reaction was completed, the sulfonated activated carbon fibers were separated by filtration using a glass filter, washed with alcohol, and washed with water repeatedly until the PTT value became neutral. After drying the obtained activated carbon fiber containing immobilized sulfonic acid groups at 120°C, the ammonia adsorption performance was evaluated. The results obtained are shown in Table 1 below and the attached Figure 3.

また、得られた固定化スルホン酸基含有活性炭繊維のス
ルホン酸基含有量を硫黄の元素分析より測定したところ
、9.7 Xl0−’モル/gであった。
Further, the sulfonic acid group content of the obtained immobilized sulfonic acid group-containing activated carbon fiber was measured by elemental analysis of sulfur, and was found to be 9.7 Xl0-' mol/g.

ちなみに、本発明者らのこの実施例や他の実験の結果か
ら、90%以上のアンモニア除去率を達成するためには
本発明の活性炭中に含まれるスルホン酸基の量は7.O
Xl0−’モル/g以上であることが好ましい。
Incidentally, from the results of this example and other experiments conducted by the present inventors, in order to achieve an ammonia removal rate of 90% or more, the amount of sulfonic acid groups contained in the activated carbon of the present invention is 7. O
It is preferable that it is Xl0-'mol/g or more.

!粗炭l 活性炭(粉状)200gを無水酢酸400dに均一に分
散させ、前記実施例1と同様の処理を行なった。
! Crude carbon 200 g of activated carbon (powder) was uniformly dispersed in 400 d of acetic anhydride, and the same treatment as in Example 1 was performed.

得られた固定化スルホン酸基含有活性炭のアンモニア吸
着性能を前記実施例1と同様にして評価した。得られた
結果を下記の第1表及び添付の第3図に示す。
The ammonia adsorption performance of the obtained immobilized sulfonic acid group-containing activated carbon was evaluated in the same manner as in Example 1 above. The results obtained are shown in Table 1 below and the attached Figure 3.

また、得られた固定化スルホン酸基含有活性炭のスルホ
ン酸基含有量を硫黄の元素分析により測定したところ、
10.6X10−’モル/gであった。
In addition, when the sulfonic acid group content of the obtained immobilized sulfonic acid group-containing activated carbon was measured by elemental analysis of sulfur,
It was 10.6 x 10-' mol/g.

さらにまた、この本発明の活性炭のアンモニア吸着特性
の持続性を評価するため、同じ吸着性能評価を3回、5
回、6回、7回にわたって繰り返し、それぞれの結果を
第2図にプロットした。また、比較のために、原料活性
炭(無添着活性炭)についても同様な操作を繰り返し、
それぞれの結果を第2図にプロットした。これらの結果
から、本発明の活性炭の場合、初期のアンモニア吸着特
性が顕著にすぐれているばかりでなくそれが長時間にわ
たって持続され、6回にわたって反復使用後にはじめて
従来の活性炭(無添着活性炭)の新品とほぼ同等のアン
モニア吸着特性を示すということが判る。
Furthermore, in order to evaluate the sustainability of the ammonia adsorption properties of the activated carbon of the present invention, the same adsorption performance evaluation was carried out three times and five times.
The test was repeated 3 times, 6 times, and 7 times, and the results are plotted in FIG. For comparison, the same operation was repeated for raw activated carbon (non-impregnated activated carbon).
The respective results are plotted in Figure 2. These results show that the activated carbon of the present invention not only has a markedly superior initial ammonia adsorption property, but also maintains it for a long time, and only after repeated use six times does it surpass the conventional activated carbon (non-impregnated activated carbon). It can be seen that the ammonia adsorption properties are almost the same as new products.

北殿五工 濃硫酸(98%) 90aeを活性炭200g中に加え
、処理温度60〜70℃で3時間にわたって反応処理を
行ない、スルホン化を完了させた。反応終了後、ガラス
フィルタを用いてスルホン化活性炭を濾別分離し、pH
値が中性になるまで水洗をくり返した。
Kitadono Goko concentrated sulfuric acid (98%) 90 ae was added to 200 g of activated carbon, and reaction treatment was carried out at a treatment temperature of 60 to 70° C. for 3 hours to complete the sulfonation. After the reaction is completed, the sulfonated activated carbon is separated by filtration using a glass filter, and the pH is adjusted.
Washing with water was repeated until the value became neutral.

得られた固定化スルホン酸含有活性炭のアンモニア吸着
性能を前記実施例1と同様にして評価した。
The ammonia adsorption performance of the obtained immobilized sulfonic acid-containing activated carbon was evaluated in the same manner as in Example 1 above.

得られた結果を下記の第1表に示す。The results obtained are shown in Table 1 below.

また、得られた固定化スルホン酸基含有活性炭のスルホ
ン酸基含有量を硫黄の元素分析により測定したところ、
2.5X10−’モル/gであった。このようにスルホ
ン酸基含有量が小さいことの理由としては、無水酢酸の
不存在下においてスルホン化を行ったので、反応効率が
非常に悪くなったことが考えられる。
In addition, when the sulfonic acid group content of the obtained immobilized sulfonic acid group-containing activated carbon was measured by elemental analysis of sulfur,
It was 2.5 x 10-' mol/g. The reason for such a small content of sulfonic acid groups is thought to be that the sulfonation was performed in the absence of acetic anhydride, resulting in a very poor reaction efficiency.

ル較拠又 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、処理温度を35〜45°Cに変更した
。得られた結果を下記の第1表及び添付の第3図に示す
。本例でも、小さいスルホン酸基含有量しか得られなか
ったが、これは、処理時間の延長によっても、反応が進
むための活性化エネルギーを低温故に越えることができ
ないので、増加させることができないためである。
The procedure described in Example 1 above was also repeated. However, in this example, for comparison, the treatment temperature was changed to 35 to 45°C. The results obtained are shown in Table 1 below and the attached Figure 3. In this example as well, only a small sulfonic acid group content was obtained, but this cannot be increased even by extending the treatment time because the activation energy for the reaction to proceed cannot be exceeded due to the low temperature. It is.

北較拠主 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、処理温度を100〜110°Cに変更
した。得られた結果を下記の第1表及び添付の第3図に
示す。本例でも、小さいスルホン酸基含有量しか得られ
なかったが、これは、処理温度が高いために活性炭表面
が硫酸によって侵かされたのが原因にあると考えられる
。すなわち、活性炭を構成している炭素と硫酸が反応し
て活性炭より炭素が欠落して活性炭が侵食されたものと
考えられる。硫酸がスルホン化に使用されるよりも、上
記反応に使用されるため、結果としてスルホン酸基の量
が少なくなったと考えられる。
The procedure described in Example 1 above was repeated. However, in this example, the treatment temperature was changed to 100 to 110°C for comparison. The results obtained are shown in Table 1 below and the attached Figure 3. In this example as well, only a small content of sulfonic acid groups was obtained, but this is thought to be because the surface of the activated carbon was attacked by sulfuric acid due to the high treatment temperature. That is, it is thought that the carbon constituting the activated carbon reacted with sulfuric acid, causing carbon to be missing from the activated carbon and the activated carbon to be eroded. It is believed that because sulfuric acid was used in the above reaction rather than in sulfonation, the amount of sulfonic acid groups was reduced as a result.

ル較桝土 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、活性炭素繊維200gに対して添加す
る濃硫酸の量を60dに変更した。得られた結果を下記
の第1表及び添付の第3図に示す。
The procedure described in Example 1 above was repeated. However, in this example, for comparison, the amount of concentrated sulfuric acid added to 200 g of activated carbon fiber was changed to 60 d. The results obtained are shown in Table 1 below and the attached Figure 3.

本例でも、小さいスルホン酸基含有量しか得られなかっ
たが、これは、濃硫酸の添加量が少ないためにスルホン
化の効率が低下したことに原因があると考えられる。
In this example as well, only a small content of sulfonic acid groups was obtained, but this is thought to be due to a decrease in the efficiency of sulfonation due to the small amount of concentrated sulfuric acid added.

北較■工 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、無水酢酸400adと濃硫酸90j!
l!の混合液に活性炭200gを加え、処理温度60〜
70℃で3時間にわたって反応処理を行なった。
The procedure described in Example 1 above was repeated. However, in this example, for comparison, 400ad of acetic anhydride and 90j of concentrated sulfuric acid!
l! Add 200g of activated carbon to the mixed solution and set the treatment temperature to 60~
The reaction treatment was carried out at 70°C for 3 hours.

得られた結果を下記の第1表及び添付の第3図に示す 此fl影 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、処理温度を50〜60℃に変更した。
The results obtained are shown in Table 1 below and in the accompanying Figure 3.The procedure described in Example 1 above was repeated. However, in this example, for comparison, the treatment temperature was changed to 50 to 60°C.

得られた結果を下記の第1表及び添付の第3図に示す。The results obtained are shown in Table 1 below and the attached Figure 3.

比較±1 前記実施例1に記載の手法を繰り返した。但し、本例で
は、比較のため、処理温度を80〜90°Cに変更した
。得られた結果を次の第1表及び添付の第3図に示す。
Comparison ±1 The procedure described in Example 1 above was repeated. However, in this example, for comparison, the treatment temperature was changed to 80 to 90°C. The results obtained are shown in the following Table 1 and the attached Figure 3.

第11 第1表に記載の結果から、本発明による脱臭用活性炭は
従来の脱臭用活性炭に較べてスルホン酸基含有量が大で
あり、これに由来してアンモニア吸着特性も顕著にすぐ
れていることが理解される。
11 From the results shown in Table 1, the activated carbon for deodorization according to the present invention has a higher content of sulfonic acid groups than the conventional activated carbon for deodorization, and due to this, its ammonia adsorption properties are also significantly superior. That is understood.

また、添付の第3図から、処理温度はアンモニア除去率
に大きく影響し、本発明の脱臭用活性炭の場合、アンモ
ニア除去率として90%以上が所望であるならば、処理
温度は好ましくは50〜90°C1より好ましくは60
〜70°Cであることが理解される。
Furthermore, from the attached Figure 3, the treatment temperature greatly affects the ammonia removal rate, and in the case of the deodorizing activated carbon of the present invention, if an ammonia removal rate of 90% or more is desired, the treatment temperature is preferably 50% to 50%. 90°C1 more preferably 60
It is understood that ~70°C.

実施■主 前記実施例1に記載の手法を繰り返した。但し、本例で
は、アンモニア除去率に及ぼす濃硫酸添加量の影響を調
べるため、濃硫酸の添加量をいろいろに変更した。得ら
れた結果をプロットしたものが添付の第4図である。第
4図のグラフから、アンモニア除去率90%以上を達成
するためには濃硫酸添加量(活性炭100に対して)は
最低60重量%が必要であることが理解される。
Implementation (2) Main The procedure described in Example 1 above was repeated. However, in this example, in order to investigate the effect of the amount of concentrated sulfuric acid added on the ammonia removal rate, the amount of concentrated sulfuric acid added was varied. The attached FIG. 4 is a plot of the obtained results. From the graph in FIG. 4, it is understood that in order to achieve an ammonia removal rate of 90% or more, the amount of concentrated sulfuric acid added (based on 100% activated carbon) must be at least 60% by weight.

〔発明の効果〕〔Effect of the invention〕

本発明による脱臭用活性炭は、一般の塩基性臭気用の硫
酸添着活性炭が水洗や、高温放置で硫酸脱離して性能が
低下するのに対し、スルホン酸基が゛活性炭に化学結合
で固定化されているため、吸着性能の低下が全く見られ
ない。また、硫酸添着活性炭の場合、硫酸が凝集してし
まい有効に作用しないのに対し、本発明の活性炭では、
スルホン酸基が活性炭の表面に均一に固定化されている
ため、塩基性ガスの除去性能は格段に優れている。
The deodorizing activated carbon according to the present invention has sulfonic acid groups fixed to the activated carbon through chemical bonds, whereas the performance of general sulfuric acid-impregnated activated carbon for basic odors is degraded by desorption of sulfuric acid when washed with water or left at high temperatures. Because of this, no deterioration in adsorption performance is observed at all. In addition, in the case of activated carbon impregnated with sulfuric acid, the sulfuric acid aggregates and does not work effectively, whereas in the activated carbon of the present invention,
Since the sulfonic acid groups are uniformly immobilized on the surface of activated carbon, the basic gas removal performance is extremely excellent.

本発明の脱臭用活性炭はこのように特に塩基性ガスの吸
着特性にすぐれているので、脱臭用として広くかつ有利
に利用できる。
Since the activated carbon for deodorization of the present invention has particularly excellent adsorption properties for basic gases, it can be widely and advantageously used for deodorization.

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

第1図は、各種の活性炭のアンモニア吸着特性をプロッ
トしたグラフであり、 第2図は、各種の活性炭のアンモニア吸着特性(繰り返
し試験)をプロットしたグラフであり、第3図は、アン
モニア除去率に及ぼす処理温度の影響をプロットしたグ
ラフであり、そして第4図は、アンモニア除去率に及ぼ
す濃硫酸添加量の影響をプロットしたグラフである。 吸着時間(分) 各種の活性炭のアンモニア吸着特性 第11 曲線1・・・固定化スルホン酸基含有活性炭曲線2・・
・硫酸添着活性炭 曲線3・・・無添着活性炭 吸着時間(分) 第2 回 一一一一無添着活性炭 アンモニア除去率に及ぼす処理温度の影響第3図 a硫酸添加量(重量%) アンモニア除去率に及ぼす濃硫酸添加量の影響第4図
Figure 1 is a graph plotting the ammonia adsorption characteristics of various activated carbons, Figure 2 is a graph plotting the ammonia adsorption characteristics (repetitive tests) of various activated carbons, and Figure 3 is a graph plotting the ammonia adsorption characteristics of various activated carbons. FIG. 4 is a graph plotting the effect of treatment temperature on the ammonia removal rate, and FIG. 4 is a graph plotting the effect of the amount of concentrated sulfuric acid added on the ammonia removal rate. Adsorption time (minutes) Ammonia adsorption characteristics of various activated carbons No. 11 Curve 1...Curve 2 of activated carbon containing immobilized sulfonic acid groups...
・Sulfuric acid impregnated activated carbon curve 3...Non-impregnated activated carbon adsorption time (minutes) 2nd 1111 Non-impregnated activated carbon Effect of treatment temperature on ammonia removal rate Figure 3a Amount of sulfuric acid added (wt%) Ammonia removal rate Figure 4 Effect of added amount of concentrated sulfuric acid on

Claims (1)

【特許請求の範囲】[Claims] 1、原料活性炭と硫酸を無水酢酸の存在下において反応
させることによって得られるものであり、かつその表面
部位に固定的に化学結合せしめられたスルホン酸基を有
してなることを特徴とする脱臭用活性炭。
1. A deodorizing product obtained by reacting raw material activated carbon and sulfuric acid in the presence of acetic anhydride, and having a sulfonic acid group fixedly chemically bonded to its surface site. activated carbon for use.
JP2329884A 1990-11-30 1990-11-30 Activated carbon for deodorization Expired - Fee Related JP2965347B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2329884A JP2965347B2 (en) 1990-11-30 1990-11-30 Activated carbon for deodorization

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2329884A JP2965347B2 (en) 1990-11-30 1990-11-30 Activated carbon for deodorization

Publications (2)

Publication Number Publication Date
JPH04200634A true JPH04200634A (en) 1992-07-21
JP2965347B2 JP2965347B2 (en) 1999-10-18

Family

ID=18226329

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2329884A Expired - Fee Related JP2965347B2 (en) 1990-11-30 1990-11-30 Activated carbon for deodorization

Country Status (1)

Country Link
JP (1) JP2965347B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2011025026A1 (en) * 2009-08-31 2011-03-03 国立大学法人東京工業大学 Sterilization method
JP2019181008A (en) * 2018-04-16 2019-10-24 エステー株式会社 Deodorant sheet and deodorant method
JP2019198562A (en) * 2018-05-18 2019-11-21 エステー株式会社 Deodorant

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2011025026A1 (en) * 2009-08-31 2011-03-03 国立大学法人東京工業大学 Sterilization method
JP4925379B2 (en) * 2009-08-31 2012-04-25 国立大学法人東京工業大学 Sterilization method
CN102596263A (en) * 2009-08-31 2012-07-18 国立大学法人东京工业大学 Sterilization method
US9357774B2 (en) 2009-08-31 2016-06-07 Tokyo Institute Of Technology Sterilization method
JP2019181008A (en) * 2018-04-16 2019-10-24 エステー株式会社 Deodorant sheet and deodorant method
JP2019198562A (en) * 2018-05-18 2019-11-21 エステー株式会社 Deodorant

Also Published As

Publication number Publication date
JP2965347B2 (en) 1999-10-18

Similar Documents

Publication Publication Date Title
US5538929A (en) Phosphorus-treated activated carbon composition
US6074974A (en) Manufacturing method of granulated complex molecular sieve composition having multi-functions
JPH04502271A (en) Method for producing catalyst for removing nitrogen oxides from waste gas
CN109179554A (en) Utilize the method for fortimicin in manganese dioxide load biological carbon materials removal water body
JP2009226265A (en) Water selectivity adsorbent and manufacturing method
JPH05811A (en) Activated carbon material, its production and use thereof
KR100214444B1 (en) Complex molecular sieve granules for deodorizer and their preparations
JPH04200634A (en) Active carbon for deodorization
KR102478521B1 (en) Composite adsorbent containing coffee beans and iron hydroxide
JPH08259344A (en) Porous adsorbing material
JPS6322184B2 (en)
JPH03151041A (en) Molded adsorbent
JP3138749B2 (en) Method for producing carbides having deodorizing ability, ion exchange ability, and catalytic ability using plant materials
EP0799178A1 (en) Improved process for the purification of aromatic polycarboxylic acids
CN114146689A (en) Aluminum/cerium bimetal organic framework material, preparation method and application thereof in phosphorus adsorption and removal
JPH11128737A (en) Bromine-bearing activated carbon and production of bromine-bearing activated carbon
JP3695845B2 (en) Water purification material
KR102478525B1 (en) Activated carbon prepared from coffee beans
KR102179393B1 (en) Adsorbent of ammonium ion and method for preparing the same
JP3269306B2 (en) Sulfur compound adsorbent
JPH05154353A (en) Method for removing nitrogen oxide
JP2002211912A (en) Method for modifying activated carbon, modified activated carbon and adsorbent using the same
JP3271380B2 (en) Deodorant and method for producing the same
TWI314473B (en) High activity chemical filter, its preparation and use in removing hazard gas by adsorption
JP2642106B2 (en) Deodorant fiber and method for producing the same

Legal Events

Date Code Title Description
LAPS Cancellation because of no payment of annual fees