JPH0947740A - Method for restraining lead in fly ash from being eluted and lead elution inhibitor - Google Patents

Method for restraining lead in fly ash from being eluted and lead elution inhibitor

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Publication number
JPH0947740A
JPH0947740A JP7221030A JP22103095A JPH0947740A JP H0947740 A JPH0947740 A JP H0947740A JP 7221030 A JP7221030 A JP 7221030A JP 22103095 A JP22103095 A JP 22103095A JP H0947740 A JPH0947740 A JP H0947740A
Authority
JP
Japan
Prior art keywords
fly ash
lead
aluminum hydroxide
amorphous aluminum
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.)
Pending
Application number
JP7221030A
Other languages
Japanese (ja)
Inventor
Yasuo Shimanaka
康雄 島中
Akira Uehara
明 上原
Hideaki Nagasawa
秀秋 永沢
Hiroyuki Iwaki
宏行 岩城
Masao Arizono
正男 有園
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.)
Fujisash Co Ltd
Original Assignee
Fujisash 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 Fujisash Co Ltd filed Critical Fujisash Co Ltd
Priority to JP7221030A priority Critical patent/JPH0947740A/en
Publication of JPH0947740A publication Critical patent/JPH0947740A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To surely restrain lead in fly ash of municipal refuse incineration from being eluted by adding amorphous aluminum hydroxide to the fly ash of municipal refuse incineration and kneading it with water to solidify it. SOLUTION: Amorphous aluminum hydroxide is added to fly ash of municipal refuse incineration and is kneaded with water to restrain lead in the fly ash from being eluted. Here the added quantity of amorphous aluminum hydroxide is made 3-50 pts.wt. to 100 pts.wt. of the fly ash. In addition to amorphous aluminum hydroxide, ferrous sulfate and/or thiourea is further added. The fly ash is made electric precipitator ash or bag filter ash of 10-30wt.% calcium content of a stoker furnace or a fluidization roaster. In this way, the elution of lead in ash of municipal refuse incineration is surely and economically restrained.

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、都市ごみ焼却飛灰
中の鉛の溶出を抑制する方法及び鉛溶出抑制剤に関す
る。
TECHNICAL FIELD The present invention relates to a method for suppressing the elution of lead in municipal waste incineration fly ash and a lead elution suppressor.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】都市ご
みは、通常機械炉(ストーカー炉)や流動床炉で焼却さ
れるが、その時発生する廃ガスは電気集塵機やバグフィ
ルターで処理されて廃ガス中に含まれる固形微粒子が除
去される。この固形微粒子、即ち都市ごみ焼却飛灰は重
金属を含んでおり、このためその処理が問題になる。従
来このような飛灰中の重金属安定化処理として、セメン
ト固化処理法や液体キレート剤を使用する薬剤処理法を
採用する場合が多い。
2. Description of the Related Art Municipal solid waste is usually incinerated in a mechanical furnace (stalker furnace) or a fluidized bed furnace, but the waste gas generated at that time is treated by an electric dust collector or a bag filter and is discarded. The solid fine particles contained in the gas are removed. The solid fine particles, that is, the incineration fly ash of municipal solid waste, contains heavy metals, which makes its treatment a problem. Conventionally, a cement solidification method or a chemical treatment method using a liquid chelating agent is often employed as the heavy metal stabilization treatment in such fly ash.

【0003】一般に、飛灰で問題となる重金属は主に鉛
であるが、従来の方法では、飛灰の性状によっては鉛の
溶出量を基準値である0.3mg/l以下にすることが
困難なケースが多い。
Generally, the heavy metal which is a problem in fly ash is mainly lead, but in the conventional method, the elution amount of lead may be set to a reference value of 0.3 mg / l or less depending on the properties of fly ash. There are many difficult cases.

【0004】特に、上記廃ガスには、これに含まれるH
Clガスの排出を抑制するため、消石灰等のカルシウム
化合物を粉体(乾式)又はスラリー状態(半乾式)で吹
き込むことが行なわれているが、地域等の状況によりH
Clの規制値も異なり、カルシウム化合物の吹き込み量
が多い所、少ない所がある。これを電気集塵機やバグフ
ィルターで捕集するので、飛灰中のカルシウム含有量は
約10%から35%と大きな幅がある。この場合、例え
ばカルシウム含有量が25%以下の飛灰はpH12以上
を示すが、アルカリ分が比較的少ないことからpHが変
動し易い不安定な状況にある。このため、セメントや液
体キレート剤による重金属溶出抑制効果が経済的な添加
量では期待できない場合が多い。これは、セメントも液
体キレート剤もそれ自体pHが高く、そのため飛灰処理
物のpHが更に高くなり、両性金属である鉛の溶解度が
高くなり、この作用が重金属抑制効果より強く影響する
ためと推定される。
Particularly, the above-mentioned waste gas contains H contained therein.
In order to suppress the emission of Cl gas, calcium compounds such as slaked lime are blown in powder (dry type) or slurry state (semi-dry type).
The regulation value of Cl is also different, and there are places where the amount of calcium compound blown in is large and places where it is small. Since this is collected by an electrostatic precipitator or a bag filter, the calcium content in the fly ash has a wide range of about 10% to 35%. In this case, for example, fly ash having a calcium content of 25% or less has a pH of 12 or more, but since the alkali content is relatively small, the pH is unstable and unstable. Therefore, the effect of suppressing the elution of heavy metals by cement and liquid chelating agents cannot often be expected with an economical addition amount. This is because both the cement and the liquid chelating agent have high pH themselves, so that the pH of the fly ash treated product becomes higher and the solubility of lead, which is an amphoteric metal, becomes higher, and this action has a stronger influence than the heavy metal suppressing effect. Presumed.

【0005】即ち、カルシウム含有量が20%程度の電
気集塵機で捕集された飛灰(EP灰)やバグフィルター
で捕集された飛灰(BF灰)の中で、鉛含有量5,00
0mg/kg、鉛溶出量200mg/lを示すものがあ
るが、このような飛灰に対し鉛溶出の基準値である0.
3mg/l以下を満足させることはセメントや液体キレ
ート剤をその通常量用いただけでは困難であり、これを
満足させるためにはかなりの多量を必要とし、しかもこ
のように多量を用いても確実に基準値を満足させるとは
限らない。
That is, in the fly ash (EP ash) collected by the electrostatic precipitator having a calcium content of about 20% and the fly ash (BF ash) collected by the bag filter, the lead content is 5,00.
There are some which show 0 mg / kg and a lead elution amount of 200 mg / l, but a lead elution standard value of 0.
Satisfying 3 mg / l or less is difficult only by using the usual amount of cement or liquid chelating agent, and a considerably large amount is required to satisfy this, and even if such a large amount is used, it is certain It does not always satisfy the standard value.

【0006】また、このような飛灰に対し、液体硫酸ア
ルミニウム等の液体系酸性材料を用いてpHを10程度
に低下させた後、液体キレート剤を添加することも考え
られるが、この方法は必要とする液体硫酸アルミニウム
の添加量が多量となり、更に混練物の強度発現が低く、
ハンドリング性に問題がある等の難点を有し、実用的で
はない。
It is also conceivable that the pH of the fly ash is lowered to about 10 using a liquid acidic material such as liquid aluminum sulfate, and then a liquid chelating agent is added. The required addition amount of liquid aluminum sulfate is large, and the strength development of the kneaded product is low,
It is not practical because it has problems such as handling problems.

【0007】本発明は上記事情に鑑みなされたもので、
都市ごみ焼却飛灰中の鉛の溶出を確実に抑制し得る、経
済的でハンドリング性の良好な方法及びこの方法に用い
る鉛溶出抑制剤を提供することを目的とする。
The present invention has been made in view of the above circumstances,
An object of the present invention is to provide an economical method with good handleability capable of reliably suppressing the elution of lead in incineration fly ash of municipal solid waste, and a lead elution inhibitor used in this method.

【0008】[0008]

【課題を解決するための手段及び発明の実施の形態】本
発明者は、上記目的を達成するため鋭意検討を行った結
果、都市ごみ焼却飛灰に対し非晶質水酸化アルミニウム
を添加して水と混練、固化することにより、比較的少な
い量で飛灰中の鉛の溶出を確実に抑制して0.3mg/
l以下の鉛溶出基準値を容易に達成することができ、ま
たこれによって処理された飛灰のハンドリング性も良好
であることを知見し、本発明をなすに至ったものであ
る。
Means for Solving the Problems and Modes for Carrying Out the Invention As a result of intensive studies to achieve the above object, the present inventor has added amorphous aluminum hydroxide to municipal waste incineration fly ash. By kneading with water and solidifying, lead elution in fly ash can be reliably suppressed with a relatively small amount of 0.3 mg /
The inventors have found that a lead elution standard value of 1 or less can be easily achieved, and that the fly ash treated with this can also be handled easily, resulting in the present invention.

【0009】従って、本発明は、都市ごみ焼却飛灰に対
し非晶質水酸化アルミニウムを添加し、水と混練するこ
とを特徴とする飛灰中の鉛溶出抑制方法及び非晶質水酸
化アルミニウムよりなる都市ごみ焼却飛灰の鉛溶出抑制
剤を提供する。
Therefore, according to the present invention, a method for suppressing the elution of lead in fly ash, which comprises adding amorphous aluminum hydroxide to municipal waste incineration fly ash and kneading with water, and amorphous aluminum hydroxide To provide a lead elution inhibitor for municipal waste incineration fly ash.

【0010】以下、本発明につき更に詳述する。The present invention will be described in more detail below.

【0011】本発明で処理の対象となる都市ごみ焼却飛
灰としては、HClガス除去のために消石灰等のカルシ
ウム化合物を粉体又はスラリー状態で吹き込んでいる乾
式又は半乾式の機械炉(ストーカー炉)や流動床炉のE
P灰又はBF灰が挙げられるが、これらのうちで特にカ
ルシウム含有量10〜30重量%である飛灰が好適であ
る。カルシウム含有量が多すぎる飛灰は、非晶質水酸化
アルミニウムを単独で用いる場合、その使用量を多くす
る必要が生じる。
As the municipal solid waste incineration fly ash to be treated in the present invention, a dry or semi-dry mechanical furnace (stoker furnace) in which a calcium compound such as slaked lime is blown in a powder or slurry state to remove HCl gas. ) And E of fluidized bed furnace
P ash or BF ash may be mentioned, and among these, fly ash having a calcium content of 10 to 30% by weight is particularly preferable. Fly ash having an excessively high calcium content needs to be used in a large amount when using amorphous aluminum hydroxide alone.

【0012】本発明では、上記飛灰に対し非晶質水酸化
アルミニウムを鉛溶出抑制剤として添加して処理する。
この場合、非晶質水酸化アルミニウムとしては、X線回
折で非晶状態にあるものが使用でき、これを得る方法と
しては特に制限されるものではないが、例えばアルミニ
ウムの陽極酸化工程で排出される酸性廃液をアルカリで
pH6〜7に中和して得られるものなどが挙げられ、こ
のような廃液から得られる非晶質水酸化アルミニウムを
用いることはコストメリットが大きい。なお、上記非晶
質水酸化アルミニウムは、2〜5重量%水スラリーのp
Hが5.8〜6.5であるものが本発明の目的の上から
好適に用いられる。
In the present invention, the above fly ash is treated by adding amorphous aluminum hydroxide as a lead elution inhibitor.
In this case, as the amorphous aluminum hydroxide, one in an amorphous state by X-ray diffraction can be used, and the method for obtaining it is not particularly limited, but, for example, it is discharged in the anodizing step of aluminum. The acidic waste liquid may be obtained by neutralizing the acidic waste liquid to pH 6 to 7 with an alkali, and the use of amorphous aluminum hydroxide obtained from such waste liquid has great cost merit. In addition, the above-mentioned amorphous aluminum hydroxide is p of 2-5 weight% water slurry.
Those in which H is 5.8 to 6.5 are preferably used for the purpose of the present invention.

【0013】上記非晶質水酸化アルミニウムの添加量
は、飛灰のカルシウム含有量、pH値等に応じて適宜選
定されるが、飛灰のpHを9〜11程度にする量がよ
く、通常飛灰100部(重量部、以下同様)に対し好ま
しくは5〜50重量部、より好ましくは5〜40部、更
に好ましくは5〜30部である。添加量が少なすぎると
処理効果が低下する。一方、添加量が多過ぎても処理効
果の点から問題はないが、それ以上効果も向上せず、経
済的でない上、操作性で問題が生じる場合がある。
The amount of the amorphous aluminum hydroxide added is appropriately selected according to the calcium content of the fly ash, the pH value, etc., but the amount of the fly ash to be about 9 to 11 is usually used. It is preferably 5 to 50 parts by weight, more preferably 5 to 40 parts, and further preferably 5 to 30 parts, relative to 100 parts of fly ash (parts by weight, the same hereinafter). If the amount added is too small, the treatment effect will be reduced. On the other hand, if the amount of addition is too large, there is no problem from the viewpoint of treatment effect, but the effect is not further improved, it is not economical, and there may be a problem in operability.

【0014】本発明においては、飛灰を上記非晶質水酸
化アルミニウムで処理するが、この場合必要によっては
硫酸第一鉄やチオ尿素を非晶質水酸化アルミニウムと併
用でき、鉛溶出抑制剤として、非晶質水酸化アルミニウ
ム5〜95重量%、硫酸第一鉄を無水硫酸第一鉄として
5〜80重量%添加したもの、更に必要に応じてチオ尿
素を0〜15重量%、特に3〜15重量%を配合したも
のを使用することができ、非晶質水酸化アルミニウムに
加えて硫酸第一鉄やチオ尿素を併用することで、より確
実な鉛溶出抑制効果を与えることができる。
In the present invention, fly ash is treated with the above-mentioned amorphous aluminum hydroxide. In this case, ferrous sulfate or thiourea can be used in combination with the amorphous aluminum hydroxide, and a lead elution inhibitor can be used. As amorphous aluminum hydroxide 5 to 95% by weight, ferrous sulfate as anhydrous ferrous sulfate 5 to 80% by weight, and if necessary, thiourea 0 to 15% by weight, especially 3% It is possible to use a mixture of ˜15% by weight, and by using ferrous sulfate or thiourea together with amorphous aluminum hydroxide, a more reliable lead elution suppressing effect can be given.

【0015】飛灰の処理は、以上のような鉛溶出抑制剤
を飛灰に添加し、水で均一に混練するものであるが、こ
の場合、これにより被処理物pHが低下し(pH低下程
度は9〜11が好ましい)、また非晶質水酸化アルミニ
ウムは、水の存在化で飛灰中の消石灰等のカルシウム化
合物と急速に反応し、カルシウムアルミネートを生成し
て固化し、鉛の溶出基準値0.3mg/l以下を確実に
達成し得ると共に、この固化物のハンドリング性は良好
なものである。
In the treatment of fly ash, the lead elution inhibitor as described above is added to fly ash and kneaded uniformly with water. In this case, however, this lowers the pH of the object to be treated (pH lowering). The degree is preferably 9 to 11), and amorphous aluminum hydroxide reacts rapidly with calcium compounds such as slaked lime in fly ash in the presence of water to form calcium aluminate and solidify, The elution standard value of 0.3 mg / l or less can be reliably achieved, and the handleability of this solidified product is good.

【0016】ここで、水の配合量は特に制限されない
が、通常15〜50重量%、好ましくは20〜45重量
%である。
The amount of water to be added is not particularly limited, but is usually 15 to 50% by weight, preferably 20 to 45% by weight.

【0017】なお、飛灰の処理に際し、上記成分に加え
て、本発明の目的を損わない範囲でセメントや液体キレ
ート剤その他の重金属処理薬剤を併用することは差し支
えない。
Incidentally, in treating fly ash, in addition to the above-mentioned components, cement, liquid chelating agent and other heavy metal treating agents may be used in combination as long as the object of the present invention is not impaired.

【0018】[0018]

【実施例】以下、実施例及び比較例を示し、本発明を具
体的に説明するが、本発明は下記の実施例に制限される
ものではない。
EXAMPLES The present invention will be specifically described below by showing Examples and Comparative Examples, but the present invention is not limited to the following Examples.

【0019】〔実施例1〕表1に示す飛灰100部に対
し、2〜5重量%水スラリーのpHが5.8〜6.5で
ある非晶質水酸化アルミニウム及び水を表1に示す量で
添加し、3分間混練し、固化物を得た。この固化物(処
理物)の鉛溶出量を環境庁告示13号により測定した。
結果を表1に示す。
[Example 1] Table 1 shows amorphous aluminum hydroxide and water having a pH of 5.8 to 6.5 in a 2 to 5 wt% water slurry based on 100 parts of fly ash shown in Table 1. The indicated amount was added, and the mixture was kneaded for 3 minutes to obtain a solidified product. The lead elution amount of this solidified product (treated product) was measured according to Notification 13 of the Environmental Agency.
The results are shown in Table 1.

【0020】[0020]

【表1】 *非晶質水酸化アルミニウム90部、無水硫酸第一鉄1
0部の割合で混合したもの
[Table 1] * Amorphous aluminum hydroxide 90 parts, anhydrous ferrous sulfate 1
A mixture of 0 parts

【0021】〔比較例1〕表1の飛灰No.3の100
部に液体硫酸アルミニウム及び水を表2に示す量で添加
して処理した後、鉛溶出量を調べた。結果を表2に示
す。
Comparative Example 1 Fly ash No. 1 in Table 1 3 of 100
After the liquid aluminum sulfate and water were added to the parts in the amounts shown in Table 2 and treated, the lead elution amount was examined. Table 2 shows the results.

【0022】[0022]

【表2】 [Table 2]

【0023】〔比較例2〕表1の飛灰No.2の100
部にセメント、液体キレート剤(ジチオカルバミン酸
系)、水を表3に示す量で添加して処理した後、鉛溶出
量を調べた。結果を表3に示す。
Comparative Example 2 Fly ash No. 1 in Table 1 2 of 100
Cement, a liquid chelating agent (dithiocarbamic acid type) and water were added to the parts in the amounts shown in Table 3 and treated, and then the lead elution amount was examined. The results are shown in Table 3.

【0024】[0024]

【表3】 注:液体キレート剤の価格は非晶質水酸化アルミニウム
の数倍であるため、経済的にはキレート剤の添加量の数
倍が非晶質水酸化アルミニウム量に匹敵する。
[Table 3] Note: Since the price of liquid chelating agents is several times that of amorphous aluminum hydroxide, economically several times the amount of chelating agents added is comparable to the amount of amorphous aluminum hydroxide.

【0025】〔実施例2〕飛灰としてCa含有量25
%、Pb含有量2500mg/kg、Pb溶出量73m
g/lの流動床炉乾式BF灰を使用し、この飛灰100
部に対し、非晶質水酸化アルミニウム40部、無水硫酸
第一鉄50部、チオ尿素10部からなる抑制剤20部を
添加して処理した結果、Pb溶出量は0.02mg/l
であった。
[Example 2] Ca content of 25 as fly ash
%, Pb content 2500 mg / kg, Pb elution amount 73 m
This fly ash 100 g / l is used with the fluidized bed furnace dry BF ash of g / l.
As a result of adding 20 parts of an inhibitor consisting of 40 parts of amorphous aluminum hydroxide, 50 parts of anhydrous ferrous sulfate and 10 parts of thiourea to the parts, the Pb elution amount was 0.02 mg / l.
Met.

【0026】[0026]

【発明の効果】本発明によれば、都市ごみ焼却飛灰中の
鉛の溶出を確実に、しかも経済的に抑制することができ
る。
According to the present invention, it is possible to reliably and economically suppress the elution of lead in fly ash from incineration of municipal solid waste.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 岩城 宏行 神奈川県川崎市中原区中丸子135番地 不 二サッシ株式会社内 (72)発明者 有園 正男 神奈川県川崎市中原区中丸子135番地 不 二サッシ株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Hiroyuki Iwaki 135 Nakamaruko Nakahara-ku, Kawasaki, Kanagawa Fuji Sash Co., Ltd. In the company

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 都市ごみ焼却飛灰に対し非晶質水酸化ア
ルミニウムを添加し、水と混練することを特徴とする飛
灰中の鉛溶出抑制方法。
1. A method for suppressing lead elution from fly ash, which comprises adding amorphous aluminum hydroxide to incinerator fly ash and kneading with water.
【請求項2】 非晶質水酸化アルミニウムの添加量が飛
灰100重量部に対して3〜50重量部である請求項1
記載の方法。
2. The amount of amorphous aluminum hydroxide added is 3 to 50 parts by weight with respect to 100 parts by weight of fly ash.
The described method.
【請求項3】 更に硫酸第一鉄及び/又はチオ尿素を添
加した請求項1又は2記載の方法。
3. The method according to claim 1, further comprising ferrous sulfate and / or thiourea.
【請求項4】 飛灰が、カルシウム含有量10〜30重
量%のストーカー炉又は流動床炉の電気集塵灰又はバグ
フィルター灰である請求項1,2又は3記載の方法。
4. The method according to claim 1, wherein the fly ash is an electrostatic precipitating ash or a bag filter ash of a stalker furnace or a fluidized bed furnace having a calcium content of 10 to 30% by weight.
【請求項5】 非晶質水酸化アルミニウムよりなる都市
ごみ焼却飛灰の鉛溶出抑制剤。
5. A lead elution inhibitor for municipal waste incineration fly ash, which comprises amorphous aluminum hydroxide.
JP7221030A 1995-08-07 1995-08-07 Method for restraining lead in fly ash from being eluted and lead elution inhibitor Pending JPH0947740A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7221030A JPH0947740A (en) 1995-08-07 1995-08-07 Method for restraining lead in fly ash from being eluted and lead elution inhibitor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7221030A JPH0947740A (en) 1995-08-07 1995-08-07 Method for restraining lead in fly ash from being eluted and lead elution inhibitor

Publications (1)

Publication Number Publication Date
JPH0947740A true JPH0947740A (en) 1997-02-18

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP7221030A Pending JPH0947740A (en) 1995-08-07 1995-08-07 Method for restraining lead in fly ash from being eluted and lead elution inhibitor

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Country Link
JP (1) JPH0947740A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000005004A1 (en) * 1998-07-21 2000-02-03 Murakashi Lime Industry Co., Ltd. Hazardous substance-fixing material

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000005004A1 (en) * 1998-07-21 2000-02-03 Murakashi Lime Industry Co., Ltd. Hazardous substance-fixing material

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