JPH0521623B2 - - Google Patents

Info

Publication number
JPH0521623B2
JPH0521623B2 JP60253415A JP25341585A JPH0521623B2 JP H0521623 B2 JPH0521623 B2 JP H0521623B2 JP 60253415 A JP60253415 A JP 60253415A JP 25341585 A JP25341585 A JP 25341585A JP H0521623 B2 JPH0521623 B2 JP H0521623B2
Authority
JP
Japan
Prior art keywords
iron
composition
granulated slag
weight
acid
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
Application number
JP60253415A
Other languages
Japanese (ja)
Other versions
JPS62114647A (en
Inventor
Yoshimasa Igari
Shoichiro Yokoyama
Chiaki Oohama
Ryosuke Fukui
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.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
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 Agency of Industrial Science and Technology filed Critical Agency of Industrial Science and Technology
Priority to JP60253415A priority Critical patent/JPS62114647A/en
Publication of JPS62114647A publication Critical patent/JPS62114647A/en
Publication of JPH0521623B2 publication Critical patent/JPH0521623B2/ja
Granted legal-status Critical Current

Links

Landscapes

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

Description

【発明の詳細な説明】[Detailed description of the invention]

(産業上の利用分野) 本発明は、アルカリ処理水砕スラグと鉄()
化合物とを組合わせてなる新規な脱臭性基剤に関
する。 (従来の技術) 鉄()化合物を主成分とし、これにアスコル
ビン酸など有機酸成分を結合させてなる組成物
(以下鉄()組成物という)が極めて活性が高
く各種の機能を示すことは先に本発明者らは見出
し、提案した(特開昭59−132937号、同60−
66753号公報)。 特にこの鉄()組成物は悪臭ガス例えば、ア
ンモニア、含硫黄化合物の吸着、除去作用が優れ
ている。 (発明が解決しようとする問題点) しかし、上記の鉄()組成物は従来のものよ
り格段に優れた脱臭機能を示すが、吸着ガスの
pHにより吸着性が影響を受け、酸性ガスの吸着
がアンモニアガスの場合より劣るという難点があ
り、この点の克服、制御の点でまだ満足すべきも
のとはいえなかつた。 また鉄()組成物単独ではコストが高いの
で、実用上の観点から、適当な担体の開発が要求
されていた。 (問題点を解決するための手段) 本発明者らは、上記の鉄()組成物の問題点
を克服するため鋭意研究を重ねた結果、本発明者
らが先に提案したアルカリ処理水砕スラグ(特許
第1115603号)に所定比率で混合し、水分を所定
量含有させることにより、コストを低下させると
ともにPH依存性の点に克服しうることを見出し、
この知見に基づき本発明を完成するに至つた。 すなわち本発明は、微粉状水砕スラグを少なく
とも0.5Nのアルカリ溶液にて少なくとも30分間
処理後、該処理水砕スラグをろ別分離、水洗後加
熱乾燥して得たかさ比重が低下され且つ比表面積
が増大された表面特性を改良した水砕スラグ(以
下、単にBSという)に対し、鉄()組成物を
混合し、かつ含水率10〜50重量%としてなること
を特徴とする脱臭性基剤(以下第1発明という)
及びBSを有機酸で中和した後、この水砕スラグ
を鉄()化合物を主成分としこれに有機酸成分
を結合させてなる組成物と混合してなることを特
徴とする脱臭性基剤(以下第2発明という)を提
供するものである。 本発明(第1発明及び第2発明をいう)におい
てBSに対する鉄()組成物の混合比は5〜60
重量%が好ましく、10〜50重量%がより好まし
く、20〜30重量%が特に好ましい。鉄()組成
物が5重量%未満では鉄()組成物が反応の主
体であるため、その量が不足であり、60重量%を
越えて多すぎると鉄()組成物の添加割合に比
しての性能向上は生じないのである。 本発明に用いられるBSは安価な比表面積の大
きな固体塩基であり、前記特許第1115603号記載
の方法により調整できる。このBSは鉄()組
成物との共存により悪臭としての酸性ガス(硫化
水素、メチルメルカプタン、二硫化メチル、悪臭
有機酸)の吸収性を著しく向上させる。すなわち
アルカリ処理水砕のみでも脱臭効果があるが、鉄
()組成物とBSを混合したものは単なる混合品
でもその効果が相乗効果的に発揮される。 本発明に用いられる鉄()組成物においてそ
の主成分である鉄()化合物の例としては、硫
酸第一鉄、塩化第一鉄、硝酸第一鉄、臭化第一
鉄、ヨウ化第一鉄、硫酸第一鉄アンモニウム(モ
ール塩)などの鉄()無機塩の外、没食子酸第
一鉄、リンゴ酸第一鉄、フマル酸第一鉄などの鉄
()有機塩があげられる。鉄()化合物は上
記例示のものに限定されるものではなく、水中に
溶解し、2価鉄イオンを形成するものであれば任
意のものを用いることができる。 本発明において、有機酸とは広義で用いられ
る。有機酸成分は鉄()化合物の2価鉄イオン
に配位して活性な2価鉄イオンを安定化させる作
用を有する。このような有機酸の例としてはアス
コルビン酸類、グルコン酸類、カルボン酸類があ
げられる。ここでアスコルビン酸類とは、アスコ
ルビン酸、イソアスコルビン酸、そのアルカリ金
属塩などをいい、D−体、L−体、DL−体の全
てが含まれる。特にL−アスコルビン酸が好まし
い。またカルボン酸類としては特に制限はない
が、オキシ酸、例えばクエン酸、イソクエン酸な
どのクエン酸、乳酸、酒石酸、リンゴ酸などが用
いられる。またアミノ酸、例えばエチレンジアミ
ン四酢酸類、4,5−ジアミノピリミジン類など
が好ましく用いられる。 この鉄()組成物において鉄()化合物を
主成分とする。鉄()化合物中の鉄()と有
機酸成分との比率は、有機酸成分がアスコルビン
酸類の場合は通常1:0.02〜0.30(重量比)の範
囲が好ましく、より好ましくは1:0.02〜0.13特
に好ましくは1:0.03〜0.10の範囲である。また
有機酸成分がクエン酸類のようなカルボン酸の場
合は鉄()と有機酸成分との比は1:0.01〜
0.80の範囲とするのが好ましい。上記の範囲の上
限を越えて有機酸類を用いても、、効果の上昇は
望めず経済的でなくなり、また下限未満では、鮮
度保持、脱臭機能が不十分となる。 本発明において有機酸成分は単独でもあるい
は、2種以上併用してもよい。併用の場合、アス
コルビン酸とクエン酸の組合せが好ましく、この
時アスコルビン酸に対しクエン酸が安定剤として
補助的に作用するので、その量は少なくてよい。 なお、この鉄()組成物中塩化ナトリウムを
0.5〜15重量%含有させるのが脱臭作用促進の上
で好ましい。 本発明の鉄()組成物は活性発現のためには
主成分としての鉄()化合物にアスコルビン
酸、グルコン酸、クエン酸のような有機酸成分と
が結合していることが必要である。このような組
成物は両成分を一旦混合、溶解した水溶液を噴霧
乾燥法、凍結乾燥法等により乾燥、粉末化して調
整できる。 また鉄()組成物中にミヨウバンを添加し脱
臭機能を安定化させるのが好ましい。このような
ミヨウバンの添加量は脱臭性基剤の用途、使用形
態によつて異なるが鉄()化合物と有機酸成分
との合計量に対し、100重量%の範囲まで用いら
れるが2〜20重量%の範囲が好ましい。ミヨウバ
ンとしては特に制限はないがカリミヨウバン、ア
ンモニアミヨウバン、ナトリウムミヨウバンなど
が好適で特に焼ミヨウバンが好適である。 本発明のBSと鉄()組成物とからなる組成
物の調整方法には特に制限はないが両者の粉末を
所定比率で混合することにより調整するのが好ま
しい。この場合のBS粉末の比表面積は50〜70
m2/gがよい。この混合物は常法により成形がし
て、板剤、錠剤、粒剤として用いられる。 第1発明の組成物において、微量の水分を保持
させると効果が一段と向上する。その含水量は通
常10重量%以上であり、好ましくは10〜50重量%
であり、20〜30重量%がより好ましい。BSは飽
和水蒸気圧で自重の60%以上の給水率を持つので
水分調整は使用する場所で放置しておくことで達
成される。 第2発明の組成物において、塩基性ガス(アン
モニア、トリメチルアミン)等の吸収をさらに高
めるにはBSをあらかじめ、有機酸で中和処理し
て乾燥したものを用いれば良い。このような有機
酸として酢酸、プロピオン酸のような一塩基酸、
マレイン酸、マロン酸、コハク酸、シユウ酸のよ
うな二塩基酸、その他のリンゴ酸、酒石酸、クエ
ン酸のようなオキシ多塩基酸で処理したBSを用
い、鉄()組成物と混合調整後、粉末もしくは
粒状にして使用すれば、アンモニア等の塩基性ガ
スの脱臭にすぐれるのみならず、BSの持つ高い
比表面積(60〜100m2/g)が改質された表層と
なり、有機溶媒等のガス成分(例えば、スチレ
ン、クレゾール、アセトアルデヒドなど)に対し
ても親和性を示し、広い用途に応用される。この
場合も、酸処理したBSと鉄()組成物の混合
割合は前記と同じで良い。またこの場合、水分5
重量%以上含有させるのが好ましく5〜10%程度
の含水率を持つものがより望ましい。 このような有機酸処理したBSを利用した組成
物は例えば次のようにして調整できる。1〜5%
程度の有機酸溶液50gにBS10gを添加し、30分攪
拌後、一夜放置ろ過乾燥(110℃一晩)した剤に
鉄()組成物を10〜50重量%、望ましくは25〜
30重量%担持させアンモニアガスの吸着性の優れ
る吸着剤を得る。 さらにBSの表面改質方法として、鉄()組
成物の水溶液を直接添加し液性を中性から酸性に
し、これからアンモニア系臭気の除去性能に優れ
た本発明の組成物の粉末を調製してもよい。 (発明の効果) 本発明は鉄()組成物をBSと組合わせてな
るものであり、それぞれを単独で用いた場合に比
べ、酸性悪臭ガス成分に対する顕著に高い吸着力
を示す。一方、鉄()組成物はアンモニアガス
に対してはもともと高い吸着性能を示すので、悪
臭ガスのPHにより吸着性能が影響されることが少
なく、高い活性を長期間にわたり維持するという
優れた効果を奏する。さらに特に第2発明の脱臭
性基剤は有機溶媒系のガスに対しても吸着性を示
す。さらにまた、本発明の組成物は、鉄()組
成物の含有量を低減してしかも、吸着活性を高め
ることができたものであり、コスト上の利点も極
めて大きい。 このような本発明の組成物は、この混合剤を板
状、単なる圧縮成形によつても(60〜150Kg/cm2
成形して、脱臭機能を有する住居、家具、包装材
として利用も可能となるのみならず、プラスチツ
クのフイーラーとして混入し、同様の機能を持た
せた成型材、及びフイルムとしても利用できる。 (実施例) 次に本発明を実施例に基づき、さらに詳細に説
明する。なお実施例中で用いた鉄−アスコルビン
酸は、硫化第一鉄中の鉄1モルに対し、L−アス
コルビン酸0.03モルを結合させた剤である。また
BSは、次のようにして調整したものである。 [調製法] 下記参考例の試料No.8の方法による。 かさ比重0.584 比表面積57.1m2/g [参考例 1] 本発明に用いられるBSの調製例を示す。
(Industrial Application Field) The present invention relates to alkali-treated granulated slag and iron ()
The present invention relates to a novel deodorizing base formed by combining a compound with a compound. (Prior art) It is known that a composition (hereinafter referred to as an iron() composition) which has an iron() compound as its main component and binds an organic acid component such as ascorbic acid thereto is extremely active and exhibits various functions. The present inventors previously discovered and proposed (Japanese Patent Application Laid-open Nos. 59-132937 and 60-
Publication No. 66753). In particular, this iron composition has excellent adsorption and removal effects on malodorous gases such as ammonia and sulfur-containing compounds. (Problem to be solved by the invention) However, although the above-mentioned iron () composition exhibits a deodorizing function that is much superior to conventional ones, it
Adsorption properties are affected by pH, and adsorption of acidic gases is inferior to that of ammonia gas, which is a disadvantage, and the ability to overcome and control this problem has not yet been satisfactory. Furthermore, since the iron () composition alone is expensive, development of an appropriate carrier has been required from a practical standpoint. (Means for Solving the Problems) As a result of extensive research in order to overcome the problems of the above-mentioned iron () composition, the present inventors have developed the alkali-treated granulated We discovered that by mixing slag (Patent No. 1115603) at a predetermined ratio and containing a predetermined amount of water, it is possible to reduce costs and overcome the PH dependence.
Based on this knowledge, we have completed the present invention. That is, the present invention provides a method for treating finely powdered granulated slag with an alkaline solution of at least 0.5N for at least 30 minutes, separating the treated granulated slag by filtration, washing with water, and heating and drying. A deodorizing group characterized by mixing an iron () composition with granulated slag (hereinafter simply referred to as BS) having improved surface properties and increased surface area, and having a water content of 10 to 50% by weight. agent (hereinafter referred to as the first invention)
and BS are neutralized with an organic acid, and then this granulated slag is mixed with a composition comprising an iron () compound as a main component and an organic acid component bonded thereto. (hereinafter referred to as the second invention). In the present invention (referring to the first invention and the second invention), the mixing ratio of the iron () composition to BS is 5 to 60
% by weight is preferred, 10-50% by weight is more preferred, and 20-30% by weight is particularly preferred. If the iron () composition is less than 5% by weight, the iron () composition is the main body of the reaction, so the amount is insufficient; if it exceeds 60% by weight, the amount is too high compared to the addition ratio of the iron () composition. Therefore, no performance improvement occurs. The BS used in the present invention is an inexpensive solid base with a large specific surface area, and can be prepared by the method described in the above-mentioned Patent No. 1115603. This BS significantly improves the absorption of malodorous acidic gases (hydrogen sulfide, methyl mercaptan, methyl disulfide, and malodorous organic acids) by coexisting with the iron() composition. In other words, alkali-treated granulated water alone has a deodorizing effect, but even a simple mixture of iron () composition and BS exhibits its effect synergistically. Examples of iron () compounds that are the main components of the iron () composition used in the present invention include ferrous sulfate, ferrous chloride, ferrous nitrate, ferrous bromide, and ferrous iodide. In addition to iron () inorganic salts such as iron and ferrous ammonium sulfate (Mohr's salt), there are iron () organic salts such as ferrous gallate, ferrous malate, and ferrous fumarate. The iron() compound is not limited to those exemplified above, and any compound can be used as long as it dissolves in water and forms divalent iron ions. In the present invention, organic acid is used in a broad sense. The organic acid component has the effect of stabilizing the active divalent iron ion by coordinating with the divalent iron ion of the iron() compound. Examples of such organic acids include ascorbic acids, gluconic acids, and carboxylic acids. Ascorbic acids herein refer to ascorbic acid, isoascorbic acid, alkali metal salts thereof, and include all of the D-form, L-form, and DL-form. Particularly preferred is L-ascorbic acid. The carboxylic acids are not particularly limited, but oxyacids such as citric acid, isocitric acid, lactic acid, tartaric acid, malic acid, etc. are used. Also, amino acids such as ethylenediaminetetraacetic acids and 4,5-diaminopyrimidines are preferably used. In this iron() composition, an iron() compound is the main component. The ratio of iron () in the iron () compound to the organic acid component is preferably in the range of 1:0.02 to 0.30 (weight ratio), more preferably 1:0.02 to 0.13 when the organic acid component is ascorbic acid. Particularly preferred is a ratio of 1:0.03 to 0.10. In addition, when the organic acid component is a carboxylic acid such as citric acid, the ratio of iron () to the organic acid component is 1:0.01 ~
A range of 0.80 is preferable. Even if the organic acids are used in amounts exceeding the upper limit of the above range, no increase in effectiveness can be expected and it becomes uneconomical, while below the lower limit, freshness preservation and deodorizing functions become insufficient. In the present invention, the organic acid components may be used alone or in combination of two or more. When used in combination, a combination of ascorbic acid and citric acid is preferred, and since citric acid acts auxiliary to ascorbic acid as a stabilizer, the amount thereof may be small. In addition, sodium chloride in this iron () composition is
It is preferable to contain 0.5 to 15% by weight in order to promote the deodorizing effect. In order for the iron () composition of the present invention to exhibit activity, it is necessary that an organic acid component such as ascorbic acid, gluconic acid, or citric acid be bound to the iron () compound as the main component. Such a composition can be prepared by mixing and dissolving the two components in an aqueous solution and drying and pulverizing the mixture by spray drying, freeze drying, or the like. It is also preferable to add alum to the iron composition to stabilize the deodorizing function. The amount of alum added varies depending on the purpose and form of use of the deodorizing base, but it is used up to 100% by weight based on the total amount of iron () compound and organic acid component, but it is 2 to 20% by weight. A range of % is preferred. The alum is not particularly limited, but potassium alum, ammonia alum, sodium alum, etc. are preferred, with roasted alum being particularly preferred. Although there are no particular limitations on the method for preparing the composition of the present invention, which consists of BS and iron () composition, it is preferable to prepare the composition by mixing powders of both in a predetermined ratio. The specific surface area of BS powder in this case is 50-70
m 2 /g is good. This mixture is molded by conventional methods and used as tablets, tablets, and granules. In the composition of the first invention, the effect is further improved when a small amount of water is retained. Its water content is usually 10% by weight or more, preferably 10-50% by weight
and more preferably 20 to 30% by weight. Since BS has a water supply rate of over 60% of its own weight at saturated vapor pressure, moisture adjustment can be achieved by leaving it in the place where it will be used. In the composition of the second invention, in order to further enhance the absorption of basic gases (ammonia, trimethylamine), etc., it is sufficient to use BS that has been previously neutralized with an organic acid and dried. Such organic acids include monobasic acids such as acetic acid and propionic acid;
Using BS treated with dibasic acids such as maleic acid, malonic acid, succinic acid, and oxalic acid, and other oxypolybasic acids such as malic acid, tartaric acid, and citric acid, after mixing and conditioning with iron () composition. When used in the form of powder or granules, it not only excels in deodorizing basic gases such as ammonia, but also has a high specific surface area (60 to 100 m 2 /g) that forms a modified surface layer that is effective against organic solvents, etc. It also shows affinity for gas components (e.g., styrene, cresol, acetaldehyde, etc.) and is used in a wide range of applications. In this case as well, the mixing ratio of the acid-treated BS and the iron () composition may be the same as above. In this case, water 5
It is preferably contained in an amount of at least 5% by weight, and more preferably has a water content of about 5 to 10%. A composition using such organic acid-treated BS can be prepared, for example, as follows. 1-5%
Add 10g of BS to 50g of organic acid solution, stir for 30 minutes, leave overnight to filter and dry (overnight at 110°C), and add 10 to 50% by weight of iron () composition, preferably 25 to 50% by weight.
An adsorbent with excellent ammonia gas adsorption properties is obtained by supporting 30% by weight. Furthermore, as a method for surface modification of BS, an aqueous solution of an iron () composition was directly added to change the liquid from neutral to acidic, and from this a powder of the composition of the present invention having excellent ammonia odor removal performance was prepared. Good too. (Effects of the Invention) The present invention combines an iron () composition with BS, and exhibits significantly higher adsorption power for acidic malodorous gas components than when each is used alone. On the other hand, since the iron () composition originally exhibits high adsorption performance for ammonia gas, the adsorption performance is less affected by the pH of the malodorous gas, and it has the excellent effect of maintaining high activity over a long period of time. play. Furthermore, in particular, the deodorizing base of the second invention also exhibits adsorption properties for organic solvent-based gases. Furthermore, the composition of the present invention can reduce the content of the iron () composition and increase the adsorption activity, and has an extremely large cost advantage. Such a composition of the present invention can be obtained by molding the mixture into a plate shape (60 to 150 kg/cm 2 ) or by simply compression molding.
Not only can it be molded and used as housing, furniture, and packaging materials that have a deodorizing function, but it can also be mixed into plastic fillers and used as molding materials and films that have similar functions. (Examples) Next, the present invention will be described in more detail based on Examples. The iron-ascorbic acid used in the examples is an agent in which 0.03 mole of L-ascorbic acid is bound to 1 mole of iron in ferrous sulfide. Also
BS was adjusted as follows. [Preparation method] According to the method of sample No. 8 of the following reference example. Bulk specific gravity: 0.584 Specific surface area: 57.1 m 2 /g [Reference Example 1] An example of preparing BS used in the present invention will be shown.

【表】 第1表に示す如き粒度分布の水砕スラグ100g
を3N−NaOH溶液1000mlに加え、90℃にて攪拌
しつつ3時間処理し、ついで処理水砕スラグをろ
別分離、水砕後110℃にて乾燥して得た各試料に
ついてかさ比重及び比表面積の測定を行つた。結
果は第2表に示す通りである。
[Table] 100g of granulated slag with particle size distribution as shown in Table 1
was added to 1000 ml of 3N-NaOH solution and treated at 90℃ for 3 hours with stirring.Then, the treated granulated slag was separated by filtration, and after pulverization, it was dried at 110℃.The bulk specific gravity and ratio of each sample were determined. The surface area was measured. The results are shown in Table 2.

【表】 第2表の結果より、粒度分布に於て325メツシ
ユ以下の量のとくに多いものがそのアルカリ処理
によりかさ比重の低下及び比表面積の増大が顕著
であることがわかる。 [実施例 1] 硫化水素初濃度4000〜5000ml/m3に調整したガ
ス2.4をテドラバツグにとり、吸着剤として、
BS及び(BS)+(鉄−アスコルビン酸)(以下、
鉄()組成物という)粉末1gを100Kg/cm2に加
圧して成型し、φ13mmの円板を成型した。これを
およそ8分画に破砕し、この脱臭基剤をデオドア
ナライザーのカラムにつめ、一定初濃度のガスを
1/minの速度で60min流し、吸着させる。初
濃度と60min後のガス濃度を測定し、初回(1
回)とする。次いで、テドラバツクのガスを初濃
度のものに置換し、そのままの吸着剤に同一条件
で吸着させる、60min後の処理ガス濃度をはか
り、2回目とし、順次、その回数をかさねおよそ
8回行つた結果を第1図に示す。次に上記の脱臭
基剤に水分を23.1重量%含有させて同様の試験を
行つた。 第1図中のグラフは次の通りである。 グラフ 鉄()組成物含有量 (重量%) 水分含有量 (重量%) A 50 0 B 10 0 C 0(BSのみ) 23.1 D 0 23.1 E 10 23.1 F 20 23.1 G 30 23.1 H 40 23.1 I 50 23.1 図面から明らかな如く乾燥状態の場合、BSな
らびに鉄−アスコルビン酸とBS混合品、及び鉄
−アスコルビン酸のみでは硫化水素の吸着量は小
さい、しかしながら、BSを鉄−アスコルビン酸
原液(およそ30%溶媒)で混合成型するか、また
は、BSと鉄−アスコルビン酸粉末(凍結乾燥品
もしくは噴霧乾燥品)を粉末混合し成型後、吸着
剤に水分を保持させると、その性能は格段に向上
することがわかる。 これは、BSの持つ固体塩基特性によるもので、
硫化水素は塩基性領域で解離してイオン状にな
り、この硫化イオン(S2-)が水硫化物イオン
(HS-)になつたものが鉄()組成物と化合物
に反応するものと解釈される。 [実施例 2] BSに対して鉄()−アスコルビン酸の添加率
を変化させた組成物を用いてH2Sの吸着試験を
行つた。1gの乾燥剤に対して、200μの水を含
ませた場合で、16.7%の含有率である。 この結果を第2図に示した。この第2図の結果
よりこれは、BSに対して、鉄()−アスコルビ
ン酸の添加率を20〜40%に変化させても、この間
では吸着性能に大きな差異が生じないことがわか
る。 [実施例 3] BSに対して、鉄−アスコルビン酸の添加率40
重量%の場合に含有率を9.1〜23.1%にまで変化
させて硫化水素の吸着試験を実施例1と同様にし
て行つた。その結果を第3図に示した。 同図の結果より、含水率10%程度では、十分な
吸着性能発現がないが、15%から25%位になる
と、その効果が増大することがわかる。 [実施例 4] BSをクエン酸溶液で処理し、この酸処理BSを
鉄−アスコルビン酸(鉄()組成物)と所定比
率で混合した組成物を用い所定濃度のアンモニア
ガスを用いた以外は実施例1の方法と同様にして
吸着試験を行つた。その結果を第4図に示した。 同図の結果より、5%クエン酸で処理したBS
と鉄−アスコルビン酸を重量比で1:1で含有す
るものは、鉄−アスコルビン酸100%のものより、
吸着回数の少ないうちは吸着性能は低いが、吸着
が繰返されると吸着性能が逆転することがわか
る。
[Table] From the results in Table 2, it can be seen that in the particle size distribution, those with a particularly large amount of 325 mesh or less showed a remarkable decrease in bulk specific gravity and increase in specific surface area by alkali treatment. [Example 1] Gas 2.4 adjusted to an initial hydrogen sulfide concentration of 4000 to 5000 ml/ m3 was placed in a Tedra bag, and used as an adsorbent.
BS and (BS) + (iron-ascorbic acid) (hereinafter referred to as
1 g of iron (referred to as composition) powder was pressurized to 100 kg/cm 2 and molded to form a disc with a diameter of 13 mm. This is crushed into approximately 8 fractions, this deodorizing base is packed into a column of a deodorant analyzer, and gas with a constant initial concentration is passed at a rate of 1/min for 60 minutes to cause adsorption. Measure the initial concentration and the gas concentration after 60 min.
times). Next, the gas in the Tedra bag was replaced with the initial concentration, and the same adsorbent was used to adsorb it under the same conditions.The concentration of the treated gas was measured after 60 minutes, and the process was repeated approximately 8 times. is shown in Figure 1. Next, a similar test was conducted using the above deodorizing base containing 23.1% by weight of water. The graph in FIG. 1 is as follows. Graph Iron () composition content (wt%) Moisture content (wt%) A 50 0 B 10 0 C 0 (BS only) 23.1 D 0 23.1 E 10 23.1 F 20 23.1 G 30 23.1 H 40 23.1 I 50 23.1 As is clear from the drawing, in dry conditions, the adsorption amount of hydrogen sulfide is small with BS, a mixture of iron-ascorbic acid and BS, and iron-ascorbic acid alone. ), or by mixing BS and iron-ascorbic acid powder (freeze-dried or spray-dried) and molding, and then allowing the adsorbent to retain moisture, its performance can be significantly improved. Recognize. This is due to the solid base properties of BS.
It is interpreted that hydrogen sulfide dissociates in the basic region and becomes ionic, and that this sulfide ion (S 2- ) becomes a hydrosulfide ion (HS - ), which reacts with iron () compositions and compounds. be done. [Example 2] An H 2 S adsorption test was conducted using compositions in which the addition ratio of iron ()-ascorbic acid to BS was varied. When 200μ of water is added to 1g of desiccant, the content is 16.7%. The results are shown in FIG. From the results shown in FIG. 2, it can be seen that even if the addition ratio of iron ()-ascorbic acid to BS is changed from 20 to 40%, there is no significant difference in adsorption performance between these changes. [Example 3] Addition rate of iron-ascorbic acid to BS: 40
A hydrogen sulfide adsorption test was conducted in the same manner as in Example 1, changing the content from 9.1 to 23.1% by weight. The results are shown in Figure 3. From the results in the same figure, it can be seen that when the water content is around 10%, sufficient adsorption performance is not expressed, but when the water content increases from 15% to 25%, the effect increases. [Example 4] Except for treating BS with a citric acid solution, using a composition in which the acid-treated BS was mixed with iron-ascorbic acid (iron() composition) at a predetermined ratio, and using ammonia gas at a predetermined concentration. An adsorption test was conducted in the same manner as in Example 1. The results are shown in Figure 4. From the results in the same figure, BS treated with 5% citric acid
and iron-ascorbic acid at a weight ratio of 1:1, compared to 100% iron-ascorbic acid.
It can be seen that the adsorption performance is low when the number of adsorptions is small, but when adsorption is repeated, the adsorption performance reverses.

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

第1図は吸着処理回数と硫化水素ガスの残留濃
度と関係を示すグラフ、第2図は鉄()組成物
含有量と硫化水素ガスの残留濃度との関係を示す
グラフ、第3図は脱臭基剤中の水分含有と硫化水
素ガスの残留濃度との関係を示すグラフ、第4図
は有機酸処理BSを用いた場合のアンモニアガス
の残留濃度を示すグラフである。
Figure 1 is a graph showing the relationship between the number of adsorption treatments and the residual concentration of hydrogen sulfide gas, Figure 2 is a graph showing the relationship between the iron () composition content and the residual concentration of hydrogen sulfide gas, and Figure 3 is deodorization. FIG. 4 is a graph showing the relationship between water content in the base and the residual concentration of hydrogen sulfide gas. FIG. 4 is a graph showing the residual concentration of ammonia gas when organic acid-treated BS is used.

Claims (1)

【特許請求の範囲】 1 微粉状水砕スラグを少なくとも0.5Nのアル
カリ溶液にて少なくとも30分間処理後、該処理水
砕スラグをろ別分離、水洗後加熱乾燥して得たか
さ比重が低下され且つ比表面積が増大された表面
特性を改良した水砕スラグと鉄()化合物を主
成分とし、これに有機酸成分を結合させてなる組
成物とを混合してなり含水率が10重量%以上であ
ることを特徴とする脱臭性基剤。 2 鉄()化合物を主成分とし、有機酸成分と
結合させてなる組成物を5〜60重量%含有する特
許請求の範囲第1項記載の脱臭性基剤。 3 微粉状水砕スラグを少なくとも0.5Nのアル
カリ溶液にて少なくとも30分間処理後、該処理水
砕スラグをろ別分離、水洗後加熱乾燥して得たか
さ比重が低下され且つ比表面積が増大された表面
特性を改良した水砕スラグを有機酸で中和した
後、この水砕スラグを鉄()化合物を主成分と
し、これに有機酸成分を結合させてなる組成物と
混合してなることを特徴とする脱臭性基剤。 4 含水率が5重量%以上である特許請求の範囲
第3項記載の脱臭性基剤。
[Claims] 1. After treating finely powdered granulated slag with an alkaline solution of at least 0.5N for at least 30 minutes, the treated granulated slag is separated by filtration, washed with water, and then heated and dried to reduce the bulk specific gravity. In addition, it is made by mixing granulated slag with improved surface characteristics with increased specific surface area and a composition consisting mainly of iron () compounds and bonding an organic acid component to this, and has a water content of 10% by weight or more. A deodorizing base characterized by: 2. The deodorizing base according to claim 1, which contains 5 to 60% by weight of a composition comprising an iron () compound as a main component and combined with an organic acid component. 3. After treating finely powdered granulated slag with an alkaline solution of at least 0.5N for at least 30 minutes, the treated granulated slag is separated by filtration, washed with water, and then heated and dried to reduce the bulk specific gravity and increase the specific surface area. granulated slag with improved surface characteristics is neutralized with an organic acid, and then this granulated slag is mixed with a composition containing an iron () compound as a main component and an organic acid component bonded to this granulated slag. A deodorizing base characterized by: 4. The deodorizing base according to claim 3, which has a water content of 5% by weight or more.
JP60253415A 1985-11-12 1985-11-12 Deodorizing base material Granted JPS62114647A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60253415A JPS62114647A (en) 1985-11-12 1985-11-12 Deodorizing base material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60253415A JPS62114647A (en) 1985-11-12 1985-11-12 Deodorizing base material

Publications (2)

Publication Number Publication Date
JPS62114647A JPS62114647A (en) 1987-05-26
JPH0521623B2 true JPH0521623B2 (en) 1993-03-25

Family

ID=17251069

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60253415A Granted JPS62114647A (en) 1985-11-12 1985-11-12 Deodorizing base material

Country Status (1)

Country Link
JP (1) JPS62114647A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0255060A (en) * 1988-08-19 1990-02-23 Sumitomo Metal Ind Ltd Deodorant
JPH044017A (en) * 1990-04-18 1992-01-08 Nippon Steel Corp Deodorizer

Also Published As

Publication number Publication date
JPS62114647A (en) 1987-05-26

Similar Documents

Publication Publication Date Title
EP0457457B1 (en) Oxygen absorbent
JPS6143091B2 (en)
CN101565338A (en) Method for preparing fertilizer adsorbing volatilizing nitrogen
KR0130460B1 (en) Oxygen absorber and method for producing same
US5236617A (en) Oxygen absorbent
WO1997025076A1 (en) Odor control for compositions containing organic sulfur compounds
WO1997025076A9 (en) Odor control for compositions containing organic sulfur compounds
JPH0521623B2 (en)
JPS631098B2 (en)
CN100360188C (en) Refrigerator deodorant of natural organics
US3137565A (en) Method of producing a non-caking fertilizer and the product thereof
JP2745424B2 (en) Deodorant
JPS61106162A (en) Deodorant
JPS58185161A (en) Solid aromatic agent
JP2738068B2 (en) Freshness preservative
JPH0712431B2 (en) Iron (▲ II ▼) composition
JPH0446615B2 (en)
JPS62277148A (en) Deoxidizer
JPS63205122A (en) Drying agent
JPH0470927B2 (en)
CN112934207B (en) Air purification material and preparation method and application thereof
JPS62186941A (en) Deoxidizer containing alcohol
JPS62292165A (en) Deodorant
JPS6282966A (en) Deodorizing granule
JPS62101251A (en) Deodorant

Legal Events

Date Code Title Description
EXPY Cancellation because of completion of term