JP2730820B2 - Method for producing zeolite - Google Patents
Method for producing zeoliteInfo
- Publication number
- JP2730820B2 JP2730820B2 JP4029125A JP2912592A JP2730820B2 JP 2730820 B2 JP2730820 B2 JP 2730820B2 JP 4029125 A JP4029125 A JP 4029125A JP 2912592 A JP2912592 A JP 2912592A JP 2730820 B2 JP2730820 B2 JP 2730820B2
- Authority
- JP
- Japan
- Prior art keywords
- zeolite
- melting furnace
- naoh
- sewage sludge
- heat
- 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
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B39/00—Compounds having molecular sieve and base-exchange properties, e.g. crystalline zeolites; Their preparation; After-treatment, e.g. ion-exchange or dealumination
- C01B39/02—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof; Direct preparation thereof; Preparation thereof starting from a reaction mixture containing a crystalline zeolite of another type, or from preformed reactants; After-treatment thereof
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Silicates, Zeolites, And Molecular Sieves (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は下水汚泥またはその焼却
灰を原料とするゼオライトの製造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 producing zeolite from sewage sludge or incinerated ash.
【0002】[0002]
【従来の技術】ゼオライトは沸石と呼ばれる鉱物であ
り、 Me2/nO ・Al2O3 ・xSiO2 ・yH2O(Me:アルカリ又
はアルカリ土類、x,y :係数)の一般式で表される三次
元結晶構造を有する含水アルミノケイ酸鉱物である。こ
のゼオライトは結晶内に多量の水分を含み、加熱したり
減圧するとこの水分を放出し、空になった結晶内に分子
を吸着する能力を持つことで知られている。BACKGROUND OF THE INVENTION Zeolites are minerals called zeolite, Me 2 / n O · Al 2 O 3 · xSiO 2 · yH 2 O (Me: alkaline or alkaline-earth, x, y: coefficient) by the general formula It is a hydrous aluminosilicate mineral having a three-dimensional crystal structure represented. This zeolite is known to contain a large amount of water in the crystal, release this water when heated or depressurized, and has the ability to adsorb molecules into the vacated crystal.
【0003】一般にゼオライトの品質は塩基置換容量
(CEC)で評価され、比較的安価な天然ゼオライトはCEC
が150 meq/100g程度である。また、アルミン酸ナトリウ
ム、ケイ酸ソーダ、NaOHを原料として工業的に製造され
る合成ゼオライトはCEC が400〜600 meq/100gという優
れた吸着性能を持つが、トン当りの価格が数100 万円と
極めて高価である欠点がある。[0003] Generally, the quality of zeolite is evaluated by base substitution capacity (CEC), and relatively inexpensive natural zeolite is CEC.
Is about 150 meq / 100g. Synthetic zeolites produced industrially from sodium aluminate, sodium silicate, and NaOH have excellent adsorption performance with a CEC of 400-600 meq / 100g, but cost per million tons of several million yen. It has the disadvantage of being very expensive.
【0004】そこで最近では、特開平2−221114
号公報、特開平3−40914号公報等に示されるよう
に、石炭灰から発生するフライアッシュをNaOH等ととも
に煮沸してゼオライトを合成する方法が研究されてい
る。しかしこの方法で合成されたゼオライトのCEC はそ
のカタログ値によれば200 〜350 meq/100gであり、従来
の合成ゼオライトよりも安価である反面、CEC 値が低い
という問題がある。しかもフライアッシュをNaOHで煮沸
するゼオライト製造装置には多量の熱量が必要であると
ともに、ゼオライト製造装置から多量のNaOH廃液が発生
するという問題もある。Therefore, recently, Japanese Patent Application Laid-Open No. Hei.
As disclosed in Japanese Patent Application Laid-Open No. HEI 3-40914, a method of synthesizing zeolite by boiling fly ash generated from coal ash together with NaOH or the like has been studied. However, the zeolite synthesized by this method has a CEC of 200 to 350 meq / 100 g according to its catalog value, which is less expensive than the conventional synthetic zeolite, but has a problem that the CEC value is low. Moreover, a zeolite manufacturing apparatus that boil fly ash with NaOH requires a large amount of heat, and also has a problem that a large amount of NaOH waste liquid is generated from the zeolite manufacturing apparatus.
【0005】[0005]
【発明が解決しようとする課題】本発明は上記したよう
な従来の問題点を解消し、CEC が合成ゼオライトとほぼ
同等であるゼオライトを極めて安価に、しかもNaOH廃液
等の問題を生ずることなく製造することができるゼオラ
イトの製造法を提供するために完成されたものである。SUMMARY OF THE INVENTION The present invention solves the above-mentioned conventional problems and produces a zeolite having a CEC almost equivalent to that of a synthetic zeolite at a very low cost and without causing problems such as NaOH waste liquid. It has been completed to provide a method for producing a zeolite.
【0006】[0006]
【課題を解決するための手段】上記の課題を解決するた
め、本発明者は無機分にSiO2、Al2O3 を主成分とする下
水汚泥のような廃棄物に着目し、従来はその処分に困っ
ていた廃棄物を原料としてゼオライトを合成できること
を見いだした。またフライアッシュを原料としたゼオラ
イトのCEC が低いのは、フライアッシュ中にゼオライト
の生成に寄与するガラス状の成分が少ないことおよび生
成物質と未生成物質との分離が困難であることが原因で
あることを見いだした。更にゼオライト生成装置に必要
な熱量は下水汚泥等の処理に広く使用されているスラグ
化のための溶融炉の排熱を利用でき、またNaOH廃液は溶
融炉の排ガス中のSOx 吸収に有効に利用できることを見
いだした。Means for Solving the Problems To solve the above problems, the present inventors have focused on wastes such as sewage sludge containing SiO 2 and Al 2 O 3 as the main components in the inorganic component. They found that zeolite can be synthesized from waste that had been difficult to dispose of as a raw material. The low CEC of zeolite made from fly ash is also low due to the small amount of glassy components contributing to the formation of zeolite in fly ash and the difficulty in separating produced and unproduced substances. I found something. Furthermore, the amount of heat required for the zeolite generator can use the waste heat of the melting furnace for slag, which is widely used in the treatment of sewage sludge, and the NaOH waste liquid can be effectively used for SOx absorption in the exhaust gas of the melting furnace. I found what I could do.
【0007】本発明は上記した知見に基づいて完成され
たものであり、下水汚泥またはその焼却灰を溶融炉で溶
融して水砕スラグとしたうえ、これにNaOHを加えて煮沸
してゼオライトを生成させるとともに、この溶融炉の排
熱を回収してゼオライト製造装置および生成されたゼオ
ライトの乾燥装置の熱源として利用し、またゼオライト
製造装置から出たNaOHの廃液を溶融炉の排ガス中のSOx
吸収に利用することを特徴とするものである。以下に本
発明を図示の実施例によって更に詳細に説明する。The present invention has been completed on the basis of the above-mentioned findings. Melting sewage sludge or its incinerated ash in a melting furnace to form granulated slag, and adding NaOH to the slag to boil the zeolite. Along with the generation, the waste heat of the melting furnace is recovered and used as a heat source for a zeolite manufacturing device and a drying device for the generated zeolite, and NaOH waste liquid from the zeolite manufacturing device is used as SOx in the exhaust gas of the melting furnace.
It is characterized in that it is used for absorption. Hereinafter, the present invention will be described in more detail with reference to the illustrated embodiments.
【0008】[0008]
実施例1・・・焼却灰を原料とした例 図1は原料として下水汚泥脱水ケーキの焼却灰を使用し
た実施例を示すものである。まず焼却灰は溶融炉1にお
いて1300〜1500℃で溶融され、これを水中に投入して水
砕スラグとする。この結果、数mm〜数10mmの水砕スラグ
が得られるが、必要に応じて破砕分級してもよい。水砕
スラグはフライアッシュとは異なり結晶部分がほとんど
なく、ゼオライト合成に適したガラス質がほぼ100 %を
占めるものである。Example 1 Example in which incinerated ash is used as a raw material FIG. 1 shows an example in which incinerated ash of a sewage sludge dewatered cake is used as a raw material. First, incinerated ash is melted in a melting furnace 1 at 1300 to 1500 ° C., and is poured into water to form granulated slag. As a result, granulated slag of several mm to several tens mm is obtained, but may be crushed and classified as needed. Granulated slag, unlike fly ash, has almost no crystal parts and almost 100% vitreous material suitable for zeolite synthesis.
【0009】この水砕スラグは次にゼオライト製造装置
2において高濃度NaOHとともに85〜100 ℃で数時間〜数
10時間煮沸される。この結果、水熱合成によりゼオライ
トが合成されるが、合成されたゼオライトは数μm 以下
の微粉であるのに対して、未反応の水砕スラグは数mm〜
数10mmの粒径を持つので、ふるい等の分離装置3によっ
て容易に分離することができる。The granulated slag is then mixed with high-concentration NaOH at 85 to 100 ° C. for several hours to several hours in the zeolite production apparatus 2.
Boil for 10 hours. As a result, zeolite is synthesized by hydrothermal synthesis.The synthesized zeolite is fine powder of several μm or less, while unreacted granulated slag is several mm to
Since it has a particle size of several tens of mm, it can be easily separated by a separation device 3 such as a sieve.
【0010】次に合成されたゼオライトは脱水装置4に
より脱水され、更に乾燥装置5により100 ℃以上の高温
で乾燥されて製品となる。このようにして得られたゼオ
ライトは純度が高く、しかも市販の合成ゼオライトのCE
C と比較しほぼ同等でありフライアッシュを原料とした
もののCEC よりもはるかに優れた品質のものである。Next, the synthesized zeolite is dehydrated by a dehydrator 4 and further dried by a drying device 5 at a high temperature of 100 ° C. or more to obtain a product. The zeolite thus obtained has a high purity and is commercially available synthetic zeolite CE
Compared to C, it is almost the same, and it is made of fly ash but has much better quality than CEC.
【0011】一方、溶融炉1から出た約1200℃の排ガス
は一般的に熱交換器6により熱交換されたうえ、除塵器
7でダストを除去され、吸収塔8で排ガス中のSOx を除
去されて大気中へ放出される。熱交換器6の形式につい
ては特に限定されるものではない。本発明ではこのよう
にして回収された熱量は図1に破線で示すように一部が
溶融炉1へ戻され、残部はゼオライト製造装置2および
生成されたゼオライトの乾燥装置5の熱源として有効に
利用される。On the other hand, the exhaust gas of about 1200 ° C. discharged from the melting furnace 1 is generally heat-exchanged by a heat exchanger 6, dust is removed by a dust remover 7, and SOx in the exhaust gas is removed by an absorption tower 8. And released into the atmosphere. The type of the heat exchanger 6 is not particularly limited. In the present invention, a part of the heat recovered in this way is returned to the melting furnace 1 as shown by a broken line in FIG. 1, and the remainder is effectively used as a heat source for the zeolite production apparatus 2 and the drying apparatus 5 for the generated zeolite. Used.
【0012】またゼオライト製造装置2では高濃度NaOH
が使用されるが、ここで消費されるものはNa+ であって
OH- は余剰となる。一方、吸収塔8で必要なものはOH-
であるから、ゼオライト製造装置2からのNaOHの廃液を
吸収塔8へ送れば、溶融炉1の排ガス中のSOx を吸収さ
せることができ、併せて系外へのNaOHの排出を大幅に減
少させることができる。In the zeolite production apparatus 2, high concentration NaOH
Is used, but what is consumed here is Na +
OH - it becomes a surplus. On the other hand, what is needed in the absorption tower 8 OH -
Therefore, if NaOH waste liquid from the zeolite manufacturing apparatus 2 is sent to the absorption tower 8, SOx in the exhaust gas of the melting furnace 1 can be absorbed, and at the same time, NaOH emission to the outside of the system is greatly reduced. be able to.
【0013】実施例2・・・下水汚泥脱水ケーキを原料
とする例 図2に示す第2の実施例では、下水汚泥脱水ケーキを原
料とする。この場合には65〜85%の水分を含む下水汚泥
脱水ケーキを、まず乾燥機9で水分が5%前後となるま
で乾燥したうえで、溶融炉1に投入して溶融して水砕ス
ラグとする。この水砕スラグからのゼオライトの合成方
法は実施例1と同一である。また溶融炉1からの排ガス
は排熱ボイラーを含む熱交換器6により回収され、これ
により発生した蒸気を前記した乾燥機9、ゼオライト製
造装置2、乾燥装置5等へ送って有効利用する。なおNa
OHの廃液を吸収塔8で有効利用する点も実施例1と同一
である。Embodiment 2—Example Using Sewage Sludge Dewatered Cake as Raw Material In the second embodiment shown in FIG. 2, a sewage sludge dewatered cake is used as a raw material. In this case, the sewage sludge dewatered cake containing 65 to 85% of water is first dried in a drier 9 until the water content becomes about 5%, and then put into the melting furnace 1 to be melted to form granulated slag. I do. The method for synthesizing zeolite from the granulated slag is the same as in Example 1. Exhaust gas from the melting furnace 1 is collected by a heat exchanger 6 including a waste heat boiler, and the steam generated thereby is sent to the above-described dryer 9, zeolite manufacturing apparatus 2, drying apparatus 5 and the like for effective use. Na
The point that the waste liquid of OH is effectively used in the absorption tower 8 is the same as in the first embodiment.
【0014】[0014]
【発明の効果】本発明のゼオライトの製造方法による効
果をまとめると次のとおりである。 従来はその処分に困っていた下水汚泥やその焼却灰
を原料として、CEC 値が高いゼオライトを合成すること
ができる。 下水汚泥の処理のために従来から設置されている溶
融炉の排熱を回収してゼオライト製造装置および生成さ
れたゼオライトの乾燥装置等の熱源として利用すること
ができ、ランニングコストを削減することができる。 ゼオライト製造装置から出たNaOHの廃液を溶融炉の
排ガス中のSOx 吸収に利用することができ、系外へのNa
OHの廃液放出量の減少を図ることができると同時に、吸
収塔のランニングコストを削減することができる。The effects of the method for producing a zeolite of the present invention are summarized as follows. Zeolite with a high CEC value can be synthesized from sewage sludge and its incinerated ash, which had previously been difficult to dispose of. The waste heat of the melting furnace that has been conventionally installed for the treatment of sewage sludge can be recovered and used as a heat source for a zeolite manufacturing device and a drying device for the generated zeolite, thereby reducing running costs. it can. The NaOH waste liquid discharged from the zeolite manufacturing equipment can be used for SOx absorption in the exhaust gas of the melting furnace,
The amount of waste liquid discharged from OH can be reduced, and at the same time, the running cost of the absorption tower can be reduced.
【図1】本発明の第1の実施例を示すフローシートであ
る。FIG. 1 is a flow sheet showing a first embodiment of the present invention.
【図2】本発明の第2の実施例を示すフローシートであ
る。FIG. 2 is a flow sheet showing a second embodiment of the present invention.
1 溶融炉 2 ゼオライト製造装置 5 乾燥装置 6 熱交換器 8 吸収塔 DESCRIPTION OF SYMBOLS 1 Melting furnace 2 Zeolite manufacturing apparatus 5 Drying apparatus 6 Heat exchanger 8 Absorption tower
Claims (1)
融して水砕スラグとしたうえ、これにNaOHを加えて煮沸
してゼオライトを生成させるとともに、この溶融炉の排
熱を回収してゼオライト製造装置および生成されたゼオ
ライトの乾燥装置の熱源として利用し、またゼオライト
製造装置から出たNaOHの廃液を溶融炉の排ガス中のSOx
吸収に利用することを特徴とするゼオライトの製造方
法。1. A sewage sludge or its incinerated ash is melted in a melting furnace to form granulated slag, and NaOH is added to the slag to boil to generate zeolite, and the waste heat of the melting furnace is recovered. It is used as a heat source for the zeolite production equipment and the drying equipment for the generated zeolite, and the NaOH waste liquid from the zeolite production equipment is used as SOx in the exhaust gas of the melting furnace.
A method for producing a zeolite, which is used for absorption.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4029125A JP2730820B2 (en) | 1992-02-17 | 1992-02-17 | Method for producing zeolite |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4029125A JP2730820B2 (en) | 1992-02-17 | 1992-02-17 | Method for producing zeolite |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH05221628A JPH05221628A (en) | 1993-08-31 |
| JP2730820B2 true JP2730820B2 (en) | 1998-03-25 |
Family
ID=12267584
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4029125A Expired - Fee Related JP2730820B2 (en) | 1992-02-17 | 1992-02-17 | Method for producing zeolite |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2730820B2 (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6299854B1 (en) | 1998-06-12 | 2001-10-09 | Teruo Henmi | Method of producing artificial zeolite |
| JP2000335916A (en) * | 1999-05-31 | 2000-12-05 | Akio Henmi | Method and apparatus for producing artificial zeolite from slag |
| US6599494B2 (en) | 1999-08-19 | 2003-07-29 | K.E.M. Corporation | Process for preparing artificial zeolite by a slurry reaction method |
| CN103318908A (en) * | 2013-07-08 | 2013-09-25 | 浙江卓嘉环境工程有限公司 | Method for marking artificial zeolite by utilizing dyeing sludge |
-
1992
- 1992-02-17 JP JP4029125A patent/JP2730820B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH05221628A (en) | 1993-08-31 |
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