JP2000093924A - Method for treating incineration residue of waste - Google Patents
Method for treating incineration residue of wasteInfo
- Publication number
- JP2000093924A JP2000093924A JP10273071A JP27307198A JP2000093924A JP 2000093924 A JP2000093924 A JP 2000093924A JP 10273071 A JP10273071 A JP 10273071A JP 27307198 A JP27307198 A JP 27307198A JP 2000093924 A JP2000093924 A JP 2000093924A
- Authority
- JP
- Japan
- Prior art keywords
- zirconium
- melting
- molten slag
- waste
- incineration residue
- 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.)
- Granted
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃棄物を焼却する
際に発生する焼却灰及び飛灰などの焼却残渣の溶融方法
に関するものであり、さらに詳しくは、発生した溶融ス
ラグから有害重金属類がほとんど溶出しない廃棄物の焼
却残渣の溶融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 a method for melting incineration residues such as incineration ash and fly ash generated during incineration of waste, and more particularly, to a method for removing harmful heavy metals from generated slag. The present invention relates to a method for melting incineration residues of wastes that hardly elute.
【0002】[0002]
【従来の技術】わが国において廃棄物の処理は、埋立処
分場の確保が困難であるという事情から、焼却処理が一
般的に採用され、廃棄物を焼却により減容させた後に埋
立処分が行われている。また、地球規模での環境問題へ
の取り組みの高まりから、リサイクル方法の一つとし
て、廃棄物を燃焼し、発生したエネルギーを回収するサ
ーマルリサイクルが行われるようになってきている。廃
棄物を焼却処理することにより、廃棄物中の可燃物はガ
ス化し、不燃物すなわち灰分は残渣として排出される。
これらの残渣中には、有害な重金属類やダイオキシン類
が含まれているため、残渣をそのまま埋立処分すると、
有害物質が溶出するという問題がある。そこで、これら
の問題点を解決し、さらに、残渣を減量化する方法とし
て、残渣を溶融固化処理して溶融スラグとする方法が提
案されている。さらに、発生した溶融スラグを路盤材、
コンクリート用骨材、埋め戻し材、コンクリート二次製
品等に再利用することが提案されており、すでに路盤材
などに利用し始めている地域もある。2. Description of the Related Art In Japan, incineration is generally adopted for waste disposal because it is difficult to secure a landfill site. Landfill disposal is performed after reducing the volume of waste by incineration. ing. In addition, due to an increase in efforts for environmental issues on a global scale, thermal recycling for burning waste and recovering generated energy has been performed as one of recycling methods. By incinerating the waste, combustibles in the waste are gasified, and non-combustibles, that is, ash are discharged as residues.
These residues contain harmful heavy metals and dioxins.
There is a problem that harmful substances elute. Therefore, as a method of solving these problems and further reducing the amount of the residue, a method of melting and solidifying the residue to obtain a molten slag has been proposed. Furthermore, the generated molten slag is used for roadbed material,
It has been proposed to reuse it for concrete aggregate, backfill material, concrete secondary products, etc., and in some areas it has already begun to be used for roadbed materials.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、溶融固
化処理によりダイオキシン類は分解するものの、重金属
類はそのまま溶融スラグに含まれているため、できた溶
融スラグを用いた2次製品から有害物質が溶出してくる
可能性があり、溶融スラグから有害物質の溶出を完全に
抑制する必要がある。さらに、平成10年4月には、溶
融スラグの再利用に関する指針値が自治体に対し通達さ
れ、鉛を含む有害物質の溶出が規制され始めた。However, although dioxins are decomposed by the melt-solidification treatment, harmful substances are eluted from secondary products using the molten slag because heavy metals are contained in the molten slag as it is. It is necessary to completely suppress the elution of harmful substances from the molten slag. Furthermore, in April 1998, a guideline value regarding the reuse of molten slag was notified to local governments, and the elution of harmful substances including lead began to be regulated.
【0004】廃棄物の焼却残渣を高温溶融固化する際に
添加する溶融助剤としては、特開昭61−238387
号公報や特開平4−321539号公報には、塩基度や
ナトリウム含有量を調整することにより溶融スラグの溶
流点を低下し、溶融固化に必要なエネルギーを低減させ
ることができることや、特公昭61−15934号公報
や特開平8−89923号公報には、ケイ素源や金属
が、スラグ層やメタル層から特定元素を減少させること
ができることなどが提案されているが、これらの溶融助
剤はいずれも、溶融スラグからの有害物質の溶出を抑制
することを目的とするものではなかった。本発明は、発
生する溶融スラグから重金属類がほとんど溶出しない廃
棄物の焼却残渣の処理方法を提供することを目的とする
ものである。[0004] As a melting aid to be added when the incineration residue of wastes is melted and solidified at a high temperature, Japanese Unexamined Patent Publication (Kokai) No. 61-238387 is used.
Japanese Patent Application Laid-Open No. 4-321439 and Japanese Patent Application Laid-Open No. 4-321538 disclose that the melt flow point of molten slag can be lowered by adjusting the basicity and the sodium content, so that the energy required for melt solidification can be reduced. 61-15934 and JP-A-8-89923 propose that a silicon source or a metal can reduce a specific element from a slag layer or a metal layer. None of them aimed at suppressing elution of harmful substances from molten slag. An object of the present invention is to provide a method for treating incineration residues of wastes in which heavy metals are hardly eluted from generated molten slag.
【0005】[0005]
【課題を解決するための手段】本発明者は、このような
課題を解決するために鋭意検討の結果、ジルコニウム含
有物を廃棄物の焼却残渣に添加して高温溶融固化後、磁
性成分を除去することにより、発生した溶融スラグから
重金属類がほとんど溶出しないということを見いだし、
本発明に到達した。Means for Solving the Problems The inventors of the present invention have made intensive studies to solve such problems, and as a result, added a zirconium-containing substance to the incineration residue of waste, solidified it at a high temperature, and then removed the magnetic component. By doing, we found that heavy metals hardly eluted from the generated molten slag,
The present invention has been reached.
【0006】すなわち、本発明は廃棄物の焼却残渣にジ
ルコニウム含有物を添加して溶融固化処理した後、処理
物から磁性成分を除去することを特徴とする焼却残渣の
溶融方法を要旨とするものである。That is, the gist of the present invention is a method for melting incineration residues, which comprises adding a zirconium-containing substance to a waste incineration residue, subjecting it to a solidification treatment, and then removing a magnetic component from the treated material. It is.
【0007】[0007]
【発明の実施の形態】以下、本発明を詳細に説明する。
本発明における廃棄物の焼却残渣とは、一般廃棄物、産
業廃棄物、下水汚泥などを焼却して生じる焼却灰及び排
ガスから集塵機などで収集した飛灰など、焼却工程で生
じるガス以外の成分すべてである。また、ガス化溶融炉
や直接溶融炉のように、焼却工程における焼却残渣を一
旦取り出さないで溶融固化する場合にも適用することが
可能である。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.
The waste incineration residue in the present invention means all components other than gas generated in the incineration process, such as incineration ash generated by incineration of general waste, industrial waste, sewage sludge, and fly ash collected from exhaust gas by a dust collector. It is. Further, the present invention can also be applied to a case where an incineration residue in an incineration process is melted and solidified without being taken out once, such as a gasification melting furnace or a direct melting furnace.
【0008】本発明においては、まず、ジルコニウム含
有物を廃棄物の焼却残渣に添加する。添加するジルコニ
ウム化合物としては、特に限定されるものではなく、ジ
ルコニウム、酸化ジルコニウム、炭化ジルコニウム、オ
キシ塩化ジルコニウム、ジルコニウムアルコキシド、窒
化ジルコニウム、けい酸ジルコニウム、塩化ジルコニウ
ム、水素化ジルコニウム、硝酸ジルコニウム、ほう化ジ
ルコニウムなどがあげられる。また、ジルコニウム含有
物の添加量としては、酸化物換算で全重量の0.5〜1
0%、好ましくは1〜5%である。ジルコニウム含有物
の添加量が上記の範囲以下では、重金属類の溶出防止効
果が少なくなり、また、範囲以上であっても添加量が増
加するのみで著しい効果は得られないため好ましくな
い。In the present invention, first, a zirconium-containing substance is added to the incineration residue of waste. The zirconium compound to be added is not particularly limited, and zirconium, zirconium oxide, zirconium carbide, zirconium oxychloride, zirconium alkoxide, zirconium nitride, zirconium silicate, zirconium chloride, zirconium hydride, zirconium nitrate, zirconium boride And so on. The amount of the zirconium-containing material added is 0.5 to 1 of the total weight in terms of oxide.
0%, preferably 1 to 5%. If the amount of the zirconium-containing material is less than the above range, the effect of preventing the elution of heavy metals decreases, and if it is more than the above range, only a large amount of addition does not provide a significant effect, so that it is not preferable.
【0009】次に、ジルコニウム含有物を添加した廃棄
物の焼却残渣を溶融処理後、水砕又は空冷して固化す
る。焼却残渣の溶融方法としては、重油、灯油、ガス、
コークスなどの補助燃料を用いて溶融する方法、アーク
式、プラズマ式、電気抵抗式、低周波誘導式などのよう
な電気を熱源とした溶融方法及び熱分解溶融やコークス
ベット方式のような直接溶融方法などがあげられる。ま
た、溶融温度としては、焼却残渣が溶融する温度であれ
ば特に限定されるものではないが、1100〜1500
℃程度で溶融することが好ましく、溶融時間としては、
溶融方法に応じて適宜選択することが好ましく、通常1
0分〜10時間溶融すればよい。Next, the incineration residue of the waste to which the zirconium-containing substance has been added is subjected to a melting treatment and then solidified by water granulation or air cooling. Methods for melting incineration residues include heavy oil, kerosene, gas,
Melting method using auxiliary fuel such as coke, melting method using electricity as heat source such as arc type, plasma type, electric resistance type, low frequency induction type, and direct melting such as pyrolysis melting or coke bed method Method. The melting temperature is not particularly limited as long as it is a temperature at which the incineration residue is melted.
It is preferable to melt at about ℃, as the melting time,
It is preferable to appropriately select according to the melting method.
It may be melted for 0 minutes to 10 hours.
【0010】次に、このような方法によって調製した処
理物には、溶融スラグとメタルが含まれているので、磁
性成分を除去することによってメタルを除去する。磁性
成分の分離は、必要に応じて処理物を破砕してから行っ
てもよい。磁性成分の除去方法としては、永久磁石、電
磁石をクロスベルト式、回転ドラム式などの磁選機を用
いて行うことができる。本発明においては、ジルコニウ
ムの存在下で焼却残渣を溶融固化処理する際に溶融スラ
グ中から重金属類、特に鉛がメタル中へ移行するため、
溶融スラグ中の重金属類の含有濃度が低下するものと考
えられる。Next, since the treated material prepared by such a method contains molten slag and metal, the metal is removed by removing the magnetic component. Separation of the magnetic component may be performed after crushing the processed material as necessary. As a method for removing the magnetic component, a permanent magnet or an electromagnet can be performed using a magnetic separator such as a cross belt type or a rotating drum type. In the present invention, when melting and solidifying the incineration residue in the presence of zirconium, heavy metals, particularly lead, from the molten slag migrate into the metal,
It is considered that the concentration of heavy metals in the molten slag decreases.
【0011】図1は、様々な条件により調製した溶融ス
ラグ中の鉛の含有量と、「土壌の汚染に係る環境基準に
ついて」(平成3年環境庁告示第46号)に定める方法
により測定した溶融スラグからの鉛の溶出濃度との関係
を示す図である。この図から、溶融スラグ中の鉛の含有
量と溶融スラグからの鉛の溶出量には、おおよそ正の相
関があることがわかる。このため、本発明においては、
発生する溶融スラグ中の重金属の含有濃度が低下してい
るので、溶融スラグから重金属類がほとんど溶出しな
い。そして、「土壌の汚染に係る環境基準について」
(平成3年環境庁告示第46号)に定める方法により溶
出試験を行った場合の溶融スラグからの各重金属類の溶
出濃度を以下の表1に示す値以下にすることができる。FIG. 1 shows the contents of lead in molten slag prepared under various conditions and measured by the method specified in "Environmental Standards for Soil Contamination" (Notification No. 46 of the Environment Agency, 1991). It is a figure which shows the relationship with the elution concentration of lead from a molten slag. From this figure, it can be seen that there is an approximately positive correlation between the content of lead in the molten slag and the amount of lead eluted from the molten slag. Therefore, in the present invention,
Since the content of heavy metals in the generated molten slag is reduced, heavy metals are hardly eluted from the molten slag. And, "About environmental standards related to soil pollution"
The elution concentration of each heavy metal from the molten slag in the case of performing the elution test according to the method specified in (Environment Agency Notification No. 46, 1991) can be set to the value shown in Table 1 below.
【0012】[0012]
【表1】 [Table 1]
【0013】このように、本発明の方法によって発生す
る溶融スラグからは重金属類、特に溶融スラグからの溶
出の可能性の高い鉛の溶出が防止されているため、様々
な用途への再利用が可能である。As described above, the molten slag generated by the method of the present invention prevents heavy metals, particularly lead, which is likely to be eluted from the molten slag, from being eluted, so that it can be reused for various uses. It is possible.
【0014】[0014]
【実施例】次に、本発明を実施例により具体的に説明す
る。 実施例1 表2に示す組成を有するストーカ式焼却場から発生した
焼却灰と飛灰を混合した焼却残渣(PbOを焼却残渣に
対し0.3重量%添加し、Pb含有量を増加してあ
る。)250gに対し、酸化ジルコニウム2.5gを添
加、混合した。小型電気炉にるつぼを入れ、昇温して1
350℃に保持し、調製した焼却残渣を投入して、30
分間溶融し、溶融処理物を水10リットルに注ぎ入れ、
水砕スラグとした。この水砕スラグを105℃で24時
間乾燥した後、粉砕し、永久磁石を用いて磁性成分を除
去した。Next, the present invention will be described in detail with reference to examples. Example 1 An incineration residue obtained by mixing incineration ash and fly ash generated from a stoker type incineration plant having the composition shown in Table 2 (PbO was added in an amount of 0.3% by weight to the incineration residue to increase the Pb content. 2.5 g of zirconium oxide was added to 250 g and mixed. Put the crucible in a small electric furnace and raise the temperature to 1
The temperature was maintained at 350 ° C., and the prepared incineration residue was charged.
Melt for 10 minutes, pour the melted product into 10 liters of water,
Granulated slag was used. The granulated slag was dried at 105 ° C. for 24 hours and then pulverized to remove magnetic components using a permanent magnet.
【0015】[0015]
【表2】 [Table 2]
【0016】この溶融スラグ中(磁性成分を除去した水
砕スラグ)の鉛の含有量をICP(高周波誘導結合プラ
ズマ)発光分析法で測定した結果、溶融スラグ中には
0.07mg/gの鉛しか含有されていなかった。ま
た、この溶融スラグからの鉛の溶出量を環境庁告示46
号法に基づいて測定した結果、鉛の溶出は検出限界以下
(<0.005mg/l)であった。As a result of measuring the lead content of the molten slag (granulated slag from which the magnetic components were removed) by ICP (high frequency inductively coupled plasma) emission spectrometry, 0.07 mg / g of lead was found in the molten slag. Was contained only. Also, the amount of lead eluted from the molten slag was determined by the Environment Agency Notification 46.
As a result of measurement based on the signal method, the elution of lead was below the detection limit (<0.005 mg / l).
【0017】比較例1 酸化ジルコニウムを添加しないで行った以外は、実施例
1と同様にして、溶融スラグを調製し、この溶融スラグ
の鉛の含有量及び溶融スラグからの鉛の溶出量を実施例
1と同様にして測定した結果、溶融スラグ中には1.5
mg/gの鉛が含有されており、溶出液には0.025
mg/lの鉛の溶出が認められた。Comparative Example 1 A molten slag was prepared in the same manner as in Example 1 except that zirconium oxide was not added, and the lead content of the molten slag and the amount of lead eluted from the molten slag were measured. As a result of measurement in the same manner as in Example 1, 1.5 was found in the molten slag.
mg / g of lead, and the eluate contained 0.025
Elution of lead of mg / l was observed.
【0018】[0018]
【発明の効果】本発明によれば、焼却残渣を溶融固化処
理して発生する溶融スラグから重金属類がほとんど溶出
しないため、発生する溶融スラグの再利用が容易とな
る。According to the present invention, since the heavy metals are hardly eluted from the molten slag generated by melting and solidifying the incineration residue, the generated molten slag can be easily reused.
【図1】溶融スラグ中の鉛の含有量と、溶融スラグから
の鉛の溶出濃度との関係を示す図である。FIG. 1 is a diagram showing the relationship between the content of lead in molten slag and the concentration of lead eluted from molten slag.
Claims (1)
を添加して溶融固化処理した後、処理物から磁性成分を
除去することを特徴とする焼却残渣の処理方法。1. A method for treating incineration residues, comprising adding a zirconium-containing substance to a waste incineration residue, subjecting it to a solidification treatment, and then removing a magnetic component from the treated product.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27307198A JP4020511B2 (en) | 1998-09-28 | 1998-09-28 | Waste incineration residue treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27307198A JP4020511B2 (en) | 1998-09-28 | 1998-09-28 | Waste incineration residue treatment method |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2000093924A true JP2000093924A (en) | 2000-04-04 |
JP4020511B2 JP4020511B2 (en) | 2007-12-12 |
Family
ID=17522748
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP27307198A Expired - Lifetime JP4020511B2 (en) | 1998-09-28 | 1998-09-28 | Waste incineration residue treatment method |
Country Status (1)
Country | Link |
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JP (1) | JP4020511B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111185464A (en) * | 2020-02-04 | 2020-05-22 | 绵竹市金坤化工有限公司 | Method and system for recycling zirconium oxide |
CN115261080A (en) * | 2022-09-01 | 2022-11-01 | 西安热工研究院有限公司 | Three-section type solid waste municipal domestic garbage gasification furnace and use method |
-
1998
- 1998-09-28 JP JP27307198A patent/JP4020511B2/en not_active Expired - Lifetime
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111185464A (en) * | 2020-02-04 | 2020-05-22 | 绵竹市金坤化工有限公司 | Method and system for recycling zirconium oxide |
CN111185464B (en) * | 2020-02-04 | 2021-10-22 | 绵竹市金坤化工有限公司 | Method and system for recycling zirconium oxide |
CN115261080A (en) * | 2022-09-01 | 2022-11-01 | 西安热工研究院有限公司 | Three-section type solid waste municipal domestic garbage gasification furnace and use method |
CN115261080B (en) * | 2022-09-01 | 2023-10-20 | 西安热工研究院有限公司 | Three-section type solid waste city household garbage gasifier and use method thereof |
Also Published As
Publication number | Publication date |
---|---|
JP4020511B2 (en) | 2007-12-12 |
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