JP3344896B2 - Treatment method for heavy metal-containing ash - Google Patents
Treatment method for heavy metal-containing ashInfo
- Publication number
- JP3344896B2 JP3344896B2 JP16419896A JP16419896A JP3344896B2 JP 3344896 B2 JP3344896 B2 JP 3344896B2 JP 16419896 A JP16419896 A JP 16419896A JP 16419896 A JP16419896 A JP 16419896A JP 3344896 B2 JP3344896 B2 JP 3344896B2
- Authority
- JP
- Japan
- Prior art keywords
- heavy metal
- weight
- fixing agent
- ash
- metal fixing
- 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 - Fee Related
Links
Landscapes
- Fire-Extinguishing Compositions (AREA)
- Processing Of Solid Wastes (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、ごみ焼却場等の焼
却プラントで排煙中から電気集塵機やバグフィルター等
で捕集された飛灰、焼却残査の焼却灰、ごみ焼却場等の
焼却プラントで排煙中から電気集塵機やバグフィルター
等で捕集された飛灰、焼却残査の焼却灰を減容化、再資
源化するための溶融炉から発生する飛灰等の重金属含有
灰に含まれる重金属の溶出を抑制することのできる重金
属含有灰の処理方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to fly ash collected from an incineration plant such as a garbage incineration plant by means of an electric dust collector or a bag filter from flue gas, incineration ash from residual incineration, and incineration of a garbage incineration plant. Heavy metal-containing ash, such as fly ash generated from a melting furnace for reducing the volume and recycling of incineration ash collected from electric dust collectors and bag filters from flue gas at plants, and incineration ash from incineration residue. The present invention relates to a method for treating heavy metal-containing ash that can suppress elution of contained heavy metals.
【0002】[0002]
【従来の技術】ごみ焼却場等で発生する飛灰や焼却灰、
あるいは、溶融飛灰等の重金属含有灰には、身体に有害
な鉛、カドミウム、水銀、クロム等の重金属が多量に含
まれているので、これらの重金属を無害化処理すること
が必要である。その処理方法として、例えば、特開平2
−6889号公報には、飛灰に水と重金属固定剤を添
加、混練する方法が開示されている。しかし、この方法
では、多量の重金属固定剤を添加することが必要とな
り、このためランニングコストが高くなるという問題点
があった。そこで、特開平7−39846号公報には、
飛灰に硫酸アルミニウムを添加、混練してpH調整を行
った後に、重金属固定剤を添加、混練する方法が提案さ
れている。[Prior Art] Fly ash and incineration ash generated in waste incineration plants, etc.
Alternatively, heavy metal-containing ash such as molten fly ash contains a large amount of heavy metals such as lead, cadmium, mercury, and chromium that are harmful to the body. Therefore, it is necessary to detoxify these heavy metals. As a processing method, for example,
Japanese Patent No. -6889 discloses a method of adding and kneading water and a heavy metal fixing agent to fly ash. However, in this method, it is necessary to add a large amount of a heavy metal fixing agent, so that there is a problem that running cost is increased. Therefore, JP-A-7-39846 discloses that
A method has been proposed in which aluminum sulfate is added to the fly ash and kneaded to adjust the pH, and then a heavy metal fixing agent is added and kneaded.
【0003】[0003]
【発明が解決しようとする課題】しかし、重金属固定剤
としては、一般にジチオカルバミン酸系の化合物が用い
られているが、ジチオカルバミン酸系の重金属固定剤と
アルミニウム化合物のpH調整剤を併用すると、多量の
二硫化炭素が発生するという問題があった。本発明は、
二硫化炭素の発生を抑制し、かつ重金属の溶出を抑制す
ることのできる重金属含有灰の処理方法を提供すること
を目的とするものである。However, a dithiocarbamic acid-based compound is generally used as a heavy metal fixing agent. However, when a dithiocarbamic acid-based heavy metal fixing agent and an aluminum compound pH adjuster are used in combination, a large amount of There was a problem that carbon disulfide was generated. The present invention
It is an object of the present invention to provide a method for treating heavy metal-containing ash, which can suppress the generation of carbon disulfide and the elution of heavy metals.
【0004】[0004]
【課題を解決するための手段】本発明者らは、このよう
な課題を解決するために鋭意検討の結果、pH調整剤と
してマグネシウム化合物を、重金属固定剤としてジチオ
カルバミン酸系の化合物を用いて重金属含有灰を処理す
ることにより、二硫化炭素の発生を抑制し、かつ重金属
の溶出を抑制することができるという事実を見いだし、
本発明に到達した。すなわち、本発明は、重金属含有灰
と、マグネシウム化合物及びジチオカルバミン酸系の重
金属固定剤とを混練することを特徴とする重金属含有灰
の処理方法を要旨とするものである。Means for Solving the Problems The inventors of the present invention have conducted intensive studies to solve such problems, and as a result, a magnesium compound has been used as a pH adjuster and a dithiocarbamic acid-based compound has been used as a heavy metal fixing agent. By treating the contained ash, it is possible to suppress the generation of carbon disulfide and to find out the fact that the elution of heavy metals can be suppressed.
The present invention has been reached. That is, the gist of the present invention is a method for treating heavy metal-containing ash, which comprises kneading a heavy metal-containing ash with a magnesium compound and a dithiocarbamic acid-based heavy metal fixing agent.
【0005】[0005]
【発明の実施の形態】以下、本発明を詳細に説明する。
本発明に用いられる重金属含有灰としては、ごみ焼却場
の焼却プラントで排煙中から電気集塵機やバグフィルタ
ー等で捕集された飛灰、焼却残査の焼却灰、ごみ焼却場
の焼却プラントで排煙中から電気集塵機やバグフィルタ
ー等で捕集された飛灰、焼却残査の焼却灰を減容化、再
資源化するための溶融炉から発生する溶融飛灰等が挙げ
られ、この重金属含有灰を10重量%水溶液として6時
間振盪させた後の上澄み水のpHを測定すると通常12
以上である。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.
As the heavy metal-containing ash used in the present invention, fly ash collected by an electric dust collector or a bag filter from flue gas in an incineration plant of a garbage incineration plant, incineration ash of incineration residue, incineration plant of a garbage incineration plant Fly ash collected by electric dust collectors and bag filters from flue gas and molten fly ash generated from a melting furnace to reduce and recycle incinerated ash from incineration residue When the pH of the supernatant water after shaking the contained ash as a 10% by weight aqueous solution for 6 hours is measured, it is usually 12%.
That is all.
【0006】本発明に用いられるマグネシウム化合物と
しては、固形塩化マグネシウム六水和物、液体塩化マグ
ネシウム、固形硫酸マグネシウム七水和物、液体硫酸マ
グネシウム等が挙げられ、塩化ナトリウム、塩化カルシ
ウム、硫酸ナトリウム、硫酸カルシウム等の不純物が5
0%以下のものが好ましい。本発明においては、これら
のマグネシウム化合物を単独で用いてもよく、また、複
数からなる混合物を用いてもよい。通常は、液体塩化マ
グネシウム(MgCl2 として換算すると28重量%、
MgCl2 ・6H2 Oとして換算すると60重量%含
有)又は液体硫酸マグネシウム(MgSO4 として換算
すると21重量%、MgSO4 ・7H2 Oとして換算す
ると43重量%含有)を用いればよいが、重金属含有灰
とマグネシウム化合物及び重金属固定剤とを混練した混
練物の含水率が過剰となる場合は、固形塩化マグネシウ
ム六水和物又は固形硫酸マグネシウム七水和物を用いる
ことが好ましい。The magnesium compound used in the present invention includes solid magnesium chloride hexahydrate, liquid magnesium chloride, solid magnesium sulfate heptahydrate, liquid magnesium sulfate, etc., such as sodium chloride, calcium chloride, sodium sulfate, and the like. 5 impurities such as calcium sulfate
Those having 0% or less are preferable. In the present invention, these magnesium compounds may be used alone, or a mixture of a plurality of them may be used. Usually, liquid magnesium chloride (28% by weight in terms of MgCl 2 ,
When calculated as MgCl 2 · 6H 2 O 60% by weight containing) or 21 wt% when converted as a liquid magnesium sulfate (MgSO 4, MgSO 4 · 7H 2 O may be used to the 43 wt% content) calculated as but containing heavy metals When the water content of the kneaded product obtained by kneading the ash, the magnesium compound and the heavy metal fixing agent becomes excessive, it is preferable to use solid magnesium chloride hexahydrate or solid magnesium sulfate heptahydrate.
【0007】本発明に用いられるジチオカルバミン酸系
の重金属固定剤としては、ジエチルジチオカルバミン
酸、ジブチルジチオカルバミン酸、トリス(ジチオカル
ボキシ)ジエチレントリアミンのナトリウム塩、カリウ
ム塩、リチウム塩等が挙げられ、現在市販されている各
種の重金属固定剤が使用できる。Examples of the dithiocarbamic acid-based heavy metal fixing agent used in the present invention include sodium, potassium and lithium salts of diethyldithiocarbamic acid, dibutyldithiocarbamic acid, and tris (dithiocarboxy) diethylenetriamine. Various heavy metal fixing agents can be used.
【0008】本発明においては、重金属含有灰と、マグ
ネシウム化合物及び重金属固定剤とを混練するが、その
ときのマグネシウム化合物としては、混練後の混練物の
pHが9〜11の範囲となるように調整することが好ま
しく、重金属含有灰の性状は、燃焼物、燃焼条件、排ガ
スの処理条件で大きく変動し、また、焼却場により異な
るため、重金属含有灰の成分を分析して決定することが
好ましい。通常、重金属含有灰100重量部に対してマ
グネシウム化合物を5〜100重量部の範囲で選択して
混練すれば上記の範囲に調整することができる。また、
重金属固定剤としては、重金属含有灰の性状、マグネシ
ウム化合物を混練後の混練物のpHによって異なること
から、あらかじめマグネシウム化合物を混練後の混練物
に応じて決定することが好ましい。通常は、重金属含有
灰100重量部に対して5重量部以下で、重金属の溶出
を十分に抑制することができる。In the present invention, the heavy metal-containing ash, the magnesium compound and the heavy metal fixing agent are kneaded. The magnesium compound at this time is adjusted so that the pH of the kneaded product after kneading is in the range of 9 to 11. It is preferable to adjust the properties of the heavy metal-containing ash, which greatly varies depending on the combustion conditions, combustion conditions, and exhaust gas treatment conditions, and also varies depending on the incineration plant. . Usually, if the magnesium compound is selected and kneaded in a range of 5 to 100 parts by weight with respect to 100 parts by weight of the heavy metal-containing ash, the above range can be adjusted. Also,
The heavy metal fixing agent is preferably determined in advance depending on the properties of the heavy metal-containing ash and the pH of the kneaded material after kneading the magnesium compound according to the kneaded material after kneading the magnesium compound. Usually, at 5 parts by weight or less based on 100 parts by weight of the heavy metal-containing ash, elution of heavy metals can be sufficiently suppressed.
【0009】また、混練する際には、水を添加すること
が好ましく、重金属含有灰にマグネシウム化合物と重金
属固定剤を混練し、混練物の水分率が30〜40%にな
るように調整すると混練物の取り扱い性がよいので好ま
しい。When kneading, it is preferable to add water. The magnesium compound and the heavy metal fixing agent are kneaded with the heavy metal-containing ash, and the mixture is adjusted so that the moisture content of the kneaded product becomes 30 to 40%. This is preferred because the handling of the product is good.
【0010】混練方法としては、重金属含有灰にマグネ
シウム化合物を添加して混練した後に、重金属固定剤を
添加してさらに混練するのが好ましい。混練は、振動
式、回転ドラム式、二軸混練式等の混練機を使用して行
えばよく、混練機はバッチ式のものでも、連続式のもの
でもよい。また、混練時間としては、2〜20分が好ま
しく、特に5〜10分が好ましい。As a kneading method, it is preferable to add a magnesium compound to the heavy metal-containing ash and knead the mixture, and then add a heavy metal fixing agent and further knead the mixture. The kneading may be performed using a kneading machine such as a vibration type, a rotating drum type, a twin-shaft kneading type, and the kneading machine may be a batch type or a continuous type. Further, the kneading time is preferably 2 to 20 minutes, particularly preferably 5 to 10 minutes.
【0011】[0011]
【実施例】次に、本発明を実施例によって具体的に説明
する。 実施例1〜2、比較例1 pH12.6、Pb6,290mg/リットルを含有す
る都市ゴミ焼却場における排ガス処理設備のバグフィル
ターで捕集された飛灰100重量に、28重量%塩化マ
グネシウム48重量部と水17重量部(実施例1)、2
1重量%硫酸マグネシウム83重量部(実施例2)を添
加して、約5分間混練した後に、ジチオカルバミン酸系
の重金属固定剤ユニチカ社製UML−7200を1〜3
重量部添加して、さらに5分間混練した。また、これと
別はに上記の飛灰100重量部に重金属固定剤を0〜5
重量部のみを添加して、約5分間混練した(比較例
1)。このようにして得られた混練物を10重量%水溶
液とし、6時間振盪させた後の上澄み水のpHの測定
と、環境庁告示第13号に定める方法に従い、重金属の
溶出試験とを行った。その結果を表1に示す。Next, the present invention will be described specifically with reference to examples. Examples 1 and 2, Comparative Example 1 28% by weight of magnesium chloride and 48% by weight of fly ash collected by a bag filter of an exhaust gas treatment facility in a municipal waste incineration plant containing pH 12.6, Pb6 and 290 mg / L Parts and 17 parts by weight of water (Example 1), 2
After adding 83 parts by weight of 1% by weight magnesium sulfate (Example 2) and kneading for about 5 minutes, a dithiocarbamic acid-based heavy metal fixing agent UML-7200 manufactured by Unitika Ltd.
Part by weight was added and kneaded for another 5 minutes. Separately, a heavy metal fixing agent is added to 100 parts by weight of the above fly ash.
Only parts by weight were added and kneaded for about 5 minutes (Comparative Example 1). The kneaded product thus obtained was made into a 10% by weight aqueous solution, shaken for 6 hours, and the pH of the supernatant water was measured, and a heavy metal dissolution test was carried out according to the method specified in Notification No. 13 of the Environment Agency. . Table 1 shows the results.
【0012】[0012]
【表1】 [Table 1]
【0013】表1に示すように、マグネシウム化合物と
ジチオカルバミン酸系の重金属固定剤を併用して処理す
ることにより、鉛の溶出を抑制することができ、鉛の溶
出濃度は「金属等を含む産業廃棄物に掛かる判定基準を
定める総理府令(昭和48年2月17日、総理府令第5
号)」に定める陸上埋立判定基準値である0.3mg/
リットルを大幅にクリアした。また、マグネシウム化合
物を併用すると重金属固定剤は1重量部添加するだけで
鉛の溶出を十分抑制することができたが、重金属固定剤
のみで処理するのに必要な重金属固定剤は5重量部であ
った。As shown in Table 1, by using a magnesium compound and a dithiocarbamic acid-based heavy metal fixing agent in combination, the elution of lead can be suppressed. Prime Minister's Ordinance Establishing Criteria for Waste (February 17, 1973, Prime Minister's Ordinance No. 5
No.) which is the landfill landfill judgment standard value of 0.3 mg /
Cleared the liter significantly. In addition, when a magnesium compound was used in combination, the elution of lead could be sufficiently suppressed by adding only 1 part by weight of the heavy metal fixing agent. However, the heavy metal fixing agent required for treatment with only the heavy metal fixing agent was 5 parts by weight. there were.
【0014】実施例3、比較例2 容量1リットルのテドラーバッグに実施例1と同じ飛灰
50重量部を封入した後、脱気を行い、純空気300ミ
リリットルと28重量%塩化マグネシウムを24重量部
(実施例3)又は52重量%硫酸アルミニウム18水和
物を12重量部(比較例2)と、ジチオカルバミン酸系
の重金属固定剤ユニチカ社製UML−7200を8.8
重量部注入し、5分間手もみ混練し、10分間放置した
後、発生ガスを他のテドラーバッグへ移し替えた。この
ようにして回収した発生ガス中の二硫化炭素の濃度をガ
スクロマトグラフ(日立製作所製)で測定した。その結
果、pH調整剤として28重量%塩化マグネシウムを用
いたときの二硫化炭素の発生量は11ppmであり、p
H調整剤として52重量%硫酸アルミニウムを用いたと
きの二硫化炭素の発生量は410ppmであった。この
結果から、マグネシウム化合物とジチオカルバミン酸系
の重金属固定剤とで処理すると、二硫化炭素の発生量
を、アルミニウム化合物とジチオカルバミン酸系の重金
属固定剤を用いて処理した場合の約1/40に抑えるこ
とができることがわかる。Example 3, Comparative Example 2 After enclosing 50 parts by weight of fly ash as in Example 1 in a Tedlar bag having a capacity of 1 liter, degassing was carried out, and 300 ml of pure air and 24 parts by weight of 28% by weight magnesium chloride were added. (Example 3) or 12 parts by weight of 52% by weight aluminum sulfate 18 hydrate (Comparative Example 2) and 8.8 of UML-7200 manufactured by Unitika, a dithiocarbamic acid-based heavy metal fixing agent.
A part by weight was injected, hand kneaded for 5 minutes, left to stand for 10 minutes, and the generated gas was transferred to another Tedlar bag. The concentration of carbon disulfide in the generated gas thus collected was measured with a gas chromatograph (manufactured by Hitachi, Ltd.). As a result, when 28% by weight of magnesium chloride was used as a pH adjuster, the amount of generated carbon disulfide was 11 ppm, and p
When 52% by weight of aluminum sulfate was used as the H adjuster, the amount of generated carbon disulfide was 410 ppm. From these results, when the treatment is performed with the magnesium compound and the dithiocarbamic acid-based heavy metal fixing agent, the amount of carbon disulfide generated is suppressed to about 1/40 that of the case where the treatment is performed using the aluminum compound and the dithiocarbamic acid-based heavy metal fixing agent. We can see that we can do it.
【0015】参考例1、比較例3 重金属含有灰貯留タンク内でのブリッジ等により混練機
に飛灰が供給されなかった場合を想定し、容量1リット
ルのテドラーバッグに純空気300ミリリットルと28
重量%塩化マグネシウムを19重量部(参考例1)又は
52重量%硫酸アルミニウム18水和物を10重量部
(比較例3)と、ジチオカルバミン酸系の重金属固定剤
ユニチカ社製UML−7200を10重量部注入し、5
分間手もみ混練し、10分間放置した後、発生ガスを他
のテドラーバッグへ移し替えた。このようにして回収し
た発生ガス中の二硫化炭素の量を実施例3と同様にして
測定した結果、28重量%塩化マグネシウムとジチオカ
ルバミン酸系の重金属固定剤を混練したときの二硫化炭
素の発生量は320ppmであり、一方、52重量%硫
酸アルミニウムとジチオカルバミン酸系の重金属固定剤
を混練したときの二硫化炭素の発生量は3,500pp
mであった。この結果から、マグネシウム化合物はジチ
オカルバミン酸系の重金属固定剤と直接接触しても、ア
ルミニウム化合物とジチオカルバミン酸系の重金属固定
剤が直接接触した場合に比べて、二硫化炭素の発生量が
1/10以下であることがわかる。Reference Example 1 and Comparative Example 3 Assuming that fly ash was not supplied to the kneader due to a bridge or the like in the heavy metal-containing ash storage tank, 300 ml of pure air and 28 ml of pure air were stored in a 1-liter tedlar bag.
19 parts by weight of magnesium chloride by weight (Reference Example 1) or 10 parts by weight of aluminum sulfate 18 hydrate by 52% by weight (Comparative Example 3) and 10 parts by weight of a dithiocarbamic acid-based heavy metal fixing agent UML-7200 manufactured by Unitika Ltd. Part injection, 5
The mixture was hand-kneaded for 10 minutes, allowed to stand for 10 minutes, and then the generated gas was transferred to another Tedlar bag. The amount of carbon disulfide in the generated gas thus collected was measured in the same manner as in Example 3. As a result, the generation of carbon disulfide when 28% by weight of magnesium chloride and a dithiocarbamic acid-based heavy metal fixing agent were kneaded. The amount was 320 ppm, while the amount of carbon disulfide generated when kneading 52% by weight of aluminum sulfate and a dithiocarbamic acid-based heavy metal fixing agent was 3,500 pp.
m. From this result, even when the magnesium compound is in direct contact with the dithiocarbamic acid-based heavy metal fixing agent, the amount of carbon disulfide generated is 1/10 as compared with the case where the aluminum compound is directly contacted with the dithiocarbamic acid-based heavy metal fixing agent. It can be seen that:
【0016】[0016]
【発明の効果】本発明によれば、ジチオカルバミン酸系
の重金属固定剤とpH調整剤とを併用した際に発生する
二硫化炭素の発生を抑制することができる。According to the present invention, the generation of carbon disulfide generated when a dithiocarbamic acid-based heavy metal fixing agent and a pH adjuster are used in combination can be suppressed.
Claims (1)
びジチオカルバミン酸系の重金属固定剤とを混練するこ
とを特徴とする重金属含有灰の無害化処理方法。1. A method for detoxifying heavy metal-containing ash, which comprises kneading a heavy metal-containing ash, a magnesium compound and a dithiocarbamic acid-based heavy metal fixing agent.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16419896A JP3344896B2 (en) | 1996-06-25 | 1996-06-25 | Treatment method for heavy metal-containing ash |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16419896A JP3344896B2 (en) | 1996-06-25 | 1996-06-25 | Treatment method for heavy metal-containing ash |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH105717A JPH105717A (en) | 1998-01-13 |
| JP3344896B2 true JP3344896B2 (en) | 2002-11-18 |
Family
ID=15788548
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP16419896A Expired - Fee Related JP3344896B2 (en) | 1996-06-25 | 1996-06-25 | Treatment method for heavy metal-containing ash |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3344896B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2226749A (en) * | 1989-01-05 | 1990-07-11 | George Wilkinson | Bakeware |
| JP4867700B2 (en) * | 2007-02-21 | 2012-02-01 | 東ソー株式会社 | Heavy metal treatment agent and method for treating heavy metal contaminants using the same |
-
1996
- 1996-06-25 JP JP16419896A patent/JP3344896B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH105717A (en) | 1998-01-13 |
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