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JPS5849319B2 - Pretreatment method for cement solidification treatment for incineration ash and dust - Google Patents
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JPS5849319B2 - Pretreatment method for cement solidification treatment for incineration ash and dust - Google Patents

Pretreatment method for cement solidification treatment for incineration ash and dust

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Publication number
JPS5849319B2
JPS5849319B2 JP51106488A JP10648876A JPS5849319B2 JP S5849319 B2 JPS5849319 B2 JP S5849319B2 JP 51106488 A JP51106488 A JP 51106488A JP 10648876 A JP10648876 A JP 10648876A JP S5849319 B2 JPS5849319 B2 JP S5849319B2
Authority
JP
Japan
Prior art keywords
dust
cement
parts
weight
ash
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
Application number
JP51106488A
Other languages
Japanese (ja)
Other versions
JPS5331573A (en
Inventor
繁夫 佐々木
安晴 城ケ崎
一郎 萩原
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.)
Niigata Engineering Co Ltd
Original Assignee
Niigata Engineering Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Niigata Engineering Co Ltd filed Critical Niigata Engineering Co Ltd
Priority to JP51106488A priority Critical patent/JPS5849319B2/en
Publication of JPS5331573A publication Critical patent/JPS5331573A/en
Publication of JPS5849319B2 publication Critical patent/JPS5849319B2/en
Expired legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【発明の詳細な説明】 本発明は塵芥、廃棄物等を焼却処分したときに発生する
焼却灰、ダスト類をセメント固形化処理するための前処
理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a pretreatment method for solidifying incineration ash and dust generated when trash, waste, etc. are incinerated into cement.

従来、焼却灰やダスト類の処理法として、これらをその
まま埋立処分することが行なわれていたが、焼却灰やダ
スト類は細かい粒子であるために粉塵公害が生じ易く、
またその中に含有されている有害重金属が溶出し、人体
に対する障害を引き起こす等、二次公害の発生のおそれ
が多分にあった。
Conventionally, the method of disposing of incinerated ash and dust was to simply dispose of it in a landfill, but since incinerated ash and dust are fine particles, they easily cause dust pollution.
In addition, there was a high risk that the harmful heavy metals contained therein would leach out and cause secondary pollution, such as causing damage to the human body.

このため、このような焼却灰、ダスト類、あるいはメッ
キ汚泥等からの二次公害を防止する手段として、従来よ
りプラスチック固形化法、焼成法、溶融法等が提案され
ているが、安定性が高く、処理費用が安価で操作が簡単
であるところからセメントによる固形化処理方法が一般
的に行われている。
For this reason, plastic solidification methods, calcination methods, melting methods, etc. have been proposed as a means of preventing secondary pollution from such incineration ash, dust, plating sludge, etc., but they are not stable. The solidification treatment method using cement is generally used because the treatment cost is low and the operation is simple.

しかるに、従来のセメント固形化法は、セメントに一般
のボルトランドセメントを使用したり、特殊な薬品を添
加したり等しているが、焼却灰、ダスト類の処理に際し
ては、いずれも充分な効果を発揮し得ていないのが現状
である。
However, conventional cement solidification methods use ordinary Boltland cement or add special chemicals, but none of them are sufficiently effective when processing incineration ash and dust. The current situation is that they are not fully demonstrating their potential.

すなわち、メッキ汚泥等をセメントにより固化するよう
な場合には、汚泥等が確実にセメント成分と混和され、
セメント成分による永和反応が迅速に生じて、比較的短
期間で強度の大きいセメント固形化物が得られ、汚泥等
を確実に処理することができるが、焼却灰、ダスト類に
は、その中に各種金属酸化物による活性戒分が存するた
めに、これがセメント成分による水和反応を阻害し、従
ってセメントの固形化が十分に行なわれ難く、例えば得
られたセメント固形物は材令28日で1 0kg/cw
t程度の一軸圧縮強度しか有さす、しかも水中に浸漬し
ておくと容易に砂状に溶解してしまう等の問題があり、
セメント固形物を製品として利用することは勿論、埋立
処分するにも不便があった。
In other words, when solidifying plating sludge etc. with cement, the sludge etc. is reliably mixed with the cement components,
Eiwa reaction by cement components occurs quickly, and a cement solidified product with high strength is obtained in a relatively short period of time, and sludge, etc. can be reliably treated, but incineration ash and dust may contain various types of Due to the presence of active substances caused by metal oxides, this inhibits the hydration reaction of cement components, making it difficult for cement to solidify sufficiently. For example, the obtained cement solids weigh 10 kg in 28 days. /cw
It has only a uniaxial compressive strength of about t, and there are problems such as it easily dissolves into sand when immersed in water.
It is inconvenient not only to use the solid cement as a product but also to dispose of it in a landfill.

また、このような焼却灰、ダスト類中の活性成分による
セメント水和反応の阻害作用は、焼却灰等が生じた直後
よりも、これらが長く放置された状態のものほど大いと
いう問題があり、このため焼却灰、ダスト類を確実に処
理する方法の開発が強く要望されていた。
Additionally, there is a problem that the inhibitory effect on the cement hydration reaction by the active components in such incinerated ash and dust is greater when the incinerated ash is left for a longer time than immediately after it is generated. Therefore, there has been a strong demand for the development of a method for reliably disposing of incinerated ash and dust.

本発明は上記事情に鑑みなされたもので、その目的とす
るところは焼却灰、ダスト類を容易かつ確実にセメント
固形化処理することができ、強度の大きいかつ水中で溶
解するような不都合のないセメント固形物を得ることが
できるようにした焼却灰、ダスト類に対するセメント固
形化処理の前処理方法を提供することにある。
The present invention has been developed in view of the above circumstances, and its purpose is to easily and reliably solidify incinerated ash and dust into cement, and to provide a cement with high strength and without the inconvenience of dissolving in water. An object of the present invention is to provide a pretreatment method for cement solidification treatment of incineration ash and dust, which makes it possible to obtain cement solids.

すなわち、本発明者らは焼却灰、ダスト類の処理法につ
き鋭意検討の結果、焼却灰、ダスト類にあらかじめ水を
加え、水酸化ナトリウム、水酸化カリウム等の苛性アル
カリを加えて充分に攪拌混合を行ない加圧接触反応させ
、必要によりさらに常圧をこえる圧力状態を保持させる
と、焼却灰、ダスト類のスラリー化物が含有されている
金属酸化物の結晶水生成反応である水和反応によって発
生する以上の温度、すなわち、100℃以上の温度を発
生し(この現象を水熱反応と称する)、これにより、ス
ラリー化され焼却灰、ダスト類が膨張すると共に、焼却
灰、ダスト類中の微細な気泡中に含まれていたセメント
固形化に障害となる活性成分(主に水素、一酸化炭素)
が焼却灰、ダスト類から排出され不活性化し、これをセ
メントと混練すると短期間で大きい強度を発揮するセメ
ント固形物が得られ、焼却灰、ダスト類を確実に処理で
きることを見出し、本発明をなすに至ったもので、本発
明は焼却灰もしくはダスト類又はこれらの混合物をセメ
ント固形化処理するに際し、あらかじめ焼却灰もしくは
ダスト類又はこれらの混合物に水、苛性アルカリを加え
て加圧接触反応を行なわせ、上記焼却灰もしくはダスト
類又はこれらの混合物のスラリーの温度を上昇させるよ
うにしたことを特徴とするものである。
That is, as a result of intensive study on the method for treating incinerated ash and dust, the present inventors added water to the incinerated ash and dust in advance, added a caustic alkali such as sodium hydroxide and potassium hydroxide, and thoroughly stirred and mixed the mixture. When a pressure contact reaction is carried out and, if necessary, a pressure state exceeding normal pressure is maintained, a hydration reaction occurs, which is a crystal water formation reaction of metal oxides containing slurry of incinerated ash and dust. (This phenomenon is called a hydrothermal reaction).As a result, the incinerated ash and dust expand into a slurry, and the fine particles in the incinerated ash and dust are expanded. Active ingredients (mainly hydrogen and carbon monoxide) that impede cement solidification contained in the air bubbles
is emitted from incinerated ash and dust and becomes inert, and when mixed with cement, a cement solid that exhibits great strength can be obtained in a short period of time, and the present invention has been developed based on the discovery that incinerated ash and dust can be reliably treated. In the present invention, when incinerated ash, dust, or a mixture thereof is solidified into cement, water and caustic alkali are added to the incinerated ash, dust, or a mixture thereof in advance, and a pressurized contact reaction is carried out. The present invention is characterized in that the temperature of the slurry of the incinerated ash, dust, or a mixture thereof is increased.

以下、本発明につき更に詳しく説明する。The present invention will be explained in more detail below.

本発明により処理される焼却灰は塵芥や廃棄物等を焼却
処分した時に発生するもの、またダスト類は廃熱ボイラ
ー、サイクロン、マルチサイクロン、バグフィルター、
電気集塵機等で捕集されるばいじん、粉じん等であり、
これらは焼却もしくは捕集直後のものでも長期間放置さ
れたものでもよい。
The incineration ash treated by the present invention is generated when garbage and waste are incinerated, and the dust is used in waste heat boilers, cyclones, multi-cyclones, bag filters, etc.
Soot, dust, etc. collected by electrostatic precipitators, etc.
These may be immediately after being incinerated or collected, or may be left for a long period of time.

而して、上記焼却灰もしくはダスト類又はこれらの混合
物をセメント固形化処理する場合は、まずこれら焼却灰
、ダスト類に水を加えるとともに、水酸化ナトリウム、
水酸化カリウム等の苛性アルカリを加えて二−ダ式等の
混練機を用いて加圧接触反応を行なわせる。
When the above-mentioned incineration ash or dust or a mixture thereof is to be solidified into cement, water is first added to the incineration ash or dust, and sodium hydroxide,
A caustic alkali such as potassium hydroxide is added and a pressurized contact reaction is carried out using a two-der kneader or the like.

この場合、各成分の混合割合は、焼却灰、ダスト類10
0重量部に対し水20〜40重量部、及び苛性アルカリ
4〜10重量部の範囲とすることが好ましく、通常この
範囲の混合割合において十分な加圧接触反応がおこなわ
れ、これにより焼却灰、ダスト類のスラリーの温度が上
昇してその活性成分が確実に不活性化される。
In this case, the mixing ratio of each component is incineration ash, dust, 10 parts
It is preferable to use 20 to 40 parts by weight of water and 4 to 10 parts by weight of caustic alkali to 0 parts by weight, and a sufficient pressurized contact reaction is normally carried out at a mixing ratio within this range, thereby causing incinerated ash, The temperature of the dust slurry increases to ensure that its active ingredients are inactivated.

なお、必要により苛性アルカリを上記上限を越えて配合
することも可能である。
Incidentally, if necessary, it is also possible to blend caustic alkali in an amount exceeding the above upper limit.

また、混練機による加圧接触反応時間は5〜10分間と
することが好ましく、また加圧接触反応後、上記スラリ
ーを必要に応じて蓄熱容器内に加圧状態で通常1〜2時
間保管、放置して100’C以上の高温を発生させ、水
熱反応を行なわせる。
Further, the pressurized contact reaction time using the kneader is preferably 5 to 10 minutes, and after the pressurized contact reaction, the slurry is stored in a heat storage container under pressure for usually 1 to 2 hours as necessary. The mixture is left to stand to generate a high temperature of 100'C or higher to carry out a hydrothermal reaction.

このように、焼却灰、ダスト類に水、更には苛性アルカ
リを加えて混線機で加圧接触反応を行なわせることによ
り、焼却灰、ダスト類のスラリ一の温度が上昇し、必要
に応じて加圧状態で保持することにより100〜120
℃程度まで上昇し、これによって焼却灰、ダスト類中の
金属酸化物等による活性成分が水熱反応し、スラリーが
膨張して活性成分が不活性化する。
In this way, by adding water and even caustic alkali to the incinerated ash and dust and causing a pressurized contact reaction in the mixer, the temperature of the slurry of incinerated ash and dust increases, and the 100-120 by holding in a pressurized state
The temperature rises to approximately 0.0°C, and as a result, the active ingredients such as metal oxides in the incinerated ash and dust undergo a hydrothermal reaction, the slurry expands, and the active ingredients are inactivated.

そして、上記前処理により活性成分が不活性になった焼
却灰、ダスト類のスラリーを用いて、常法によりセメン
ト固形化処理を行う。
Then, using the slurry of incinerated ash and dust whose active ingredients have been rendered inactive by the above pretreatment, cement solidification treatment is performed in a conventional manner.

すなわち、上記スラIJ−100重量部に対し、通常水
20〜30重量部、及びセメント15〜30重量部を混
合し、加圧成形による固形化を行う。
That is, 20 to 30 parts by weight of ordinary water and 15 to 30 parts by weight of cement are mixed with 100 parts by weight of the above slug IJ-1, and solidified by pressure molding.

かくして得られた固形化物は短期間で、例えば材令3日
で1 0 0 kg/crA程度の一軸圧縮強度を有す
る一般コンクリートレンガと同等の性状の強度の太きい
ものであり、また水中で溶解するようなことはなく、有
用なものである。
The solidified material obtained in this way is strong in a short period of time, for example, has properties equivalent to general concrete bricks having an unconfined compressive strength of about 100 kg/crA after 3 days of age, and is soluble in water. There's nothing you can do about it, and it's useful.

以上説明したように、本発明は焼却灰、ダスト類に水、
苛性アルカリを加えて加圧接触反応を行なわせることに
より、焼却灰、ダスト類中の活性成分が不活性化され、
従って焼却灰、ダスト類が効果的に前処理されて、これ
を容易かつ確実にセメント固形化処理することができ、
短期間で大キい強度を発揮しかつ水中で溶解するような
不都合のない有効利用可能な固化或形品が得られ、埋立
処分しか処理方法がなくて2次公害のもとであった焼却
灰、ダスト類を有効に社会に還元することができる。
As explained above, the present invention provides incineration ash and dust with water,
By adding caustic alkali and causing a pressurized contact reaction, the active ingredients in the incineration ash and dust are inactivated.
Therefore, incineration ash and dust are effectively pretreated and can be easily and reliably solidified into cement.
A solidified or molded product that exhibits great strength in a short period of time and can be effectively used without the inconvenience of dissolving in water can be obtained, and incineration, which was the only disposal method and caused secondary pollution, could be obtained. Ash and dust can be effectively returned to society.

以下、実施例と比較例を示し、本発明を更に具体的に説
明する。
EXAMPLES Hereinafter, the present invention will be explained in more detail by showing Examples and Comparative Examples.

実施例 後述する比較例の方法でセメント固形化処理を行っても
十分に処理がなし得なかったダストを使用し、このダス
ト100重量部に水30重量部及び水酸化ナトリウム7
重量部を加え、加圧混線機によって10分間加圧接触反
応を行い、加圧状態で2時間放置したところその温度が
約110゜Cまで上昇した。
Example Using dust that could not be sufficiently treated by cement solidification treatment by the method of the comparative example described later, 30 parts by weight of water and 7 parts by weight of sodium hydroxide were added to 100 parts by weight of this dust.
Parts by weight were added, a pressurized contact reaction was carried out for 10 minutes using a pressure mixer, and when the mixture was left under pressure for 2 hours, the temperature rose to about 110°C.

反応終了後、これに水20重量部、セメント15重量部
を加えて圧縮固形化したものは材令3日で1 0 0
kg/cr7fの一軸圧縮強度を有し、水中で溶解する
不都合は生せず、一般コンクリートレンガと同等の性状
を示した。
After the reaction was completed, 20 parts by weight of water and 15 parts by weight of cement were added to the mixture and the material was compressed and solidified.
It had an unconfined compressive strength of kg/cr7f, did not have the disadvantage of dissolving in water, and exhibited properties equivalent to ordinary concrete bricks.

比較例 ダスト100重量部を使用し、これに水25重量部及び
セメント40重量部を加えて圧縮固形化を行った。
Comparative Example Using 100 parts by weight of dust, 25 parts by weight of water and 40 parts by weight of cement were added to perform compression solidification.

得られたものは材令28日で10kg/crtiの一軸
圧縮強度しかだすことができず、また水中に浸漬してお
くと砂状に溶解してしまうという現象を呈し、非常にも
ろいものであった。
The material obtained had a uniaxial compressive strength of only 10 kg/crti after 28 days of age, and was extremely brittle, dissolving into sand when immersed in water. Ta.

以上の結果から、本発明に係るセメント固形化処理の前
処理方法を採用することにより確実にダスト類を処理で
き、強度の大きいかつ水中で溶解するごとき不都合を生
じることのないセメント固形化物が容易に得られること
が知見される。
From the above results, by adopting the pretreatment method for cement solidification treatment according to the present invention, dust can be reliably treated and cement solidified products with high strength and without inconveniences such as dissolution in water can be easily produced. It is found that this can be obtained.

Claims (1)

【特許請求の範囲】 1 焼却灰もしくはダスト類又はこれらの混合物をセメ
ント固形化処理するに際し、あらかじめ焼却灰もしくは
ダスト類又はこれらの混合物に水及び苛性アルカリを加
えて加圧接触反応を行なわせて、上記焼却灰もしくはダ
スト類又はこれらの混合物のスラリ一の温度を上昇させ
ることを特徴とする焼却灰、ダスト類に対するセメント
固形化処理の前処理方法。 2 ・焼却灰もしくはダスト類又はこれらの混合物10
0重量部に対し水20〜40重量部及び苛性アルカリ4
〜10重量部を混合するようにした特許請求の範囲第1
項記載の焼却灰、ダスト類に対するセメント固形化処理
の前処理方法。
[Claims] 1. When incinerated ash, dust, or a mixture thereof is subjected to cement solidification treatment, water and caustic alkali are added to the incinerated ash, dust, or a mixture thereof in advance to carry out a pressurized contact reaction. A pretreatment method for cement solidification treatment of incinerated ash and dust, which comprises raising the temperature of a slurry of the above-mentioned incinerated ash, dust, or a mixture thereof. 2 ・Incineration ash or dust or a mixture thereof10
0 parts by weight to 20 to 40 parts by weight of water and 4 parts by weight of caustic alkali
Claim 1: ~10 parts by weight are mixed.
A pretreatment method for cement solidification treatment for incineration ash and dust described in Section 1.
JP51106488A 1976-09-06 1976-09-06 Pretreatment method for cement solidification treatment for incineration ash and dust Expired JPS5849319B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51106488A JPS5849319B2 (en) 1976-09-06 1976-09-06 Pretreatment method for cement solidification treatment for incineration ash and dust

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51106488A JPS5849319B2 (en) 1976-09-06 1976-09-06 Pretreatment method for cement solidification treatment for incineration ash and dust

Publications (2)

Publication Number Publication Date
JPS5331573A JPS5331573A (en) 1978-03-24
JPS5849319B2 true JPS5849319B2 (en) 1983-11-02

Family

ID=14434838

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51106488A Expired JPS5849319B2 (en) 1976-09-06 1976-09-06 Pretreatment method for cement solidification treatment for incineration ash and dust

Country Status (1)

Country Link
JP (1) JPS5849319B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0464812A (en) * 1990-07-04 1992-02-28 Mitsubishi Heavy Ind Ltd Disposing method for combustion ash of fluidized bed

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5230468B2 (en) * 1972-02-08 1977-08-08
JPS5117504B2 (en) * 1972-09-06 1976-06-02

Also Published As

Publication number Publication date
JPS5331573A (en) 1978-03-24

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