JPH0319178B2 - - Google Patents

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Publication number
JPH0319178B2
JPH0319178B2 JP1129687A JP1129687A JPH0319178B2 JP H0319178 B2 JPH0319178 B2 JP H0319178B2 JP 1129687 A JP1129687 A JP 1129687A JP 1129687 A JP1129687 A JP 1129687A JP H0319178 B2 JPH0319178 B2 JP H0319178B2
Authority
JP
Japan
Prior art keywords
degrees
brittle
cement
hardened
around
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 - Lifetime
Application number
JP1129687A
Other languages
Japanese (ja)
Other versions
JPS63182241A (en
Inventor
Hikoitsu Watanabe
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP62011296A priority Critical patent/JPS63182241A/en
Publication of JPS63182241A publication Critical patent/JPS63182241A/en
Publication of JPH0319178B2 publication Critical patent/JPH0319178B2/ja
Granted legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/06Combustion residues, e.g. purification products of smoke, fumes or exhaust gases
    • C04B18/10Burned or pyrolised refuse
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Description

【発明の詳細な説明】 (発明の目的) (イ) 産業上の利用分野 本願発明は主として一般家庭より排出される塵
芥を焼却処理施設にて焼却した後、大量に発生す
る焼却灰を利用して人造石材や砂利等を造成する
ための製造方法に関するものである。
[Detailed Description of the Invention] (Objective of the Invention) (a) Field of Industrial Application The present invention utilizes the incineration ash generated in large quantities after incinerating garbage mainly from ordinary households in an incineration treatment facility. This invention relates to a manufacturing method for creating artificial stone, gravel, etc.

(ロ) 従来の技術 一般家庭より排出される塵芥は全国自治体に共
通して原則として焼却処理をしているのである
が、その焼却方法は一般的に約700度の回転焼却
炉中を一定速度で塵芥を通過せしめて焼却してい
るのである。
(b) Conventional technology As a general rule, all local governments across the nation incinerate garbage generated from households, but the incineration method is generally to burn it at a constant speed in a rotating incinerator at a temperature of about 700 degrees. The garbage is passed through and incinerated.

処が一般家庭より排出される塵芥は燃えるゴミ
と燃えないゴミに分別排出するべき自治体の指導
にも拘らず所謂粗大ゴミと称される大型は別とし
て罐詰の空罐や薬ビン等のビン類から厨房用陶磁
器破片類や、破損金属玩具類並びに使用済電池
等々の不燃性物質が燃えるゴミと無分別のまま排
出されているのである。
Despite the local government's guidance that garbage discharged from ordinary households should be separated into combustible garbage and non-combustible garbage, there are still large items such as so-called oversized garbage, such as empty cans and bottles such as medicine bottles. Incombustible materials such as broken kitchen ceramics, broken metal toys, and used batteries are being disposed of without being classified as combustible garbage.

これ等の不燃性物質は例えばガラス類は溶融変
形し、空罐金属類も一部溶融変形し又陶磁器類は
破壊されて粗粒子状となつて可燃性物質の微粉末
灰と混然一体となつた焼却灰となるのであり、更
に又合成樹脂製食品包装類の如き難燃性物質も相
当量となるのであるがこれ等も700度程度では完
全燃焼し得るものではなく相当量が溶融して粗微
粒子状となつて残留するのである。
These non-combustible substances, for example, glass are melted and deformed, metals in empty cans are partially melted and deformed, and ceramics are destroyed and become coarse particles that are mixed with the fine powder ash of combustible substances. In addition, there is a considerable amount of flame-retardant materials such as synthetic resin food packaging, which cannot be completely combusted at around 700 degrees and a considerable amount will melt. It remains in the form of coarse and fine particles.

そして又更に重視されるべきは煙草や菓子類の
包装並びに調理用として使用されるアルミニウム
箔も相当量となるのであるがこれは殆ど微粒子状
に変形されてそのまま残留するのである。
What is even more important is that a considerable amount of aluminum foil is used for packaging cigarettes and confectionery as well as for cooking, and most of this is deformed into fine particles and remains as is.

このため例えば焼却灰をセメントにて硬化せし
めて何等かの用に供さんとしても、相当量のアル
ミニウム粒子がセメントの強アルカリ成分と作用
して酸化アルミニウムに変質する過程の発生ガス
に依り硬化を阻害れて充分な硬度が得られず、他
に適当な手段が見当たらぬ侭一部の自治体ではセ
メントやアスフアルトにて一応の固形状態として
海洋投棄をしているのが殆どの自治体では地中に
埋入処理をしているのが現状である。
For this reason, for example, even if incineration ash is hardened with cement and used for some purpose, a considerable amount of aluminum particles interact with the strong alkaline components of cement and change into aluminum oxide. Some local governments dispose of cement or asphalt in a solid state and dump it into the ocean, but most local governments dump it underground. The current situation is that they are being implanted.

しかし近似に於いては焼却灰をその内容物のす
べてが完全燃焼すると共に完全溶融せしめるべき
高熱処理をした後急冷硬化せしめてガラス状の脆
弱固体に造成し、これを粉砕して砂状として道路
造成時の路床材に転用せんとする技術も検討され
たが、如何にせん脆弱性であり且軽比重のため天
然砂内に一定量を混入し得る程度にて用途は限定
され仲々にして実用化されないのである。
However, in approximation, incineration ash is subjected to high heat treatment to completely burn and completely melt all of its contents, and then rapidly cooled and hardened to form a brittle glass-like solid, which is then crushed to form a sand-like road surface. The technology of using it as a roadbed material during land reclamation was also considered, but its use was limited because it was fragile and had a low specific gravity, so it could be mixed into natural sand in a certain amount. It will not be put into practical use.

(ハ) 発明が解決しようとする問題点 さて以上の如き難処理焼却灰の全国的年間発生
量は驚異的な厖大量とされつつもその実数は仲々
にして正確に掌握し得ないのであるが、例えば本
願発明者の事業所が所在する埼玉県川口市を引例
すると、40万の人工を以つて年間2万tonの焼却
灰が実数として発生するのであるからこれを以つ
て推測すると全国的発生量は正に驚異的でありし
かもこれは着実に逐年増加しているのである。
(c) Problems to be solved by the invention Although the annual amount of difficult-to-process incineration ash mentioned above is said to be a staggering amount, the actual number cannot be accurately determined. For example, taking Kawaguchi City, Saitama Prefecture, where the present inventor's business office is located, 400,000 people generate 20,000 tons of incinerated ash per year, so it can be estimated that this will occur nationwide. The amount is truly astonishing, and it is steadily increasing every year.

そしてその処理手段は殆どが遊休地を求めては
これを借受け、地中深部に埋入した上所定の深度
迄の表土を周囲と同様に修復して返却しているの
であるが年間2万tonともなれば近時は最早該当
地が皆無となりつつあつて困窮し、該実体は周辺
各都市も同様であり又国土全体としても同様に苦
慮しているのである。
Most of the treatment methods involve renting idle land, burying it deep underground, restoring the topsoil to a certain depth, and returning it in the same manner as the surrounding area, which amounts to 20,000 tons per year. In other words, these days, there is no longer any suitable land available, and we are in dire straits, and the reality is that surrounding cities are also struggling, and the country as a whole is also struggling.

処が焼却灰の実体は更に重大事態が内蔵されて
いるのであつて、それは焼却灰中には使用済電池
に依る有機水銀を殆どダイオキシン、六価クロム
等の有害物質も相当量含有しているのである。
However, the reality of the incinerated ash is that it contains an even more serious problem, and that is that the incinerated ash contains organic mercury from used batteries, as well as considerable amounts of harmful substances such as dioxins and hexavalent chromium. It is.

これ等の有害物質は降雨の都度地中に浸透する
雨水に依つて次第に地下深部へと遊離降下し、終
には地下水に到達するは必定でありすべての天然
資源が枯渇した我が国土に於いて残された唯一の
資源たる地下水さえも失わんとする危機に直面し
ているのである。
These harmful substances gradually fall freely deep underground due to the rainwater that permeates into the ground every time it rains, and it is inevitable that they will eventually reach the groundwater, and in a country where all natural resources have been depleted, Even groundwater, the only remaining resource, is in danger of being lost.

吾人は遠き祖先より四季の変化を満喫し清浄に
して無垢なる大地を継承しここに未曾有の平和と
繁栄を築き上げたのであるが、その代償として子
孫に最早絶対に修復し得ない地下汚染の大地を残
さんとしているのであつてかかる暴挙は早急に阻
止されなくてはならない重大問題である。
We inherited from our distant ancestors a clean and pure land where we could enjoy the changing seasons, and here we built an unprecedented peace and prosperity, but at the cost of that, our descendants were left with an underground contaminated land that could never be repaired. This outrageous behavior is a serious problem that must be stopped as soon as possible.

ここに於いて焼却灰の処理手段を考える時最も
有効にして且可能性を有するものはその構成分子
を以つて人造石材の造成であり或いは又これを破
砕して砂利に転用せんとする手段である。
When considering the means of disposing of incineration ash, the most effective and possible option is to use its constituent molecules to create artificial stone, or to crush it and convert it into gravel. be.

詳記する迄もなく現在国内の砂利需要量は数億
tonであるが一般河川よりの採取が禁止された今
日砕石砂利に活路を求めその需給関係は日を追つ
て逼迫化しつつあるのであつて、かかる時厖大量
の焼却灰が石材や砂利に転用されるとなれば正に
国家的朗報というべきものである。
Needless to say in detail, the current domestic demand for gravel is in the hundreds of millions.
Today, the extraction of ash from ordinary rivers is prohibited, and the demand and supply relationship is becoming tighter day by day. If so, this can truly be called good news for the nation.

(ニ) 問題を解決するための手段 焼却灰を高熱処理をしてすべての金属類を除去
して硬化せしめるとガラス状の黒褐色固体となる
のであるがその内容を大別すると、 (1) 陶磁器破片類やガラス等による珪素化合物 (2) 可燃性物質と難燃性物質に依る炭素化合物 が主成分となるのであるからこれにカルシウム系
物質を添加融合すると石状体となる如きは当該技
術者としては一応予見し得るものであるが、添加
カルシウム系物質とこれに依つて大きく変化する
溶融温度、並びに加熱溶融温度の上昇に伴つて激
しく発生する発煙ガスに依つて多数の気泡が石状
体内に造成され石状体としての硬度が消滅し、或
いは又相当量に含有する各種金属類の除去手段や
これ等を処理しつつ設定されるべき最適加熱温度
等々は焼却灰の内容が複雑物質の集合体なるが故
に極めて複雑なものとなるのであつて、厖大量の
実験結果上記の各種問題の解決こそが本願発明達
成のための絶対的手段であると確信するに到つた
のである。
(d) Means to solve the problem When incineration ash is subjected to high heat treatment to remove all metals and harden it, it becomes a glass-like dark brown solid.The contents can be roughly divided into: (1) Ceramics. Silicon compounds from debris, glass, etc. (2) Since the main component is carbon compounds from combustible and flame-retardant substances, if a calcium-based substance is added and fused to this, it will turn into a stone-like substance. However, it is foreseeable that many bubbles will form inside the stone due to the addition of calcium-based substances, the melting temperature that changes greatly due to this, and the fuming gas that is violently generated as the heated melting temperature rises. If the incineration ash contains complex substances, the hardness of the stone-like bodies disappears, or the methods for removing the various metals contained in a considerable amount and the optimum heating temperature that should be set while processing these are required. Since it is an aggregate, it is extremely complex, and after a large amount of experimental results, I have come to believe that solving the various problems mentioned above is the absolute means to achieve the invention of the present application.

(発明の構成) (ホ) 実施例及び作用 焼却灰を溶融してこれを天然石に匹敵せる結晶
と硬度を有する人造石にするための溶融温度は各
種実験の結果、炉内温度1200度前後(以下記述さ
れる温度はすべて炉内温度である)が最適であ
る。
(Structure of the Invention) (E) Examples and Effects As a result of various experiments, the melting temperature for melting incineration ash and turning it into artificial stone with crystals and hardness comparable to natural stone was determined to be around 1200 degrees Celsius (inside the furnace). All temperatures described below are furnace temperatures).

そこで検討されるべきは1200度前後に於いて焼
却灰と溶融混和するカルシウム系添加物質である
が、本願発明の目的が人造石や砂利である以上な
し得る限り低廉価額にて且安定せる供給量が必須
の要件となるのであつてその種類には自ら限界が
あり、かかる条件下に於ける各種実験の結果その
生成過程に於いて既に1400度程度にて高熱処理さ
れたセメントが最も効果的であり、これを以つて
焼却灰は1200度前後に於いて希望する粘度のマグ
マ状に融合し、且これを除冷硬化せしめると希望
する緻密結晶と硬度の石状体となることが確認さ
れたのである。
Therefore, what should be considered is a calcium-based additive that melts and mixes with the incinerated ash at around 1200 degrees, but since the purpose of the present invention is artificial stone and gravel, it should be supplied at the lowest possible price and in a stable supply amount. is an essential requirement, and there is a limit to the types of cement that can be used.The results of various experiments under such conditions have shown that cement that has already been subjected to high heat treatment at about 1400 degrees during the production process is the most effective. With this, it was confirmed that incineration ash fuses into a magma with the desired viscosity at around 1200 degrees Celsius, and when this is slowly cooled and hardened, it becomes a stone-like body with the desired dense crystals and hardness. It is.

処がここで問題となるものは焼却灰を1200度前
後迄加熱すると難燃性残留物質は激しく燃焼して
発煙ガスを噴出し続けるのであつて、これを徐冷
硬化しても折角の緻密結晶でありながら石状体内
には大小無数の気泡が造成されてそのため脆弱化
されてしまうことになり、加えて更に問題視され
るのは焼却灰中に30%〜40%の比率を以つて混入
せる鉄類を始めとする各種非鉄金属類であつて、
これが1200度程度では粗粒子状となつて石状体中
に散在し時日の経過と共に石状体の表面に発錆状
態となつて露出するのである。
However, the problem here is that when the incineration ash is heated to around 1200 degrees, the flame-retardant residual substances burn violently and continue to spew out smoking gas, and even if they are slowly cooled and hardened, they become dense crystals. However, countless large and small air bubbles are created inside the stone bodies, which makes them brittle.Additionally, what is considered a further problem is that they are mixed into the incineration ash at a ratio of 30% to 40%. various non-ferrous metals including ferrous metals,
At temperatures around 1,200 degrees, it becomes coarse particles and is scattered throughout the stone body, and as time passes, it becomes exposed as rust on the surface of the stone body.

以上の発生ガスと金属類の散在状態は何として
も除去しなくてはならず先ずガス処理対策として
種々薬剤処理手段を試みたが如何にせん焼却灰残
留物の内容が不特定のため何れも殆ど実効が得ら
れなかつたのである。
The above-mentioned scattered state of generated gas and metals must be removed at all costs. First, various chemical treatment methods were tried as a gas treatment measure, but none were successful as the content of the incineration ash residue was unspecified. It was hardly effective.

ここに於いて止むなく実施した手段は焼却灰の
みを先ず1200度前後より大きく超過上昇せしめ、
即ち1200度前後にて燃焼し続ける残留物を更に高
温加熱して完全燃焼しつくした上、自然冷却した
焼却灰のみに依る脆弱硬化体を一旦造成し、改め
てこれを適量のセメントと混合して1200度前後に
て溶融する手段である。
The measures we had to take here were to first raise the temperature of the incinerated ash to a temperature much higher than around 1200 degrees.
In other words, the residue that continues to burn at around 1200 degrees is heated to a higher temperature until it is completely combusted, and then a brittle hardened material is created using only the naturally cooled incineration ash, which is then mixed with an appropriate amount of cement. It is a means of melting at around 1200 degrees.

以上を以つて1200度前後以上の超過上昇温度を
どの程度に設定せしめるべきか各種実験過程に於
いて望外の事態が発見されることとなつたのであ
る。
As a result of the above, an unexpected situation was discovered during various experiments to determine how high the excessive temperature rise above 1200 degrees should be set.

それは1500度前後迄上昇せしめると焼却灰中の
各種金属は殆ど完全に溶融して合体化し、比重差
を以つて溶融焼却灰の下底に合金塊となつて焼却
灰のみの脆弱硬化体と分離沈澱するため容易に分
離回収し得ることとなり、又1200度程度では相当
量に残留する陶磁器類の粗粒子も殆ど溶融するこ
とが判明し、ここに於いて合金塊と分離した焼却
灰のみの脆弱硬化体と適量のセメントを混合して
改めて1200度前後にて溶融すると最早ガス発生の
危惧はなく一定時間を以つて希望する程度のマグ
マ状に溶融するのであつて、これを徐冷硬化せし
めると灰褐色にして緻密なる結晶体となり、その
一軸圧縮強度は800Kg/cm程度となつて天然岩石
に於ける白亜期後期以降の花崗岩に匹敵する状態
に生成されることになつたものである。
When the temperature rises to around 1,500 degrees, the various metals in the incinerated ash almost completely melt and coalesce, and due to the difference in specific gravity, an alloy mass forms at the bottom of the molten incinerated ash and separates from the brittle hardened body of incinerated ash alone. Because it precipitates, it can be easily separated and recovered, and it has also been found that at about 1200 degrees, most of the remaining ceramic particles, which remain in considerable amounts, are melted. If you mix the hardened material and an appropriate amount of cement and melt it again at around 1200 degrees, there is no longer any risk of gas generation, and it will melt into the desired magma shape over a certain period of time. It becomes a grayish-brown, dense crystalline substance with an unconfined compressive strength of approximately 800 kg/cm, which is comparable to natural rock of late Cretaceous granite.

ここで、上述の焼却灰のみの脆弱硬化体と混合
したセメントの作用について記述すると、発煙ガ
ス及び合金塊となつた金属成分を完全に除去した
後の焼却灰のみの脆弱硬化体を最終的には石状体
にしその硬度を如何様に強化するかにセメントを
混合した意味を有するものであり、そのための要
件としては焼却灰のみの脆弱硬化体をまず溶融
し、次いで徐冷後に高硬度の石状体にするという
添加剤の条件を備える必要がある。しかるに、こ
れらの要求を満たした添加剤を得るため、当初各
種の石灰類を試料としたが良好な溶融状態が得ら
れず、その後種々の実験結果により、遂に市販さ
れるポルトランドセメントを焼却灰のみの脆弱硬
化体に混合して1200度前後にて約1時間程度加熱
することにより好適な溶融状態を得、且つ徐冷に
より高硬度の石状体を得るに至り、これにて安価
且つ簡易に入手し得るポルトランドセメントの利
便なることにも鑑み、焼却灰のみの脆弱硬化体に
対する最適なる硬度強化剤としてポルトランドセ
メントを採用するに至つたのである。
Here, to describe the action of cement mixed with the brittle hardened body made only of incinerated ash mentioned above, the brittle hardened body made only of incinerated ash is finally It has the meaning of mixing cement into a stone-like body and how to strengthen its hardness.The requirements for this are to first melt the brittle hardened body of incinerated ash, and then slowly cool it and then turn it into a hardened stone. It is necessary to provide the conditions for additives to form stone-like bodies. However, in order to obtain an additive that met these requirements, various types of lime were initially used as samples, but a good molten state could not be obtained.Afterwards, various experimental results led to the use of only incinerated ash to make commercially available Portland cement. By mixing it with a brittle hardened material and heating it at around 1200 degrees for about 1 hour, a suitable molten state is obtained, and by slow cooling, a stone-like material with high hardness is obtained. In view of the convenience of available Portland cement, Portland cement was adopted as the optimal hardening agent for the brittle hardened material made only of incineration ash.

しかして、このポルトランドセメントが焼却灰
のみの脆弱硬化体に作用する態様は、コンクリー
ト造成における水和凝結剤としての作用ではな
く、焼却灰のみの脆弱硬化体に対する硬度強化剤
として作用させるという全く新規な用途としての
作用であり、1200度前後の高温下において焼却灰
の主成分たる珪素化合物と炭素化合物とに対して
セメントの主成分たるカルシウムが良く融合し、
且つ脆弱硬化体の硬度強化剤として作用すること
により徐冷により高硬度の緻密なる結晶体を得る
ものである。
However, the manner in which this Portland cement acts on brittle hardened bodies made only of incinerated ash is a completely new method in which it acts not as a hydration coagulant in concrete construction, but as a hardening agent for brittle hardened bodies made only of incinerated ash. Calcium, which is the main component of cement, fuses well with the silicon compounds and carbon compounds, which are the main components of incineration ash, at high temperatures of around 1200 degrees.
In addition, by acting as a hardness strengthening agent for the brittle cured product, a dense crystalline product with high hardness can be obtained by slow cooling.

そして又その形状は徐冷硬化時の容器に依つて
自在に造成し得るものであり、必要に応じて破砕
して砂利とする時は殆どの金属類を除去した良質
砂利としてコンクリート骨材ともなり得るもので
ある。
Moreover, its shape can be freely created depending on the container used during slow cooling and hardening, and when it is crushed to make gravel as necessary, it can be used as concrete aggregate as high-quality gravel with most of the metals removed. It's something you get.

尚実験結果に於いて上記溶融温度を1200度前後
より上昇せしめると上昇率に比例して結晶密度は
次第に粗状となつて強度が低下し又1200度前後以
下では充分に溶融せず結局1200度前後が最も効果
的とされるのである。
In addition, the experimental results show that when the above melting temperature is increased from around 1200 degrees, the crystal density gradually becomes coarser and the strength decreases in proportion to the rate of increase, and when the melting temperature is lower than around 1200 degrees, it is not sufficiently melted and the temperature eventually reaches 1200 degrees. Before and after is said to be the most effective.

(ヘ) 発明の効果 以上記述せる如く本願発明方法に依れば今正に
国土全域が地下深部に於いて汚染しつくされんと
しその処理対策に苦悩しある厖大量の塵芥焼却灰
が一転して人造石材となり、更にこれを以つて殆
どの金属類が除去された良質砂利に破砕転用され
ることとなり、これは現在天然川砂利が全面採取
禁止となり又山砂利も殆ど採取しつくされ、止む
なく砕石砂利に活路を求めざるを得なくなつてそ
の結果夫々の石粒の表面に露出せる金属類が未処
理のままコンクリート骨材として使用され、これ
が酸化ガスに依つてコンクリートの膨張やヒビ割
れ事故となる如き危惧は完全に払拭さることにな
るのである。
(f) Effects of the Invention As described above, by using the method of the present invention, the entire country is now completely contaminated deep underground, and the huge amount of garbage incineration ash, for which it is difficult to find a way to dispose of it, can be completely eliminated. This is then turned into artificial stone, which is then crushed and converted into high-quality gravel from which most of the metals have been removed.Currently, natural river gravel is completely prohibited from being mined, and mountain gravel has almost all been mined. As a result, the metals exposed on the surface of each stone grain are used as concrete aggregate without treatment, and this causes expansion and cracking of concrete due to oxidizing gas. The fear of an accident will be completely dispelled.

処が人造石や砂利等の市価は決して高額なもの
ではないのであるが、比するに本願発明に依る製
造価額は溶融エネルギー費と副材料たるセメン
ト、並びに人件費や償却費等の直接費や間接費を
勘案すると採算面において画餅に期する如き憾を
受けるのであるがこれは余りにも短絡的な見解で
ある。
However, while the market price of artificial stone and gravel is not high, the manufacturing cost according to the present invention is comparatively low due to direct costs such as melting energy costs, cement as an auxiliary material, labor costs, and depreciation costs. When indirect costs are taken into account, it seems like the project is just a flop in terms of profitability, but this is an extremely short-sighted view.

何故ならば現在各自治体に於ける焼却灰処理手
段は前記もせる如く遊休民有地を賃借し、これを
深く堀削して埋入した上一定量の表土を冠して周
囲の土壌と同一状態に復元返却するのであるから
借地料、堀削費、修復費、運搬費等の総計は決し
て少額なものではなく、況してやコンクリートや
アスフアルトにて固形化して海洋投棄をする如き
は一層高額化出費となるのであつて本願発明製造
費の40%〜50%程度となるのである。
This is because the current means of disposing of incinerated ash in each local government is to lease idle private land as mentioned above, dig it deeply and bury it, and then cover it with a certain amount of topsoil so that it is in the same condition as the surrounding soil. The total cost of land lease, excavation, restoration, transportation, etc. is not a small amount, and if the material is solidified with concrete or asphalt and then dumped into the ocean, the cost becomes even more expensive. Therefore, it is about 40% to 50% of the manufacturing cost of the present invention.

そして又本願発明に於いて焼却灰中より回収さ
れる合金塊量は焼却灰に対して約30%〜40%とな
るのであり、これはその複雑成分より一般の鋳造
原料として使用すう事は困難であるが一般鋳造用
原料銑鉄に比して50%程度の廉価にて供給し得る
とすれば、材質を不問として硬度と比重のみにて
使用される例えばフオークリフト車輌やクレーン
車輌等の重錘や養殖漁業用漁網の定置アンカー
等々其の他の用途は厖大量であり、これを加算し
更に又溶融処理エネルギーは復水タービン方式を
以つてこれを回収再利用をすればエネルギー処理
費は少なくとも30%程度は軽減されることになり
これ等を以つて採算点は漸くにして維持し得るも
のである。
Furthermore, in the present invention, the amount of alloy lumps recovered from the incinerated ash is about 30% to 40% of the incinerated ash, which makes it difficult to use as a general casting raw material due to its complex components. However, if it can be supplied at a price about 50% lower than that of raw material pig iron for general casting, it can be used for heavy weights such as forklift vehicles and crane vehicles, which are used only based on hardness and specific gravity, regardless of the material. Other uses, such as fixed anchors for fishing nets for aquaculture and fish farming, require a large amount of energy, and if you add this up, and the melting processing energy is recovered and reused using a condensate turbine system, the energy processing cost can be reduced at least. Approximately 30% of the cost will be reduced, and with this, it will be possible to maintain a break-even point.

然し乍ら本願発明の主眼とするものは企業的利
益を追求するものではなく飽迄も貴重なる国土の
保全を願うものである以上、若しも採算面に於い
て不足分が生じたとしても極微量であり、これは
国費を以つて補捉しても断乎活用されるべき重大
技術とされるべきである。
However, since the main purpose of the claimed invention is not to pursue corporate profits but to preserve the precious national land, even if there is a shortfall in terms of profitability, it will be minimal. Therefore, this should be considered an important technology that should be fully utilized even if it is covered by national funds.

Claims (1)

【特許請求の範囲】[Claims] 1 塵芥を焼却して発生した焼却灰を一旦炉内温
度1500度前後に加熱溶融し、該時点に到る迄の焼
却発煙ガスを全て発散処理をした上これを冷却硬
化せしめて脆弱硬化体となし、該脆弱硬化体の底
部に比重差を以つて分離沈殿せる各種金属に依つ
て合成された金属塊を除去してこれを組成鋳造原
料として活用し、改めて該脆弱硬化体を適量のセ
メントと混和して該セメントを前記脆弱硬化体の
硬度強化剤として用い、炉内温度1200度前後にて
一定時間加熱溶融した後、これを徐冷硬化せしめ
て人造石材に造製したり又これを破砕して砂利と
する等を特徴とした塵芥焼却灰を利用した人造石
や砂利等の製造方法。
1 The incineration ash generated by incinerating the garbage is heated and melted to a furnace temperature of around 1500 degrees, and all the fumes from the incineration up to that point are released, and then it is cooled and hardened to form a brittle hardened body. None, the metal lump synthesized by various metals that are separated and precipitated with a difference in specific gravity at the bottom of the brittle hardened body is removed and used as a composition casting raw material, and the brittle hardened body is reused with an appropriate amount of cement. The cement is mixed and used as a hardening agent for the brittle hardened body, heated and melted at a furnace temperature of around 1200 degrees for a certain period of time, and then slowly cooled and hardened to produce artificial stone or crushed. A method for producing artificial stones, gravel, etc. using garbage incineration ash, which is characterized by the following characteristics:
JP62011296A 1987-01-22 1987-01-22 Manufacture of gravel from garbage incinerated ash Granted JPS63182241A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62011296A JPS63182241A (en) 1987-01-22 1987-01-22 Manufacture of gravel from garbage incinerated ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62011296A JPS63182241A (en) 1987-01-22 1987-01-22 Manufacture of gravel from garbage incinerated ash

Publications (2)

Publication Number Publication Date
JPS63182241A JPS63182241A (en) 1988-07-27
JPH0319178B2 true JPH0319178B2 (en) 1991-03-14

Family

ID=11774033

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62011296A Granted JPS63182241A (en) 1987-01-22 1987-01-22 Manufacture of gravel from garbage incinerated ash

Country Status (1)

Country Link
JP (1) JPS63182241A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT410288B (en) 2001-07-23 2003-03-25 Ash Dec Umwelttechnologien Ges METHOD FOR DECONTAMINATING AND INERTIZING FILTER AND FLIGHT BAGS

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56164063A (en) * 1980-05-20 1981-12-16 Daido Steel Co Ltd Manufacture of aggregate
JPS57200259A (en) * 1981-05-30 1982-12-08 Daido Steel Co Ltd Manufacture of hard aggregate from wastes

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56164063A (en) * 1980-05-20 1981-12-16 Daido Steel Co Ltd Manufacture of aggregate
JPS57200259A (en) * 1981-05-30 1982-12-08 Daido Steel Co Ltd Manufacture of hard aggregate from wastes

Also Published As

Publication number Publication date
JPS63182241A (en) 1988-07-27

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