JPH05253319A - Agent for treating incineration ash containing poisonous substance such as heavy metal - Google Patents

Agent for treating incineration ash containing poisonous substance such as heavy metal

Info

Publication number
JPH05253319A
JPH05253319A JP4058180A JP5818092A JPH05253319A JP H05253319 A JPH05253319 A JP H05253319A JP 4058180 A JP4058180 A JP 4058180A JP 5818092 A JP5818092 A JP 5818092A JP H05253319 A JPH05253319 A JP H05253319A
Authority
JP
Japan
Prior art keywords
weight
incineration ash
agent
heavy metal
borate
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP4058180A
Other languages
Japanese (ja)
Inventor
Hajime Ozaki
肇 尾崎
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 JP4058180A priority Critical patent/JPH05253319A/en
Publication of JPH05253319A publication Critical patent/JPH05253319A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To provide an incineration ash treating agent which makes poisonous substances such as heavy metal contained in the incineration ash harmless or prevents elusion by sealing up the substances. CONSTITUTION:This agent for treating incineration ash containing poisonous substances such as heavy metal comprises 4.0-6.0wt.% of sodium chloride, 0.3-2.0wt.% of ammonium chloride, 4.0-6.5wt.% of potassium carbonate, 0.1-0.4wt.% of cobalt chloride, 4.0-7.0wt.% of sodium carbonate and 0.6-3.0wt.% of boric acid. The rest are water and inevitable impurities.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、重金属等の有害物質を
含む産業廃棄物・都市ゴミ・汚泥等の各種廃棄物の焼却
灰を無害化する重金属等有害物質含有焼却灰処理剤に関
するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an incineration ash treatment agent containing harmful substances such as heavy metals for detoxifying incineration ash of various wastes such as heavy metals and other hazardous substances such as industrial waste, municipal waste and sludge. is there.

【0002】[0002]

【従来技術および発明が解決しようとする課題】各種廃
棄物はほとんどの場合最終的に焼却灰として排出され
る。この各種廃棄物の焼却灰は一般に水銀、六価クロ
ム、鉛、カドミウム、シアン、有機リン、ヒ素、PC
B、トリクロロエチレン、テトラクロロエチレン、有機
塩素、銅、亜鉛、ふっ化物などの重金属等の有害物質を
含むため、厳しく規制された方法で所定の最終処分場に
おいて処理されなければならない。
BACKGROUND OF THE INVENTION In most cases, various kinds of waste are finally discharged as incinerated ash. The incineration ash of these various wastes is generally mercury, hexavalent chromium, lead, cadmium, cyan, organic phosphorus, arsenic, PC.
Since it contains harmful substances such as B, trichlorethylene, tetrachloroethylene, organic chlorine, heavy metals such as copper, zinc, and fluoride, it must be treated at a given final disposal site in a strictly regulated manner.

【0003】一方、このような重金属等有害物質含有焼
却灰を直接埋立・海洋投棄することは、危険な処理方法
であって、含有される重金属等の有害物質が溶出し、再
び環境を汚染する二次公害の原因となったり、焼却灰の
形状が不定形あるいは微細な粉末状のため、収集運搬等
の点で取扱いが極めて困難であり、かつ、最終的にこれ
らが処分された埋立地は土質的にも不安定であり、危険
を伴うものである。
On the other hand, direct landfilling or dumping of incineration ash containing such harmful substances as heavy metals is a dangerous treatment method, and harmful substances such as heavy metals contained therein are eluted and pollute the environment again. It is extremely difficult to handle in terms of collection and transportation because it causes secondary pollution and the shape of incineration ash is amorphous or fine powder, and the landfill site where these are finally disposed is The soil is also unstable and dangerous.

【0004】しかし、最終処分場の設置は、用地難や、
不適正処理などによる地域での問題化などの事情により
困難となりつつある。特に大都市圏における最終処分場
の逼迫は著しく、焼却灰も県域を越えて広域移動してい
るのが現状である。
However, installation of the final disposal site is difficult due to land use,
It is becoming difficult due to problems such as improper processing and other problems in the area. In particular, the tightness of final disposal sites in metropolitan areas is severe, and the incineration ash is currently moving over a wide area beyond the prefecture.

【0005】この現状を打開するために、重金属等の有
害物質の無害化、焼却灰の資源化・減量化‐再生利用の
道が模索されている。
[0005] In order to overcome this situation, a method of detoxifying harmful substances such as heavy metals, recycling and reducing the amount of incinerated ash, and recycling it is being sought.

【0006】本発明処理剤は、焼却灰に含有されている
重金属等の有害物質を無害化し、あるいは封じ込めて、
溶出を防止することを目的としたものである。また、こ
れにより、焼却灰の二次利用、再資源化を可能にせんと
するものである。
The treatment agent of the present invention renders harmful substances such as heavy metals contained in incinerated ash harmless or contains them.
The purpose is to prevent elution. In addition, this will enable the secondary use of incinerated ash and recycling.

【0007】[0007]

【課題を解決するための手段】本発明は上記のような問
題点を解決せんとするものであり、その要旨とするとこ
ろは本願特許請求の範囲に記載の通りである。
The present invention is intended to solve the above problems, and the gist thereof is as set forth in the claims of the present application.

【0008】すなわち、本発明焼却灰処理剤は、塩化ナ
トリウム、塩化アンモニウム、炭酸カリウム、塩化コバ
ルト、炭酸ナトリウム、および、ホウ酸又はホウ酸塩、
を特定量含むことを特徴とするものである。
That is, the incineration ash treating agent of the present invention comprises sodium chloride, ammonium chloride, potassium carbonate, cobalt chloride, sodium carbonate, boric acid or borate,
Is included in a specific amount.

【0009】各成分の配合量は、塩化ナトリウム4.0
〜6.0重量%、塩化アンモニウム0.3〜2.0重量
%、炭酸カリウム4.0〜6.5重量%、塩化コバルト
0.1〜0.4重量%、炭酸ナトリウム4.0〜7.0
重量%、ホウ酸(ホウ酸塩の場合はホウ酸換算で)0.
6〜3.0重量%、残部水および不可避不純物、とす
る。
The content of each component is sodium chloride 4.0.
-6.0 wt%, ammonium chloride 0.3-2.0 wt%, potassium carbonate 4.0-6.5 wt%, cobalt chloride 0.1-0.4 wt%, sodium carbonate 4.0-7 .0
% By weight, boric acid (in the case of borate, converted to boric acid) 0.
6 to 3.0% by weight, balance water and unavoidable impurities.

【0010】各成分の配合量の限定理由は、下限未満で
は重金属等の有害物質の無害化、封じ込めが困難とな
り、一方、上限を越えて添加しても効果は変わらず、ま
た、溶解度にも限度があり、多量に添加すると溶解しき
らず濁りとなって残る等の悪影響がでるからである。勿
論、不経済でもある。
The reason for limiting the blending amount of each component is that if it is less than the lower limit, it becomes difficult to render harmful substances such as heavy metals harmless and contain it, while if it exceeds the upper limit, the effect does not change, and the solubility is also increased. This is because there is a limit, and when a large amount is added, adverse effects such as not being completely dissolved and remaining as turbidity occur. Of course, it is uneconomical.

【0011】ホウ酸又はホウ酸塩の添加量(ホウ酸塩の
場合はホウ酸換算での添加量)は全液中0.6重量%以
上3重量%以下存在すればよく、好ましくは0.6〜2
重量%である。あまり多量に添加しても溶解度に限度が
あり、少量だと重金属等の有害物質封じ込めが困難とな
る。
The addition amount of boric acid or borate salt (in the case of borate salt, the addition amount in terms of boric acid) may be 0.6 wt% or more and 3 wt% or less in the total liquid, preferably 0. 6 to 2
% By weight. Even if added in a large amount, the solubility is limited, and in a small amount, it becomes difficult to contain harmful substances such as heavy metals.

【0012】本発明において使用するホウ酸は、オルト
ホウ酸、メタホウ酸、四ホウ酸、酸化ホウ酸などであ
り、いずれも使用できる。また本発明において使用する
ホウ酸塩とは、メタホウ酸塩、オルトホウ酸塩、二ホウ
酸塩、四ホウ酸塩、五ホウ酸塩、六ホウ酸塩、八ホウ酸
塩、の7種のうち一種又は二種以上である。
The boric acid used in the present invention is orthoboric acid, metaboric acid, tetraboric acid, oxidized boric acid, etc., and any of them can be used. The borate used in the present invention includes metaborate, orthoborate, diborate, tetraborate, pentaborate, hexaborate and octaborate among seven types. One or two or more.

【0013】ホウ酸塩は、ホウ酸ナトリウム又はホウ酸
カリウム、又はホウ酸ナトリウムとホウ酸カリウムの混
合物が推奨されるが、四ホウ酸ナトリウム(Na24
7)が特に好ましい。
The preferred borate is sodium or potassium borate, or a mixture of sodium borate and potassium borate, but sodium tetraborate (Na 2 B 4
O 7 ) is particularly preferred.

【0014】[0014]

【実施例】以下本発明実施例を比較例とともに示す。以
下の表1に示す各処方に従って本発明実施例および比較
例処理剤を製造した。各実施例及び比較例の処理液処方
は表1に示す通りである。
EXAMPLES Examples of the present invention will be shown below together with comparative examples. The treatment agents of the examples of the present invention and comparative examples were produced according to the formulations shown in Table 1 below. The treatment liquid formulations of Examples and Comparative Examples are as shown in Table 1.

【0015】[0015]

【表1】 [Table 1]

【0016】次に、下記の割合で、有害物質を含有する
焼却灰に上記各実施例及び比較例処理剤を少量ずつ添加
撹伴しながら常温で10〜15分間混合攪拌して均一に
混合した後、1〜2週間自然乾燥した。こうして得られ
た焼却灰は乾燥した粉末状であった。
Next, the treating agents of the above Examples and Comparative Examples were added little by little to the incineration ash containing harmful substances in the following proportions, and were mixed and stirred at room temperature for 10 to 15 minutes to uniformly mix them. Then, it was naturally dried for 1 to 2 weeks. The incinerated ash thus obtained was in the form of dry powder.

【0017】(処理) 焼却灰 100重量% 処理液 1.8重量% 上記各実施例及び比較例処理剤で処理した上記焼却灰粉
末品と未処理の焼却灰の重金属等の有害物質を溶出分析
した。その結果を表2に示す。表2に明らかなように、
未処理の焼却灰および比較例処理剤で処理した焼却灰で
は、重金属等の有害物質の溶出が認められるのに対し
て、本発明実施例処理剤によって処理した焼却灰は、重
金属等の有害物質の溶出がほとんど認められず、封じ込
め、無害化されたことが分かる。表2の最右欄に、廃棄
物の処理及び清掃に関する法律(表2中では廃棄物処理
法と略記)の規定に基づく判定基準を併記する。
(Treatment) 100% by weight of incinerated ash Treatment liquid 1.8% by weight Elution analysis of harmful substances such as heavy metals in the incinerated ash powder products treated with the treating agents of the above Examples and Comparative Examples and untreated incinerated ash did. The results are shown in Table 2. As is clear from Table 2,
In the untreated incineration ash and the incineration ash treated with the comparative treatment agent, elution of harmful substances such as heavy metals is observed, whereas the incinerated ash treated with the treatment agent of the present invention contains harmful substances such as heavy metals. Almost no elution was observed, indicating that it was contained and rendered harmless. In the rightmost column of Table 2, the judgment criteria based on the provisions of the law on waste treatment and cleaning (abbreviated as Waste Treatment Law in Table 2) are also shown.

【0018】[0018]

【表2】 [Table 2]

【0019】[0019]

【発明の効果】以上のように、本発明によれば、産業廃
棄物、都市ごみ、などの焼却灰中に含まれる重金属等の
有害物質を封じ込め、無害化することができ、よって焼
却灰の処分を容易にすることができ、その産業上の効果
は極めて大なるものである。しかも、焼却灰の無害化に
より、舗設材料としての利用やブロック化などの二次利
用も可能とし、省資源やリサイクルの観点からも有用な
発明である。
Industrial Applicability As described above, according to the present invention, harmful substances such as heavy metals contained in incinerated ash of industrial waste, municipal waste, etc. can be contained and made harmless. Disposal can be facilitated and its industrial effect is extremely large. In addition, since the incinerated ash is made harmless, it can be used as a paving material or can be used for a secondary purpose such as in blocks, which is a useful invention from the viewpoint of resource saving and recycling.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 塩化ナトリウム4.0〜6.0重量
%、塩化アンモニウム0.3〜2.0重量%、炭酸カリ
ウム4.0〜6.5重量%、塩化コバルト0.1〜0.
4重量%、炭酸ナトリウム4.0〜7.0重量%、ホウ
酸0.6〜3.0重量%、残部水および不可避不純物、
より成る重金属等有害物質含有焼却灰処理剤。
1. Sodium chloride 4.0 to 6.0% by weight, ammonium chloride 0.3 to 2.0% by weight, potassium carbonate 4.0 to 6.5% by weight, cobalt chloride 0.1 to 0.
4% by weight, sodium carbonate 4.0 to 7.0% by weight, boric acid 0.6 to 3.0% by weight, balance water and unavoidable impurities,
Incinerator ash treatment agent containing hazardous substances such as heavy metals.
【請求項2】 塩化ナトリウム4.0〜6.0重量
%、塩化アンモニウム0.3〜2.0重量%、炭酸カリ
ウム4.0〜6.5重量%、塩化コバルト0.1〜0.
4重量%、炭酸ナトリウム4.0〜7.0重量%、ホウ
酸塩をホウ酸換算で0.6〜3.0重量%、残部水およ
び不可避不純物、より成る重金属等有害物質含有焼却灰
処理剤。
2. Sodium chloride 4.0 to 6.0% by weight, ammonium chloride 0.3 to 2.0% by weight, potassium carbonate 4.0 to 6.5% by weight, cobalt chloride 0.1 to 0.
4% by weight, sodium carbonate 4.0-7.0% by weight, borate 0.6-3.0% by weight in terms of boric acid, balance water and unavoidable impurities Agent.
【請求項3】 ホウ酸塩が、ホウ酸ナトリウム及び/
又はホウ酸カリウムであることを特徴とする請求項2記
載の重金属等有害物質含有焼却灰処理剤。
3. The borate is sodium borate and / or
Alternatively, it is potassium borate, and the incineration ash treatment agent containing harmful substances such as heavy metals according to claim 2.
JP4058180A 1992-03-16 1992-03-16 Agent for treating incineration ash containing poisonous substance such as heavy metal Pending JPH05253319A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4058180A JPH05253319A (en) 1992-03-16 1992-03-16 Agent for treating incineration ash containing poisonous substance such as heavy metal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4058180A JPH05253319A (en) 1992-03-16 1992-03-16 Agent for treating incineration ash containing poisonous substance such as heavy metal

Publications (1)

Publication Number Publication Date
JPH05253319A true JPH05253319A (en) 1993-10-05

Family

ID=13076813

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4058180A Pending JPH05253319A (en) 1992-03-16 1992-03-16 Agent for treating incineration ash containing poisonous substance such as heavy metal

Country Status (1)

Country Link
JP (1) JPH05253319A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SG106567A1 (en) * 1998-10-16 2004-10-29 Martin Umwelt & Energietech Process for the treatment of combustion residues, in particular slag from waste incineration plants
JP2007268332A (en) * 2006-03-30 2007-10-18 Actree Corp Method for burning heavy metal containing raw material
WO2008003101A1 (en) * 2006-07-04 2008-01-10 Gaston Glock Method for the removal of heavy metals

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SG106567A1 (en) * 1998-10-16 2004-10-29 Martin Umwelt & Energietech Process for the treatment of combustion residues, in particular slag from waste incineration plants
JP2007268332A (en) * 2006-03-30 2007-10-18 Actree Corp Method for burning heavy metal containing raw material
WO2008003101A1 (en) * 2006-07-04 2008-01-10 Gaston Glock Method for the removal of heavy metals

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