JP3360974B2 - Adsorbed oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. and method for producing the same - Google Patents
Adsorbed oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. and method for producing the sameInfo
- Publication number
- JP3360974B2 JP3360974B2 JP17285095A JP17285095A JP3360974B2 JP 3360974 B2 JP3360974 B2 JP 3360974B2 JP 17285095 A JP17285095 A JP 17285095A JP 17285095 A JP17285095 A JP 17285095A JP 3360974 B2 JP3360974 B2 JP 3360974B2
- Authority
- JP
- Japan
- Prior art keywords
- ash
- incineration
- aggregate
- fly ash
- sludge
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
- Processing Of Solid Wastes (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Catalysts (AREA)
Description
【産業上の利用分野】本発明は、人工骨材・軽量骨材等
として用いる吸着酸化触媒材及びその製造方法に関する
ものであり、詳しくは、特に灰塵(一般ゴミの焼却灰や
焼却飛灰)の低コスト処理が可能であるとともに灰塵の
無害化が可能であり環境浄化機能をも備えた人工骨材・
軽量骨材等として用いる吸着酸化触媒材及びその製造方
法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate and the like, and a method for producing the same, and more specifically, ash dust (incineration ash of general waste and incineration fly ash). The artificial aggregate that can be processed at low cost and is also harmless to ash dust and has an environmental purification function.
The present invention relates to an adsorption oxidation catalyst material used as a lightweight aggregate or the like and a method for producing the same.
【従来の技術】従来、焼却灰、飛灰等の灰塵の処理方法
として、最終処分場において地中に埋め立てたり、コン
クリートに混ぜて固化したり、更には樹脂を用いて硬化
させたり、高温の炉中で溶かす溶融炉法等が実施され又
は検討されているのが実情である。2. Description of the Related Art Conventionally, as a method of treating ash dust such as incineration ash and fly ash, it is buried in the ground at the final disposal site, mixed with concrete and solidified, and further cured with a resin, The fact is that a melting furnace method for melting in a furnace has been implemented or is being studied.
【発明が解決しようとする課題】しかしながら、灰塵を
最終処分場において地中に埋め立ることは、過去に行っ
てきた同様な埋め立て処理による地下水の汚染や環境汚
染が顕在しつつあることに鑑み、近々、法規制により不
可能になるという状況にある。また、灰塵をコンクリー
トに混ぜて固化することは、酸性雨や酸度の高い水など
でコンクリートが溶解することから灰塵に含まれる重金
属の溶出が懸念される。更に、灰塵を樹脂を用いて硬化
させることは、樹脂層の亀裂、劣化、崩壊等によりコン
クリート固化の場合と同様に溶出汚染が懸念される。ま
た、灰塵を高温の炉中で溶かす溶融炉法の場合には、頑
丈で高価な溶融炉を建造し、且つ、焼却灰、飛灰の溶解
に摂氏1400度以上の高温で、しかも、多大な熱エネ
ルギーを必要とすることから、その処理コストの高騰を
招くとともに建設費、運転維持管理費が莫大になってし
まうという問題がある。そこで、本発明は、このような
従来の実情に鑑み開発されたものであり、その目的とす
るところは、灰塵の低コスト処理が可能であるとともに
灰塵の無害化が可能であり環境浄化機能をも備えた新規
な人工骨材・軽量骨材等として用いる吸着酸化触媒材及
びその製造方法を提供することにある。However, landfilling ash dust into the ground at the final disposal site is due to the fact that groundwater pollution and environmental pollution due to similar landfill treatment that has been performed in the past are becoming apparent. , It is in a situation that it will soon be impossible due to legal regulations. Further, when ash dust is mixed with concrete to solidify it, there is a concern that heavy metal contained in the ash dust may be eluted since the concrete is dissolved by acid rain or water having high acidity. Further, when ash dust is cured with a resin, elution contamination may occur due to cracking, deterioration, collapse, etc. of the resin layer as in the case of solidification of concrete. Further, in the case of the melting furnace method in which ash dust is melted in a high temperature furnace, a sturdy and expensive melting furnace is constructed, and the melting of incineration ash and fly ash is performed at a high temperature of 1400 degrees Celsius or more, and a large amount. Since heat energy is required, there is a problem that the processing cost thereof rises and the construction cost and operation and maintenance cost become enormous. Therefore, the present invention has been developed in view of such conventional circumstances, the purpose is to be able to low-cost treatment of ash dust and detoxification of ash dust, environmental purification function An object of the present invention is to provide an adsorption oxidation catalyst material used as a novel artificial aggregate, a lightweight aggregate, etc., which is also provided, and a method for producing the same.
【課題を解決するための手段】請求項1記載の人工骨材
・軽量骨材等として用いる吸着酸化触媒材は、一般ゴミ
の焼却灰や焼却飛灰等の灰塵と、ベントナイト、ゼオラ
イト、ガラスカレット及び屎尿汚泥等の汚泥焼却灰から
なる原料とを、混練・造粒処理、焼結焼成処理、電磁波
の照射処理又はオゾン処理して塊状に形成したものであ
る。請求項2記載の人工骨材・軽量骨材等として用いる
吸着酸化触媒材は、一般ゴミの焼却灰や焼却飛灰等の灰
塵と、ベントナイト、ゼオライト、ガラスカレット及び
屎尿汚泥等の汚泥焼却飛灰からなる原料とを、混練・造
粒処理、焼結焼成処理、電磁波の照射処理又はオゾン処
理して塊状に形成したものである。請求項3記載の人工
骨材・軽量骨材等として用いる吸着酸化触媒材は、一般
ゴミの焼却灰や焼却飛灰等に代替して又は一般ゴミの焼
却灰や焼却飛灰等に混在した汚泥焼却灰又は汚泥焼却飛
灰、例えば屎尿汚泥焼却灰又は屎尿汚泥焼却飛灰の灰塵
と、ベントナイト、ゼオライト及びガラスカレットから
なる原料とを、混練・造粒処理、焼結焼成処理、電磁波
の照射処理又はオゾン処理して塊状に形成したものであ
る。請求項4記載の人工骨材・軽量骨材等として用いる
吸着酸化触媒材は、前記請求項1乃至3のいずれか1項
に記載の人工骨材・軽量骨材等として用いる吸着酸化触
媒材を、直径5乃至15mm程度の球状に形成したもの
である。請求項5記載の人工骨材・軽量骨材等として用
いる吸着酸化触媒材の製造方法は、一般ゴミの焼却灰や
焼却飛灰等の灰塵を篩にかけて夾雑物を除去した後、加
熱乾燥し、磁力選別手段により鉄等の金属類を除去した
前記灰塵と、原料としてのベントナイト、ゼオライト、
ガラスカレット及び屎尿汚泥等の汚泥焼却灰とを混合し
て粉砕し、加湿しながらこれらを混練して造粒し素材と
する工程と,前記造粒した素材に対し、摂氏250度乃
至500℃前後の温度で予備乾燥を行った後、摂氏60
0乃至950度の温度範囲内で素材の焼結焼成を行う工
程と,前記焼結焼成処理した素材を摂氏200度前後ま
で冷却した後、この素材に対する電磁波の照射処理又は
オゾン雰囲気を通過させるオゾン処理工程とからなるも
のである。請求項6記載の人工骨材・軽量骨材等として
用いる吸着酸化触媒材の製造方法は、一般ゴミの焼却灰
や焼却飛灰等の灰塵を篩にかけて夾雑物を除去した後、
加熱乾燥し、磁力選別手段により鉄等の金属類を除去し
た前記灰塵と、原料としてのベントナイト、ゼオライ
ト、ガラスカレット及び屎尿汚泥等の汚泥焼却飛灰とを
混合して粉砕し、加湿しながらこれらを混練して造粒し
素材とする工程と,前記造粒した素材に対し、摂氏25
0度乃至500℃前後の温度で予備乾燥を行った後、摂
氏600乃至950度の温度範囲内で素材の焼結焼成を
行う工程と,前記焼結焼成処理した素材を摂氏200度
前後まで冷却した後、この素材に対する電磁波の照射処
理又はオゾン雰囲気を通過させるオゾン処理工程とから
なるものである。請求項7記載の人工骨材・軽量骨材等
として用いる吸着酸化触媒材の製造方法は、一般ゴミの
焼却灰や焼却飛灰等に代替して又は一般ゴミの焼却灰や
焼却飛灰等に混在した汚泥焼却灰又は汚泥焼却飛灰、例
えば屎尿汚泥焼却灰又は屎尿汚泥焼却飛灰の灰塵を篩に
かけて夾雑物を除去した後、加熱乾燥し、磁力選別手段
により鉄等の金属類を除去した前記灰塵と、原料として
のベントナイト、ゼオライト及びガラスカレットとを混
合して粉砕し、加湿しながらこれらを混練して造粒し素
材とする工程と,前記造粒した素材に対し、摂氏250
度乃至500℃前後の温度で予備乾燥を行った後、摂氏
600乃至950度の温度範囲内で素材の焼結焼成を行
う工程と,前記焼結焼成処理した素材を摂氏200度前
後まで冷却した後、この素材に対する電磁波の照射処理
又はオゾン雰囲気を通過させるオゾン処理工程とからな
るものである。The adsorption oxidation catalyst material used as an artificial aggregate or a lightweight aggregate according to claim 1 is ash dust such as incineration ash of general waste or incineration fly ash, bentonite, zeolite, glass cullet. And a raw material composed of sludge incineration ash such as human waste sludge, and kneaded / granulated, sintered / fired, irradiated with electromagnetic waves or treated with ozone to form a lump. The adsorptive oxidation catalyst material used as the artificial aggregate or lightweight aggregate according to claim 2 is ash dust such as incineration ash or incineration fly ash of general waste, and sludge incineration fly ash such as bentonite, zeolite, glass cullet and human waste sludge. And a raw material consisting of the above are kneaded / granulated, sintered and fired, irradiated with electromagnetic waves, or treated with ozone to form lumps. The adsorptive oxidation catalyst material used as the artificial aggregate or lightweight aggregate according to claim 3 is a sludge which is substituted for incineration ash or incineration fly ash of general waste or mixed in incineration ash or incineration fly ash of general waste. Incineration ash or sludge incineration fly ash, for example, ash dust of incinerator sludge incineration ash or incinerator sludge incinerator fly ash, and a raw material consisting of bentonite, zeolite and glass cullet, kneading, granulation treatment, sintering firing treatment, electromagnetic wave irradiation treatment Alternatively, it is formed into a lump by ozone treatment. The adsorptive oxidation catalyst material used as the artificial aggregate / light weight aggregate according to claim 4 is the adsorption oxidation catalyst material used as the artificial aggregate / light weight aggregate according to any one of claims 1 to 3. It has a spherical shape with a diameter of about 5 to 15 mm. The method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, etc. according to claim 5 is a method of sieving ash dust such as incineration ash or incineration fly ash of general refuse to remove impurities, and then heat drying. The ash dust from which metals such as iron have been removed by magnetic force selection means, and bentonite as a raw material, zeolite,
A step of mixing and crushing glass cullet and sludge incineration ash such as human waste sludge, kneading and granulating them while humidifying, and about 250 ° C to 500 ° C with respect to the granulated material After pre-drying at a temperature of 60 degrees Celsius
The step of sintering and firing the material within a temperature range of 0 to 950 degrees, and the step of cooling the sintered and fired material to around 200 degrees Celsius, and then irradiating the material with electromagnetic waves or passing ozone through the atmosphere. Processing steps. The method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, etc. according to claim 6 is a method in which ash dust such as incineration ash of general waste or incineration fly ash is sieved to remove impurities,
Heat-dried, the ash dust from which metals such as iron have been removed by magnetic separation means, and bentonite as a raw material, zeolite, glass cullet and sludge incineration fly ash such as human waste sludge are mixed and pulverized, and these are moisturized. The step of kneading and granulating to make a raw material,
After pre-drying at a temperature of 0 to 500 ° C., sintering and firing the material within a temperature range of 600 to 950 ° C., and cooling the sintered and fired material to around 200 ° C. After that, this material is subjected to an electromagnetic wave irradiation treatment or an ozone treatment step of passing the material through an ozone atmosphere. The method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, etc. according to claim 7 is as an alternative to incineration ash or incineration fly ash of general waste, or incineration ash or incineration fly ash of general waste. Sludge incineration ash or sludge incineration fly ash, for example, sewage sludge incineration ash or sewage in sludge incineration fly ash was sieved to remove impurities, then heat-dried, and metals such as iron were removed by magnetic separation means. A step of mixing the ash dust with bentonite, zeolite and glass cullet as raw materials and pulverizing them and kneading them while moisturizing to granulate them to obtain a raw material;
After pre-drying at a temperature of around 600 to 950 ° C., sintering and firing the material within a temperature range of 600 to 950 ° C., and cooling the sintered and fired material to around 200 ° C. Then, this material is subjected to an electromagnetic wave irradiation treatment or an ozone treatment step of passing the material through an ozone atmosphere.
【作用】請求項1、2記載の人工骨材・軽量骨材等とし
て用いる吸着酸化触媒材によれば、灰塵と、ベントナイ
ト、ゼオライト、ガラスカレット、汚泥焼却灰又は汚泥
焼却飛灰、例えば屎尿汚泥焼却灰又は屎尿汚泥焼却飛灰
からなる原料とを、混練・造粒処理、焼結焼成処理、電
磁波の照射処理又はオゾン処理して塊状に形成したもの
であるから、焼結焼成処理により、原料としてのベント
ナイト、ゼオライトの組成に物理的、化学的変化を生
じ、結晶水を除いた後の空洞に細孔を通じて灰塵が含有
している重金属類を吸着し担持する作用を著しく強化さ
れ、これにより、重金属類の溶出が無くなって無害化を
図れる。また、このような焼結焼成処理により、原料と
してのベントナイト、ゼオライトの組成に含まれている
アルミナ(Al 2 O 3 )の分子が変化し、これにより、人
工骨材・軽量骨材等として用いる吸着酸化触媒材によっ
て遠赤外線作用を発揮させることができる。更に電磁波
の照射を行うことで、又は、オゾン雰囲気を通過させる
オゾン処理によって、オゾンを前記ベントナイト、ゼオ
ライトの細孔に最大限包含でき、オゾンによる殺菌、脱
臭、除菌の各作用を発揮させることができ、且つ、製品
そのものの他、当該製品の周囲の重金属、悪臭分子成分
の吸着分解をも可能とする特性を持たせることもでき
る。請求項3記載に係る人工骨材・軽量骨材等として用
いる吸着酸化触媒材によれば、一般ゴミの焼却灰や焼却
飛灰等に代替して又は一般ゴミの焼却灰や焼却飛灰等に
混在した汚泥焼却灰又は汚泥焼却飛灰、例えば屎尿汚泥
焼却灰又は屎尿汚泥焼却飛灰の灰塵と、ベントナイト、
ゼオライト及びガラスカレットからなる原料とを、混練
・造粒処理、焼結焼成処理、電磁波の照射処理又はオゾ
ン処理して塊状に形成したものであることにより、前記
請求項1、2記載の人工骨材・軽量骨材等として用いる
吸着酸化触媒材と同様の作用を発揮できる。請求項4記
載に係る人工骨材・軽量骨材等として用いる吸着酸化触
媒材によれば、前記請求項1乃至3のいずれか1項に記
載の人工骨材・軽量骨材等として用いる吸着酸化触媒材
を、直径5乃至15mm程度の球状に形成したので、製
品として扱い易い形状となり、取扱いが容易となる。請
求項5、6、7記載に係る人工骨材・軽量骨材等として
用いる吸着酸化触媒材の製造方法によれば、前記従来の
ような溶融炉法の如く高温処理と比較し、省エネルギー
化、設備コストの低廉化を図れるとともに、低コストで
前記請求項1乃至4記載の人工骨材・軽量骨材等として
用いる吸着酸化触媒材を製造することができる。According to the adsorptive oxidation catalyst material used as the artificial aggregate or lightweight aggregate according to claims 1 and 2, ash dust, bentonite, zeolite, glass cullet, sludge incineration ash or sludge incineration fly ash, for example, human waste sludge. A raw material consisting of incinerated ash or incinerator sludge incineration fly ash is kneaded / granulated, sintered and fired, irradiated with electromagnetic waves or treated with ozone to form lumps. As a bentonite, a physical and chemical change occurs in the composition of the zeolite, and the action of adsorbing and carrying heavy metals contained in ash dust through the pores in the cavity after removing the water of crystallization is significantly enhanced, and , Elimination of heavy metals is eliminated, and harmless can be achieved. Further, by such a sintering and firing treatment, the molecules of bentonite as a raw material and alumina ( Al 2 O 3 ) contained in the composition of zeolite are changed, and as a result, they are used as artificial aggregates, lightweight aggregates, etc. The far-infrared effect can be exerted by the adsorption oxidation catalyst material. Further, by irradiating an electromagnetic wave, or by an ozone treatment of passing an ozone atmosphere, ozone can be contained in the bentonite and the pores of the zeolite to the maximum extent, and each effect of sterilization by ozone, deodorization, and sterilization can be exhibited. In addition to the product itself, it is also possible to provide the product with a property that enables adsorption and decomposition of heavy metals and malodorous molecular components around the product. According to the adsorptive oxidation catalyst material used as the artificial aggregate or the lightweight aggregate according to claim 3, the incineration ash of general waste, the incineration fly ash, or the like is used in place of the incineration ash or incineration fly ash of general waste. Mixed sludge incineration ash or sludge incineration fly ash, such as sewage of human waste sludge incineration ash or human sewage sludge incineration ash, and bentonite,
The artificial bone according to claim 1 or 2, wherein the raw material composed of zeolite and glass cullet is kneaded / granulated, sintered / sintered, irradiated with electromagnetic waves or treated with ozone to be formed into a lump. It can exhibit the same action as the adsorption oxidation catalyst material used as a material, lightweight aggregate, etc. According to the adsorptive oxidation catalyst material used as the artificial aggregate / lightweight aggregate according to claim 4, the adsorptive oxidation used as the artificial aggregate / lightweight aggregate according to any one of claims 1 to 3 Since the catalyst material is formed into a spherical shape having a diameter of about 5 to 15 mm, it has a shape that is easy to handle as a product, and handling is easy. According to the method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, etc. according to claims 5, 6, and 7, energy saving is achieved as compared with high temperature treatment as in the conventional melting furnace method. It is possible to reduce the equipment cost and to manufacture the adsorptive oxidation catalyst material used as the artificial aggregate, the lightweight aggregate, or the like according to any one of claims 1 to 4 at low cost.
【実施例】以下、本発明に係る人工骨材・軽量骨材等と
して用いる吸着酸化触媒材及びその製造方法の実施例を
詳細に説明する。図1に示す人工骨材・軽量骨材等とし
て用いる吸着酸化触媒材1は、塊状、例えば直径5乃至
15mm程度の球状に形成されている。この人工骨材・
軽量骨材等として用いる吸着酸化触媒材1は、一般ゴミ
の焼却灰や焼却飛灰等の灰塵2(図1において●状で示
す)と、原料としてのベントナイト3(図1において○
で示す)、ゼオライト4(図1において△で示す)、ガ
ラスカレット5(図1において□で示す)、汚泥焼却灰
又は汚泥焼却飛灰(図示せず)、例えば、屎尿汚泥焼却
灰又は屎尿汚泥焼却飛灰からなる原料とを、混合・微粉
砕・混練・造粒し、更に、焼結焼成処理及び電磁波の照
射又はオゾン処理を行って直径5乃至15mm程度の球
状に形成したものである。次に、上述した人工骨材・軽
量骨材等として用いる吸着酸化触媒材1の製造方法に係
る製造工程を図2を参照して詳細に説明する。図2に示
すように、先ず、一般ゴミの焼却灰や焼却飛灰等の灰塵
2を篩にかけて夾雑物を除去した後、加熱乾燥し、更
に、磁気作用を利用した磁力選別手段により鉄をはじめ
とする磁力に吸引される金属類を除去した灰塵2と、原
料としてのベントナイト3、ゼオライト4、ガラスカレ
ット5、汚泥焼却灰又は汚泥焼却飛灰、例えば、屎尿汚
泥焼却灰又は屎尿汚泥焼却飛灰とを混合して微粉砕し、
更に、加湿しながらこれらを混練し、所望の大きさ、例
えば直径5乃至15mm程度の球状に造粒し素材とす
る。上記混合、微粉砕工程や混練工程における加湿は、
必ずしもこれを必須のものとするものではない。この場
合、ベントナイト3とゼオライト4とは、灰塵2に対し
て、5乃至10重量%程度用いる場合、10乃至15重
量%程度用いる場合、15乃至20重量%程度用いる場
合を挙げることができる。上述のようにして造粒した素
材に対し、摂氏250乃至500度前後の温度で予備乾
燥を行った後、更に、摂氏600乃至950度の温度範
囲内で素材の焼結焼成を行う。この後、焼結焼成処理し
た素材を摂氏200度前後まで冷却した後、この素材に
対する電磁波の照射又はオゾン雰囲気を通過させるオゾ
ン処理を行い製品としての人工骨材・軽量骨材等として
用いる吸着酸化触媒材1を得る。原料としてのベントナ
イト3は、別名モンモリロライトと称され、食品添加物
として認められ、また、古くから医薬品原料としても用
いられている。このベントナイト2は含水アルミニウム
ケイ酸塩(粘土鉱物)の一種で理論組成はAl 2 O 3 ・4
SiO 2 ・nH 2 Oで示され、塩基置換量が極めて大きく
吸着性に優れている。このベントナイト3は、粉砕され
て用いられる。原料としてのゼオライト4は、結晶性ア
ルミノケイ酸塩の一種で、理論組成の代表例はNa 12 A
l 12 Si 12 O 48 ・27H 2 Oで示され、均一細孔径をも
ち、細孔を通じての吸着作用に優れている。このゼオラ
イト4も粉砕されて用いられる。本実施例で用いる原料
としてのガラスカレット5は、別名ガラス粉と称され粉
状である。原料としての汚泥焼却灰又は汚泥焼却飛灰
は、各種の汚泥を焼却した灰や飛灰を用いることができ
るが、屎尿汚泥焼却灰又は屎尿汚泥焼却飛灰を用いるこ
とが好ましい。上述した製造工程において、灰塵2と前
記各原料とを混練し5乃至15mm程度の球状に造粒す
るのは、その後の焼結焼成処理における均一化を図るこ
と、製品として扱い易い形状にすること等の理由によ
る。また、焼結焼成処理を行うのは、原料としてのベン
トナイト3、ゼオライト4を加熱してこれらが具備して
いる組成に物理的、化学的変化を与え、結晶水を除いた
後の空洞に細孔を通じて灰塵2が含有している重金属類
を吸着し担持する作用を著しく強化するためである。こ
の結果、この人工骨材・軽量骨材等として用いる吸着酸
化触媒材1を大量に埋め立てても灰塵2が含有している
重金属類の溶出がなく、この人工骨材・軽量骨材等とし
て用いる吸着酸化触媒材1を埋め立て材、軽量コンクリ
ート材、グランド整備材等々として積極的に使用する事
が可能となる。また、このような焼結焼成処理により、
原料としてのベントナイト3、ゼオライト4の組成に含
まれているアルミナ(Al 2 O 3 )の分子が変化し、遠赤
外線作用を発揮する。更に、摂氏600乃至950度の
温度範囲内で素材の焼結焼成を行うので、従来例に比
べ、省エネルギー化、設備コストの低廉化をも図れる。
前記本実施例において、原料として汚泥焼却灰又は汚泥
焼却飛灰、例えば、屎尿汚泥焼却灰又は屎尿汚泥焼却飛
灰を用いる理由は、造粒形成が一層円滑になることによ
る。更にまた、焼結焼成処理した素材を摂氏200度前
後まで冷却した後、この素材に対する電磁波の照射を行
うことで、又はオゾン雰囲気を通過させるオゾン処理に
よって、オゾンを前記ベントナイト3、ゼオライト4の
細孔に最大限包含でき、オゾンによる殺菌、脱臭、除菌
の各作用を発揮させることができ、且つ、製品そのもの
の他、当該製品の周囲の重金属、悪臭分子成分の吸着分
解をも可能とする特性を持たせることができる。また、
この人工骨材・軽量骨材等として用いる吸着酸化触媒材
1を悪環境に用いることで、環境改善の作用効果をも奏
する。以上詳述したように、本発明に係る人工骨材・軽
量骨材等として用いる吸着酸化触媒材及びその製造方法
によれば、重金属類の溶出が無くなって無害化を図るこ
とができ、遠赤外線作用、殺菌、脱臭、除菌の各作用、
重金属、悪臭分子成分の吸着分解作用をも発揮させるこ
とが可能になる吸着酸化触媒材を実現できるとともに、
摂氏600乃至950度の温度範囲内で素材の焼結焼成
を行うことができるので、この種の従来の処理手段に比
べ、低コスト処理、省エネルギー化、設備コストの低廉
化をも図ることができる。本発明は、上述した実施例に
限定されるものではなく、その要旨の範囲内で種々の変
形が可能である。例えば、前記人工骨材・軽量骨材等と
して用いる吸着酸化触媒材1は、球状とする他、楕円球
状、立方体状、直方体状等をはじめとした任意形状の塊
として実施可能である。EXAMPLES Examples of the adsorptive oxidation catalyst material used as the artificial aggregate, the lightweight aggregate and the like according to the present invention and the method for producing the same will be described in detail below. The adsorptive oxidation catalyst material 1 used as the artificial aggregate / light weight aggregate shown in FIG. 1 is formed in a lump shape, for example, a spherical shape having a diameter of about 5 to 15 mm. This artificial aggregate
The adsorptive oxidation catalyst material 1 used as a lightweight aggregate or the like includes ash dust 2 (indicated by a black circle in FIG. 1) such as incineration ash of general waste and incineration fly ash, and bentonite 3 as a raw material (○ in FIG. 1).
, Zeolite 4 (indicated by Δ in FIG. 1), glass cullet 5 (indicated by □ in FIG. 1), sludge incineration ash or sludge incineration fly ash (not shown), for example, human waste sludge incineration ash or human waste sludge. A raw material composed of incinerated fly ash is mixed, finely pulverized, kneaded, and granulated, and further subjected to sintering and firing treatment and irradiation of electromagnetic waves or ozone treatment to form a spherical shape having a diameter of about 5 to 15 mm. Next, the manufacturing process according to the manufacturing method of the adsorptive oxidation catalyst material 1 used as the above-mentioned artificial aggregate, lightweight aggregate, etc. will be described in detail with reference to FIG. As shown in FIG. 2, first, ash dust 2 such as incineration ash of general waste and incineration fly ash is sieved to remove impurities, and then heat-dried, and further, iron is started by a magnetic force selection means utilizing magnetic action. Ashes 2 from which metals that are attracted to the magnetic force are removed, and bentonite 3, zeolite 4, glass cullet 5, sludge incineration ash or sludge incineration fly ash as a raw material, for example, human waste sludge incineration ash or human sewage sludge incineration fly ash And finely pulverized,
Further, these are kneaded while being moistened, and granulated into a desired size, for example, a spherical shape having a diameter of about 5 to 15 mm, to obtain a raw material. Humidification in the above mixing, fine pulverization step and kneading step,
This is not necessarily mandatory. In this case, bentonite 3 and zeolite 4 may be used in an amount of about 5 to 10% by weight, about 10 to 15% by weight, or about 15 to 20% by weight, based on the ash dust 2. The material granulated as described above is pre-dried at a temperature of around 250 to 500 degrees Celsius and then sintered and fired within a temperature range of 600 to 950 degrees Celsius. After that, after the sintered and fired material is cooled to around 200 degrees Celsius, the material is irradiated with electromagnetic waves or ozone-treated to pass through an ozone atmosphere to perform adsorption oxidation to be used as an artificial aggregate or lightweight aggregate as a product. The catalyst material 1 is obtained. Bentonite 3 as a raw material is also known as montmorillonite, is recognized as a food additive, and has been used as a pharmaceutical raw material for a long time. The bentonite 2 theoretical composition a kind of hydrous aluminum silicate (clay minerals) of Al 2 O 3 · 4
It is represented by SiO 2 · nH 2 O and has an extremely large amount of base substitution and excellent adsorption. The bentonite 3 is crushed before use. Zeolite 4 as a raw material is a kind of crystalline aluminosilicate, and the typical example of the theoretical composition is Na 12 A.
indicated by l 12 Si 12 O 48 · 27H 2 O, has a uniform pore size, has excellent adsorption through pores. This zeolite 4 is also crushed and used. The glass cullet 5 as a raw material used in this example is also called glass powder and is in powder form. As the sludge incineration ash or the sludge incineration fly ash as a raw material, ash or fly ash obtained by incinerating various sludges can be used, but it is preferable to use the human waste sludge incineration ash or the human sewage sludge incineration fly ash. In the manufacturing process described above, kneading the ash dust 2 and each of the above raw materials and granulating them into spherical particles of about 5 to 15 mm is to make them uniform in the subsequent sintering and firing treatment, and to make them into shapes that are easy to handle as products. Etc. Further, the sintering and firing treatment is performed by heating bentonite 3 and zeolite 4 as raw materials to physically and chemically change the composition of these materials and removing fine water of crystallization into fine cavities. This is because the action of adsorbing and carrying the heavy metals contained in the ash dust 2 through the holes is significantly enhanced. As a result, even if a large amount of the adsorptive oxidation catalyst material 1 used as the artificial aggregate / lightweight aggregate etc. is landfilled, the heavy metals contained in the ash dust 2 do not elute, and it is used as the artificial aggregate / lightweight aggregate etc. It is possible to positively use the adsorptive oxidation catalyst material 1 as a landfill material, a lightweight concrete material, a ground maintenance material, and the like. Also, by such a sintering and firing process,
The molecules of alumina ( Al 2 O 3 ) contained in the composition of bentonite 3 and zeolite 4 as raw materials are changed to exert a far infrared ray action. Further, since the material is sintered and fired within a temperature range of 600 to 950 degrees Celsius, energy saving and equipment cost reduction can be achieved as compared with the conventional example.
The reason why sludge incinerated ash or sludge incinerated fly ash, for example, human waste sludge incinerated ash or human sewage sludge incinerated fly ash, is used as a raw material in the present Example is that granulation is further facilitated. Furthermore, after cooling the sintered and fired material to around 200 degrees Celsius, the material is irradiated with electromagnetic waves, or ozone is passed through an ozone atmosphere to remove ozone from the bentonite 3 and zeolite 4. It can be contained in the pores as much as possible, and it can exert each action of sterilization, deodorization, and sterilization by ozone, and it can adsorb and decompose heavy metal and malodorous molecular components around the product itself in addition to the product itself. It can have characteristics. Also,
By using the adsorptive oxidation catalyst material 1 used as the artificial aggregate or the lightweight aggregate in a bad environment, the effect of improving the environment can be obtained. As described in detail above, according to the adsorptive oxidation catalyst material used as the artificial aggregate / light weight aggregate and the like according to the present invention and the method for producing the same, it is possible to eliminate the elution of heavy metals and to detoxify the far infrared rays. Action, sterilization, deodorization, sterilization,
It is possible to realize an adsorptive oxidation catalyst material that can also exert the adsorptive decomposition action of heavy metals and malodorous molecular components,
Since the material can be sintered and fired within a temperature range of 600 to 950 degrees Celsius, it is possible to achieve low cost treatment, energy saving, and facility cost reduction as compared with the conventional treatment means of this type. . The present invention is not limited to the above-described embodiments, and various modifications can be made within the scope of the invention. For example, the adsorptive oxidation catalyst material 1 used as the artificial aggregate, the lightweight aggregate, or the like can be formed into a spherical shape, or can be embodied as a lump having an arbitrary shape such as an elliptic spherical shape, a cubic shape, or a rectangular parallelepiped shape.
【発明の効果】以上詳述した本発明の人工骨材・軽量骨
材等として用いる吸着酸化触媒材及びその製造方法によ
れば、以下の効果を奏する。請求項1、2、3記載に係
る人工骨材・軽量骨材等として用いる吸着酸化触媒材に
よれば、重金属類の溶出が無くなって無害化を図ること
ができ、遠赤外線作用、殺菌、脱臭、除菌の各作用、悪
臭分子成分の吸着分解作用をも発揮させることができ
る。請求項4記載に係る人工骨材・軽量骨材等として用
いる吸着酸化触媒材によれば、直径5乃至15mm程度
の球状に形成したので、製品として扱い易い形状とな
り、取扱いが容易となる。請求項5、6、7記載に係る
人工骨材・軽量骨材等として用いる吸着酸化触媒材の製
造方法によれば、摂氏600乃至950度の温度範囲内
で素材の焼結焼成を行うことができるので、この種の従
来の処理手段に比べ、省エネルギー化、設備コストの低
廉化を図れるとともに、低コストで前記請求項1乃至4
記載の人工骨材・軽量骨材等として用いる吸着酸化触媒
材を製造することができる。EFFECTS OF THE INVENTION According to the adsorptive oxidation catalyst material used as the artificial aggregate, the lightweight aggregate and the like of the present invention and the method for producing the same, the following effects are obtained. According to the adsorptive oxidation catalyst material used as the artificial aggregate or the lightweight aggregate according to claims 1, 2 and 3, the elution of heavy metals can be eliminated to render it harmless, and far-infrared action, sterilization and deodorization can be achieved. It is also possible to exert each action of sterilization and the adsorptive decomposition action of malodorous molecular components. According to the adsorptive oxidation catalyst material used as the artificial aggregate or the lightweight aggregate according to the fourth aspect, since it is formed into a spherical shape having a diameter of about 5 to 15 mm, the product has a shape that is easy to handle and easy to handle. According to the method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, etc. according to claims 5, 6, and 7, the material can be sintered and fired within a temperature range of 600 to 950 degrees Celsius. Therefore, as compared with the conventional processing means of this type, energy saving and equipment cost reduction can be achieved, and the cost can be reduced.
It is possible to manufacture the adsorptive oxidation catalyst material used as the described artificial aggregate, lightweight aggregate, and the like.
【図1】本発明の人工骨材・軽量骨材等として用いる吸
着酸化触媒材の実施例を示す概略断面図FIG. 1 is a schematic cross-sectional view showing an embodiment of an adsorptive oxidation catalyst material used as an artificial aggregate / light weight aggregate of the present invention.
【図2】本発明の人工骨材・軽量骨材等として用いる吸
着酸化触媒材の製造工程を示す工程図FIG. 2 is a process diagram showing a manufacturing process of an adsorptive oxidation catalyst material used as an artificial aggregate or a lightweight aggregate of the present invention.
1 人工骨材・軽量骨材等として用いる吸着酸化触媒材 2 灰塵 3 ベントナイト 4 ゼオライト 5 ガラスカレット 1 Adsorption oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. 2 ash dust 3 Bentonite 4 Zeolite 5 glass cullet
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI B09B 3/00 B09B 3/00 ZAB 301 303L ZAB ─────────────────────────────────────────────────── ─── Continued Front Page (51) Int.Cl. 7 Identification Code FI B09B 3/00 B09B 3/00 ZAB 301 303L ZAB
Claims (7)
ベントナイト、ゼオライト、ガラスカレット及び屎尿汚
泥等の汚泥焼却灰からなる原料とを、混練・造粒処理、
焼結焼成処理、電磁波の照射処理又はオゾン処理して塊
状に形成したことを特徴とする人工骨材・軽量骨材等と
して用いる吸着酸化触媒材。[Claim 1] Ash dust such as incineration ash of general waste and incineration fly ash;
Kneading and granulating the raw materials consisting of sludge incineration ash such as bentonite, zeolite, glass cullet and human waste sludge,
An adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, or the like, which is formed into a lump by sintering and firing treatment, electromagnetic wave irradiation treatment, or ozone treatment.
ベントナイト、ゼオライト、ガラスカレット及び屎尿汚
泥等の汚泥焼却飛灰からなる原料とを、混練・造粒処
理、焼結焼成処理、電磁波の照射処理又はオゾン処理し
て塊状に形成したことを特徴とする人工骨材・軽量骨材
等として用いる吸着酸化触媒材。2. Ash dust such as incineration ash of general waste and incineration fly ash,
Characteristically, a raw material consisting of sludge incineration fly ash such as bentonite, zeolite, glass cullet and human waste sludge is kneaded / granulated, sintered / fired, irradiated with electromagnetic waves or treated with ozone to form a lump. Adsorption oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc.
又は一般ゴミの焼却灰や焼却飛灰等に混在した汚泥焼却
灰又は汚泥焼却飛灰、例えば屎尿汚泥焼却灰又は屎尿汚
泥焼却飛灰の灰塵と、ベントナイト、ゼオライト及びガ
ラスカレットからなる原料とを、混練・造粒処理、焼結
焼成処理、電磁波の照射処理又はオゾン処理して塊状に
形成したことを特徴とする人工骨材・軽量骨材等として
用いる吸着酸化触媒材。3. Sludge incineration ash or sludge incineration fly ash, which is substituted for incineration ash or incineration fly ash of general trash, or mixed in incineration ash or incineration fly ash of general trash, for example, human waste sludge incineration ash or human waste sludge An artificial bone characterized by being formed into a lump by kneading / granulating treatment, sintering / firing treatment, electromagnetic wave irradiation treatment or ozone treatment of ash dust of incinerated fly ash and a raw material composed of bentonite, zeolite and glass cullet. Adsorption oxidation catalyst material used as materials, lightweight aggregates, etc.
着酸化触媒材は、直径5乃至15mm程度の球状に形成
されたものである請求項1乃至3のいずれか1項に記載
の人工骨材・軽量骨材等として用いる吸着酸化触媒材。4. The artificial body according to any one of claims 1 to 3, wherein the adsorptive oxidation catalyst material used as the artificial aggregate, the lightweight aggregate or the like is formed into a spherical shape having a diameter of about 5 to 15 mm. Adsorption oxidation catalyst material used as aggregate, lightweight aggregate, etc.
にかけて夾雑物を除去した後、加熱乾燥し、磁力選別手
段により鉄等の金属類を除去した前記灰塵と、原料とし
てのベントナイト、ゼオライト、ガラスカレット及び屎
尿汚泥等の汚泥焼却灰とを混合して粉砕し、加湿しなが
らこれらを混練して造粒し素材とする工程と,前記造粒
した素材に対し、摂氏250度乃至500℃前後の温度
で予備乾燥を行った後、摂氏600乃至950度の温度
範囲内で素材の焼結焼成を行う工程と,前記焼結焼成処
理した素材を摂氏200度前後まで冷却した後、この素
材に対する電磁波の照射処理又はオゾン雰囲気を通過さ
せるオゾン処理工程とからなる人工骨材・軽量骨材等と
して用いる吸着酸化触媒材の製造方法。5. The ash dust obtained by sieving ash dust such as incinerated ash or incinerated fly ash of general trash to remove impurities and then heat-drying and removing metals such as iron by magnetic separation means and a raw material. A process of mixing and crushing bentonite, zeolite, glass cullet, sludge incineration ash such as raw sewage sludge, and kneading and granulating them while humidifying, and 250 ° C with respect to the granulated material To pre-drying at a temperature of about 500 to 500 ° C., and then sintering and firing the material within a temperature range of 600 to 950 degrees Celsius, and cooling the sintered and fired material to about 200 degrees Celsius. A method for producing an adsorptive oxidation catalyst material used as an artificial aggregate, a lightweight aggregate, or the like, which comprises a step of irradiating this material with electromagnetic waves or an ozone treatment step of passing an ozone atmosphere.
にかけて夾雑物を除去した後、加熱乾燥し、磁力選別手
段により鉄等の金属類を除去した前記灰塵と、原料とし
てのベントナイト、ゼオライト、ガラスカレット及び屎
尿汚泥等の汚泥焼却飛灰とを混合して粉砕し、加湿しな
がらこれらを混練して造粒し素材とする工程と,前記造
粒した素材に対し、摂氏250度乃至500℃前後の温
度で予備乾燥を行った後、摂氏600乃至950度の温
度範囲内で素材の焼結焼成を行う工程と,前記焼結焼成
処理した素材を摂氏200度前後まで冷却した後、この
素材に対する電磁波の照射処理又はオゾン雰囲気を通過
させるオゾン処理工程とからなる人工骨材・軽量骨材等
として用いる吸着酸化触媒材の製造方法。6. Ash dust such as incinerated ash of general waste and incinerated fly ash is sieved to remove impurities, and then heated and dried, and the ash dust obtained by removing metals such as iron by magnetic separation means and a raw material A process of mixing and crushing sludge incineration fly ash such as bentonite, zeolite, glass cullet, and human waste sludge, and kneading and granulating them while humidifying, and a step of 250 ° C. for the granulated material After pre-drying at a temperature of around 600 to 950 ° C., sintering and firing the material within a temperature range of 600 to 950 ° C., and cooling the sintered and fired material to around 200 ° C. Then, a method for producing an adsorptive oxidation catalyst material to be used as an artificial aggregate, a lightweight aggregate, or the like, which comprises a step of irradiating the material with electromagnetic waves or an ozone treatment step of passing an ozone atmosphere.
又は一般ゴミの焼却灰や焼却飛灰等に混在した汚泥焼却
灰又は汚泥焼却飛灰、例えば屎尿汚泥焼却灰又は屎尿汚
泥焼却飛灰の灰塵を篩にかけて夾雑物を除去した後、加
熱乾燥し、磁力選別手段により鉄等の金属類を除去した
前記灰塵と、原料としてのベントナイト、ゼオライト及
びガラスカレットとを混合して粉砕し、加湿しながらこ
れらを混練して造粒し素材とする工程と,前記造粒した
素材に対し、摂氏250度乃至500℃前後の温度で予
備乾燥を行った後、摂氏600乃至950度の温度範囲
内で素材の焼結焼成を行う工程と,前記焼結焼成処理し
た素材を摂氏200度前後まで冷却した後、この素材に
対する電磁波の照射処理又はオゾン雰囲気を通過させる
オゾン処理工程とからなる人工骨材・軽量骨材等として
用いる吸着酸化触媒材の製造方法。7. Sludge incineration ash or sludge incineration fly ash, which is substituted for incineration ash, incineration fly ash, etc. of general trash, or mixed in incineration ash, incineration fly ash, etc. of general trash, for example, human waste sludge incineration ash or human waste sludge After removing the contaminants by sieving the ash dust of incineration fly ash, heating and drying, the ash dust from which metals such as iron have been removed by magnetic sorting means, and bentonite as a raw material, zeolite and glass cullet are mixed and ground. Then, a step of kneading and granulating them while moisturizing them to obtain a raw material, and pre-drying the granulated raw material at a temperature of around 250 to 500 ° C., and then at 600 to 950 ° C. A step of performing sintering and firing of the material within a temperature range, and a step of cooling the material subjected to the sintering and firing treatment to around 200 degrees Celsius, and then performing an electromagnetic wave irradiation treatment or an ozone treatment step of passing the material through an ozone atmosphere. Ranaru method for producing -AO catalyst material used as artificial bone materials, lightweight aggregates like.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17285095A JP3360974B2 (en) | 1995-06-15 | 1995-06-15 | Adsorbed oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. and method for producing the same |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17285095A JP3360974B2 (en) | 1995-06-15 | 1995-06-15 | Adsorbed oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. and method for producing the same |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH09917A JPH09917A (en) | 1997-01-07 |
| JP3360974B2 true JP3360974B2 (en) | 2003-01-07 |
Family
ID=15949467
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP17285095A Expired - Fee Related JP3360974B2 (en) | 1995-06-15 | 1995-06-15 | Adsorbed oxidation catalyst material used as artificial aggregate, lightweight aggregate, etc. and method for producing the same |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3360974B2 (en) |
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| KR100832579B1 (en) * | 2007-02-22 | 2008-05-27 | 주식회사 포스코건설 | Method for preventing heavy metal leaching from mortar, concrete and earthworks using low ash aggregate |
| JP5867825B2 (en) * | 2012-03-28 | 2016-02-24 | 住友大阪セメント株式会社 | Exhaust gas treatment method and exhaust gas treatment apparatus |
| CN117865534B (en) * | 2024-01-08 | 2024-07-26 | 浙江大学 | Artificial aggregate for cooperatively recycling household garbage incineration fly ash and sludge incineration ash and preparation method thereof |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP3000271U (en) | 1994-01-19 | 1994-08-02 | 株式会社ボーゲンファイル | Adsorption oxidation catalyst material used as lightweight aggregate |
-
1995
- 1995-06-15 JP JP17285095A patent/JP3360974B2/en not_active Expired - Fee Related
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP3000271U (en) | 1994-01-19 | 1994-08-02 | 株式会社ボーゲンファイル | Adsorption oxidation catalyst material used as lightweight aggregate |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH09917A (en) | 1997-01-07 |
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