JPH10113634A - Solidification treatment of flying ashes - Google Patents

Solidification treatment of flying ashes

Info

Publication number
JPH10113634A
JPH10113634A JP8265973A JP26597396A JPH10113634A JP H10113634 A JPH10113634 A JP H10113634A JP 8265973 A JP8265973 A JP 8265973A JP 26597396 A JP26597396 A JP 26597396A JP H10113634 A JPH10113634 A JP H10113634A
Authority
JP
Japan
Prior art keywords
fly ash
solidification
hydraulic material
flying ashes
acid
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
JP8265973A
Other languages
Japanese (ja)
Inventor
Koichi Nakagawa
公一 中川
Takeshi Mizuta
武 水多
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.)
Chemitech Inc
Original Assignee
Chemitech Inc
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 Chemitech Inc filed Critical Chemitech Inc
Priority to JP8265973A priority Critical patent/JPH10113634A/en
Publication of JPH10113634A publication Critical patent/JPH10113634A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To prevent the elution of harmful materials, such as heavy metals by treating flying ashes with a mineral acid or acidic salt, then subjecting the flying ashes to a solidification treatment by making combination use of a hydraulic material and a solidification assistant. SOLUTION: The flying ashes and the mineral acid or the acidic salt are mixed by a mixer, etc., to lower the alkalinity thereof. The hydraulic material and the solidification assistant are then added thereto simultaneously or in this order to solidify the flying ashes. For example, about 85% phosphoric acid is added at about 2 pts.wt. to about 100 pts.wt. flying ashes recovered by a dust collector of municipal waste incineration plants and the flying ashes are mixed, by which the pH thereof is lowered by about 0.5 to 2. Ordinary Portland cement is added as the hydraulic material thereto at about 3 to 30 pts.wt. and higher fatty acid salt, etc., such as zinc steerage, are added as the solidification assistant thereto at about 0.5 to 5 pts.wt. to solidify the flying ashes. The solidified molding is cured to form the solidified matter. The pH elution amt. of the solidified matter attains a value smaller than an elution reference value of 0.3mg/l and the elution of the harmful materials, such as heavy metals, is prevented.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、都市ごみや下水汚
泥等の焼却炉など、あるいはそれらの焼却灰の溶融固化
炉などから排出され、鉛、カドミウム等の有害物質を含
有する飛灰の固化処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the solidification of fly ash containing harmful substances such as lead and cadmium discharged from incinerators for municipal solid waste and sewage sludge or the like, or for melting and solidifying such incineration ash. Regarding the processing method.

【0002】[0002]

【従来の技術】産業廃棄物の処理及び清掃に関する法律
が制定され、産業廃棄物について厳しい規制が定められ
ている。廃棄業者はこの規制に適合したものでなければ
廃棄処分ができない。例えば、重金属等を含む産業廃棄
物は、溶出試験を行い、水銀、カドミウム、鉛、6価ク
ロム等が規制値以下でなければ、埋立処分をしたり、最
終処分場に廃棄することが禁止されている。
2. Description of the Related Art Laws concerning the treatment and cleaning of industrial waste have been enacted, and strict regulations have been set for industrial waste. Disposers cannot dispose of them unless they comply with these regulations. For example, for industrial waste containing heavy metals, etc., a leach test is performed, and if mercury, cadmium, lead, hexavalent chromium, etc. are not below the regulated value, it is prohibited to landfill or dispose of it at the final disposal site. ing.

【0003】都市ごみ、下水汚泥等の焼却炉、溶融炉な
どやあるいはこれらの焼却灰の溶融固化炉などに設置さ
れるバグフィルター、電気集塵機等の集塵装置で捕集さ
れる飛灰(フライアッシュ)には、重金属等の有害物質
が含まれ、なんらかの処理をしなければ、このまま廃棄
などの処分をすることができない。特に、飛灰はカドミ
ウム、鉛、亜鉛等の低融点の金属類や塩類を含有し、溶
出試験における溶出値もきわめて高く、特別管理廃棄物
に該当する。
[0003] Fly ash (fly) collected by a dust filter such as an incinerator or a melting furnace for municipal solid waste or sewage sludge, or a melting and solidifying furnace for these incinerated ash, and an electric dust collector. Ash) contains harmful substances such as heavy metals, and cannot be disposed of as it is without any treatment. In particular, fly ash contains metals and salts with low melting points such as cadmium, lead, and zinc, and has extremely high dissolution values in dissolution tests, and falls under specially controlled waste.

【0004】また、都市ゴミや下水汚泥等を焼却炉等で
焼却又は溶融する際に、これらに含有される塩素化合物
に起因する塩化水素やイオウ化合物に起因するイオウ酸
化物等の酸性物質が発生する。そのため、ゴミなどの焼
却の際に、石灰等のアルカリ性物質を混合して酸性物質
の発生を抑制したり、飛灰を回収する集塵機に消石灰や
カセイソーダ等のアルカリ性物質を投入して、これらの
大気への放散を抑えるなどの対策が講じられている。そ
れゆえ、回収された飛灰は、きわめて強アルカリ性を呈
し、アルカリ性廃棄物に該当する。
When municipal garbage or sewage sludge is incinerated or melted in an incinerator or the like, acidic substances such as hydrogen chloride caused by chlorine compounds and sulfur oxides caused by sulfur compounds contained therein are generated. I do. For this reason, when incinerating garbage, etc., alkaline substances such as lime are mixed to suppress the generation of acidic substances, or alkaline substances such as slaked lime and caustic soda are introduced into a dust collector that collects fly ash, and these air Measures have been taken, such as suppressing emissions to the public. Therefore, the collected fly ash exhibits extremely strong alkalinity and corresponds to alkaline waste.

【0005】かかる飛灰の処理技術としては、例えば、
セメント等の水硬性材料による固化処理、アスファルト
による固化処理やプラスチックによる固化処理のほか
に、焼却炉等の排ガスで中和して炭酸塩化処理したり、
酸抽出した後硫化物として固定化したり、液体キレート
等の重金属固定化剤で安定化する方法などが提案されて
いる。しかしながら、これらの従来の処理技術では、溶
出試験の規制値に完全に適合するものは少ない。特に、
可溶性の重金属等を多量に含有する飛灰は、セメント等
の固化処理を施しても、溶出試験に適合しないことが多
く、固化処理しただけでは最終処分することができな
い。また、飛灰の強いアルカリ性のため、セメント等の
水硬性材料による固化処理に障害をきたしている。この
強アルカリを酸で中和するしても、多量の酸を必要と
し、処理コストの増大を招いている。
As a technique for treating such fly ash, for example,
In addition to solidification treatment with hydraulic material such as cement, solidification treatment with asphalt and solidification treatment with plastic, neutralization with exhaust gas from incinerators etc.
A method has been proposed in which acid extraction is followed by immobilization as a sulfide or stabilization with a heavy metal immobilizing agent such as a liquid chelate. However, few of these conventional processing technologies completely comply with the regulation values of the dissolution test. Especially,
Fly ash containing a large amount of soluble heavy metals and the like often does not conform to the dissolution test even after solidification of cement or the like, and cannot be finally disposed of only by solidification. Further, the strong alkalinity of fly ash hinders solidification treatment with a hydraulic material such as cement. Even if this strong alkali is neutralized with an acid, a large amount of acid is required, resulting in an increase in processing cost.

【0006】最近、固化物をより長期的に安定化するた
めに、飛灰をあらかじめ何らかの前処理をした後に固化
する方法が検討されている。例えば、飛灰を酸で洗浄し
て洗浄液に塩類や重金属等を移行させる方法や、飛灰を
過熱して重金属等を再度揮発させる方法や、飛灰に含有
される重金属等を化学薬品で固定してそれらの溶出を抑
制する方法などがある。しかしながら、酸洗浄方式で
は、当然、重金属等を含む廃酸や汚泥が発生し、これら
の処理が新たな問題となる。また、過熱方式では、有害
物質を含む過熱排ガスの処理の問題が残る。さらに、薬
品固定方式では、幅広いpHで効果があるものや、有害
ガスを発生しないとか、廃棄物を三分の一に減容できる
などの効能をうたうものもあるが、きわめて高価なため
実用性に乏しい。
[0006] Recently, in order to stabilize the solidified material for a longer period of time, a method of solidifying fly ash after performing some pretreatment in advance has been studied. For example, a method of washing fly ash with acid to transfer salts and heavy metals to the cleaning solution, a method of overheating fly ash to re-evaporate heavy metals, and a method of fixing heavy metals contained in fly ash with chemicals And the method of suppressing their dissolution. However, in the acid washing method, naturally, waste acid and sludge containing heavy metals and the like are generated, and these treatments become a new problem. Further, in the superheating method, there remains a problem of treating superheated exhaust gas containing harmful substances. In addition, the chemical fixation method is effective at a wide range of pH, does not generate harmful gas, and has the effect of reducing the volume of waste to one third, but is extremely expensive and practical. Poor.

【0007】[0007]

【発明が解決しようとする課題】したがって、本発明の
目的は、飛灰を水硬性材料で固化処理して、重金属等の
有害物質を固化物に封じ込め、それらの溶出を抑えるこ
とができる方法を提供することにある。
SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide a method for solidifying fly ash with a hydraulic material to seal harmful substances such as heavy metals in the solidified material and to suppress their elution. To provide.

【0008】[0008]

【課題を解決するための手段】本発明者らは、かかる問
題点を解決すべく鋭意検討を重ねた結果、まず飛灰を鉱
酸等で処理し、ついで水硬性材料と固化助剤とを併用し
て固化助処理することによって、固化物に重金属等を封
じ込め、それらの溶出が抑えられることを見出し、本発
明を完成した。
Means for Solving the Problems The inventors of the present invention have made intensive studies to solve such problems, and as a result, firstly treated fly ash with a mineral acid or the like, and then separated the hydraulic material and the solidification aid. The present inventors have found that heavy metals and the like are contained in the solidified product and the elution thereof is suppressed by performing the solidification assisting treatment in combination, and the present invention has been completed.

【0009】すなわち、本発明は、都市ゴミ、下水汚泥
等の焼却炉等から排出され、有害物質を含有するアルカ
リ性の飛灰を水硬性材料で固化処理する方法において、
飛灰を鉱酸又はその酸性塩で処理した後、水硬性材料と
固化助剤を併用して固化処理することを特徴とする飛灰
の固化処理方法である。
That is, the present invention relates to a method of solidifying alkaline fly ash discharged from an incinerator or the like of municipal waste and sewage sludge and containing harmful substances with a hydraulic material,
This is a method for solidifying fly ash, comprising treating fly ash with a mineral acid or an acid salt thereof, and then solidifying using a hydraulic material and a solidification aid.

【0010】以下、本発明の固化処理方法について詳細
に説明する。本発明の固化処理方法を適用できる飛灰と
しては、都市ごみや下水汚泥等の焼却炉や溶融炉などに
設置される、バグフィルター、電気集塵機等の集塵装置
で捕集される飛灰(フライアッシュ)があげられる。ま
た、これらの焼却灰等を減容するための溶融固化炉等に
設置される、バグフィルター、電気集塵機等の集塵装置
で捕集される飛灰も本発明により処理可能である。その
他、各種の産業廃棄物等の焼却炉などから排出され、重
金属等の有害物質を含むものも本発明により処理可能で
ある。そして、この飛灰は、塩化水素やイオウ酸化物な
どの大気への放散を抑えるために、排ガス中の酸性物質
の2〜3倍当のアルカリ性物質が添加されるので、p
H12を超える強アルカリ性を呈する。
Hereinafter, the solidification treatment method of the present invention will be described in detail. As fly ash to which the solidification treatment method of the present invention can be applied, fly ash collected by a dust collector such as a bag filter or an electric dust collector installed in an incinerator or a melting furnace of municipal waste or sewage sludge or the like. Fly ash). Further, fly ash collected by a dust collecting device such as a bag filter or an electric dust collector installed in a melting and solidifying furnace for reducing the volume of the incinerated ash and the like can be treated by the present invention. In addition, those discharged from incinerators of various industrial wastes and the like and containing harmful substances such as heavy metals can be treated by the present invention. The fly ash is added with an alkaline substance in an amount equivalent to 2 to 3 times the amount of the acidic substance in the exhaust gas in order to suppress the emission of hydrogen chloride and sulfur oxides into the atmosphere.
It exhibits strong alkalinity exceeding H12.

【0011】本発明では、この強アルカリ性の飛灰を、
まず、鉱酸又はその酸性塩で処理する。この処理に使用
される鉱酸としては、例えば硫酸、塩酸、リン酸などが
あげられる。飛灰のアルカリ性成分が消石灰である場合
は、消石灰と反応して不溶性化合物を形成する硫酸やリ
ン酸が好ましい。
In the present invention, this strongly alkaline fly ash is
First, it is treated with a mineral acid or an acid salt thereof. Mineral acids used in this treatment include, for example, sulfuric acid, hydrochloric acid, phosphoric acid and the like. When the alkaline component of fly ash is slaked lime, sulfuric acid or phosphoric acid which reacts with slaked lime to form an insoluble compound is preferred.

【0012】また、鉱酸の酸性塩としては、例えば硫酸
鉄、硫酸アルミニウム、みょうばん、塩化鉄、塩化アル
ミニウム、リン酸鉄、リン酸アルミニウム、リン酸一水
素カルシウム、リン酸二水素カルシウムなどがあげられ
る。この酸性塩は、当然のことながら、それ自体有害物
質であってはならず、またセメント等の水硬性材料の水
和反応を阻害するものであってはならない。特に、硫酸
第一鉄等の還元性酸性塩を飛灰の処理に使用すると、飛
灰の中和剤である石灰と反応して安定なせっこうを生成
するとともに、飛灰に少量含まれることのある有害物質
であるCr6+を還元し、無害なクロム化合物に変えるこ
とができ、また低廉な化合物であるので処理費用の低減
に役立つ。
Examples of the acid salts of mineral acids include iron sulfate, aluminum sulfate, alum, iron chloride, aluminum chloride, iron phosphate, aluminum phosphate, calcium monohydrogen phosphate, calcium dihydrogen phosphate, and the like. Can be The acid salt must not, of course, be a harmful substance itself, nor should it inhibit the hydration of hydraulic materials such as cement. In particular, when reducing acid salts such as ferrous sulfate are used for fly ash treatment, they react with lime, which is a neutralizing agent for fly ash, to produce stable gypsum and be contained in small amounts in fly ash. Cr 6+ , which is a harmful substance, can be reduced and converted to a harmless chromium compound, and since it is an inexpensive compound, it is useful for reducing processing costs.

【0013】この処理は、含水状態の飛灰に鉱酸又はそ
の酸性塩を添加し、ミキサーなどで混合することにより
行うことができる。鉱酸又はその酸性塩の添加量は、飛
灰(乾燥重量基準)100重量部に対し0.5〜20重
量部、好ましくは1〜5重量部である。鉱酸又はその弱
塩基塩の添加によって、飛灰のpHを0.5〜2程度下
げればよい。もちろん、鉱酸等の添加量を増やしてpH
を更に下げることもできるが、処理コストの増加を招く
ので好ましくない。
This treatment can be carried out by adding a mineral acid or an acid salt thereof to the water-containing fly ash and mixing with a mixer or the like. The amount of the mineral acid or acid salt thereof added is 0.5 to 20 parts by weight, preferably 1 to 5 parts by weight, per 100 parts by weight of fly ash (based on dry weight). The pH of fly ash may be lowered by about 0.5 to 2 by adding a mineral acid or a weak base salt thereof. Of course, the amount of mineral acid
Can be further reduced, but this is not preferable because it increases the processing cost.

【0014】ついで、鉱酸又はその弱塩基塩で処理した
飛灰を、水硬性材料と固化助剤を併用して固化処理す
る。このような水硬性材料としては、ポルトランドセメ
ント、早強ポルトランドセメント、超早強ポルトランド
セメント、中庸熱ポルトランドセメント等の各種ポルト
ランドセメントのほか、高炉セメント、フラィアッシュ
セメント等の混合セメントがあげられる。また、地盤改
良材として市販されている、セメントに高炉スラグ、石
灰、石こうなど配合したセメント系の特殊な水硬性材料
も効果がある。
Next, the fly ash treated with a mineral acid or a weak base salt thereof is solidified using a hydraulic material and a solidification aid in combination. Examples of such hydraulic materials include various portland cements such as portland cement, early-strength portland cement, ultra-high-strength portland cement, and moderately heated portland cement, as well as mixed cements such as blast furnace cement and fly ash cement. In addition, a cement-based special hydraulic material which is commercially available as a ground improvement material and is mixed with cement, such as blast furnace slag, lime, and gypsum, is also effective.

【0015】また、本発明の固化処理方法で使用される
固化助剤には、水硬性材料との併用によって、有害物質
の固化を促進し、固化物の強度を増進し、高密度の固化
物をつくるなど物理的効能をもち、あわせて、有害物質
中の重金属と不溶性錯体を形成し、汚染物質等と分子結
合効果など化学的効能をもつものが望ましい。
The solidification aid used in the solidification treatment method of the present invention, when used in combination with a hydraulic material, promotes the solidification of harmful substances, increases the strength of the solidified material, and increases the density of the solidified material. It is desirable to have a physical effect such as the formation of a compound, form an insoluble complex with heavy metals in harmful substances, and have a chemical effect such as a molecular bonding effect with pollutants and the like.

【0016】このような固化助剤としては、高級脂肪酸
金属塩及び有機アミノ化合物を主剤とし、そのほかpH
調整剤、分散剤、凝集剤などを配合したものが好まし
い。高級脂肪酸金属塩は、重金属と結合して不溶性錯体
を形成するだけでなく、固化物から汚染物質の溶出を防
止するものである。また、有機アミノ化合物は水和反応
を促進すると共に不溶性錯体の形成によって有害物質を
不溶化するのに役立つものである。
[0016] Such a solidification aid mainly comprises a metal salt of a higher fatty acid and an organic amino compound.
Those containing a regulator, a dispersant, a flocculant and the like are preferred. The higher fatty acid metal salt not only combines with the heavy metal to form an insoluble complex, but also prevents elution of contaminants from the solidified material. In addition, the organic amino compound promotes the hydration reaction and helps to insolubilize harmful substances by forming an insoluble complex.

【0017】本発明の固化処理方法において、通常、飛
灰に対する水硬性材料と固化助剤の配合割合は、飛灰1
00重量部(乾燥重量基準)に対し、水硬性材料が5〜
30重量部、固化助剤が0.5〜5重量部程度である。
水硬性材料が5重量部より少ないと飛灰を固化させるの
に支障を来し、30重量部を超えると経済性が低下す
る。また、固化助剤が0.5重量部より少ないと溶出濃
度の低減効果が小さく、5重量部を超えても効果が増加
しない。
In the solidification method of the present invention, the mixing ratio of the hydraulic material and the solidification aid to the fly ash is usually 1
Hydraulic material is 5 to 00 parts by weight (dry weight basis)
30 parts by weight, and the amount of the solidification aid is about 0.5 to 5 parts by weight.
If the hydraulic material is less than 5 parts by weight, it will hinder the solidification of fly ash, and if it exceeds 30 parts by weight, the economic efficiency will be reduced. If the amount of the solidification aid is less than 0.5 part by weight, the effect of reducing the elution concentration is small, and if it exceeds 5 parts by weight, the effect does not increase.

【0018】本発明の固化処理方法において、飛灰に対
する水硬性材料及び固化助剤の好ましい配合割合は、飛
灰100重量部(乾燥重量基準)に対し、水硬性材料が
10〜25重量部、固化助剤が1.5〜3重量部であ
る。
In the solidification treatment method of the present invention, a preferable mixing ratio of the hydraulic material and the solidification aid to the fly ash is 10 to 25 parts by weight of the hydraulic material with respect to 100 parts by weight of the fly ash (dry weight basis). The solidification aid is 1.5 to 3 parts by weight.

【0019】そして、主材の水硬性材料に併用される固
化助剤は、その配合目的を達成する有効量であればよい
が、飛灰に含有される重金属の種類や量によって、上記
の配合割合の範囲内で両者の配合割合を適宜変えること
がよい。
The solidification aid used in combination with the main hydraulic material may be any effective amount for achieving its compounding purpose, but depending on the type and amount of heavy metal contained in the fly ash, It is preferable to appropriately change the mixing ratio of the two within the range of the ratio.

【0020】[0020]

【発明の実施の形態】本発明方法によって飛灰の固化処
理を行うには、まず飛灰と鉱酸又はその酸性塩をミキサ
ー等で混合してアルカリ性を低下させる処理を行ったあ
と、水硬性材料と固化助剤を同時に添加して混合しても
よいし、あるいは飛灰にこれらを順次混合してもよい。
BEST MODE FOR CARRYING OUT THE INVENTION In order to solidify fly ash by the method of the present invention, first, a fly ash and a mineral acid or an acid salt thereof are mixed with a mixer or the like to reduce alkalinity, and then the hydraulic ash is hardened. The material and the solidification aid may be added and mixed simultaneously, or they may be sequentially mixed with fly ash.

【0021】[0021]

【実施例】以下、実施例及び比較例によって本発明を説
明するが、本発明はこれらによってなんら制限を受ける
ものではない。
The present invention will be described below with reference to examples and comparative examples, but the present invention is not limited by these examples.

【0022】実施例1、2及び比較例1、2 都市ゴミ焼却場の集塵装置(電気集塵機)で回収された
飛灰を、次の処方によって固化処理試験を行った。この
飛灰のpHは12.5であり、含水率は2.1重量%、
Pb含有量は2730mg/kgであった。
Examples 1 and 2 and Comparative Examples 1 and 2 Fly ash collected by a dust collector (electric dust collector) at a municipal waste incineration plant was subjected to a solidification test according to the following formulation. The fly ash had a pH of 12.5, a moisture content of 2.1% by weight,
The Pb content was 2730 mg / kg.

【0023】この飛灰100重量部にリン酸(85%)
を2重量部添加してミキサーで混合したところ、飛灰の
pHは12に低下した。実施例1と2ではこのリン酸処
理飛灰を、比較例1と2では未処理の飛灰をそれぞれ固
化処理した。
Phosphoric acid (85%) is added to 100 parts by weight of the fly ash.
Was added and mixed with a mixer, and the pH of the fly ash was reduced to 12. The phosphoric acid-treated fly ash was solidified in Examples 1 and 2, and the untreated fly ash was solidified in Comparative Examples 1 and 2.

【0024】水硬性材料として普通ポルトランドセメン
ト(以下、セメントという)を、固化助剤として日本ケ
ミタック株式会社のゲオドール(商標)を使用した。ゲ
オドールはステアリン酸亜鉛等の高級脂肪酸塩、エタノ
ールアミン等の有機アミノ化合物、界面活性剤等をアン
モニア性水溶液に分散溶解させたものであり、市販原液
を20倍に希釈して使用した。
As a hydraulic material, ordinary Portland cement (hereinafter, referred to as cement) was used, and as a solidification aid, Geodol (trademark) of Nippon Chemi-Tac Corporation was used. Geodol is obtained by dispersing and dissolving a higher fatty acid salt such as zinc stearate, an organic amino compound such as ethanolamine, a surfactant and the like in an aqueous ammonia solution, and diluting a commercially available stock solution 20-fold.

【0025】上記の飛灰に所定量の水を加えて十分に混
練した後、セメントと固化助剤を加えて更に混練して、
その混練物を4×4×16cmの金属製の型枠に打ち込
み成型した。1日後成型物を型枠からはずし、約4週間
常温の室内で養生して固化物を調製した。
After a predetermined amount of water is added to the above fly ash and sufficiently kneaded, cement and a solidification aid are added and further kneaded.
The kneaded material was cast into a 4 × 4 × 16 cm metal mold. One day later, the molded product was removed from the mold and cured in a room at room temperature for about 4 weeks to prepare a solidified product.

【0026】次に、これらの固化物について、重金属の
溶出試験を行い、鉛(Pb)の含有量を測定した。溶出
試験は、環境庁告示第13号(S48.2.17)に基
づいて行った。なお、最新の溶出基準は、Pbが0.3
mg/lである。各成分の配合割合と固化物の溶出試験
結果を表1に掲げる。表1において、飛灰は乾燥重量基
準であり、水は混練水と飛灰中の水分の合計でもって表
されている。Pb含有量は溶出液1リットル当たりのm
gで表されている。
Next, the solidified product was subjected to a heavy metal dissolution test to measure the content of lead (Pb). The dissolution test was performed based on the notification of the Environment Agency No. 13 (S4.2.17). The latest elution standard is Pb of 0.3
mg / l. Table 1 shows the mixing ratio of each component and the results of the dissolution test of the solidified product. In Table 1, fly ash is on a dry weight basis, and water is represented by the sum of kneading water and water in the fly ash. The Pb content is m per liter of eluate.
It is represented by g.

【0027】[0027]

【表1】 [Table 1]

【0028】実施例3、4及び比較例3 都市ゴミ焼却場の集塵装置(バグフィルター)で回収さ
れた飛灰を、上記と同様な処方によって固化処理試験を
行った。この飛灰のpHは12.5であり、含水率は
0.4重量%、Pb含有量は1570mg/kgであっ
た。得られた固化物及び未処理飛灰について、同様に重
金属の溶出試験を行い、鉛(Pb)の含有量を測定し
た。各成分の配合割合とリン酸処理後のpH及び固化物
の溶出試験結果を表2に掲げる。表2において、飛灰は
乾燥重量基準であり、水は混練水と飛灰中の水分の合計
で以て表されている。Pb含有量は溶出液1リットル当
たりのmgで表されている。
Examples 3, 4 and Comparative Example 3 Fly ash collected by a dust collector (bag filter) at an incineration plant for municipal garbage was subjected to a solidification test according to the same recipe as above. The fly ash had a pH of 12.5, a water content of 0.4% by weight, and a Pb content of 1570 mg / kg. The obtained solidified material and untreated fly ash were similarly subjected to a heavy metal elution test to measure the content of lead (Pb). Table 2 shows the mixing ratio of each component, the pH after the phosphoric acid treatment, and the dissolution test result of the solidified product. In Table 2, fly ash is on a dry weight basis, and water is represented by the sum of kneading water and water in fly ash. The Pb content is expressed in mg per liter of eluate.

【0029】[0029]

【表2】 [Table 2]

【0030】[0030]

【発明の効果】本発明は、重金属等特に鉛で汚染された
飛灰を水硬性材料で固化処理する方法において、まず飛
灰を鉱酸又はその酸性塩で処理し、ついで水硬性材料と
固化助剤を併用して固化処理することによって、従来の
処理技術では困難であった重金属等の溶出試験の規制値
を満たすことができ、しかも処理コストも低廉である。
According to the present invention, there is provided a method for solidifying fly ash contaminated with heavy metals or the like, particularly lead, with a hydraulic material. First, the fly ash is treated with a mineral acid or an acid salt thereof, and then solidified with the hydraulic material. By performing the solidification treatment in combination with an auxiliary agent, it is possible to satisfy the regulation value of the elution test for heavy metals and the like, which was difficult with the conventional treatment technology, and the treatment cost is low.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 都市ゴミ、下水汚泥等の焼却炉等から排
出され、有害物質を含有するアルカリ性の飛灰を水硬性
材料で固化処理する方法において、飛灰を鉱酸又はその
酸性塩で処理した後、水硬性材料と固化助剤を併用して
固化処理することを特徴とする飛灰の固化処理方法。
1. A method of solidifying alkaline fly ash containing harmful substances discharged from an incinerator of municipal waste and sewage sludge with a hydraulic material, wherein the fly ash is treated with a mineral acid or an acid salt thereof. And then solidifying using a hydraulic material and a solidification aid in combination.
【請求項2】 飛灰の鉱酸又はその酸性塩による処理に
よって、飛灰のpHを0.5〜2程度下げる請求項1記
載の飛灰の固化処理方法。
2. The method for solidifying fly ash according to claim 1, wherein the pH of the fly ash is lowered by about 0.5 to 2 by treating the fly ash with a mineral acid or an acid salt thereof.
【請求項3】 固化助剤が、高級脂肪酸金属塩及び有機
アミノ化合物を含んでなる請求項1又は請求項2記載の
飛灰の固化処理方法。
3. The method for solidifying fly ash according to claim 1, wherein the solidification aid comprises a metal salt of a higher fatty acid and an organic amino compound.
【請求項4】 飛灰に対する水硬性材料及び固化助剤の
配合割合は、飛灰100重量部(乾燥重量基準)に対
し、水硬性材料が5〜30重量部、固化助剤が0.5〜
5重量部である請求項1ないし請求項3のいずれかに記
載の飛灰の固化処理方法。
4. The mixing ratio of the hydraulic material and the solidification aid to the fly ash is 5 to 30 parts by weight of the hydraulic material and 0.5 to 0.5 parts by weight of the solidification aid with respect to 100 parts by weight of the fly ash (dry weight basis). ~
The method for solidifying fly ash according to any one of claims 1 to 3, wherein the amount is 5 parts by weight.
JP8265973A 1996-10-07 1996-10-07 Solidification treatment of flying ashes Pending JPH10113634A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8265973A JPH10113634A (en) 1996-10-07 1996-10-07 Solidification treatment of flying ashes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8265973A JPH10113634A (en) 1996-10-07 1996-10-07 Solidification treatment of flying ashes

Publications (1)

Publication Number Publication Date
JPH10113634A true JPH10113634A (en) 1998-05-06

Family

ID=17424614

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8265973A Pending JPH10113634A (en) 1996-10-07 1996-10-07 Solidification treatment of flying ashes

Country Status (1)

Country Link
JP (1) JPH10113634A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002136944A (en) * 2000-11-06 2002-05-14 Hitachi Zosen Corp Method for fixing heavy metal contained in ash and fixing agent
JP2006218373A (en) * 2005-02-09 2006-08-24 Miyoshi Oil & Fat Co Ltd Solid waste disposal agent and treatment method of solid waste
JP2008272580A (en) * 2007-02-09 2008-11-13 Jikco Ltd Treatment method for heavy metals in waste ash
JP2009078197A (en) * 2007-09-25 2009-04-16 Kurita Water Ind Ltd Heavy metal fixing agent and ash treatment method using it
JP2020000968A (en) * 2018-06-26 2020-01-09 花王株式会社 Method of treating combustion ash

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002136944A (en) * 2000-11-06 2002-05-14 Hitachi Zosen Corp Method for fixing heavy metal contained in ash and fixing agent
JP2006218373A (en) * 2005-02-09 2006-08-24 Miyoshi Oil & Fat Co Ltd Solid waste disposal agent and treatment method of solid waste
JP2008272580A (en) * 2007-02-09 2008-11-13 Jikco Ltd Treatment method for heavy metals in waste ash
JP2009078197A (en) * 2007-09-25 2009-04-16 Kurita Water Ind Ltd Heavy metal fixing agent and ash treatment method using it
JP2020000968A (en) * 2018-06-26 2020-01-09 花王株式会社 Method of treating combustion ash

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