JPH0461978A - Preparation of solidifying material - Google Patents
Preparation of solidifying materialInfo
- Publication number
- JPH0461978A JPH0461978A JP2168368A JP16836890A JPH0461978A JP H0461978 A JPH0461978 A JP H0461978A JP 2168368 A JP2168368 A JP 2168368A JP 16836890 A JP16836890 A JP 16836890A JP H0461978 A JPH0461978 A JP H0461978A
- Authority
- JP
- Japan
- Prior art keywords
- incineration ash
- heavy metals
- garbage incineration
- solidifying material
- powder
- 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
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、重金属を除去した後の生ゴミ焼却灰を原料と
した固化材の製法に関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for producing a solidifying material using raw garbage incineration ash from which heavy metals have been removed.
日常生活により排出される都市ゴミと産業廃棄物は、経
済活動の発展に伴って年毎に増大し、今日生活環境問題
として注目されている。BACKGROUND OF THE INVENTION Urban garbage and industrial waste generated in daily life are increasing every year with the development of economic activities, and are now attracting attention as a living environment problem.
建築基礎ポーリング魔性、浚渫工事やトンネル、〔課題
を解決するための手段〕
本発明は、これらの魔性を効果的に処理し得る固化材を
製造する方法に関する。すなわち、本発明は重金属を除
去した後の生ゴミ焼却灰を、動物骨粉、石灰及び珪質石
灰岩の粉末と混合し、焼成することを特徴とする固化材
の製法である。Architectural foundation polling, dredging and tunneling, [Means for solving the problems] The present invention relates to a method for producing a solidification material that can effectively deal with these problems. That is, the present invention is a method for producing a solidified material, which is characterized in that garbage incineration ash from which heavy metals have been removed is mixed with animal bone powder, lime, and siliceous limestone powder, and then fired.
以下、第1図に示した工程図を参照しながら詳細に説明
する。Hereinafter, a detailed explanation will be given with reference to the process diagram shown in FIG.
本発明においては固化材の原料として重金属を除去した
後の生ゴミ焼却灰を用いる。In the present invention, garbage incineration ash from which heavy metals have been removed is used as a raw material for the solidifying material.
即ち、まずゴミ焼却場等から出る生ゴミ焼却灰を振動ふ
るいにかけて分級する(工程S1)、これにより、生ゴ
ミ焼却灰中から鉄くずや小石等の固形物を除去する。That is, first, garbage incineration ash from a garbage incineration plant or the like is classified using a vibrating sieve (step S1), thereby removing solids such as iron scraps and pebbles from the garbage incineration ash.
次いで、固形物が除去された生ゴミ焼却灰から重金属を
除去する(工程S2)。Next, heavy metals are removed from the garbage incineration ash from which solids have been removed (step S2).
一般に都市ゴミを焼却すると、焼却灰中に有害重金属が
混入(例えば、カドミウム4.8ppm、鉛2600p
Pm、クロム540ppm、水銀0.1ppm)してい
る。都市ゴミ焼却灰は臨海都市の港湾埋め立て地などの
処分地で処理され、海岸線を持たない内陸都市は山間部
などの陸上処分地て処理しているが、雨水、地下水等の
浸透によって焼却灰から有害重金属が溶出する可能性が
社会問題化している。Generally, when municipal waste is incinerated, harmful heavy metals are mixed into the incinerated ash (for example, 4.8 ppm of cadmium, 2,600 ppm of lead).
Pm, chromium 540ppm, mercury 0.1ppm). Municipal garbage incineration ash is disposed of at disposal sites such as port landfills in coastal cities, and inland cities without coastlines are disposed of at land disposal sites such as mountainous areas, but incineration ash is disposed of by infiltration of rainwater, groundwater, etc. The possibility of toxic heavy metals being leached has become a social issue.
本発明で用いる生ゴミ焼却灰は生ゴミ焼却時に重金属を
除去したり、重金属を含む焼却灰から重金属を除去した
ものであり、廃棄しても重金属が雨水、地下水等により
溶出する危険性のないものである。The garbage incineration ash used in the present invention is obtained by removing heavy metals during garbage incineration or from incineration ash containing heavy metals, and there is no risk of heavy metals leaching into rainwater, groundwater, etc. even when disposed of. It is something.
重金属を含む焼却灰から重金属を除去する方法としては
、例えば動物骨粉を有効成分として含有する粒状物と生
ゴミ焼却灰を加熱、混合することにより、重金属を粒状
物に吸着させて除去する方法があげられる。A method for removing heavy metals from incineration ash containing heavy metals is, for example, heating and mixing granules containing animal bone meal as an active ingredient with garbage incineration ash, thereby adsorbing the heavy metals onto the granules and removing them. can give.
本発明において用いる動物骨粉は、従来畜産場等で殆ど
廃棄されていた骨、特に牛、馬、羊等の硬骨が主体の動
物の骨が採用される。The animal bone meal used in the present invention employs bones that have conventionally been mostly discarded at livestock farms, particularly bones of animals such as cows, horses, sheep, etc., which are mainly composed of hard bones.
これらの動物の生骨は焼成しやすい大きさに切断し、そ
の上で圧力釜に投入し、200〜400℃前後て、約9
0分前後煮沸する。次いでこの骨を焼成炉に入れ、90
0〜1100℃前後で、60〜180分前後焼成し、そ
のまま炉内で60分前後自然冷却させて室温乃至これに
近い状態に戻す。骨に骨成分以外のゼラチン、脂肪、蛋
白質にかわ等の有機物が残存すると酸化腐敗の原因とな
るので、これを確実に除去しておくことが重要である。The raw bones of these animals are cut into sizes that are easy to burn, then put into a pressure cooker and heated at about 200 to 400 degrees Celsius for about 90 minutes.
Boil for about 0 minutes. The bones were then placed in a kiln for 90
It is fired at about 0 to 1100°C for about 60 to 180 minutes, and then allowed to naturally cool in the furnace for about 60 minutes to return to room temperature or a state close to this temperature. If organic matter other than bone components such as gelatin, fat, protein, glue, etc. remains on the bone, it will cause oxidation and putrefaction, so it is important to ensure that this is removed.
上記煮沸工程によって、外側のみならず気孔内に付着し
ている有機物を骨から六方分離除去することができる。By the above boiling process, organic matter adhering not only to the outside but also to the inside of the pores can be separated and removed from the bone in all directions.
その上で上記焼成工程を通すことによって、残存する有
機物を完全に除去することができ、同時に骨中の湿度(
水分)を数%以下、好ましくはほぼ0%にまで低下させ
ることができる。上記焼成条件によれば、骨は白骨化し
て無数の気孔を有した原形組織状態を維持する。By then passing through the above baking process, remaining organic matter can be completely removed, and at the same time the humidity in the bone can be reduced.
The water content can be reduced to several percent or less, preferably to almost 0%. According to the above-mentioned firing conditions, the bone turns into a skeleton and maintains its original tissue state having countless pores.
上記焼成冷却後、この骨を破砕しパウダー機にかけて2
0〜200メツシユ前後、特に好ましくは50〜100
メツシユの粉状の骨粉とする。After the above firing and cooling, the bones are crushed and put into a powder machine for 2
Around 0 to 200 meshes, particularly preferably 50 to 100 meshes
It is made into powdered bone meal.
上記骨粉は、牛骨の場合、原料の生骨に比して重量比的
40%の収量が得られる。粒子は、カルシウム(約33
重量%)を主成分とし、リン(約16.7%)、バリウ
ム(約1.03%)、ナトリウム(約0.76%)、イ
オウ(約0.64%)、他にマグネシウム、カリウム、
塩素、アミン、鉄等から成っており、粒子の内外に渡っ
て無数の微小気孔が連通存在している。この骨粉はカル
シウムを含有するためアルカリ性である。In the case of bovine bones, the above-mentioned bone powder has a yield of 40% by weight compared to raw raw bones. The particles contain calcium (approximately 33
The main components are phosphorus (about 16.7%), barium (about 1.03%), sodium (about 0.76%), sulfur (about 0.64%), and magnesium, potassium,
It is composed of chlorine, amine, iron, etc., and has countless microscopic pores that communicate with each other both inside and outside the particle. This bone meal is alkaline because it contains calcium.
次いで、上記で得られた生ゴミ焼却灰に添加材を加えて
混合する(工程S3)。ここで用いる添加材としては、
動物骨粉、石灰、及び珪質石灰岩の粉末を用いる。動物
骨粉は、上記方法で得られたものを使用し得る。また、
石灰及び珪質石灰岩の粉末は粉状、粒状の一般的なもの
を使用し得るこれらの成分の他に必要に応じ他の充填材
、添加材等を添加してもよい。Next, additives are added to and mixed with the garbage incineration ash obtained above (step S3). The additives used here are:
Animal bone meal, lime, and siliceous limestone powder are used. The animal bone meal obtained by the above method can be used. Also,
Common lime and siliceous limestone powders can be used in the form of powder or granules.In addition to these ingredients, other fillers, additives, etc. may be added as necessary.
生ゴミ焼却灰と、動物骨粉、石灰、及び珪質石灰岩の粉
末との使用割合は、生ゴミ焼却灰100重量部に対して
通常、動物骨粉1〜6重量部、石灰4〜14重量部、珪
質石灰岩の粉末6〜19重量部、好ましくは動物骨粉2
〜5重量部、石灰6〜11重量部、珪質石灰岩の粉末9
〜16重量部である。The usage ratio of garbage incineration ash and powder of animal bone meal, lime, and siliceous limestone is usually 1 to 6 parts by weight of animal bone powder, 4 to 14 parts by weight of lime, and 1 to 6 parts by weight of animal bone powder, 4 to 14 parts by weight of lime, 6 to 19 parts by weight of siliceous limestone powder, preferably animal bone powder 2
~5 parts by weight, 6-11 parts by weight of lime, 9 parts by weight of siliceous limestone
~16 parts by weight.
これらの成分の混合は混合ミルを用いて行う。Mixing of these components is carried out using a mixing mill.
次いで、得られた混合物を焼成することにより固化材を
得る(工程S4)。焼成温度は通常、1000〜140
0℃で行う6
得られた固化材は取り扱いの便宜上、焼成後、徐冷しく
工程S5)、計量しく工程S6)、袋詰めしく工程S7
)、この状態で製品とするのが好ましい。Next, a solidified material is obtained by firing the obtained mixture (step S4). Firing temperature is usually 1000-140
6. For convenience of handling, the obtained solidified material is baked and then slowly cooled in step S5), weighed in step S6), and packed in bags in step S7.
), it is preferable to use this state as a product.
本発明の固化材を用いれば、従来、取り扱いに困ってい
た廃泥を効果的に処理し、取り扱いの容易な粒状物に変
換することができる。すなわち、廃泥に凝集剤を添加し
たり、遠心力を利用したりして、大まかに水を分離した
後に、本発明の固化材を添加、混合しながら、適当な大
きさに造粒し、乾燥し、焼成することによって粒状物を
得る。By using the solidifying material of the present invention, it is possible to effectively process waste mud, which has conventionally been difficult to handle, and convert it into granular material that is easy to handle. That is, after roughly separating water by adding a flocculant to waste mud or using centrifugal force, the solidifying material of the present invention is added and mixed while granulating to an appropriate size. Granules are obtained by drying and calcination.
得られる粒状物の取り扱いの便宜のためには、焼成後、
徐冷し、計量し、袋詰をした状態とするのが好ましい。For convenience in handling the resulting granules, after firing,
It is preferable to slowly cool the product, weigh it, and package it in bags.
この粒状物は、廃棄する場合には特別の場所を選ばずに
廃棄できる利点があるだけでな−く、土壌改良材、舗装
道路下地材、ゴルフ場下敷材、等として利用できる利点
がある。This granular material not only has the advantage that it can be disposed of anywhere, but also has the advantage that it can be used as a soil conditioner, a base material for paved roads, a golf course underlay material, and the like.
本発明によれば、焼却灰を資源として利用できるので、
本発明は生ゴミ焼却灰処理問題を解決する一つの有力な
手段ともなり得る。According to the present invention, since incineration ash can be used as a resource,
The present invention can also be an effective means for solving the problem of garbage incineration ash disposal.
■固化材の製造
重金属を除去した後の焼却灰(200メツシュ以上)、
牛骨粉、石灰、及び珪質石灰岩の粉末を、各々の割合が
80%、3%、7%、10%になるように混合し、12
00℃で焼成し、徐冷して固化材を得た。■Manufacture of solidification material Incineration ash (200 mesh or more) after removing heavy metals,
Mix beef bone powder, lime, and siliceous limestone powder so that the respective ratios are 80%, 3%, 7%, and 10%, and
The material was fired at 00°C and slowly cooled to obtain a solidified material.
■固化材の使用例
上記で得た固化材を用いてポーリング魔性(水を大まか
に分離済みのもの)を処理した一例を第2図の工程図を
参照しながら説明する。■Example of use of solidifying material An example of treating Pauling magic (from which water has been roughly separated) using the solidifying material obtained above will be explained with reference to the process diagram shown in FIG.
まず、水を大まかに分離して含水率を50〜70%まで
減少せしめたポーリング魔性100部に、上記で得た固
化材10部を添加して混合したく工程511)。この混
合によりポーリング魔性は凝固し、所定の粘性を有する
混合物が得られた。First, 10 parts of the solidifying material obtained above is added to 100 parts of Pauling's Magical Soil, which has been roughly separated from water to reduce the water content to 50-70%, and mixed (Step 511). By this mixing, Pauling's magic solidified and a mixture having a predetermined viscosity was obtained.
次いで、上記混合物を径5mm前後に造粒しく工程S1
2>、乾燥させた(工程813)。Next, the above mixture is granulated to a diameter of about 5 mm in step S1.
2>, dried (step 813).
次いで、乾燥させた粒状物を600〜1000℃で焼成
しく工程514) 、自然冷却(工程515)すること
によって強固な粒状物を得た。Next, the dried granules were fired at 600 to 1000°C (step 514) and naturally cooled (step 515) to obtain strong granules.
この粒状物は取り扱いの便宜上、自然冷却後、計量しく
工程516)、袋詰め(工程517)をした状態で製品
とすることが好ましい。For convenience of handling, it is preferable that the granular material is naturally cooled, then weighed (step 516) and packed into bags (step 517) to form a product.
上記粒状物は取り扱いが容易であり、しかも各種の用途
(土壌改良材、舗装道路下地材)に使用し得るものであ
った。The above-mentioned granules were easy to handle and could be used for various purposes (soil improvement material, pavement road base material).
なお、上記混合工程Sllで得られた混合物は所定の粘
性を有するので、従来の含水率の高い廃泥をそのまま捨
てる場合に比べて捨て場所の自由度が増す。したがって
、工程SL2以下を省略し、凝固せしめな廃泥をそのま
ま廃棄処分することも可能である。In addition, since the mixture obtained in the above-mentioned mixing step Sll has a predetermined viscosity, the degree of freedom in the disposal location is increased compared to the conventional case where waste mud with a high water content is discarded as it is. Therefore, it is also possible to omit steps SL2 and subsequent steps and dispose of solidified waste mud as it is.
第1図は本発明の固化材の製造工程を示す工程図、 第2図は本発明の固化材の使用例を示す工程図である。 FIG. 1 is a process diagram showing the manufacturing process of the solidification material of the present invention, FIG. 2 is a process diagram showing an example of the use of the solidifying material of the present invention.
Claims (1)
及び珪質石灰岩の粉末と混合し、焼成することを特徴と
する固化材の製法。A method for producing a solidified material, which comprises mixing garbage incineration ash from which heavy metals have been removed with animal bone meal, lime and siliceous limestone powder, and firing the mixture.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2168368A JP2522718B2 (en) | 1990-06-28 | 1990-06-28 | Manufacturing method of solidified material |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2168368A JP2522718B2 (en) | 1990-06-28 | 1990-06-28 | Manufacturing method of solidified material |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0461978A true JPH0461978A (en) | 1992-02-27 |
| JP2522718B2 JP2522718B2 (en) | 1996-08-07 |
Family
ID=15866799
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2168368A Expired - Lifetime JP2522718B2 (en) | 1990-06-28 | 1990-06-28 | Manufacturing method of solidified material |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2522718B2 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0639365A (en) * | 1992-07-20 | 1994-02-15 | Haruo Unno | Method and apparatus for producing improved soil by incineration ash such as soil discharge, sludge and waste |
| US6940553B1 (en) | 1997-01-28 | 2005-09-06 | Nec Corporation | Solid-state camera including a charge coupled device |
| US7479988B2 (en) | 1998-07-22 | 2009-01-20 | Sony Corporation | Video camera apparatus using an image sensor |
| WO2019009303A1 (en) * | 2017-07-04 | 2019-01-10 | 宇部興産株式会社 | Solid waste treatment method |
-
1990
- 1990-06-28 JP JP2168368A patent/JP2522718B2/en not_active Expired - Lifetime
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0639365A (en) * | 1992-07-20 | 1994-02-15 | Haruo Unno | Method and apparatus for producing improved soil by incineration ash such as soil discharge, sludge and waste |
| US6940553B1 (en) | 1997-01-28 | 2005-09-06 | Nec Corporation | Solid-state camera including a charge coupled device |
| US7479988B2 (en) | 1998-07-22 | 2009-01-20 | Sony Corporation | Video camera apparatus using an image sensor |
| WO2019009303A1 (en) * | 2017-07-04 | 2019-01-10 | 宇部興産株式会社 | Solid waste treatment method |
| JPWO2019009303A1 (en) * | 2017-07-04 | 2020-07-02 | 宇部興産株式会社 | Solid waste treatment method |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2522718B2 (en) | 1996-08-07 |
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