JPS6297641A - Adsorbing material for carcinogen - Google Patents

Adsorbing material for carcinogen

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Publication number
JPS6297641A
JPS6297641A JP23755185A JP23755185A JPS6297641A JP S6297641 A JPS6297641 A JP S6297641A JP 23755185 A JP23755185 A JP 23755185A JP 23755185 A JP23755185 A JP 23755185A JP S6297641 A JPS6297641 A JP S6297641A
Authority
JP
Japan
Prior art keywords
adsorbent
synthetic mica
ions
mica
swellable
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP23755185A
Other languages
Japanese (ja)
Inventor
Shigeo Ichise
市瀬 茂男
Shigenobu Mizusaki
水崎 茂暢
Daisuke Yoshida
大輔 吉田
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.)
Topy Industries Ltd
Japan Tobacco Inc
Original Assignee
Topy Industries Ltd
Japan Tobacco Inc
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 Topy Industries Ltd, Japan Tobacco Inc filed Critical Topy Industries Ltd
Priority to JP23755185A priority Critical patent/JPS6297641A/en
Publication of JPS6297641A publication Critical patent/JPS6297641A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To enhance the adsorbing capacity of a carcinogen, by forming an adsorbing material from a synthetic mica substituted product prepared by substituting the interlayer ion of swellable synthetic mica with an alkaline earth metal or other metal ion by an ion exchange method. CONSTITUTION:Sodium tetrasilicic mica of swellable synthetic mica or sodium hectorite of swellable OH-type synthetic mica is converted to a substitution product wherein Al<3+> and Ti<4+> ions between layers of said mica are brought to a state of polynuclear hydroxide ions. Subsequently, the substitution product is heat-treated at 200-300 deg.C for 15-30min in air to prepare an adsorbent for a carcinogen. This adsorbent has a versatile high adsorbing ratio reaching 94-99% with respect to both substances of benz(alpha) pyrene and TrpP2. The aforementioned adsorbent can be used according to a column filter system, a system impregnating filter paper and a tea bag system, etc.

Description

【発明の詳細な説明】 「産業上の利用分野」 本発明は、膨潤性合成雲母の金属イオン置換体を主材と
する発癌性物質用吸着材に関するものである。
DETAILED DESCRIPTION OF THE INVENTION "Industrial Application Field" The present invention relates to an adsorbent for carcinogenic substances that is based on a metal ion substituted product of swellable synthetic mica.

「従来技術とその問題点」 動物が呼気吸入したり、経口摂取したりすると悪性腫瘍
を発生させる物質及び皮膚表面に長期にわたり繰り返し
接触させると悪性腫瘍を発生させる物質を総称して、1
発癌性物質」と呼んでいる、過去の幾多の研究の結果、
このような発癌性物質が多数種類生活環境中に存在する
ことが立証されている。
``Prior art and its problems'' Substances that cause malignant tumors when inhaled or ingested by animals, and substances that cause malignant tumors when repeatedly contacted with the skin surface over a long period of time are collectively referred to as 1.
As a result of numerous past studies,
It has been demonstrated that many types of such carcinogenic substances exist in the living environment.

すなわち、動物実験による証明によると、皮膚癌を発生
させるものとして、ベンツ(α)ピレン、3−メチルコ
ラントレン、9.lO−ジメチル−1,2−ベンツアン
トラセンなどの多核芳香族炭化水素類が、また経口投与
実験の結果肝癌その他の悪性腫瘍を発生させるものとし
て、O−アミノアゾトルエン及びp−ジメチルアミノア
ゾベンゼン(バタミニロー)を初めとする各種アゾ化合
物、2−7セチルアミノフルオレンなどの各種芳香族ア
ミン類とその誘導体、更にニトロソアミンなどが判明し
ている。また上記の発癌性物質と併用すると、その発癌
性を著しく促進するものとして、フェノバルビタール、
フェノール、ウレタン等が知られている。特に人体に対
してその発癌性が注目される物質としては、4−アミノ
ビフェノール、2−ナフチルアミン、ベンジジン、ベン
ゾ(α)ピレンが有名である。多くの発癌性物質が加工
食品の焼魚、ネテーキ、ハンバーグ等の焼成食品や、紅
茶、コーヒー等のカフェイン飲料及びブランデー、ウィ
スキー、ラム酒等のアルコール飲料や山菜ワラビ等の食
品中に存在することが知られている。
That is, according to evidence from animal experiments, benz(α)pyrene, 3-methylcholanthrene, 9. Polynuclear aromatic hydrocarbons such as lO-dimethyl-1,2-benzanthracene have been shown to cause liver cancer and other malignant tumors in oral administration experiments, as well as O-aminoazotoluene and p-dimethylaminoazobenzene (Bataminilow). ), various aromatic amines and their derivatives such as 2-7cetylaminofluorene, and nitrosamines. Furthermore, when used in combination with the above carcinogenic substances, phenobarbital,
Phenol, urethane, etc. are known. 4-aminobiphenol, 2-naphthylamine, benzidine, and benzo(α)pyrene are well-known as substances that are particularly noteworthy for their carcinogenicity to the human body. Many carcinogenic substances are present in processed foods such as grilled fish, netteki, and hamburgers, caffeinated drinks such as tea and coffee, alcoholic drinks such as brandy, whiskey, and rum, and foods such as wild vegetables bracken. It has been known.

従って、これら発癌性物質を効率良く除去する吸着材の
開発が社会ニーズとして、切望されている。
Therefore, the development of adsorbents that can efficiently remove these carcinogenic substances is a social need.

しかしながら、−概に発癌性物質といってもその性質は
千差万別であるから、これを吸着する吸着材としても吸
着する発癌性物質によって、性能的に得失がある。現在
、万能的に発癌性物質を吸着する吸着材の実例は殆ど見
当らない。
However, since the properties of carcinogenic substances generally vary widely, there are advantages and disadvantages in terms of performance depending on whether the adsorbent adsorbs the carcinogenic substance or the adsorbent. Currently, there are almost no examples of adsorbents that can universally adsorb carcinogenic substances.

このことを実際の例を挙げて説明すると、セルローズは
ベンゾ(α)ピレンについては高い吸着性能を発揮する
が、水溶性のトリプトファン熱分解物中の変異原物質T
rpP2(3−アミノ−1−メチル5H−ピリド[4,
3−b ] インドールに対しては、吸着能力は大幅に
低下する。
To explain this using an actual example, cellulose exhibits high adsorption performance for benzo(α)pyrene, but it does not absorb the mutagen T in the water-soluble tryptophan pyrolysis product.
rpP2 (3-amino-1-methyl 5H-pyrido[4,
3-b] For indole, the adsorption capacity is significantly reduced.

食品中のものに対しての不活性化手段として亜硫酸塩類
、例えば亜硫酸ナトリウム、亜硫酸水素ナトリウム、ピ
ロ硫酸カリウム、亜ニチオン酸ナトリウム及び無水亜硫
酸等の少量を添加し、=2 (So3’)  イオンの作用により不活性化すること
が提案されているが1元来これらの薬剤は、食品用の漂
白剤、保存料及び酸化防止剤として既に使用されている
ので、自ずから添加量に許容限度があると共に、嗜好品
に於いては味覚に影響を与える欠点もあった。上記薬剤
は、不活性化の効果を期待するには、200〜300P
P層の量溶存させる必要があり、溶存濃度を稀薄化すれ
ば不活性化の効果も低下し、依然として変異原である発
癌性物質の活性物は残存することになる。
Small amounts of sulfites, such as sodium sulfite, sodium hydrogen sulfite, potassium pyrosulfate, sodium dithionite and sulfite anhydride, are added as a means of inactivation to those in foods, resulting in the addition of =2 (So3') ions. However, since these agents are already used as food bleaches, preservatives, and antioxidants, there are naturally permissible limits to the amount they can be added. However, when it comes to luxury goods, it also has the disadvantage of affecting taste. The above drug requires 20 to 300 P to expect an inactivation effect.
It is necessary to dissolve a sufficient amount of the P layer, and if the dissolved concentration is diluted, the inactivation effect will be reduced, and the active substance of the carcinogenic substance, which is a mutagen, will still remain.

「問題点を解決するための手段」 本発明者等は、この点に着目し鋭意研究の結果、前記発
癌性物質は、前記単一的な吸着方式では万能的に吸着さ
せることは困難であるが、膨潤性を有する合成雲母の層
間イオンを、イオン交換法により、アルカリ土類金属イ
オンまたは金属イオンの置換体とした化合物は、適正な
熱処理条件による加工を施すことによって、水溶性有機
物も非水溶性有機物も多面的に吸着し得ることを見出し
、本発明に到達した。
"Means for Solving the Problem" The present inventors focused on this point and as a result of intensive research, it was found that it is difficult to universally adsorb the carcinogenic substance using the single adsorption method described above. However, compounds in which interlayer ions of swellable synthetic mica are substituted with alkaline earth metal ions or metal ions by an ion exchange method can be processed under appropriate heat treatment conditions to eliminate water-soluble organic substances. It was discovered that water-soluble organic substances can also be adsorbed in a multifaceted manner, and the present invention was achieved.

このことを更に明らかにするため、本発明の原材料であ
る合成雲母の構造と特性並びに該合成雲11に如何なる
加工を施せば、前記発癌性物質を多面的に吸着する性渣
を有する吸着材が得られるかを説明する。
In order to further clarify this, we will discuss the structure and characteristics of synthetic mica, which is the raw material of the present invention, and what kind of processing can be applied to the synthetic mica 11 to create an adsorbent with residues that adsorbs the carcinogen from multiple angles. Explain what you can get.

本発明吸着材の原料は、溶融合成法によって得られる膨
潤性を示す合成雲母であり、いわゆる雲母構造を成し、
無a質の層状構造を示す結晶体であり、一般にその結晶
構造成分に一〇H基を有しない点で天然物と異なる。即
ち、天然物の−OHの結晶構造部分に相当するものが、
Fによって構成されているのである。尚、近時に於いて
は、−OH型(フッソの無い)合成雲母も試作され始め
ている、本発明に於いては、膨潤性合成雲母であれば。
The raw material for the adsorbent of the present invention is synthetic mica that exhibits swelling properties and is obtained by a melt synthesis method, and has a so-called mica structure.
It is a crystalline substance exhibiting an amorphous layered structure, and differs from natural products in that it generally does not have an 10H group as a component of its crystal structure. That is, what corresponds to the crystal structure part of -OH in natural products is
It is composed of F. Incidentally, in recent years, trial production of -OH type (fluorine-free) synthetic mica has begun.In the present invention, swellable synthetic mica is used.

その結晶構造内にFまたは(OH)2のいずれを有する
ものでもよい。
It may have either F or (OH)2 in its crystal structure.

このような、一連の合成雲母の基本組成を示性式的に示
すと、次式(I)で表される一般式となる。
The basic composition of such a series of synthetic mica can be expressed as a general formula expressed by the following formula (I).

×0.2〜1.0 2.0〜3.5”’4”10.(F
2または(OH)2)、Y (式中、Xは層間イオンテあって1.、+、、+、に+
×0.2~1.0 2.0~3.5"'4"10. (F
2 or (OH)2), Y (wherein,
.

+   +   +   2+   2◆Rb 、Cs
 、TI 、Ca  、Sr  及びBa2+からなる
群から選ばれる1種または2種以上のイオンを表し、Y
ハへ面体位置ノイオンテアッテ、Mg”、Li”、Fe
”。
+ + + 2+ 2◆Rb, Cs
, TI , Ca , Sr , and Ba 2+ , and represents one or more ions selected from the group consisting of , Y
Hahehedron position Neuonteatte, Mg", Li", Fe
”.

Ni”、 Go”、 Zn”、M?r”、Cu”、Cr
”7j−びFe3+からなる群から選ばれる1種または
2種以上のイオンを表し、そしてZは四面体位置のイオ
ンであって、AI”、Si”、Ge”、Zn2”、Go
”、B”Fe”、Cr3+及びV3+からなる群から選
ばれる1種または2種以上のイオンを表す。
Ni”, Go”, Zn”, M?r”, Cu”, Cr
"7j-" represents one or more kinds of ions selected from the group consisting of
", B" represents one or more ions selected from the group consisting of "Fe", Cr3+, and V3+.

第1図に、膨潤性合成雲母の一種であるナトリウムテニ
オライトの結晶の断面モデルを示す0式(I)で第1図
に示すリチウムテニオライトを例示すれば、Li、Mg
2L1(Si、0、。)F2となる。
Figure 1 shows a cross-sectional model of the crystal of sodium taeniolite, which is a type of swellable synthetic mica.
2L1(Si,0,.)F2.

第1図に示すように、合成雲母の結晶単位層は、表面に
S iO2の四面体が連なって平板を成しており、二枚
のSiO平板の間をMgO,F2を主成分とする八面体
層が埋め合せた三層構造の結晶体である。
As shown in Figure 1, the crystalline unit layer of synthetic mica has SiO2 tetrahedrons connected to each other on the surface to form a flat plate, and between the two SiO flat plates is a crystal unit layer consisting of MgO and F2 as main components. It is a crystalline body with a three-layer structure filled with facet layers.

この単位層の陰、陽電荷の総和値は、陰電荷が若干余る
ようになっており、この電荷を中和するために、結晶層
間にアルカリイオンが配位して、何層もの層を積重ねた
構造となっている。この層間のアルカリイオン(K+を
除く)は、湿潤状態で水分子を層間に引込むので、湿潤
状態で結晶は膨張する性質を示す、この現象をr水和膨
潤jと言い、この層間に侵入した水分をr層間水1とい
う。
The total value of negative and positive charges in this unit layer is such that there is a slight surplus of negative charges, and in order to neutralize this charge, alkali ions are coordinated between the crystal layers, and many layers are stacked. It has a similar structure. The alkali ions (excluding K+) between these layers draw water molecules between the layers in a wet state, so the crystal exhibits the property of expanding in a wet state. The water is called r interlayer water 1.

この層間水は、結晶水と異り自由にイオンを溶解し得る
。また層間のアルカリイオンは、イオン交換性を有し、
他の有機物を含めたカチオンとイオン交換により置き変
えることができる。この性質を利用して1種々のカチオ
ンを雲母の層間に入れた置換体をつくることができる。
This interlayer water, unlike crystal water, can freely dissolve ions. In addition, the alkali ions between the layers have ion exchange properties,
Can be replaced by ion exchange with cations, including other organic substances. Utilizing this property, it is possible to create a substituted product in which one of various cations is inserted between the layers of mica.

本発明の吸着材は、上記11潤性の合成雲母の層間のア
ルカリイオンを、金属イオンやアルカリ土類金属イオン
で置換する加工を施すことによって、製造することがで
きる。特に多核水酸化物イオンを形成する2価、3価、
4価の金属イオンで置換させると、置換体を形成させた
後、適正な熱処理を加えることにより1種々の特性を示
すr層間化合物による多孔体Jとなることが判明してい
る、本発明者等は、このことを利用して非水溶性有機溶
媒の高性能吸着材を得、既に特許出願している(特願昭
59−187287号)。
The adsorbent of the present invention can be produced by processing the above-mentioned 11-moisture synthetic mica to replace the interlayer alkali ions with metal ions or alkaline earth metal ions. Especially divalent, trivalent, which forms polynuclear hydroxide ions,
The present inventor has found that when substituted with a tetravalent metal ion, a porous body J made of an intercalation compound exhibiting various properties can be obtained by forming a substituted substance and then applying appropriate heat treatment. Utilizing this fact, et al. obtained a high-performance adsorbent for water-insoluble organic solvents and have already filed a patent application (Japanese Patent Application No. 187287-1987).

しかしながら、1発癌性物質の吸着材jとしては、水溶
性の有機物質と非水溶性の有機物質の両方を同時に暖着
させる特性を付与させるのが望ましい、そこで、異性質
の発癌性物質の代表例として、それぞれ「ベンズ(α)
ピレンJ及び「トリプトファン熱分解物質中のTrpP
2 jを選択して、この三者に対する各種置換体の熱処
理条件と吸着率との関係を追求した(実施例の結果を示
す第2図及び第3図参照)。
However, as an adsorbent for carcinogenic substances, it is desirable to have the property of absorbing both water-soluble and water-insoluble organic substances at the same time. As an example, "benz (α)"
Pyrene J and “TrpP in tryptophan pyrolysis products”
2j was selected, and the relationship between heat treatment conditions and adsorption rates of various substituents for these three substances was investigated (see FIGS. 2 and 3 showing the results of Examples).

上記実験の結果、rベンズ(α)ピレン」に関しては、
3価、4価の金属イオンの多核水酸化物イオンによる置
換体が有効であり、合成雲母の種類によって若干特性的
には異なるが、300℃〜600℃の熱処理条件の領域
に於いて高水準の吸着率を示すことが判明した。 Ca
2′″、Ba”″1Mg2ゝイオン置換体は、300〜
400℃の処理条件では吸着率は低く、aOO℃の処理
を受けて非水溶性有機物に対する良い吸着率を示すよう
になる。
As a result of the above experiment, regarding rbenz(α)pyrene,
Substitution products of trivalent and tetravalent metal ions with polynuclear hydroxide ions are effective, and although the characteristics differ slightly depending on the type of synthetic mica, they have a high level of performance under heat treatment conditions of 300°C to 600°C. It was found that the adsorption rate was as follows. Ca
2''', Ba''''1Mg2' ion substituted product is 300~
Under the treatment condition of 400°C, the adsorption rate is low, and when treated at aOO°C, it shows a good adsorption rate for water-insoluble organic substances.

一方、rTrpP2J  (水溶性)に対しては、金属
イオン及びアルカリ土類金属イオンのいずれの置換体も
300〜400℃の熱処理温度で高い吸着吸着率は大幅
に低下する。
On the other hand, for rTrpP2J (water-soluble), the high adsorption adsorption rate of both metal ion and alkaline earth metal ion substitutes is significantly reduced at a heat treatment temperature of 300 to 400°C.

上記したように、吸着率が向上する原理は定かではない
が1層間置換体が、200〜300℃の熱処理を受ける
過程で、脱水→多孔体化の変化を受け、急速に両物質に
対する吸着親和力を増すものと推察される。特に、Al
31、Ti4+の置換体は、陽子供与体若しくは電子受
容体として作用する固体酸を形成するため、多核芳香族
塩基性炭化水素の吸着に於いてm著な性flを示すと考
えられる。
As mentioned above, the principle by which the adsorption rate improves is not clear, but in the process of heat treatment at 200 to 300°C, the one-layer substituted material undergoes a change from dehydration to porous material, rapidly increasing the adsorption affinity for both substances. It is assumed that this increases the In particular, Al
31, Ti4+ substituted product forms a solid acid that acts as a proton donor or an electron acceptor, and is therefore considered to exhibit remarkable properties fl in the adsorption of polynuclear aromatic basic hydrocarbons.

更に加えて、脱水過程で形成される層間化合物の微細空
孔は、水溶性の分解物質である変異原物質TrpP2に
対しても「空孔内表面の吸着Jを発揮する。しかしなが
ら、固体酸をあまりに強固に形成する熱処理を施すと、
水溶性物質の吸着性が低下してくる結果となるため、固
体酸形成温度領域に於ける低温端側に熱処理条件をとど
めておく必要がある。
In addition, the micropores of the intercalation compound formed during the dehydration process also exhibit adsorption on the inner surface of the pores for the mutagen TrpP2, which is a water-soluble decomposition substance. If heat treatment is applied to make it too strong,
Since this results in a decrease in adsorption of water-soluble substances, it is necessary to keep the heat treatment conditions at the low temperature end in the solid acid formation temperature range.

本発明の吸着材の使用方法は、既知の方法で良く1例え
ばカラムフィルタ一方式、濾紙に抄き込+1±」I−毒
、−パー、h士乎竺も1旧、1柄Iギ←/ −のように
して、発癌性物質を効率良く吸着除去することが出来る
The adsorbent of the present invention may be used by any known method, for example, using a column filter, applying it to a filter paper + 1±'' I-poison, -par, h し乎纺 also 1 old, 1 pattern I ← / - Carcinogenic substances can be efficiently adsorbed and removed.

「実施例」 次に実施例を挙げて木兄IJIを更に説明するが、本発
明はこれら実施例に限定されない。
"Example" Next, Kinoi IJI will be further explained with reference to Examples, but the present invention is not limited to these Examples.

実施例1 合成雲母Ha−丁Sを0.6%wt/マO1で含有する
懸濁水2000電lに、酸性硫酸チタン溶液(2mgT
i/璽l e If )約200m1を攪拌下に添加し
、ついで攪拌を続けながら、積HaOIl溶液及び福H
2SO4溶液を必要に応じ適宜添加し、PH−1,5〜
1.8に調節する。引続き約30分間攪拌を継続して、
イオン交′  換による合成雲母のチタン多核水酸化物
置換体の凝集物を得た。上澄液を拾棄し、濾過若しくは
遠心分子t (3000rpm、30分間)等の手段に
よって、凝集状の置換体を単離する。この時置換体を再
度酸性水に分散させて分離する方法を1〜2回繰り返し
て過剰のチタンイオンを洗浄除去した。このようにして
得た置換体を80〜100℃で一昼夜風乾させた後、凝
集をはごす程度に粉砕して、粉状の置換体約logを得
た。この置換体を約2g宛磁製ルツボに入れ、これを電
子式温度調節機を備えたマツフル炉に移し、空気雰囲気
中、所定の温度で約30分間ずつの熱処理を施した。熱
処理を終了した粉体は、空気中で放冷した後、発癌性物
質の吸着試験の試料に供した。
Example 1 An acidic titanium sulfate solution (2 mg T
Add about 200 ml of the HaOIl solution and FukuH
Add 2SO4 solution as needed to adjust the pH to 1.5~
Adjust to 1.8. Continue stirring for about 30 minutes,
Aggregates of synthetic mica substituted with titanium polynuclear hydroxide were obtained by ion exchange. The supernatant is discarded, and the aggregated substituents are isolated by means such as filtration or centrifugation (3000 rpm, 30 minutes). At this time, the method of dispersing and separating the substituted product in acidic water was repeated once or twice to wash away excess titanium ions. The thus obtained substituted product was air-dried at 80 to 100° C. for a day and night, and then pulverized to the extent that the agglomerates were removed to obtain approximately log of the substituted product in powder form. Approximately 2 g of this substituted product was placed in a magnetic crucible, transferred to a Matsufuru furnace equipped with an electronic temperature controller, and heat-treated at a predetermined temperature for approximately 30 minutes each in an air atmosphere. After the heat treatment was completed, the powder was left to cool in the air and then used as a sample for a carcinogenic substance adsorption test.

実施例2 実施例1と同様の処理を実施することによって、置換イ
オンをAI” (塩化アルミニウム若しくは硝酸アルミ
ニウム使用でPH=3.5〜3.8の条件)、Zr”(
オキシ塩化ジルコニウム使用でPH= 1.5〜1.9
の条件)またはCa”、M 、21″、Ba”″C中性
P)を条件)とする多種類の置換体を得た。
Example 2 By carrying out the same treatment as in Example 1, the substitution ions were changed to AI" (using aluminum chloride or aluminum nitrate, pH = 3.5 to 3.8), Zr" (
PH=1.5-1.9 using zirconium oxychloride
A wide variety of substituents were obtained with the following conditions: Ca'', M, 21'', Ba''''C neutral P).

また、膨潤性雲母の種類を変えることによって、多種類
の雲母置換体を得た。これらは、それぞれ所定の熱処理
を施して、発癌性物質の吸着試験用試料に供した。
Furthermore, by changing the type of swellable mica, many types of mica substitutes were obtained. Each of these samples was subjected to a prescribed heat treatment and then used as a sample for a carcinogenic substance adsorption test.

実施例3 −(OH)2を結晶構造成分とする市販の「ラボナイ)
J  (Laporo  Industries  L
im1ted  P、0.Box13.KingSwa
y、 Luton、BedfordShire、 LI
J48EW製)粉体及び国峯工業製「クニビアFj粉体
は、F2を結晶構造成分とする「ナトリウムへクトライ
ト(Na qMg2%Li3,1(Si40.。)F2
(Ha−HTと略記する)と同構造のモンモリロナイト
系膨潤性雲母に属する。
Example 3 - Commercially available “Rabonai” containing (OH)2 as a crystal structure component
J (Laporo Industries L
im1ted P, 0. Box13. KingSwa
y, Luton, Bedfordshire, LI
J48EW) powder and Kunimine Kogyo's "Kunivia Fj powder" are sodium hectorite (Na qMg2%Li3,1 (Si40..) F2 whose crystal structure component is F2.
(abbreviated as Ha-HT) belongs to montmorillonite-based swelling mica with the same structure.

上記原料を使用し、実施例1と同様にして、層間置換体
を製造した。但し、Vラポナイト1については、結晶構
造の発達成長が劣るため、実施例1と同一操作による置
換体の固液分離工程に於ける収率は、「ナトリウムへク
トライト1 「クニピアFjの5〜10%程度にとどま
った。これらTi多核水酸化物置換体は、200℃〜4
00℃で30分間熱処理を施した後1発癌性物質の吸着
試験用試料に供した。
An interlayer replacement body was produced in the same manner as in Example 1 using the above raw materials. However, as for V Laponite 1, the development and growth of the crystal structure is inferior, so the yield in the solid-liquid separation process of the substituted product by the same operation as in Example 1 is ``Sodium Hectorite 1'', ``Kunipia Fj's 5-10 These Ti polynuclear hydroxide substituted products were heated at 200°C to 4%.
After heat treatment at 00°C for 30 minutes, it was used as a sample for adsorption test of a carcinogenic substance.

実施例4 (1)吸着実験の方法 ベンズ(α)ピL/7、丁rp F2の0.2 XIG
−6M溶液11に、上記実施例1〜3で得た試料を10
mg宛加え1時々振とうしながら、30分間放置した。
Example 4 (1) Method of adsorption experiment 0.2 XIG of benz(α)piL/7, dirpF2
-10% of the sample obtained in Examples 1 to 3 above was added to 11% of the 6M solution.
Add 1 mg to 1 mg and leave to stand for 30 minutes with occasional shaking.

、上澄液を測定試料とした。The supernatant liquid was used as the measurement sample.

(2)ベンズ(α)ピレンの分析方法 試料液0.21にジメチルスルホキシド0.21を加え
、蛍光分光光度計により、励起波長368n■に於ける
蛍光波長410nmの蛍光強度を測定した。
(2) Method for analyzing benz(α)pyrene 0.21 l of dimethyl sulfoxide was added to 0.2 l of the sample solution, and the fluorescence intensity at a fluorescence wavelength of 410 nm at an excitation wavelength of 368 nm was measured using a fluorescence spectrophotometer.

(3)TrpP2の測定方法 試料液0.21を使用し、サルモネラ・ティフィムリウ
ムTA98株を用いる変異原性検定法(エームス法)に
よって、ラット肝ホモジネート存在下で測定した。
(3) TrpP2 measurement method Using a sample solution of 0.21, measurement was performed in the presence of rat liver homogenate by a mutagenicity assay (Ames method) using Salmonella typhimurium TA98 strain.

(4)吸着率の計算方法 ベンズ(α)ピレンの吸着率=[(A−吸着剤添加溶液
のベンズ(α)ピレンのピーク高さ)/吸着剤無添加溶
液のベンズ(α)ピレンのピーク高さくA) ) ] 
X100 Trp F2の吸着率= (B−吸着剤添加溶液の旧S
+変異コロニー数/吸着剤無添加溶液の旧Sゝ変異コロ
ニーa(B) X 100 結果を第2図及び第3図に示す。
(4) Calculation method for adsorption rate Adsorption rate of benz (α) pyrene = [(A - peak height of benz (α) pyrene in solution with adsorbent added) / peak of benz (α) pyrene in solution without adsorbent Height A) )]
X100 Trp F2 adsorption rate = (B-old S of adsorbent added solution
+Number of mutant colonies/old S mutant colony a(B) X 100 of solution without adsorbent The results are shown in FIGS. 2 and 3.

実施例5 ■ナトリウムへクトライト[(F型)膨潤性雲母]、■
クニビアF[精製天然モンモリロナイト、(OH型)膨
潤性雲母]及びラポナイト[(OH)型膨潤性雲母]の
各々の多核水酸化物置換体に、300〜400℃で30
分間の熱処理を施した粉体20層gを採取し、この粉体
3を第4図に示す硝子型のミクロ漏斗lの脚部管2内に
充填する、尚1図中4は硝子綿を示す。
Example 5 ■ Sodium hectorite [(F type) swellable mica], ■
Knivia F [purified natural montmorillonite, (OH type) swellable mica] and Laponite [(OH) type swellable mica] were added to each polynuclear hydroxide substituted product at 300 to 400°C.
Collect 20 layers (g) of powder that has been heat-treated for 30 minutes, and fill this powder 3 into the leg tube 2 of a glass-shaped microfunnel 1 shown in Figure 4. 4 in Figure 1 is glass cotton. show.

漏斗上部から、ベンズ(α)ピレン、Trp F2の0
.2 X10−8M溶液2mlを滴下させながら加えて
、充填カラムを通過させた0通過液をガラス皿に受けて
集め、測定試料とし、実施例4の方法により吸着率を測
定した。
From the top of the funnel, benz(α)pyrene, Trp F2 0
.. 2 ml of 2.times.10.sup.-8 M solution was added dropwise, and the 0-pass liquid that had passed through the packed column was collected in a glass dish, used as a measurement sample, and the adsorption rate was measured by the method of Example 4.

結果は、■、■、■の各粉体とも、ベンズ(α)ピレン
、Trp F2の両方に対し、99.5%以上の吸着率
を示した。
The results showed that each of the powders ■, ■, and ■ had an adsorption rate of 99.5% or more for both benz(α)pyrene and Trp F2.

実施例6 実施例5に使用した吸着材の発癌性物質に対する平衡吸
着による吸着率の測定を、実施例4の方法により行った
。但し、検出感度を良くするためTrpP−2の濃度を
、2 Xl0−6M  (実施例4では0.2X lO
’M )に上げたものを使用した。更に、吸着材の使用
料を10層g/mlと5mg/層lとし、吸着材の使用
料が1/2に減少した吸着率も測定した。熱処理条件は
、380℃と500℃とした。結果を次表に示す。
Example 6 The adsorption rate of carcinogenic substances of the adsorbent used in Example 5 was measured by the method of Example 4 by equilibrium adsorption. However, in order to improve the detection sensitivity, the concentration of TrpP-2 was adjusted to 2XlO-6M (0.2XlO in Example 4).
'M) was used. Furthermore, the amount of adsorbent used was set to 10 g/ml and 5 mg/l of layer, and the adsorption rate at which the amount of adsorbent used was reduced to 1/2 was also measured. The heat treatment conditions were 380°C and 500°C. The results are shown in the table below.

※印は380℃熱処理品、■印は500℃熱処理品 上記結果より次のことが判明した。*marked is 380℃ heat treated product, ■ mark is 500℃ heat treated product The above results revealed the following.

(1)゛雲母結晶構造が、F2型であっても(OH) 
2型であっても、結晶構造が同一であれば、吸着性能に
は殆ど差異がみられない。
(1) Even if the mica crystal structure is F2 type (OH)
Even in type 2, if the crystal structure is the same, there is almost no difference in adsorption performance.

(2)10諺g/鳳l、5■g/slと吸着材の使用料
を1/2に減じても、吸着能率の大幅な低下は認められ
ず、良好な性能を示した。
(2) Even when the amount of adsorbent used was reduced to 1/2 to 10 g/l and 5 g/sl, no significant decrease in adsorption efficiency was observed and good performance was exhibited.

(3)熱処理を与えると、非親水性のベンゾ(α)ピレ
ン及び親水性のTrpP−2のいずれも高衡率の吸着性
能を示した。
(3) When subjected to heat treatment, both non-hydrophilic benzo(α)pyrene and hydrophilic TrpP-2 exhibited high adsorption performance.

「発明の効果」 以上述べた如く、本発明の吸着剤は1発癌性物質に対し
多面的に高い吸着率を示す0例えば、膨潤性合成雲母の
ナトリウムテトラシリシックマイカまたは膨潤性OH型
合成雲母のナトリウムへクトライトの層間に、 AI”
、T14+イオンを多核水酸化物イオンの状態の置換体
とした後、空気中で2゜吸着剤は、1ベンズ(α)ピレ
ンJ及びrTrpP2」の両方の物質に対し、84〜9
9%に及ぶ多面的な高吸着率を示した。これは、従来知
られているシリカゲル、セルローズ、γ−アルミナ等に
はみることのできない高性能のものであり、しかも非水
溶性及び水溶性の両特性の発癌性物質を多面的に吸着す
る特性を有する。
``Effects of the Invention'' As described above, the adsorbent of the present invention exhibits a multifaceted high adsorption rate for a single carcinogenic substance. Between the layers of sodium hectorite,
, after making the T14+ ion a substituent in the state of polynuclear hydroxide ion, the 2° adsorbent in air has 84-9
It showed a multifaceted high adsorption rate of up to 9%. This has a high performance that cannot be found in conventionally known silica gel, cellulose, γ-alumina, etc., and has the ability to adsorb both water-insoluble and water-soluble carcinogenic substances in a multifaceted manner. has.

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

第1図は、リチウムテニオライトの断面模型間第2図及
び第3図は、実施例の結果を示すグラフ、 第4図は、吸着率の測定に使用したミクロ漏斗の断面図
である。 特許出願人  トピー工業株式会社 日本たばこ産業株式会社 代理人 弁理士 稲 垣 仁 義パ 第1図 磐 ○○・ ○0 0Mg5iLiF 第2図 (0ん) スハ圧邑叉(’C) 第3図 第4図 3()mrn□ \廻二ニ/
FIG. 1 is a cross-sectional model of lithium taeniolite, FIGS. 2 and 3 are graphs showing the results of the examples, and FIG. 4 is a cross-sectional view of the microfunnel used to measure the adsorption rate. Patent Applicant Topy Industries, Ltd. Japan Tobacco Inc. Agent Patent Attorney Hitoshi Inagaki Yoshipa Figure 1 Iwa○○・○0 0Mg5iLiF Figure 2 (0n) Suha pressure fork ('C) Figure 3 4Figure 3()mrn□ \Mawari Nini/

Claims (4)

【特許請求の範囲】[Claims] (1)膨潤性合成雲母の層間イオンを、イオン交換法に
よりアルカリ土類金属若しくは他の金属イオンで置換し
てなる合成雲母置換体を主材とする発癌性物質用吸着材
(1) An adsorbent for carcinogenic substances whose main material is a substituted synthetic mica obtained by replacing the interlayer ions of swellable synthetic mica with alkaline earth metal or other metal ions using an ion exchange method.
(2)交換するイオンが、可溶性多核水酸化物イオンを
形成するアルカリ土類金属若しくは他の金属イオンであ
る特許請求の範囲第1項に記載の吸着材。
(2) The adsorbent according to claim 1, wherein the ions to be exchanged are alkaline earth metal or other metal ions that form soluble polynuclear hydroxide ions.
(3)合成雲母置換体に更に熱処理を施こしてなる特許
請求の範囲第2項に記載の吸着材。
(3) The adsorbent according to claim 2, which is obtained by further subjecting the synthetic mica substitute to heat treatment.
(4)原料として用いる膨潤性合成雲母が、F_2また
は(OH)_2を結晶構成成分とする特許請求の範囲第
1項ないし第3項のいずれか1項に記載の吸着材。
(4) The adsorbent according to any one of claims 1 to 3, wherein the swellable synthetic mica used as a raw material has F_2 or (OH)_2 as a crystal constituent component.
JP23755185A 1985-10-25 1985-10-25 Adsorbing material for carcinogen Pending JPS6297641A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23755185A JPS6297641A (en) 1985-10-25 1985-10-25 Adsorbing material for carcinogen

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP23755185A JPS6297641A (en) 1985-10-25 1985-10-25 Adsorbing material for carcinogen

Publications (1)

Publication Number Publication Date
JPS6297641A true JPS6297641A (en) 1987-05-07

Family

ID=17017006

Family Applications (1)

Application Number Title Priority Date Filing Date
JP23755185A Pending JPS6297641A (en) 1985-10-25 1985-10-25 Adsorbing material for carcinogen

Country Status (1)

Country Link
JP (1) JPS6297641A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2019049782A1 (en) * 2017-09-05 2019-03-14 国立研究開発法人物質・材料研究機構 Adsorbent material for purine base, adsorption filter for purine base using same, adsorption column filler for purine base, and system for removing purine base using these

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2019049782A1 (en) * 2017-09-05 2019-03-14 国立研究開発法人物質・材料研究機構 Adsorbent material for purine base, adsorption filter for purine base using same, adsorption column filler for purine base, and system for removing purine base using these
JPWO2019049782A1 (en) * 2017-09-05 2020-10-15 国立研究開発法人物質・材料研究機構 Purine base adsorption material, purine base adsorption filter using it, purine base adsorption column packing material, and purine base removal system using them

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