JPH11173528A - Treating method for waste - Google Patents

Treating method for waste

Info

Publication number
JPH11173528A
JPH11173528A JP9362248A JP36224897A JPH11173528A JP H11173528 A JPH11173528 A JP H11173528A JP 9362248 A JP9362248 A JP 9362248A JP 36224897 A JP36224897 A JP 36224897A JP H11173528 A JPH11173528 A JP H11173528A
Authority
JP
Japan
Prior art keywords
waste
acid
incinerator
residue
furnace
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
JP9362248A
Other languages
Japanese (ja)
Inventor
Kazuo Doi
一雄 土居
Akihiro Kodama
昭弘 児玉
Akio Katsuura
彰夫 勝浦
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.)
Nippon Synthetic Chemical Industry Co Ltd
Original Assignee
Nippon Synthetic Chemical Industry 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 Nippon Synthetic Chemical Industry Co Ltd filed Critical Nippon Synthetic Chemical Industry Co Ltd
Priority to JP9362248A priority Critical patent/JPH11173528A/en
Publication of JPH11173528A publication Critical patent/JPH11173528A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To prevent generation of clinker in an incinerating furnace and stabilize the operation of the incinerating furnace for a long period of time by a method wherein industrial waste, containing alkali metals, is neutralized by acid and, thereafter, is incinerated. SOLUTION: Waste, containing alkaline metals, is the residue of distillation, which contains alkali metals such as sodium hydroxide or the like which is added at the time of preparation of imidazoles such as imidazole or 2-methyl imidazole or the like, while the residue is treated as the waste finally through incineration. Hydrochloric acid, sulfuric acid, nitric acid or the like can be recommended as the acid employed for the neutralization of residue of such distillation, however, sulfuric acid is preferably employed from a view point that the melting point of salt produced after neutralization is higher than a temperature in the incinerating furnace. A furnace, used for the incineration of waste generally or a dry distillation gasifying incinerator, a direct combustion type incinerator, a rotary kiln type incinerator, a fluidized bed type incinerator or the like, for example, is utilized, however, the fluidized bed type incinerator is preferably used among these furnaces.

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、アルカリ金属を含
む廃棄物、例えばイミダゾール類の製造時に発生する蒸
留残渣等の廃棄物の処理法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating a waste containing an alkali metal, for example, a waste such as a distillation residue generated during the production of imidazoles.

【0002】[0002]

【従来の技術】一般に、イミダゾールや2−メチルイミ
ダゾール等のイミダゾール類の製造時においては、副生
物の分解のために、水酸化ナトリウムや水酸化カリウム
等のアルカリを添加して処理することが行われており、
かかる製造時には、水酸化ナトリムや水酸化カリウム等
のアルカリ金属を含む廃棄物が発生し、かかる廃棄物は
焼却炉等で焼却処理されているのが現状である。
2. Description of the Related Art Generally, in the production of imidazoles such as imidazole and 2-methylimidazole, an alkali such as sodium hydroxide or potassium hydroxide is added to decompose by-products. Have been
At the time of such production, waste containing alkali metals such as sodium hydroxide and potassium hydroxide is generated, and at present, such waste is incinerated in an incinerator or the like.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、上記の
廃棄物をそのまま焼却処理に供すると、該廃棄物中のア
ルカリ金属が焼却炉中の熱媒体(ケイ砂)や炉材(煉
瓦)に含有されるシリカ(SiO2)と反応(結合)し
て、焼却炉内にNa2SiO3やK2SiO3等の所謂ガラ
ス状クリンカーを生成して、焼却炉の操業が困難となっ
たり、あるいは操業継続が不可能となる場合もある。
However, when the above-mentioned waste is subjected to incineration as it is, the alkali metal in the waste is contained in the heat medium (silica sand) and the furnace material (brick) in the incinerator. Reacts (combines) with the silica (SiO 2 ) to form a so-called glassy clinker such as Na 2 SiO 3 or K 2 SiO 3 in the incinerator, which makes the operation of the incinerator difficult or difficult In some cases, continuation is not possible.

【0004】[0004]

【課題を解決するための手段】そこで、本発明者は、か
かる現況に鑑みて鋭意研究を重ねた結果、アルカリ金属
を含む廃棄物を酸で中和した後、焼却することにより、
上記の課題を解決することができることを見出し、本発
明を完成するに至った。
Accordingly, the present inventor has conducted intensive studies in view of the present situation. As a result, the waste containing alkali metals is neutralized with an acid and then incinerated.
The inventors have found that the above problems can be solved, and have completed the present invention.

【0005】[0005]

【発明の実施の形態】以下に、本発明を詳細に述べる。
本発明の処理法が適用されるアルカリ金属を含む廃棄物
とは、イミダゾールや2−メチルイミダゾール等のイミ
ダゾール類の製造時に添加された水酸化ナトリム、水酸
化カリウム等のアルカリ金属を含む蒸留残渣で、最終的
に廃棄物として焼却処理されるものである。すなわち、
アンモニア、グリオキザール及びホルマリン(イミダゾ
ールの場合)又はアセトアルデヒド(2−メチルイミダ
ゾールの場合)等を原料として、反応を行って、その
後、生成した副生物の分解のために水酸化ナトリム、水
酸化カリウム等のアルカリを添加して、目的とするイミ
ダゾールや2−メチルイミダゾール等のイミダゾール類
を蒸留により得る時に、蒸留残渣として発生するもので
ある。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail.
The waste containing an alkali metal to which the treatment method of the present invention is applied is sodium hydroxide added during production of imidazoles such as imidazole and 2-methylimidazole, and a distillation residue containing an alkali metal such as potassium hydroxide. Finally, it is incinerated as waste. That is,
The reaction is carried out using ammonia, glyoxal and formalin (in the case of imidazole) or acetaldehyde (in the case of 2-methylimidazole) as the raw materials, and then sodium hydroxide, potassium hydroxide, etc. for the decomposition of the generated by-products. When an imidazole such as imidazole or 2-methylimidazole is obtained by distillation by adding an alkali, it is generated as a distillation residue.

【0006】本発明においては、かかる蒸留残渣(廃棄
物)を、焼却処理に供する前に酸で中和することを最大
の特徴とするものであり、かかる中和処理について詳細
に説明する。中和に用いる酸としては、特に限定されず
塩酸、硫酸、硝酸、リン酸等を挙げることができるが、
中和後に生成する塩の融点が焼却炉内の温度より高いと
いう点で硫酸を用いることが好ましく、通常は、市販の
硫酸を用いることができる。中和にあたっては、上記の
蒸留前に使用したアルカリと同当量の酸を廃棄物に20
〜50℃で、pHが9以下になるように滴下すればよ
い。
The most characteristic feature of the present invention is that such a distillation residue (waste) is neutralized with an acid before being subjected to incineration. The neutralization will be described in detail. The acid used for neutralization is not particularly limited, and examples thereof include hydrochloric acid, sulfuric acid, nitric acid, and phosphoric acid.
It is preferable to use sulfuric acid from the viewpoint that the melting point of the salt formed after the neutralization is higher than the temperature in the incinerator, and usually, commercially available sulfuric acid can be used. In the neutralization, the same amount of acid as the alkali used before the above-mentioned distillation was added to the waste as 20%.
What is necessary is just to drop at about 50 degreeC so that pH may be set to 9 or less.

【0007】かくして、中和処理された廃棄物は、次い
で焼却炉に供されるのであるが、かかる焼却炉の形式や
焼却時の諸条件などに特別の制限はなく、一般に廃棄物
の焼却に使用されている焼却炉、例えばマグネシア煉
瓦、硅石煉瓦、アルミナ質煉瓦などの炉材からなる、乾
留ガス化焼却炉、直燃式焼却炉、ロータリーキルン式焼
却炉、流動層式焼却炉などのタイプの焼却炉を用いるこ
とができ、中でも流動層式焼却炉を用いるとき本発明の
効果を顕著に得ることができる。
[0007] The neutralized waste is then supplied to an incinerator, but there are no particular restrictions on the type of incinerator and various conditions at the time of incineration. Incinerators used are made of furnace materials such as magnesia bricks, silica bricks, and alumina bricks. An incinerator can be used, and when a fluidized bed incinerator is used, the effect of the present invention can be remarkably obtained.

【0008】中和処理された廃棄物を焼却炉に供給する
方法としては、特に限定されないが、該廃棄物をフィー
ダー等により連続的に供給する方法、スプレー等により
噴霧する方法等を挙げることができるが、特に限定はさ
れない。
The method of supplying the neutralized waste to the incinerator is not particularly limited, and examples thereof include a method of continuously supplying the waste with a feeder or the like, a method of spraying with a spray or the like, and the like. Although possible, there is no particular limitation.

【0009】[0009]

【実施例】以下、実施例を挙げて本発明を具体的に説明
する。 実施例1 25%アンモニア水(4527kg)、40%グリオキ
ザール水溶液(4387kg)及び37%ホルマリン水
溶液(2087kg)を反応させて、イミダゾールを得
る際に、発生した副生物553kgに水酸化カリウム2
7.2kgを添加して、蒸留した後、得られた蒸留残渣
(廃棄物)350kgに対して、98%の硫酸24.2
kgを、30℃で120分かけて滴下して、中和処理
(pH=8.5)を行った。
The present invention will be specifically described below with reference to examples. Example 1 25% ammonia water (4527 kg), 40% glyoxal aqueous solution (4387 kg) and 37% formalin aqueous solution (2087 kg) were reacted to obtain imidazole.
After adding 7.2 kg and distilling, 98% sulfuric acid 24.2% was added to 350 kg of the obtained distillation residue (waste).
kg was dropped at 30 ° C. over 120 minutes to perform a neutralization treatment (pH = 8.5).

【0010】次いで、処理された廃棄物を40kg/h
rの割合で連続的に流動層式焼却炉(内容積22m3
に供給して、炉内温度750℃で焼却を行った。この焼
却炉の運転を90日間行ったが、炉内にはクリンカーの
発生もなく、良好な操業を行うことができた。
Next, the treated waste is reduced to 40 kg / h.
Continuously in a fluidized bed incinerator at a rate of r (internal volume 22 m 3 )
And incinerated at a furnace temperature of 750 ° C. The operation of the incinerator was performed for 90 days, and no clinker was generated in the incinerator, and good operation could be performed.

【0011】実施例2 実施例1において、25%アンモニア水(1847k
g)、40%グリオキザール水溶液(1824kg)及
び70%アセトアルデヒド水溶液(877kg)を反応
させて、2−メチルイミダゾールの製造とした以外は同
様に行って、焼却炉の運転を90日間行ったが、炉内に
はクリンカーの発生もなく、良好な操業を行うことがで
きた。
Example 2 In Example 1, 25% aqueous ammonia (1847 k
g), a 40% aqueous glyoxal solution (1824 kg) and a 70% acetaldehyde aqueous solution (877 kg) were reacted to produce 2-methylimidazole in the same manner, and the incinerator was operated for 90 days. There was no clinker inside and good operation was possible.

【0012】実施例3 実施例1において、硫酸24.2kgに変えて、75%
のリン酸を310kg用いた以外は同様に行って、焼却
炉の運転を60日間行ったが、炉内にはクリンカーの発
生もなく、良好な操業を行うことができた。
Example 3 In Example 1, 75% was used instead of 24.2 kg of sulfuric acid.
The incinerator was operated for 60 days in the same manner except that 310 kg of phosphoric acid was used. However, no clinker was generated in the furnace, and good operation could be performed.

【0013】比較例1 実施例1において、廃棄物の中和処理を行わずに直接焼
却処理を行ったが、30日後には炉内にクリンカーが多
量に生成して、操業を中止せざるを得なかった。
Comparative Example 1 In Example 1, the waste was directly incinerated without being neutralized, but after 30 days a large amount of clinker was generated in the furnace, and the operation had to be stopped. I didn't get it.

【0014】[0014]

【発明の効果】本発明においては、アルカリ金属を含む
産業廃棄物を酸で中和した後、焼却しているため、焼却
炉内にクリンカーが発生することなく、焼却炉運転を長
期にわたって安定的に行うことができる。
According to the present invention, since industrial waste containing alkali metals is incinerated after neutralization with an acid, clinker does not occur in the incinerator, and the operation of the incinerator can be stabilized for a long period of time. Can be done.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI F23G 5/02 ZAB F23G 7/00 ZABA 7/00 ZAB B09B 3/00 303J ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI F23G 5/02 ZAB F23G 7/00 ZABA 7/00 ZAB B09B 3/00 303J

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 アルカリ金属を含む廃棄物を酸で中和し
た後、焼却することを特徴とする廃棄物の処理法。
1. A method for treating waste, comprising: neutralizing waste containing an alkali metal with an acid and then incinerating the waste.
【請求項2】 アルカリ金属が水酸化カリウムまたは水
酸化ナトリウムで、かつ酸が硫酸であることを特徴とす
る請求項1記載の廃棄物の処理法。
2. The method for treating waste according to claim 1, wherein the alkali metal is potassium hydroxide or sodium hydroxide and the acid is sulfuric acid.
【請求項3】 焼却に用いる焼却炉が流動層式焼却炉で
あることを特徴とする請求項1または2記載の廃棄物の
処理法。
3. The method for treating waste according to claim 1, wherein the incinerator used for incineration is a fluidized bed incinerator.
JP9362248A 1997-12-10 1997-12-10 Treating method for waste Pending JPH11173528A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9362248A JPH11173528A (en) 1997-12-10 1997-12-10 Treating method for waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9362248A JPH11173528A (en) 1997-12-10 1997-12-10 Treating method for waste

Publications (1)

Publication Number Publication Date
JPH11173528A true JPH11173528A (en) 1999-06-29

Family

ID=18476370

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9362248A Pending JPH11173528A (en) 1997-12-10 1997-12-10 Treating method for waste

Country Status (1)

Country Link
JP (1) JPH11173528A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002349819A (en) * 2001-05-28 2002-12-04 Takuma Co Ltd Fluidized bed type combustion method and device for waste containing agglomerate component

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002349819A (en) * 2001-05-28 2002-12-04 Takuma Co Ltd Fluidized bed type combustion method and device for waste containing agglomerate component

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