JPS60827A - Manufacture of air purifying agent - Google Patents

Manufacture of air purifying agent

Info

Publication number
JPS60827A
JPS60827A JP58109430A JP10943083A JPS60827A JP S60827 A JPS60827 A JP S60827A JP 58109430 A JP58109430 A JP 58109430A JP 10943083 A JP10943083 A JP 10943083A JP S60827 A JPS60827 A JP S60827A
Authority
JP
Japan
Prior art keywords
air purifying
purifying agent
colloidal silica
slaked lime
water
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
JP58109430A
Other languages
Japanese (ja)
Other versions
JPH0339734B2 (en
Inventor
Yoshiharu Kobayashi
小林 美春
Shozo Ichimura
市村 正三
Michinori Hashimoto
橋本 道憲
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.)
Nippon Chemical Industrial Co Ltd
Original Assignee
Nippon Chemical Industrial 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 Chemical Industrial Co Ltd filed Critical Nippon Chemical Industrial Co Ltd
Priority to JP58109430A priority Critical patent/JPS60827A/en
Priority to KR1019840003433A priority patent/KR880002540B1/en
Publication of JPS60827A publication Critical patent/JPS60827A/en
Publication of JPH0339734B2 publication Critical patent/JPH0339734B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C14SKINS; HIDES; PELTS; LEATHER
    • C14BMECHANICAL TREATMENT OR PROCESSING OF SKINS, HIDES OR LEATHER IN GENERAL; PELT-SHEARING MACHINES; INTESTINE-SPLITTING MACHINES
    • C14B1/00Manufacture of leather; Machines or devices therefor
    • C14B1/26Leather tensioning or stretching frames; Stretching-machines; Setting-out boards; Pasting boards

Landscapes

  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Mechanical Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

PURPOSE:To manufacture an air purifying agent having excellent water resistance, strength, and air pollutant removing efficiency by adding water to potassium permanganate, zeolite, slaked lime, and colloidal silica, kneading, molding, and drying. CONSTITUTION:3-30pts.wt. potassium permanganate, 10-70pts.wt. zeolite, and 6-70pts.wt. slaked lime and colloidal silica are blended to obtain 100pts.wt. total solids. Then 10-100pts.wt. water is added to the 100pts.wt. total solids, and the mixture is kneaded, molded, and then dried at 50-150 deg.C. In that case, slaked lime and colloidal silica are blended in 0.5-10mol ratio of CaO/SiO2. The air purifying agent thus obtained exhibits a high absorbing and adsorbing performance of harmful gases such as NOx, SOx, and gaseous NH3, and does not disintegrate even in water. The agent, having water resistance and high particle strength, without generating dust, and easy to handle, can be utilized industrially.

Description

【発明の詳細な説明】 本発明は空気浄化剤、特に耐水性、強度及び大気汚染物
質除去率の向上した改良された空気浄化剤の製造方法に
関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an air purifying agent, and more particularly to a method for producing an improved air purifying agent having improved water resistance, strength, and air pollutant removal rate.

本発明者等は既に特願昭!3−610t11.号(特開
昭5II−/!r2/、b/号公報)において過マンガ
ン酸カリウム、ベントナイトおよびゼオライトを有効成
分としてなる混練成型物による大気汚染物質の除去方法
を提案している。かかる方法の大気汚染物質の除去効率
は良好であるが、ここで使用する上記混練成型物は水中
に入れたり、多量の水滴と接触すると崩壊し耐水性がな
く、また、−粒強度が小さいため輸送、充填の際等に粉
塵が発生し取扱い上問題がある。
The inventors have already filed a patent application! 3-610t11. No. (JP-A-5II-/!r2/, b/) proposes a method for removing air pollutants using a kneaded molded product containing potassium permanganate, bentonite, and zeolite as active ingredients. Although the removal efficiency of air pollutants by this method is good, the kneaded molded product used here disintegrates when placed in water or comes into contact with a large amount of water droplets, and has no water resistance, and also has low particle strength. Dust is generated during transportation, filling, etc., which poses a problem in handling.

そこで本発明者等は上記に鑑み、改良された空気浄化剤
の製造方法について鋭意研究した結果、過マンガン酸カ
リとゼオライトの混合物を消石灰とコロイダルシリカで
混練成型し乾燥することにより耐水性が得られ、−粒強
度が増大し、大気汚染物質除去率も向上して空気浄化剤
としての性能を最も有効且適切に発揮できることを知見
し本発明を完成した。
In view of the above, the inventors of the present invention have conducted intensive research on a method for producing an improved air purifying agent. As a result, water resistance can be obtained by kneading and molding a mixture of potassium permanganate and zeolite with slaked lime and colloidal silica, and drying the mixture. The present invention was completed based on the finding that the particle strength is increased and the removal rate of air pollutants is also improved, so that the performance as an air purifying agent can be exhibited most effectively and appropriately.

即ち本発明は過マンガン酸カリ、ゼオライト、消石灰お
よびコロイダルシリカlこ水を加え混線成型した後乾燥
するこきを特徴とする空気浄化剤の製造方法である。
That is, the present invention is a method for producing an air purifying agent, which includes adding potassium permanganate, zeolite, slaked lime, and colloidal silica water, cross-molding, and then drying.

本発明において大気汚染物質の除去材料として主材をな
すKMnO,はNoXおよびSoxガスに対してすぐれ
た浄化作用がある。特にKMnO,は吸着しにくいNo
ガスを酸化してNo2ガスとなして除去する作用がある
In the present invention, KMnO, which is the main material used as a material for removing air pollutants, has an excellent purifying effect on NoX and Sox gases. In particular, KMnO is a hard-to-adsorb No.
It has the effect of oxidizing the gas to form No2 gas and removing it.

また、この酸化作用のためH2Sガスやアミン類、メル
カプタン、硫化アルキルなどの有機硫黄化合物の悪臭ガ
スと反応して脱臭する効果もある。一方、他の材料であ
るゼオライトは上記の材料では除去されないNH3ガス
を吸着除去するとともに後述するコロイダルシリカと消
石灰の反′見を促進する。本発明で用いられるゼオライ
トは合成品または天然品のいずれでもよく、t f、ニ
ー 該セ、tライトを酸または塩化アンモニウムなどで
処理して得られるH型の七オライドであってもよい。特
に本発明の目的から天然産のモルデナイトが好適である
Furthermore, due to this oxidizing action, it also has the effect of deodorizing by reacting with the malodorous gases of organic sulfur compounds such as H2S gas, amines, mercaptans, and alkyl sulfides. On the other hand, zeolite, which is another material, adsorbs and removes NH3 gas which cannot be removed by the above-mentioned materials, and also promotes the interaction between colloidal silica and slaked lime, which will be described later. The zeolite used in the present invention may be either a synthetic product or a natural product, and may be an H-type heptaolide obtained by treating tf, ni, t-lite with an acid or ammonium chloride. Naturally produced mordenite is particularly suitable for the purposes of the present invention.

ところで、一般にKMnO4の酸化作用によりN。By the way, N is generally produced by the oxidizing action of KMnO4.

カスをNo、ガスに転換して除去することやゼオライト
がアンモニアを吸着する作用のあることは、公知である
が、前者においては一般に溶液として反応性のよい状態
で高濃度ガスの除去に使用され、一方ゼ芽ライトのアン
モニアの除去は廃液中のNH4+の吸着除去でよく知ら
れている。
It is well known that zeolites can be removed by converting them into gas, and that zeolites have the effect of adsorbing ammonia, but in the former case, they are generally used as a solution in a highly reactive state to remove highly concentrated gases. , On the other hand, the removal of ammonia by zebulite is well known as the adsorption removal of NH4+ in waste liquid.

しかしながら、本発明におけるような各材料を固体状の
空気浄化剤として短時間に有害ガスを同時にかつ実質的
に除去することは又全く別の困難さを伴う。
However, as in the present invention, using each material as a solid air purifying agent to simultaneously and substantially remove harmful gases in a short period of time involves completely different difficulties.

すなわち、各材料の有害ガスに対する特性が混合成型に
よってそのまま発揮できるとは限らない場合が多い。
That is, in many cases, the characteristics of each material against harmful gases cannot be directly exhibited by mixing and molding.

又このことは各有効成分の材料を混線成型するためのバ
インダーの選択によっても大きく異なる。
This also varies greatly depending on the selection of a binder for cross-molding the materials of each active ingredient.

このようなことから、本発明者等は数多くの実験により
、消石灰とコロイダルシリカの反応生成物を介して、K
MnO4およびゼオライトの各材料を組合せたものが各
材料の特色を阻害することなくそのまま効果的に発揮す
ることはもちろん相乗的に作用することを認めたもので
ある。
For this reason, the present inventors have conducted numerous experiments to find that K
It has been recognized that a combination of MnO4 and zeolite materials can not only effectively exhibit the characteristics of each material without inhibiting them, but also work synergistically.

本発明に用いられるコロイダルシリカはコロイド状シリ
カゾルとして平均粒子径30mμ以下のシリカ成分をS
in、として5〜50重量%、通常10〜30重量%を
コロイド状に水中分散させたものである。かかるコロイ
ダルシリカ水溶液の市販品として日産化学工業株式会社
製のスノーテックスシリーズまたは触媒化成株式会社製
のカタロイドシリーズ等が知られている。また、消石灰
としては試薬、工業品いずれも使用できるが粒度の細か
いものがコロイダルシリカとの反応性が良く好ましい。
The colloidal silica used in the present invention is a silica component with an average particle size of 30 mμ or less as a colloidal silica sol.
In, 5 to 50% by weight, usually 10 to 30% by weight, is colloidally dispersed in water. Known commercial products of such colloidal silica aqueous solutions include the Snowtex series manufactured by Nissan Chemical Industries, Ltd. and the Cataloid series manufactured by Catalysts Kasei Co., Ltd. Further, as the slaked lime, both reagent and industrial products can be used, but one with fine particle size is preferred because it has good reactivity with colloidal silica.

例えば工業用消石灰特号(JISRi(7/)などが挙
げられる。
For example, industrial slaked lime special issue (JISRi (7/)) etc. are mentioned.

本発明においてはコロイダルシリカと消石灰はその反応
モル比にもよるが反応した結果、結合力のあまり強くな
い非晶質ケイ酸カルシウムないし結合力のある繊維状ま
たは帯鋼状若しくは板状の結晶質ケイ酸カルシウムを形
成し、過マンガン酸カリおよびゼオライトを結合せしめ
る作用を果すとともに、それ自体大気汚染物質を吸収ま
たは吸着したり吸湿能力もあるため大気中より水分を吸
収し、過マンガン酸カリを溶解させる作用も呈する。
In the present invention, colloidal silica and slaked lime react with each other, depending on their reaction molar ratio, resulting in either amorphous calcium silicate, which does not have a very strong bonding force, or a fibrous, strip-like, or plate-like crystalline calcium silicate, which has a strong bonding force. It forms calcium silicate, which acts to bind potassium permanganate and zeolite, and it also has the ability to absorb or adsorb air pollutants and absorb moisture, so it absorbs moisture from the atmosphere and binds potassium permanganate. It also exhibits a dissolving action.

本発明の空気浄化剤は以上の原料の全固型分ioo重量
部に対して更に10〜100重量部の水を加え充分混練
し、泥状ないしスラリー状になし通常の方法で適宜の形
状例えば粒状または破砕状に成型した後乾燥する。ここ
で水量は原料の種類、量、混線機、成型機などにより一
様ではないがいずれにせよ10重量部未満では混練成型
が充分でなく、ioo重量部を超える水の使用は成型後
乾燥するので通常熱管理上不経済である。
The air purifying agent of the present invention is prepared by adding 10 to 100 parts by weight of water to the total solid content of the above-mentioned raw materials and thoroughly kneading it to form a mud or slurry. It is molded into granules or crushed shapes and then dried. The amount of water here varies depending on the type and amount of raw materials, mixer, molding machine, etc., but in any case, if it is less than 10 parts by weight, kneading and molding will not be sufficient, and if more than 100 parts by weight of water is used, it will be dried after molding. Therefore, it is usually uneconomical in terms of heat management.

また、本発明の空気浄化剤を製造する際に上記原料以外
に過マンガン酸カリと反応しないものでカサ比重が小さ
く、比表面積および空孔容積が比較的大きい多孔質の無
機吸着性物質例えば珪酸カルシウム、珪酸マグネシウム
、微粉末珪酸、活性アルミナ、シリカアルミナ等を助剤
として添加することは一層好ましい。
In addition, when producing the air purifying agent of the present invention, in addition to the above-mentioned raw materials, porous inorganic adsorptive materials that do not react with potassium permanganate and have a small bulk specific gravity and a relatively large specific surface area and pore volume, such as silicic acid, are used. It is more preferable to add calcium, magnesium silicate, finely powdered silicic acid, activated alumina, silica alumina, etc. as auxiliaries.

更に除去すべき対象ガスの如何によっては必要に応じて
Mg(OH)22Mg01滑石、白土、けいそう土、粘
土、カオリン、右前などの一種または二種以上を配合さ
せることができる。
Further, depending on the target gas to be removed, one or more of Mg(OH)22Mg01 talc, white clay, diatomaceous earth, clay, kaolin, right front, etc. can be blended as necessary.

各原料の配合割合については処理すべき大気汚染物質の
種類、組成、得られる空気浄化剤の耐水性、強度、大気
汚染物質の処理能力などによって決定されるものである
が、基本的には全固型分100重量部尚り過マンガン酸
カリを3〜30重量部、ゼオライトを10〜70重量部
、消石灰およびコロイダルシリカを6〜り0重量部の範
囲が好適である。特に消石灰およびコロイダルシリカに
ついては/、0〜35重量部でしかもC! aO/S 
i Otモル比で0.!;−10の範囲内に入るように
配合するのが好適である。
The mixing ratio of each raw material is determined by the type and composition of the air pollutants to be treated, the water resistance and strength of the resulting air purifying agent, and the ability to treat air pollutants, but basically all A suitable range of 100 parts by weight of solid content is 3 to 30 parts by weight of potassium permanganate, 10 to 70 parts by weight of zeolite, and 6 to 0 parts by weight of slaked lime and colloidal silica. Especially for slaked lime and colloidal silica, it is 0 to 35 parts by weight and C! aO/S
i Ot molar ratio 0. ! ; It is preferable to mix it so that it falls within the range of -10.

ここで過マンガン酸カリの配合割合が3重量部未満では
大気汚染物質の処理能力が充分でなく30重量部を超え
る使用量では空気浄化剤の表面に析出し粉化の原因とな
るとともに強度を低下させる袖向となる。またゼオライ
トについては10重量部未満では特にアンモニアの除去
性能が低下するばかりか空気浄化剤の吸水能が低少し延
いては他の大気汚染物質の除去性能を低下させ、70重
量部を超える使用量は空気浄化剤自体の強度を下げる。
If the mixing ratio of potassium permanganate is less than 3 parts by weight, the ability to treat air pollutants will not be sufficient, and if it exceeds 30 parts by weight, it will precipitate on the surface of the air purifying agent, causing powdering and reducing the strength. Lower the sleeve direction. Regarding zeolite, if the amount used is less than 10 parts by weight, not only will the removal performance of ammonia in particular deteriorate, but also the water absorption capacity of the air purifying agent will be low. reduces the strength of the air purifying agent itself.

消石灰およびコロイダルシリカについては配合割合、O
aO/S iOtモル比とも上記範囲外では、空気浄化
剤の強度が充分でなく、耐水性も良くなく過マンガン酸
カリおよびゼオライトのバインダー効果を充分に発揮し
得ない。
For slaked lime and colloidal silica, the blending ratio, O
If both the aO/SiOt molar ratios are outside the above ranges, the air purifying agent will not have sufficient strength and water resistance, and the binder effect of potassium permanganate and zeolite will not be fully exhibited.

次に本発明の乾燥工程につき述べればこの工程は消石灰
とコロイダルシリカを反応させ非晶質ケイ酸カルシウム
ないし結晶質ケイ酸カルシウムを形成させ、過マンガン
酸カリおよびゼオライトを大気汚染物質の処理能力を損
うことなく結合させるために不可欠の工程である。一般
に特に建材関係の技術分野において、消石灰とコロイダ
ルシリカとが反応して種々の形態のケイ酸カルシウムが
生成すること自体は公知であるが、主に過マンガン酸カ
リとゼオライトからなる空気浄化剤の製造方法において
、生成直後のケイ酸カルシウムをバインダーとしてばか
りでなくそれ自体大気汚染物質の処理剤に利用すること
、ゼオライトの一部をその反応の触媒として利用するこ
と、既定のモル比に拘わらずゼオライトとKMnO,の
組合せの兼合いで好適な空気浄化剤を製造し得ることを
見出したのは本発明者等の検討の結果である。消石灰と
コロイダルシリカは低温から高温に亘って種々のモル比
で種々の形態のケイ酸カルシウムを形成するが、本発明
では既述した配合割合、モル比において10℃〜/10
℃ の温度範囲で反応させるとともに乾燥するのが好ま
しい。SO℃未満では空気浄化剤の強度が低下するばか
りか乾燥時間がかかり工業的でなく、130℃を超える
乾燥温度はKMnO4の分解を紡ぐ意味からもなるべく
避けるのが得策である。尚乾燥時間については、原料の
種類・配合割合その他の乾燥条件、空気浄化剤の物性な
どにより一様ではないが、上記乾燥温度範囲内で目的物
の空気浄化剤中の含水量が/ % 70重量−程度にな
るまで乾燥するのが良い。何故なら上記範囲内において
空気浄化剤の耐水性、強度、大気汚染物質除去率が大い
に改良されるからである。
Next, regarding the drying process of the present invention, in this process, slaked lime and colloidal silica are reacted to form amorphous calcium silicate or crystalline calcium silicate, and potassium permanganate and zeolite are used to improve the ability to treat air pollutants. This is an essential step for bonding without damage. It is generally known, particularly in the technical field related to building materials, that slaked lime and colloidal silica react to produce various forms of calcium silicate. In the manufacturing method, the calcium silicate immediately after production is used not only as a binder but also as a treatment agent for air pollutants, and a part of the zeolite is used as a catalyst for the reaction, regardless of the predetermined molar ratio. It is the result of studies by the present inventors that it was discovered that a suitable air purifying agent can be produced by combining zeolite and KMnO. Slaked lime and colloidal silica form various forms of calcium silicate at various molar ratios from low to high temperatures.
It is preferred to carry out the reaction and dry at a temperature range of . If the drying temperature is below 130°C, the strength of the air purifying agent will not only decrease, but also the drying time will be long, making it unsuitable for industrial use.It is best to avoid drying temperatures above 130°C as much as possible from the viewpoint of decomposition of KMnO4. The drying time varies depending on the type of raw materials, blending ratio, other drying conditions, physical properties of the air purifying agent, etc., but within the above drying temperature range, the moisture content of the target air purifying agent is 70%. It is best to dry it until it reaches about 100 lbs. This is because within the above range, the water resistance, strength, and air pollutant removal rate of the air purifying agent are greatly improved.

かくして本発明に係る空気浄化剤は製造できるのである
が本発明のゼオライト、消石灰およびコロイダルシリカ
という組合せはその他の第3物質を配合して、オゾン除
去剤、酸性ガス除去剤、鮮度保持剤、脱湿剤等の他の耐
水性の成型物を得る場合にも適用可能である。
In this way, the air purifying agent according to the present invention can be produced, but the combination of zeolite, slaked lime, and colloidal silica of the present invention can be combined with other third substances to produce an ozone remover, an acidic gas remover, a freshness-preserving agent, and a dehydrator. It can also be applied to the production of other water-resistant molded products such as moisturizers.

本発明に係る空気浄化剤は、大きい空孔容積をもつため
、NOx、SOxおよびNH,ガスなどの有害ガスに対
して非常に効果的に高い吸収吸着性能を示すとともに、
水中でも崩壊しない所謂耐水性と粉塵発生がなく取扱い
容易であるという一粒強度が大きいという特性を有し工
業的に有用なものである。
Since the air purifying agent according to the present invention has a large pore volume, it exhibits highly effective absorption and adsorption performance against harmful gases such as NOx, SOx, and NH gas, and
It is industrially useful because it has the characteristics of so-called water resistance that does not disintegrate even in water, and high single grain strength that does not generate dust and is easy to handle.

また、本発明の空気浄化剤ではKMnO,の強い酸化力
のため上記の如く臭気成分を酸化分解する性質があり同
時に脱臭効果も充分期待できる。
Further, the air purifying agent of the present invention has the property of oxidizing and decomposing odor components as described above due to the strong oxidizing power of KMnO, and at the same time, a sufficient deodorizing effect can be expected.

本発明にかかる空気浄化剤の使用に商っては、適当な容
器に充填して使用することができる。
When using the air purifying agent according to the present invention, it can be used by filling it into a suitable container.

以下、実施例を挙げて本発明を更に具体的に説明する。Hereinafter, the present invention will be explained in more detail with reference to Examples.

KMnO,の微粉末結晶、無機吸着性物質(例:珪酸カ
ルシウム)、天然産ゼオライト、消石灰の各粉末を第1
表の所定量とり、よく混合した後、所定量のSin、 
20 %含有のコロイダルシリカ水溶液と水と共によく
混練して、押出し成型機にて直径3mの円柱状としこれ
をそれぞれ所定の温度で所定の時間乾燥して各空気浄化
剤を製造した。
First, each powder of KMnO, fine powder crystal, inorganic adsorptive substance (e.g. calcium silicate), naturally produced zeolite, and slaked lime was added.
After taking the specified amount in the table and mixing well, add the specified amount of Sin,
The mixture was thoroughly kneaded with a 20% colloidal silica aqueous solution and water, formed into a cylindrical shape with a diameter of 3 m using an extrusion molding machine, and dried at a predetermined temperature for a predetermined time to produce each air purifying agent.

上記各空気浄化剤を一夜水中に放置した場合の耐水性と
、錠裂破壊強度測定器で一粒強度(n=10で上下1個
づ\カットし3個の平均)を測定した。空孔容積は試料
を四塩化炭素(001,)中に21I時間浸漬し、含浸
したcc’t、の容積より計算した。
The water resistance of each of the above air purifying agents was measured when they were left in water overnight, and the strength of each tablet was measured using a tablet breaking strength measuring device (n=10, one upper and lower one was cut, and the average of three pieces). The pore volume was calculated from the volume of cc't impregnated by immersing the sample in carbon tetrachloride (001,) for 21 hours.

\ \1、 ゛\ \ \ 実施例/〜g及び比較例/−2のOak/Sin。\ \1, ゛\ \ \ Oak/Sin of Examples/~g and Comparative Example/-2.

モル比と一粒強度の関係を第1図に示す。図中に示す温
度は乾燥温度である。図中縦軸側から順次実施例1〜実
施例g及び比較例/−Jのデータをプロットした。Oa
O/El iO2モル比す0及びiooの上の点は比較
例である。
Figure 1 shows the relationship between molar ratio and single grain strength. The temperatures shown in the figure are drying temperatures. In the figure, data of Examples 1 to Example g and Comparative Example/-J are plotted sequentially from the vertical axis side. Oa
The points above O/El iO2 molar ratio 0 and ioo are comparative examples.

実施例9〜13及び比較例3〜S 全固型分当りの消石灰およびコロイダルシリカの配合割
合と空気浄化剤の物性との関係を検討するため第2表の
配合割合で実施例1と同様に各空気浄化剤を製造し、そ
の物性を測定し同表にまとめた。
Examples 9 to 13 and Comparative Examples 3 to S In order to examine the relationship between the blending ratio of slaked lime and colloidal silica per total solid content and the physical properties of the air purifying agent, the same procedure as in Example 1 was carried out using the blending ratios shown in Table 2. Each air purifying agent was manufactured and its physical properties were measured and summarized in the same table.

゛・1、 ′・、 \、 ゛\ 〜・、 \ に示す。図中の温度は乾燥温度である。゛・1、 ′・、 \、 ゛\ 〜・、 \ Shown below. The temperature in the figure is the drying temperature.

・、O・及びマ〕は比較例である。, O, and Ma] are comparative examples.

実施例/II−/g及び比較例6 空気浄化剤製造時の無機吸着性物質と水の量と物性との
関係を検討するため第3表の配合害u合で実施例1と同
様に各空気浄化剤を製造し、その物性を測定し同表にま
とめた。又各空気浄化剤のH,S除去性能も併せて同表
−こまとめた。
Example/II-/g and Comparative Example 6 In order to examine the relationship between the amount of inorganic adsorptive substances and water and physical properties during the production of air purifying agents, each sample was prepared in the same manner as in Example 1 using the combinations shown in Table 3. An air purifying agent was manufactured and its physical properties were measured and summarized in the same table. The H and S removal performance of each air purifying agent is also summarized in the same table.

\、 \\ \ \ゝ、 〜゛・、 〜 第3表 註l)耐水性(−夜放置後)0=崩れない、×=崩れる
\、 \\ \ \ゝ、 〜゛・、 〜 Table 3 Note l) Water resistance (-after being left overnight) 0 = does not collapse, × = collapses.

2)比較例6は特開昭5e−isコロ6/による従来品
3)尚H,8除去試験の条件は次の通りである。
2) Comparative Example 6 is a conventional product manufactured by JP-A-5E-IS Colo 6/3) The conditions for the H,8 removal test are as follows.

湿度so〜AO’ly、室温、入ロH,S濃度20pp
m。
Humidity so~AO'ly, room temperature, H, S concentration 20pp
m.

空間速1tC8V) 20000 ノ条件でH2E+を
吸収させた(sv試験例1 実施例/Sの空気浄化剤につl、Nて湿度3Q−60チ
、室温、NOガス濃度ti、sppmおよびBv/:1
000の条件でNOガスを吸収させたところNO除去率
はbo分後において92%であった。
H2E+ was absorbed under the following conditions (sv test example 1 Example/S air purifier: room velocity, NO gas concentration ti, sppm and Bv/: 1
When NO gas was absorbed under the conditions of 000, the NO removal rate was 92% after bo minutes.

試験例λ 実施例10の空気浄化剤につ0て、湿度SOチ、温度2
3℃、 so2ガス濃度u、Oppm、eV /200
0の条件でSO,ガスを吸収させたところSO,除去率
は60分後において99%であった。
Test Example λ Regarding the air purifying agent of Example 10, humidity is SO, temperature is 2.
3℃, SO2 gas concentration u, Oppm, eV /200
When SO gas was absorbed under conditions of 0, the SO removal rate was 99% after 60 minutes.

試験例3 実施例ダの空気浄化剤について湿度qo%、温度20℃
、NH3ガス濃度200 ppm %BV120θOの
条件でNH,ガスを吸収させたところ、klH,除去率
は60分後において93%であった。
Test Example 3 Regarding the air purifying agent of Example DA, humidity qo%, temperature 20°C
When NH gas was absorbed under the conditions of NH3 gas concentration of 200 ppm% BV120θO, the klH removal rate was 93% after 60 minutes.

試験例V 実施例9の空気浄化剤について湿度50−60チ、室温
、トリメチルアミン(CH3)3Nガス濃度20 pp
m、EVlooooの条件で(OH8)、Nを吸収させ
たところ(CH3)3N除去率は60分後において9g
%で′あった。
Test Example V Regarding the air purifying agent of Example 9, humidity 50-60 degrees, room temperature, trimethylamine (CH3)3N gas concentration 20 pp
When N was absorbed under the conditions of (OH8) and EVlooooo (CH3), the 3N removal rate was 9g after 60 minutes.
%Met.

試験例! 実施例/3の空気浄化剤について湿度bo%、室温、ト
リエチルアミン(C2HI+)11Nガス濃度10pp
m 、 SV / 0000の条件で(C2H1+)3
Nを吸収させたところ(0,H,)、N除去率は60分
後において95%であった。
Test example! Regarding the air purifying agent of Example 3, humidity bo%, room temperature, triethylamine (C2HI+) 11N gas concentration 10 pp
m, (C2H1+)3 under the condition of SV / 0000
When N was absorbed (0, H,), the N removal rate was 95% after 60 minutes.

試験例6 実施例1の空気浄化剤について湿度sro%、室温、メ
チルメルカプタン0H3SHガス濃度5θppm 、 
8V / 0000の条件でCH3SH全3SHヲ吸収
サセタH38H除去率は60分後において99%であっ
た。
Test Example 6 Regarding the air purifying agent of Example 1, humidity sro%, room temperature, methyl mercaptan 0H3SH gas concentration 5θppm,
Under the condition of 8V/0000, the removal rate of all 3SH of CH3SH was 99% after 60 minutes.

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

第1図は実施例/−g及び比較例/〜−の浄化剤のOa
k/Sin、モル比と一粒強度との関係を示す図、第2
図は実施例9〜13と比較例3〜グ特許出願人 日本化
学工業株式会社
Figure 1 shows the Oa of the purifying agents of Example/-g and Comparative Examples/--.
Figure 2 showing the relationship between k/Sin, molar ratio and single grain strength
The figures show Examples 9 to 13 and Comparative Examples 3 to 3. Patent applicant: Nippon Chemical Industry Co., Ltd.

Claims (1)

【特許請求の範囲】 l 過マンガン酸カリ、ゼオライト、消石灰およびコロ
イダルシリカに水を加え混練成型した後乾燥することを
特徴とする空気浄化剤の製造方法。 ユ 全固型分ioo重量部肖り過マンガン酸カリを3〜
30重量部、ゼオライトを10〜70重量部、消石灰お
よびコロイダルシリカを6〜り0重量部の範囲内に配合
する特許請求の範囲第1項記載の空気浄化剤の製造方法
。 3 全固型分100重量部に対して10〜io。 重量部の水を加える特許請求の範囲第1項または第2項
記載の空気浄化剤の製造方法。 ダ 消石灰とコロイダルシリカをOak/Sin、モル
比でO,S〜IOの範囲に配合する特許請求の範囲第1
項ないし第3項いずれか1項記載の空気浄化剤の製造方
法。 !rSO℃〜/30℃の温度範囲で乾燥する特許請求の
範囲第1項ないし第v項のいずれか1項記載の空気浄化
剤の製造方法。
[Claims] 1. A method for producing an air purifying agent, which comprises adding water to potassium permanganate, zeolite, slaked lime, and colloidal silica, kneading and molding the mixture, and then drying the mixture. Total solid content ioo weight part Potassium permanganate 3~
30 parts by weight of zeolite, 10 to 70 parts by weight of slaked lime and colloidal silica, and 6 to 0 parts by weight of slaked lime and colloidal silica. 3 10 to io per 100 parts by weight of total solids. The method for producing an air purifying agent according to claim 1 or 2, wherein parts by weight of water are added. DA Claim 1, in which slaked lime and colloidal silica are mixed in an Oak/Sin molar ratio in the range of O, S to IO.
A method for producing an air purifying agent according to any one of Items 3 to 3. ! The method for producing an air purifying agent according to any one of claims 1 to v, wherein the air purifying agent is dried in a temperature range of rSO°C to /30°C.
JP58109430A 1983-06-20 1983-06-20 Manufacture of air purifying agent Granted JPS60827A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP58109430A JPS60827A (en) 1983-06-20 1983-06-20 Manufacture of air purifying agent
KR1019840003433A KR880002540B1 (en) 1983-06-20 1984-06-19 The preparation method of air-filtering material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58109430A JPS60827A (en) 1983-06-20 1983-06-20 Manufacture of air purifying agent

Publications (2)

Publication Number Publication Date
JPS60827A true JPS60827A (en) 1985-01-05
JPH0339734B2 JPH0339734B2 (en) 1991-06-14

Family

ID=14510042

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58109430A Granted JPS60827A (en) 1983-06-20 1983-06-20 Manufacture of air purifying agent

Country Status (2)

Country Link
JP (1) JPS60827A (en)
KR (1) KR880002540B1 (en)

Cited By (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61293546A (en) * 1985-06-21 1986-12-24 Nippon Chem Ind Co Ltd:The Acidic gas removing agent
JPS6271534A (en) * 1985-09-25 1987-04-02 Nippon Chem Ind Co Ltd:The Sour gas removing agent
JPS63156537A (en) * 1987-11-20 1988-06-29 Nippon Sanso Kk Absorbent for waste gas containing harmful component
US4782804A (en) * 1985-12-06 1988-11-08 Robert Bosch Gmbh Centrifugal speed governor for internal combustion engines
US4933555A (en) * 1987-02-03 1990-06-12 Gec-Marconi Limited Thermal imager
US5278112A (en) * 1992-11-13 1994-01-11 Fred Klatte Chemically impregnated zeolite and method for chemically impregnating and coating zeolite
WO1995016518A1 (en) * 1993-12-15 1995-06-22 Purafil, Inc. Improved solid filtration media incorporating elevated levels of permanganate and water
US5464598A (en) * 1992-11-13 1995-11-07 Klatte; Fred Method for removing a contaminant from a fluid using a chemically impregnated and coated zeolite
US5567405A (en) * 1992-11-13 1996-10-22 Klatte Inc. Method for producing chlorine dioxide using chemically impregnated zeolite
US5573743A (en) * 1992-11-13 1996-11-12 Klatte Inc. Method for producing chlorine dioxide and removing chlorine dioxide using chemically impregnated zeolite
US5730948A (en) * 1992-11-13 1998-03-24 Klatte Inc. Method for producing chlorine dioxide using chemically impregnated zeolite
US5833739A (en) * 1992-11-13 1998-11-10 Klatte; Fred Chemically coated zeolite and method for chemically coating zeolite and using coated zeolite
US5942323A (en) * 1995-01-27 1999-08-24 Purafil, Inc. Fiber filter and methods of use thereof
WO1999061134A1 (en) * 1998-05-26 1999-12-02 Takasago Thermal Engineering Co., Ltd. Air cleaning filter, process for preparing the same, and high-level cleaner
US6605558B2 (en) 1997-02-11 2003-08-12 Fred Klatte Composition for producing chlorine dioxide
US7347994B2 (en) 2002-09-13 2008-03-25 Ica Trinova, Llc Method and composition for attracting arthropods by volatilizing an acid
JP2010240620A (en) * 2009-04-09 2010-10-28 Japan Pionics Co Ltd Treatment method and treatment apparatus for gas containing nitrogen oxide
US9382116B2 (en) 2013-01-10 2016-07-05 Ica Trinova, Llc Mixtures for producing chlorine dioxide gas in enclosures and methods of making the same

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106582531B (en) * 2016-12-30 2019-01-25 广州博能能源科技有限公司 A kind of composite air purifying agent and preparation method thereof and air cleaning unit

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52102894A (en) * 1976-02-25 1977-08-29 Matsushita Electric Ind Co Ltd Air purifier
JPS5667521A (en) * 1979-11-07 1981-06-06 Daiichi Nouzai Kk Adsorptive annihilating method of toxic gases diffusing from adhered part or the like of furnitures

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52102894A (en) * 1976-02-25 1977-08-29 Matsushita Electric Ind Co Ltd Air purifier
JPS5667521A (en) * 1979-11-07 1981-06-06 Daiichi Nouzai Kk Adsorptive annihilating method of toxic gases diffusing from adhered part or the like of furnitures

Cited By (24)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61293546A (en) * 1985-06-21 1986-12-24 Nippon Chem Ind Co Ltd:The Acidic gas removing agent
JPS6271534A (en) * 1985-09-25 1987-04-02 Nippon Chem Ind Co Ltd:The Sour gas removing agent
US4782804A (en) * 1985-12-06 1988-11-08 Robert Bosch Gmbh Centrifugal speed governor for internal combustion engines
US4933555A (en) * 1987-02-03 1990-06-12 Gec-Marconi Limited Thermal imager
JPS63156537A (en) * 1987-11-20 1988-06-29 Nippon Sanso Kk Absorbent for waste gas containing harmful component
JPH0378132B2 (en) * 1987-11-20 1991-12-12 Nippon Oxygen Co Ltd
US5833739A (en) * 1992-11-13 1998-11-10 Klatte; Fred Chemically coated zeolite and method for chemically coating zeolite and using coated zeolite
US5464598A (en) * 1992-11-13 1995-11-07 Klatte; Fred Method for removing a contaminant from a fluid using a chemically impregnated and coated zeolite
US5567405A (en) * 1992-11-13 1996-10-22 Klatte Inc. Method for producing chlorine dioxide using chemically impregnated zeolite
US5573743A (en) * 1992-11-13 1996-11-12 Klatte Inc. Method for producing chlorine dioxide and removing chlorine dioxide using chemically impregnated zeolite
US5730948A (en) * 1992-11-13 1998-03-24 Klatte Inc. Method for producing chlorine dioxide using chemically impregnated zeolite
US5278112A (en) * 1992-11-13 1994-01-11 Fred Klatte Chemically impregnated zeolite and method for chemically impregnating and coating zeolite
WO1995016518A1 (en) * 1993-12-15 1995-06-22 Purafil, Inc. Improved solid filtration media incorporating elevated levels of permanganate and water
US6265024B1 (en) 1995-01-27 2001-07-24 Purafil, Inc. Fiber filter and methods of use thereof
US5942323A (en) * 1995-01-27 1999-08-24 Purafil, Inc. Fiber filter and methods of use thereof
US6605558B2 (en) 1997-02-11 2003-08-12 Fred Klatte Composition for producing chlorine dioxide
US6635230B2 (en) 1997-02-11 2003-10-21 Fred Klatte Method for producing chlorine dioxide
WO1999061134A1 (en) * 1998-05-26 1999-12-02 Takasago Thermal Engineering Co., Ltd. Air cleaning filter, process for preparing the same, and high-level cleaner
US6352578B1 (en) * 1998-05-26 2002-03-05 Takasago Thermal Engineering Co., Ltd. Air cleaning filter, process for preparing the same, and high-level cleaner
US7347994B2 (en) 2002-09-13 2008-03-25 Ica Trinova, Llc Method and composition for attracting arthropods by volatilizing an acid
US7922992B2 (en) 2002-09-13 2011-04-12 Ica Trinova, Llc Composition and method for producing carbon dioxide
US8709396B2 (en) 2002-09-13 2014-04-29 Premark Feg L.L.C. Method and composition for attracting arthropods by volatizing an acid
JP2010240620A (en) * 2009-04-09 2010-10-28 Japan Pionics Co Ltd Treatment method and treatment apparatus for gas containing nitrogen oxide
US9382116B2 (en) 2013-01-10 2016-07-05 Ica Trinova, Llc Mixtures for producing chlorine dioxide gas in enclosures and methods of making the same

Also Published As

Publication number Publication date
JPH0339734B2 (en) 1991-06-14
KR880002540B1 (en) 1988-11-29
KR850000256A (en) 1985-02-26

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