JPH09278557A - Porous sintered product, and water-purifying material comprising the same - Google Patents

Porous sintered product, and water-purifying material comprising the same

Info

Publication number
JPH09278557A
JPH09278557A JP8114211A JP11421196A JPH09278557A JP H09278557 A JPH09278557 A JP H09278557A JP 8114211 A JP8114211 A JP 8114211A JP 11421196 A JP11421196 A JP 11421196A JP H09278557 A JPH09278557 A JP H09278557A
Authority
JP
Japan
Prior art keywords
water
sintered body
porous sintered
dust
mixture
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
JP8114211A
Other languages
Japanese (ja)
Inventor
Yoshitsugu Gunji
義次 軍司
Shinya Idezu
新也 出津
Yoshiaki Kobayashi
良紀 小林
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.)
AUTOMOBILE FOUNDRY
JIDOSHA IMONO KK
Original Assignee
AUTOMOBILE FOUNDRY
JIDOSHA IMONO KK
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 AUTOMOBILE FOUNDRY, JIDOSHA IMONO KK filed Critical AUTOMOBILE FOUNDRY
Priority to JP8114211A priority Critical patent/JPH09278557A/en
Publication of JPH09278557A publication Critical patent/JPH09278557A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To obtain a porous sintered product having uniformly distributed pores, excellent in strength and gas permeability, and capable of adsorbing and photochemically decomposing organic substances, etc., over a long period, and to obtain a water-purifying material comprising the same. SOLUTION: This porous sintered product is obtained by adding water to the collected mixture dust of inorganic oxides containing at least zinc oxide and evaporated from a smelting furnace for cast iron, kneading the mixture, molding the kneaded product, and subsequently sintering the molded product. A water-floating porous sintered product is obtained by combining the above porous sintered product with another sintered product such as a water-floating sintered product or with a sintering raw material having a bulk specific gravity of <=0.5. This water-purifying material comprises the porous sintered products.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、長期間にわたって
水質浄化材として優れた性能を発揮する多孔質焼結体に
関する。
TECHNICAL FIELD The present invention relates to a porous sintered body that exhibits excellent performance as a water purification material for a long period of time.

【0002】[0002]

【従来の技術】近年、環境問題に対する関心が高まり、
我国においても産業界、学界、官界挙げてその対策に取
り組んでいる。具体的には、廃棄物処理・リサイクルな
どに関する立法措置が講じられ、それに応じて企業にお
いても環境保全と経済性の確保との調和を図るための革
新的な技術開発が求められている。
2. Description of the Related Art In recent years, interest in environmental issues has increased,
In Japan as well, the industry, academia and government are working on countermeasures. Specifically, legislative measures regarding waste treatment / recycling, etc. are taken, and accordingly, companies are required to develop innovative technologies to achieve harmony between environmental protection and economic efficiency.

【0003】鋳物業界においても、鋳造の各工程におい
て、廃棄処分すべき砂やダストなどが多量に発生する。
これらの砂やダストは再生処理して、極力リサイクルし
ているが、再生処理しても再利用できない砂やダストが
依然として多量に発生し、これらは埋め立て処理などに
より処分している。
Even in the casting industry, a large amount of sand, dust and the like to be discarded is generated in each casting process.
Although these sands and dusts are recycled and recycled as much as possible, a large amount of sands and dusts that cannot be reused are still generated even if they are recycled, and they are disposed of by landfilling.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、前記の
再利用できない廃棄砂やダストを埋め立て処理などする
ためには、かなりの費用を要するだけでなく、埋め立て
場所にも限界がある。
However, landfilling the waste sand and dust that cannot be reused requires not only a considerable cost but also a limit in the landfill site.

【0005】本発明は、鋳鉄原料を溶解する炉から発生
し少なくとも酸化亜鉛を含有する無機酸化物などの混合
物ダストを使用して、気孔が均一に分布しており、強度
及び通気性に優れ、長期間にわたって有機物などを吸着
し光分解しうる焼結体、並びにこれからなる水質浄化材
を提供することを目的とする。
The present invention uses a mixture dust such as an inorganic oxide containing at least zinc oxide generated from a furnace that melts a cast iron raw material, has pores uniformly distributed, is excellent in strength and air permeability, An object of the present invention is to provide a sintered body capable of adsorbing an organic substance and the like and photodecomposing for a long period of time, and a water purification material comprising the same.

【0006】[0006]

【課題を解決するための手段】前記目的を達成するため
に、本発明は、鋳鉄用溶解炉から蒸発し集塵された少な
くとも酸化亜鉛を含有する無機酸化物の混合物ダストに
水を加えて混練し成形した成形物を焼成して得られる多
孔質焼結体である。
In order to achieve the above object, the present invention is to knead by adding water to a mixture dust of an inorganic oxide containing at least zinc oxide evaporated and collected from a melting furnace for cast iron. It is a porous sintered body obtained by firing a molded product that has been molded.

【0007】本発明は、鋳鉄用溶解炉から蒸発し集塵さ
れた少なくとも酸化亜鉛を含有する無機酸化物の混合物
ダストにかさ比重0.5以下の焼結体形成原料と水を加
えて混練し成形した成形物を焼成して得られる水浮揚性
の多孔質焼結体である。
According to the present invention, the mixture dust of the inorganic oxide containing at least zinc oxide evaporated from the melting furnace for cast iron and collected, and the raw material for forming a sintered body having a bulk specific gravity of 0.5 or less and water are kneaded. It is a water-floating porous sintered body obtained by firing a molded product.

【0008】本発明は、鋳鉄用溶解炉から蒸発し集塵さ
れた少なくとも酸化亜鉛を含有する無機酸化物の混合物
ダストに水を加えて混練したペーストを、焼結体に付着
させて成形した成形物を焼成して得られる、多孔質焼結
体である。
According to the present invention, a paste obtained by adding water to a mixture dust of an inorganic oxide containing at least zinc oxide, which has been evaporated and dust-collected from a melting furnace for cast iron and kneaded, is formed by adhering it to a sintered body. It is a porous sintered body obtained by firing a product.

【0009】本発明は、鋳鉄用溶解炉から蒸発し集塵さ
れた少なくとも酸化亜鉛を含有する無機酸化物の混合物
ダストに水を加えて混練したペーストを、水浮揚性の焼
結体に付着させて成形した成形物を焼成して得られる、
水浮揚性の多孔質焼結体である。
According to the present invention, water is added to a mixture dust of a mixture of inorganic oxides containing at least zinc oxide, which has been evaporated and collected from a melting furnace for cast iron, and the mixture is kneaded to make it adhere to a water-floating sintered body. Obtained by firing a molded product molded by
It is a water-buoyant porous sintered body.

【0010】本発明は、前記の各多孔質焼結体におい
て、成形体を焼成する前に乾燥することを特徴とする前
記多孔質焼結体である。
The present invention is the above-mentioned porous sintered body, characterized in that the molded body is dried before firing.

【0011】また本発明は、前記の各多孔質焼結体から
なることを特徴とする水質浄化材である。
Further, the present invention is a water purification material characterized by comprising each of the above-mentioned porous sintered bodies.

【0012】[0012]

【発明の実施の形態】本発明の多孔質焼結体の製造に使
用されるダストは、鋳鉄用溶解炉から蒸発し集塵され
る、少なくとも酸化亜鉛を含有する無機酸化物の混合物
の微粒子である。一般に、鋳鉄は、銑鉄や鉄くずなどの
鉄原料に、コークスなどの加炭剤、石灰石や蛍石などの
溶剤、及びMg、Ni−Mg合金、Cu−Fe−Si−
Mg合金、Fe−Si−Mg合金、Fe−Si−Mg−
Ca合金、Mg−コークス、Ca−Siの希土類元素や
塩化カルシウム被覆物、MgF2 −希土類弗化物−Ca
−Siの混合物、CeLaなどの添加材料を加えて、キ
ュポラ、アーク炉、誘導炉、反射炉、回転炉などの溶解
炉で例えば1500〜1600℃で溶解される。この鉄
原料として、通常、亜鉛被覆鉄板が多量に使用されるた
め、溶解の際に、酸化亜鉛を多量に含む無機酸化物の混
合物が蒸発し、溶解炉の集塵装置でダストとして回収さ
れる。このダストの成分及びその比率は、使用される原
料によって異なるが、通常、主成分の酸化亜鉛(Zn
O)以外に、MgO、Al23 、SiO2 、P2
5、SO3 、K2 O、CaO、Cr23 、MnO、
Fe23 、PbOなどの無機酸化物の1種以上を含有
しており、場合によっては更にClやCe、La、Ac
などを含有している。ダストの主成分である酸化亜鉛は
光反応性半導体であり、これと前記無機酸化物の1種以
上とが混在する本発明におけるダストは、これらの無機
酸化物により酸化亜鉛の光反応性半導体としての性質が
顕著に助長されるものと考えられる。回収されるダスト
の粒径は、通常、10〜30μmである。
BEST MODE FOR CARRYING OUT THE INVENTION The dust used for producing the porous sintered body of the present invention is fine particles of a mixture of inorganic oxides containing at least zinc oxide, which are evaporated and collected from a melting furnace for cast iron. is there. In general, cast iron is a raw material for iron such as pig iron or iron scrap, a carburizing agent such as coke, a solvent such as limestone or fluorite, and Mg, Ni-Mg alloy, Cu-Fe-Si-.
Mg alloy, Fe-Si-Mg alloy, Fe-Si-Mg-
Ca alloy, Mg-coke, Ca-Si rare earth element or calcium chloride coating, MgF 2 -rare earth fluoride-Ca
A mixture of -Si and an additive material such as CeLa are added and melted at, for example, 1500 to 1600 ° C in a melting furnace such as a cupola, an arc furnace, an induction furnace, a reverberation furnace, and a rotary furnace. Since a large amount of zinc-coated iron plate is usually used as this iron raw material, a mixture of inorganic oxides containing a large amount of zinc oxide is evaporated during melting and is recovered as dust in the dust collector of the melting furnace. . The components of this dust and the ratio thereof differ depending on the raw materials used, but usually zinc oxide (Zn oxide) as the main component is used.
O), MgO, Al 2 O 3 , SiO 2 , P 2
O 5 , SO 3 , K 2 O, CaO, Cr 2 O 3 , MnO,
It contains one or more kinds of inorganic oxides such as Fe 2 O 3 and PbO, and may further contain Cl, Ce, La, Ac.
Etc. are included. Zinc oxide, which is the main component of dust, is a photoreactive semiconductor, and the dust in the present invention in which it is mixed with one or more of the above inorganic oxides is used as a photoreactive semiconductor of zinc oxide due to these inorganic oxides. It is considered that the property of is significantly promoted. The particle size of the collected dust is usually 10 to 30 μm.

【0013】本発明において使用されるかさ比重0.5
以下の焼結体形成原料としては、例えば、シリカ、アル
ミナを主成分とする火山噴出ガラス粒子を加熱膨張させ
た中空状の独立気泡粒子を挙げることができ、この粒子
は例えば平均粒径37μm〜1.6mmの場合にはかさ
比重は0.07〜0.5である。このようなかさ比重
0.5以下の焼結体形成原料は、鋳鉄用溶解炉から集塵
したダストと配合して使用される以外に、それ自体をベ
ントナイトと水と共に混練し、目的に応じ所定の大き
さ、形状(粒状、カプセル状、球状など)に成形し(乾
燥して)焼成するか、あるいはそれ自体を焼成し所定の
大きさ、形状に成形して、水浮揚性の焼結体を製造す
る。
The bulk specific gravity used in the present invention is 0.5.
Examples of the raw material for forming a sintered body below include hollow closed-cell particles obtained by heating and expanding volcanic eruption glass particles containing silica or alumina as a main component, and the particles have, for example, an average particle diameter of 37 μm to In the case of 1.6 mm, the bulk specific gravity is 0.07 to 0.5. Such a raw material for forming a sintered body having a bulk specific gravity of 0.5 or less is used by mixing with the dust collected from the melting furnace for cast iron, kneading itself with bentonite and water, and then being mixed in a predetermined amount according to the purpose. Form into a size and shape (granular, capsule-like, spherical, etc.) and fire (dry), or fire itself to form a predetermined size and shape to give a water-floating sintered body. To manufacture.

【0014】本発明の多孔質焼結体の製造において、前
記のダスト微粒子に、まず水を加えて混練し、目的に応
じ所定の大きさ、形状(粒状、カプセル状、球状など)
に成形する。水は微粒子を所定の形状を保持することが
できる必要量添加する。成形物は、好ましくは自然乾燥
あるいは熱などにより強制乾燥した後、強度及び破壊性
などの点から、電気炉、重油炉などで好ましくは500
〜1100℃、特に好ましくは600〜900℃で所定
時間(例えば50〜70分間)焼成する。焼成により形
成物は一部溶解して、多孔性の焼結体となる。得られる
焼結体は、通常、通気度25〜200、気孔率25〜4
5%、圧縮強さ(破壊強度)は600℃で焼成したもの
5〜10kg、600〜900℃で焼成したもの20k
g以上の強度の高い多孔質焼結体である。
In the production of the porous sintered body of the present invention, the above dust fine particles are first mixed with water and kneaded to have a predetermined size and shape (granular, capsule-like, spherical, etc.) according to the purpose.
Mold into Water is added in the required amount of fine particles capable of maintaining a predetermined shape. The molded product is preferably dried in an electric furnace, a heavy oil furnace, etc., preferably 500 from the viewpoint of strength and destructiveness after being dried naturally or forcedly dried by heat.
˜1100 ° C., particularly preferably 600 to 900 ° C. for a predetermined time (for example, 50 to 70 minutes). A part of the formed product is melted by the firing to become a porous sintered body. The obtained sintered body usually has an air permeability of 25 to 200 and a porosity of 25 to 4
5%, compressive strength (breaking strength) 5 to 10 kg fired at 600 ° C, 20k fired at 600 to 900 ° C
It is a porous sintered body having a high strength of g or more.

【0015】鋳鉄用溶解炉から集塵したダストとかさ比
重0.5以下の焼結体原料とを使用する本発明の水浮揚
性の多孔質焼結体も、前記と同様にして製造することが
できる。
The water-buoyant porous sintered body of the present invention using the dust collected from the melting furnace for cast iron and the raw material for the sintered body having a bulk specific gravity of 0.5 or less can be produced in the same manner as described above. You can

【0016】また、本発明の他の多孔質焼結体は、所望
の性質を持った焼結体に、前記のダスト微粒子に水を加
えて混練したペーストを付着させて成形し、この成形物
を好ましくは自然乾燥あるいは強制乾燥したのち焼成し
て製造することができる。特に焼結体として水浮揚性の
焼結体を使用して、これに前記ペーストを付着させて成
形し、好ましくは乾燥して焼成することにより、本発明
の水浮揚性の多孔質焼結体を製造することができ、これ
は水に浮くので、水の表面に浮揚している油などの汚染
物の浄化に特に有効である。
Another porous sintered body of the present invention is formed by adhering a paste obtained by adding water to the dust particles and kneading the same to a sintered body having a desired property. Can be preferably dried by natural drying or forced drying and then calcined. In particular, a water-buoyant porous sintered body of the present invention is used by using a water-buoyant sintered body as the sintered body, adhering the paste to the molded body, molding, and preferably drying and firing. Since it can be produced, it floats on water, and is particularly effective for cleaning contaminants such as oil floating on the surface of water.

【0017】前記多孔質焼結体からなる本発明の水質浄
化材は、水槽、池、沼、湖、河川などに単に投入して日
光を当てるだけでも、藻類、農薬(除草剤など)、殺菌
剤、鉱油、水溶性樹脂などの有機物や、肥料などの無機
物などを光分解して水質を改善することができるが、更
に、水流を生じさせたり、あるいは水を循環させて水質
浄化材に更に接触しやすくさせることにより、有機物や
無機物などを吸着して水質浄化に効率的である。水質浄
化材の使用量は浄化する水の水質により著しく異なる
が、使用量が多ければ多いほどBOD(生物化学的酸素
要求量)、COD(化学的酸素要求量)、浮遊物量、色
度、濁度などを改善することができる。
The water purification material of the present invention comprising the above-mentioned porous sintered body can be algae, pesticides (herbicides, etc.), sterilized by simply putting it in a water tank, pond, swamp, lake, river or the like and exposing it to sunlight. Organic substances such as agents, mineral oil and water-soluble resins, and inorganic substances such as fertilizers can be photolyzed to improve water quality, but further, water flow is generated or water is circulated to further improve the water purification material. By making it easy to contact, it is effective for water purification by adsorbing organic substances and inorganic substances. The amount of water purification agent used varies significantly depending on the quality of the water to be purified, but the higher the amount used, the higher the BOD (biochemical oxygen demand), COD (chemical oxygen demand), suspended solids, chromaticity, and turbidity. The degree etc. can be improved.

【0018】[0018]

【実施例】以下、実施例により本発明を更に詳細に説明
する。なお、実施例及び比較例において、「%」は原則
として「重量%」を意味する。実施例1 多孔質焼結体の製造とその特性 鋳鉄溶解用低周波炉の集塵ダスト(粒径:10〜30μ
m、成分:MgO 2.615%、Al23 0.1
33%、SiO2 0.828%、P25 0.009
%、SO3 0.296%、Cl 1.137%、K2
O 0.045%、CaO 0.048%、Cr23
0.045%、MnO 0.264%、Fe23
8.489%、ZnO 85.656%、PbO 0.
349%、Ac 0.086%)1000gに対し、水
を200mlの割合で加えて、ニーダーで均一に混練し
た。次いで、スクリュー式の押し出し機で混練物を押し
出し、造粒機で平均粒径1.0〜1.5cmのほぼ球状
体に成形した。この成形物を常温で一昼夜乾燥し、更に
電気炉中で900℃で60分間焼成して、本発明の多孔
質焼結体を製造した。得られた多孔質焼結体の粒子構造
(多孔質構造)の顕微鏡写真(8倍拡大写真)を図1
に、電子顕微鏡写真(EPMA、70倍拡大写真)を図
2に示す。
The present invention will be described in more detail with reference to the following examples. In the examples and comparative examples, “%” means “% by weight” in principle. Example 1 Production of porous sintered body and its characteristics Dust collection dust of low frequency furnace for melting cast iron (particle size: 10 to 30 μm)
m, component: MgO 2.615%, Al 2 O 3 0.1
33%, SiO 2 0.828%, P 2 O 5 0.009
%, SO 3 0.296%, Cl 1.137%, K 2
O 0.045%, CaO 0.048%, Cr 2 O 3
0.045%, MnO 0.264%, Fe 2 O 3
8.489%, ZnO 85.656%, PbO 0.
349%, Ac 0.086%) 1000 g, water was added at a ratio of 200 ml, and the mixture was kneaded uniformly with a kneader. Next, the kneaded product was extruded with a screw type extruder and molded with a granulator into a substantially spherical body having an average particle size of 1.0 to 1.5 cm. The molded product was dried at room temperature for a whole day and night, and further baked in an electric furnace at 900 ° C. for 60 minutes to produce the porous sintered body of the present invention. A micrograph (8 times enlarged photograph) of the particle structure (porous structure) of the obtained porous sintered body is shown in FIG.
2 shows an electron micrograph (EPMA, 70 × magnified photograph).

【0019】得られた多孔質焼結体の特性を以下に示
す。 かさ比重:0.85 pH:7 通気度:150 気孔率:45(容積)% 圧縮強さ(破壊強度):20kg 水分:0.02%
The characteristics of the obtained porous sintered body are shown below. Bulk specific gravity: 0.85 pH: 7 Air permeability: 150 Porosity: 45 (volume)% Compressive strength (breaking strength): 20 kg Moisture: 0.02%

【0020】用水の浄化 自社内用水(地下水及び工業用水を主体としたもの)か
ら採取した水8リットルと前記多孔質焼結体1000g
を200cm×200cm×50cmの水槽に入れ、水
温10〜25℃にて、15Wの紫外線蛍光ランプを水面
の約5cm上方から24時間照射した。紫外線光の照射
前と後における用水の透視度をJIS−K0102の方
法によって測定したところ、それぞれ15cmと100
cmであった。なお、前記水のみを水温10〜25℃で
24時間放置した後の透視度は10cmであった。ま
た、紫外線照射後の用水中の亜鉛溶出量は、0.03m
g/リットルであった。
Purification of water 8 liters of water taken from in-house water (mainly groundwater and industrial water) and 1000 g of the porous sintered body
Was placed in a 200 cm × 200 cm × 50 cm water tank, and a 15 W ultraviolet fluorescent lamp was irradiated from about 5 cm above the water surface for 24 hours at a water temperature of 10 to 25 ° C. The transparency of the water before and after the irradiation with the ultraviolet light was measured by the method of JIS-K0102, and was 15 cm and 100, respectively.
cm. The transparency after leaving the above water alone at a water temperature of 10 to 25 ° C. for 24 hours was 10 cm. In addition, the zinc elution amount in the water after UV irradiation is 0.03 m
g / liter.

【0021】実施例2 水浮揚性の多孔質焼結体の製造 実施例1におけるのと同じ鋳鉄溶解用低周波炉の集塵ダ
スト1000gに対し、シリカ、アルミナを主成分とす
るかさ比重0.07〜0.5、平均粒径37μm〜1.
6mmの発泡粒子(株式会社シラックスウ製Sila
x)を1000gと水を200mlの割合で加え、実施
例1と同様にして平均粒径1.0〜1.5cmのほぼ球
状体に成形した。この成形物を常温で一昼夜乾燥し、更
に電気炉中で850℃で60分間焼成して、本発明の水
浮揚性の多孔質焼結体を製造した。得られた水浮揚性の
多孔質焼結体の粒子構造(多孔質構造)の顕微鏡写真
(8倍拡大写真)を図3に、電子顕微鏡写真(EPM
A、280倍拡大写真)を図4に示す。
Example 2 Production of Water Floatable Porous Sintered Body With respect to 1000 g of dust collected in the same low frequency furnace for melting cast iron as in Example 1, a bulk specific gravity of silica and alumina as main components was 0. 07-0.5, average particle size 37 μm-1.
6 mm foamed particles (Sila Sil Ltd. Sila
x) was added at a ratio of 1000 g and water at a ratio of 200 ml to form a substantially spherical body having an average particle diameter of 1.0 to 1.5 cm in the same manner as in Example 1. This molded product was dried at room temperature for a whole day and night, and further baked in an electric furnace at 850 ° C. for 60 minutes to produce the water-floating porous sintered body of the present invention. The microscopic photograph (8 times enlarged photograph) of the particle structure (porous structure) of the obtained water-floating porous sintered body is shown in FIG.
A, 280 times enlarged photograph) is shown in FIG.

【0022】得られた水浮揚性の多孔質焼結体の特性を
以下に示す。 かさ比重:0.60 pH:7 通気度:180 気孔率:40(容積)% 圧縮強さ(破壊強度):15kg 水分:0.02%
The characteristics of the obtained water-floating porous sintered body are shown below. Bulk specific gravity: 0.60 pH: 7 Air permeability: 180 Porosity: 40 (volume)% Compressive strength (breaking strength): 15 kg Moisture: 0.02%

【0023】切削油含有廃水の浄化 水溶性切削油(鉱油50〜80%、油脂及び脂肪酸0〜
30%、極圧添加剤0〜30%、界面活性剤15〜35
%、アルカノールアミン及び無機アルカリ0〜5%、有
機インヒビター0〜5%、防腐剤0〜2%、非鉄金属防
食剤0〜1%、消泡剤0〜1%、カストロール株式会社
製EP−690)を11.32Brix%(蔗糖を水に
溶解した時の重量%)含有する廃水8リットルと前記の
水浮揚性の多孔質焼結体150gを200cm×200
cm×50cmの水槽に入れ、水温約15℃にて、太陽
光に1日間そして更に2日間(日照)曝した。太陽光照
射1日後及び3日後の廃水の屈折率を測定し、これから
Brix%を求めたところ、それぞれ1.98Brix
%及び1.67Brix%であった。また、紫外線照射
後の廃水中の亜鉛溶出量は、0.01mg/リットルで
あった。
Purification of waste water containing cutting oil Water-soluble cutting oil (mineral oil 50 to 80%, fats and oils and fatty acids 0 to
30%, extreme pressure additive 0-30%, surfactant 15-35
%, Alkanolamine and inorganic alkali 0-5%, organic inhibitor 0-5%, preservative 0-2%, non-ferrous metal anticorrosive 0-1%, defoamer 0-1%, Castrol Co., Ltd. EP-690. ) Of 11.32 Brix% (weight% when sucrose is dissolved in water) and 8 liters of waste water and 150 g of the above water-floating porous sintered body are 200 cm × 200.
The sample was placed in a cm × 50 cm water tank, and exposed to sunlight at a water temperature of about 15 ° C. for 1 day and another 2 days (sunshine). The refractive index of the wastewater was measured 1 day and 3 days after sunlight irradiation, and the Brix% was calculated from the refractive index.
% And 1.67 Brix%. Further, the amount of zinc eluted in the waste water after irradiation with ultraviolet rays was 0.01 mg / liter.

【0024】比較例1及び2 切削油含有廃水の浄化 水溶性切削油(カストロール株式会社製EP−690)
を11.32Brix%含有する前記廃水8リットルと
酸化チタン粒子(3メッシュ)又は酸化亜鉛粒子(3メ
ッシュ)150gを200cm×200cm×50cm
の水槽に入れ、水温約13℃にて、太陽光に1日間そし
て更に2日間(日照)曝した。太陽光照射1日後及び3
日後の廃水の屈折率を測定し、これからBrix%を求
めたところ、次の表1のようであった。
Comparative Examples 1 and 2 Purification of Waste Water Containing Cutting Oil Water-soluble cutting oil (EP-690 manufactured by Castrol Co., Ltd.)
20 liters of the waste water containing 11.32 Brix% and 150 g of titanium oxide particles (3 mesh) or zinc oxide particles (3 mesh) are 200 cm × 200 cm × 50 cm.
, And exposed to sunlight at a water temperature of about 13 ° C. for 1 day and a further 2 days (sunshine). 1 day after solar irradiation and 3
The refractive index of the wastewater after the day was measured, and the Brix% was calculated from this, and the results are shown in Table 1 below.

【0025】[0025]

【表1】 [Table 1]

【0026】実施例3 水浮揚性の多孔質焼結体の製造 実施例1におけるのと同じ鋳鉄溶解用低周波炉の集塵ダ
スト1000gに対し、水を200mlの割合で加え、
ニーダーで均一に混練して、ペーストを調製した。一
方、シリカ、アルミナを主成分とするかさ比重0.07
〜0.5、平均粒径37μm〜1.6mmの発泡粒子
(株式会社シラックスウ製Silax)1000gに対
し、水200mlとベントナイト100gの割合で加え
て、ニーダーで均一に混練した。次いで、スクリュー式
の押し出し機で混練物を押し出し、造粒機で平均粒径約
1.0cmのほぼ球状体に成形した。この成形物を常温
で一昼夜乾燥し、更に電気炉中で1000℃で60分間
焼成して、かさ比重約0.55の球状の水浮揚性焼結体
を製造した。この水浮揚性の焼結体1000gに対し、
前記ペーストを100gの割合で混合して球状体の表面
にペーストを付着させ、常温で一昼夜乾燥し、更に電気
炉で900℃で60分間焼成して、水浮揚性の多孔質焼
結体を製造した。
Example 3 Production of Water Floatable Porous Sintered Body Water was added at a rate of 200 ml to 1000 g of dust collecting dust of the same low frequency furnace for melting cast iron as in Example 1.
A paste was prepared by uniformly kneading with a kneader. On the other hand, the bulk specific gravity of silica and alumina is 0.07
To 0.5 g, and foamed particles having an average particle diameter of 37 μm to 1.6 mm (Silux, manufactured by Shirasu Co., Ltd.) to 1000 g, 200 ml of water and 100 g of bentonite were added at a ratio and kneaded uniformly with a kneader. Then, the kneaded product was extruded by a screw type extruder and molded into a substantially spherical body having an average particle size of about 1.0 cm by a granulator. The molded product was dried at room temperature for a whole day and night, and further fired at 1000 ° C. for 60 minutes in an electric furnace to produce a spherical water-floating sintered body having a bulk specific gravity of about 0.55. For 1000 g of this water floatable sintered body,
The paste was mixed at a ratio of 100 g to adhere the paste to the surface of the spherical body, dried at room temperature for a whole day and night, and further baked in an electric furnace at 900 ° C. for 60 minutes to produce a water-floating porous sintered body. did.

【0027】得られた水浮揚性の多孔質焼結体の特性を
以下に示す。 かさ比重:0.60 pH:7 通気度:140 気孔率:40(容積)% 圧縮強さ(破壊強度):15kg 水分:0.02%
The characteristics of the obtained water-floating porous sintered body are shown below. Bulk specific gravity: 0.60 pH: 7 Air permeability: 140 Porosity: 40 (volume)% Compressive strength (breaking strength): 15 kg Moisture: 0.02%

【0028】フェノール樹脂含有廃水の浄化 鋳造用砂型を硬化させるために使用するアルカリ性フェ
ノール樹脂を固形分として1.2%含有するpH12の
廃水3リットルと前記の水浮揚性の多孔質焼結体150
0gを直径10cm×高さ50cmのアクリル樹脂製透
明円筒に入れ、水温10〜25℃にて、昼間は太陽光そ
して夜間は15Wの紫外線蛍光ランプに約5cm離れた
ところから5日間曝した。5日間照射後の廃水のpH測
定及びフェノール樹脂とホルムアルデヒドのガスクロマ
トグラフィー分析を行ったところ、pHは7.51であ
り、フェノール樹脂とホルムアルデヒドの残存量は共に
0.0002%以下であった。また、紫外線照射後の廃
水中の亜鉛溶出量は、0.01mg/リットルであっ
た。
Purification of wastewater containing phenolic resin 3 liters of wastewater of pH 12 containing 1.2% as a solid content of an alkaline phenolic resin used for hardening the sand mold for casting, and the above water-floating porous sintered body 150.
0 g was placed in a transparent cylinder made of acrylic resin having a diameter of 10 cm and a height of 50 cm, and exposed to sunlight at daytime and sunlight at 15 ° C for 5 days and an ultraviolet fluorescent lamp of 15 W at night for about 5 cm. When pH of the wastewater after irradiation for 5 days and gas chromatography analysis of the phenol resin and formaldehyde were carried out, the pH was 7.51 and the residual amounts of the phenol resin and formaldehyde were both 0.0002% or less. Further, the amount of zinc eluted in the waste water after irradiation with ultraviolet rays was 0.01 mg / liter.

【0029】[0029]

【発明の効果】以上説明した通り、本発明により、気孔
が均一に分布しており、強度及び通気性に優れ、長期間
にわたって有機物などを吸着し光分解しうる焼結体、並
びにこれからなる水質浄化材を提供することが可能とな
った。また本発明においては、鋳鉄原料を溶解する炉か
ら発生し少なくとも酸化亜鉛を含有する無機酸化物など
の混合物ダストを使用しているので、廃棄処分すべきダ
ストの発生量を減らすことができ、環境保全にも貢献す
ることができる。更に、本発明の多孔質焼結体は、水へ
の亜鉛の溶出量が極めて低いので、法定水質基準(亜鉛
溶出量1.0mg以下)を充分満たしている。
As described above, according to the present invention, pores are evenly distributed, strength and air permeability are excellent, and a sintered body capable of adsorbing and photodecomposing an organic substance and the like for a long period of time, and a water quality comprising the same. It has become possible to provide purification materials. Further, in the present invention, since a mixture dust such as an inorganic oxide containing at least zinc oxide generated from a furnace that melts a cast iron raw material is used, it is possible to reduce the amount of dust to be disposed of, and to reduce the environment. It can also contribute to conservation. Further, the porous sintered body of the present invention has an extremely low elution amount of zinc in water, and therefore sufficiently satisfies the legal water quality standard (zinc elution amount of 1.0 mg or less).

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

【図1】本発明の一実施例の多孔質焼結体の粒子構造の
顕微鏡写真である。
FIG. 1 is a micrograph of a particle structure of a porous sintered body according to an example of the present invention.

【図2】本発明の一実施例の多孔質焼結体の粒子構造の
電子顕微鏡写真である。
FIG. 2 is an electron micrograph of a particle structure of a porous sintered body according to an example of the present invention.

【図3】本発明の一実施例の水浮揚性の多孔質焼結体の
粒子構造の顕微鏡写真である。
FIG. 3 is a micrograph of a particle structure of a water-buoyant porous sintered body according to an example of the present invention.

【図4】本発明の一実施例の水浮揚性の多孔質焼結体の
粒子構造の電子顕微鏡写真である。
FIG. 4 is an electron micrograph showing a particle structure of a water-floating porous sintered body according to an example of the present invention.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 鋳鉄用溶解炉から蒸発し集塵された少な
くとも酸化亜鉛を含有する無機酸化物の混合物ダストに
水を加えて混練し成形した成形物を焼成して得られる多
孔質焼結体。
1. A porous sintered body obtained by adding water to a mixture dust of an inorganic oxide containing at least zinc oxide, which has been evaporated and dust-collected from a melting furnace for cast iron, and kneaded the mixture to form a molded product. .
【請求項2】 鋳鉄用溶解炉から蒸発し集塵された少な
くとも酸化亜鉛を含有する無機酸化物の混合物ダストに
かさ比重0.5以下の焼結体形成原料と水を加えて混練
し成形した成形物を焼成して得られる水浮揚性の多孔質
焼結体。
2. A raw material for forming a sintered body having a bulk specific gravity of 0.5 or less and water are added to a mixture dust of an inorganic oxide containing at least zinc oxide, which is evaporated and collected from a melting furnace for cast iron, and kneaded and molded. A water-floating porous sintered body obtained by firing a molded product.
【請求項3】 鋳鉄用溶解炉から蒸発し集塵された少な
くとも酸化亜鉛を含有する無機酸化物の混合物ダストに
水を加えて混練したペーストを、焼結体に付着させて成
形した成形物を焼成して得られる、多孔質焼結体。
3. A molded product obtained by adhering to a sintered body a paste prepared by admixing water with a mixture dust of a mixture of inorganic oxides containing at least zinc oxide, which is evaporated and collected from a melting furnace for cast iron. A porous sintered body obtained by firing.
【請求項4】 鋳鉄用溶解炉から蒸発し集塵された少な
くとも酸化亜鉛を含有する無機酸化物の混合物ダストに
水を加えて混練したペーストを、水浮揚性の焼結体に付
着させて成形した成形物を焼成して得られる、水浮揚性
の多孔質焼結体。
4. A paste obtained by adding water to a mixture dust of a mixture of inorganic oxides containing at least zinc oxide, which has been evaporated and dust-collected from a melting furnace for cast iron, is attached to a water-buoyant sintered body to be molded. A water-floating porous sintered body obtained by firing the molded product.
【請求項5】 請求項1〜4のいずれか一項に記載の多
孔質焼結体において、成形体を焼成する前に乾燥するこ
とを特徴とする前記多孔質焼結体。
5. The porous sintered body according to any one of claims 1 to 4, wherein the molded body is dried before firing.
【請求項6】 請求項1、2、3、4又は5に記載の多
孔質焼結体からなることを特徴とする水質浄化材。
6. A water purification material comprising the porous sintered body according to claim 1, 2, 3, 4 or 5.
JP8114211A 1996-04-11 1996-04-11 Porous sintered product, and water-purifying material comprising the same Pending JPH09278557A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8114211A JPH09278557A (en) 1996-04-11 1996-04-11 Porous sintered product, and water-purifying material comprising the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8114211A JPH09278557A (en) 1996-04-11 1996-04-11 Porous sintered product, and water-purifying material comprising the same

Publications (1)

Publication Number Publication Date
JPH09278557A true JPH09278557A (en) 1997-10-28

Family

ID=14632002

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8114211A Pending JPH09278557A (en) 1996-04-11 1996-04-11 Porous sintered product, and water-purifying material comprising the same

Country Status (1)

Country Link
JP (1) JPH09278557A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020072856A (en) * 2001-03-13 2002-09-19 주식회사 디.아이 A sinter-ceramic and manufacturing method for water purification
KR20020072855A (en) * 2001-03-13 2002-09-19 주식회사 디.아이 A sinter-ceramic and its manufacturing method for phosphorus decomposition

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020072856A (en) * 2001-03-13 2002-09-19 주식회사 디.아이 A sinter-ceramic and manufacturing method for water purification
KR20020072855A (en) * 2001-03-13 2002-09-19 주식회사 디.아이 A sinter-ceramic and its manufacturing method for phosphorus decomposition

Similar Documents

Publication Publication Date Title
JP5658270B2 (en) Manufacturing method of lightweight construction materials using sludge waste
US20070104949A1 (en) Granulate made of sintered or cellular broken glass
KR101216411B1 (en) The method of preparing lightweight-aggregate for concrete products using sludge of dyeing-waste water
KR100305091B1 (en) Ceramic Zeolite Purifier Using Fine Spray from Lime and Casting Sand Mold and Its Manufacturing Method
JPH09278557A (en) Porous sintered product, and water-purifying material comprising the same
KR101215067B1 (en) Method for Manufacturing Lightweight Construction Material Using Waste from Asbestos
KR100358888B1 (en) The multi-pore ceramic using the slag of the by-products from iron-steel-industry and waste casting sand dust and method of making the same
CN101318737B (en) Baking-free stephanoporate water slag filtering material and preparation method thereof
EP3140055B1 (en) A method of disposal and utilisation of dusts from an incineration installation and sludge from flotation enrichment of non-ferrous metal ores containing hazardous substances in the process of light aggregate production for the construction industry
Su et al. Remediation treatment and resource utilization trends of electrolytic manganese residue
JPH03177330A (en) Silicate glass building material
JP2000117020A (en) Contact purifying material and its production
JP4822369B2 (en) Water quality improving treatment agent and method for producing the same
JP2002361266A (en) Chemicals for water treatment and method for using the same
JP2001162288A (en) Dephosphorizing material
KR102628977B1 (en) Method of Preparing Porous Ceramic Filter Media for Reducing Non-Point Pollution by Recycling Disaster Waste
KR102136043B1 (en) Manufacturing method of large ceramic panel for artificial reef using purified water sludge
KR101400851B1 (en) The method of preparing lightweight-aggregate for concrete products using sludge of dyeing-waste water
JP2009280439A (en) Cement molded body, cement composition and method for producing cement molded body
JP4633604B2 (en) Adsorbent production method, adsorbent, adsorbent granule, and adsorbent granule production method
JP3382914B2 (en) Deodorizing filter material and method for producing the same
KR20240067054A (en) Method of Preparing Porous Ceramic Filter Media for Reducing Non-Point Pollution by Recycling Disaster Waste
KR20240067053A (en) Method of Preparing Porous Ceramic Filter Media for Reducing Non-Point Pollution by Recycling Disaster Waste
CN115259343A (en) Simple microbial carrier and preparation method thereof
WO2003010108A2 (en) Method for rendering filter and fly ash inert