JPS59138804A - Method of fluidized combustion of waste - Google Patents
Method of fluidized combustion of wasteInfo
- Publication number
- JPS59138804A JPS59138804A JP1243583A JP1243583A JPS59138804A JP S59138804 A JPS59138804 A JP S59138804A JP 1243583 A JP1243583 A JP 1243583A JP 1243583 A JP1243583 A JP 1243583A JP S59138804 A JPS59138804 A JP S59138804A
- Authority
- JP
- Japan
- Prior art keywords
- temperature
- alkali
- waste water
- layer
- waste
- 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
Links
Abstract
Description
【発明の詳細な説明】
類金属の少なくとも一方を含む廃棄物を流動床焼却炉で
焼却する際に流動媒体の焼結等によるトラブルを回避し
ながら焼却処理する廃棄物の流動焼却方法の改良に関す
るものである。DETAILED DESCRIPTION OF THE INVENTION This invention relates to an improvement in a fluidized incineration method for waste that avoids troubles such as sintering of the fluidized medium when incinerating waste containing at least one of the metals in a fluidized bed incinerator. It is something.
従来、バルプ廃液汚泥,食品または医薬品製造工場等か
ら排出される廃液もしくは汚泥を流動床焼却炉で焼却処
理する際には砕砂(Si02を主成分とする)を流動媒
体として用いかつ流動層内の温度をアルカリ金属又はア
ルカリ土類金属化合物の融点以下に制御して運転する方
法が通常用いられていた。流動層内の温度をアルカリ金
属又はアルカリ土類金属化合物の融点以下にする理由と
しては、融点以上で運転を行なうと砕砂(S;O2)と
アルカリ金属化合物、例えばNact。Conventionally, when waste liquid sludge, waste liquid or sludge discharged from food or pharmaceutical manufacturing factories, etc., is incinerated in a fluidized bed incinerator, crushed sand (mainly composed of Si02) is used as a fluidized medium and A method in which the temperature is controlled to be below the melting point of the alkali metal or alkaline earth metal compound has been commonly used. The reason why the temperature in the fluidized bed is kept below the melting point of the alkali metal or alkaline earth metal compound is that if the operation is carried out above the melting point, crushed sand (S; O2) and the alkali metal compound, such as Nact, will be generated.
Kc7等の溶融塩が反応しガラス質化合物を生成し、該
ガラス質化合物が互いに固着して所謂焼結を生じせしめ
流動不能におちいることになるからである。This is because the molten salt such as Kc7 reacts to produce a glassy compound, and the glassy compounds stick to each other, causing so-called sintering and becoming unable to flow.
流動媒体としてSi02を用いる通常の流動層の場合は
、次のような反応によって焼結現象を生ずる。In the case of a normal fluidized bed using Si02 as a fluidizing medium, the following reaction causes a sintering phenomenon.
3SiO2+2Naca+H20 →Na20 命3s
+(h+2HclNa20・3Si02(融点1175
°F)Na20 ・3Si02+3sio 2+ 3C
aO −+ Na20− 3Ca() 5Si02(デ
ビトライト)
(融点1885°F)
Na20@3S102+2CaO→Na2Q・2CaO
・3S102(融点2343°F)
これら6理由により流動層内温度は通常アルカリ金属又
はアルカリ土類金属化合物の融点以下に制御して運転し
ているが、本方法には次の問題点がある。3SiO2+2Naca+H20 →Na20 Life 3s
+(h+2HclNa20・3Si02 (melting point 1175
°F) Na20 ・3Si02+3sio 2+ 3C
aO −+ Na20− 3Ca() 5Si02 (Devitrite) (Melting point 1885°F) Na20@3S102+2CaO→Na2Q・2CaO
-3S102 (Melting point 2343°F) For these six reasons, the fluidized bed temperature is usually controlled to be below the melting point of the alkali metal or alkaline earth metal compound, but this method has the following problems.
すなわち、融点以下に流動層内温度を制御して運転する
と、該アルカリ金属もしくはアルカリ土類金属化合物が
流動層内に蓄積し、特にNacl。That is, when the fluidized bed is operated with the temperature controlled below its melting point, the alkali metal or alkaline earth metal compound accumulates in the fluidized bed, especially NaCl.
Kct等のアルカリ金属塩化物の場合には流動層内に設
置されている空気分散ノズル等の金属製付帯装置が腐食
によって損耗し、ひいては運転不能におちいることにな
る。In the case of alkali metal chlorides such as Kct, metal accessories such as air dispersion nozzles installed in the fluidized bed are worn out due to corrosion, and eventually become inoperable.
本発明は、このような欠点を解消するため長年研究した
結果、高温下においてもアルカリ金属もしくはアルカリ
土類化合物と反応せず焼結現象を生じないような流動媒
体を見い出したものである。The present invention has been made as a result of many years of research to eliminate these drawbacks, and has resulted in the discovery of a fluid medium that does not react with alkali metals or alkaline earth compounds and does not cause sintering even at high temperatures.
すなわち、流動媒体としてアルミナ(A−!20a:
95〜97%、51o2:2〜3%、 ’CaO1〜2
%)を用い、かつ流動層内温度はアルカリ金属化合物等
が溶融する温度以上、好ましくは炉焼装置が許容可能な
温度程度の高温に維持し、アルカリ金属化合物を蒸気と
して層外に揮蔽゛せしめ層内には蓄積させないように運
転することを目的とし、その特徴とするところは、アル
カリ金属又はアルカリ土類金属を含む廃棄物を酸化アル
ミニウムを主成分とする流動媒体とともに焼却処理する
ことにある。That is, alumina (A-!20a:
95-97%, 51o2:2-3%, 'CaO1-2
%), and the temperature inside the fluidized bed is maintained at a temperature higher than the melting temperature of the alkali metal compounds, preferably at a temperature that can be tolerated by the furnace, and the alkali metal compounds are volatilized outside the bed as vapor. The purpose is to operate in a manner that prevents accumulation in the sediment layer, and its feature is that waste containing alkali metals or alkaline earth metals is incinerated together with a fluid medium mainly composed of aluminum oxide. be.
このような構成とすることにより、流動媒体であるアル
ミナは上述の塩類とは反応せず焼結現象は生じないので
パルプ廃液汚泥2食品廃液汚泥及び医薬品製造廃液汚泥
等のアルカリ金属又はアルカリ土類金属を含む廃棄物の
焼却処理が安定かつ連続して行えるという利点がある。With this structure, alumina, which is a fluid medium, does not react with the above-mentioned salts and no sintering phenomenon occurs, so that it can be used for alkali metals or alkaline earths such as pulp waste liquid sludge, food waste liquid sludge, and pharmaceutical manufacturing waste liquid sludge. This method has the advantage that waste containing metal can be incinerated stably and continuously.
以下本発明の最も好ましい実施例について図面に基づい
て詳細に説明する。The most preferred embodiments of the present invention will be described in detail below with reference to the drawings.
流動用通風機1から供給される。流−動炉焼用空気は空
気配管2を通り、ウィンドボックス3に送られる。It is supplied from the flow ventilation fan 1. Air for fluidized furnace firing passes through an air pipe 2 and is sent to a wind box 3.
5は流動層で、被焼却物供給口9から投入された被焼却
物は空気分散ノズル4から流動層5に供給される空気に
よって流動焼却される。未燃物はフリーボード7で完全
焼却された後炉出口8から排出される。また6は焼却炉
本体で内面耐火物構造である。下記に主要諸元を示す。Reference numeral 5 denotes a fluidized bed, in which the material to be incinerated is introduced from the material supply port 9 and is fluidized and incinerated by air supplied from the air dispersion nozzle 4 to the fluidized bed 5. Unburnt materials are completely incinerated in the freeboard 7 and then discharged from the furnace outlet 8. Further, 6 is the incinerator main body, which has an internal refractory structure. The main specifications are shown below.
次に流動媒体としてアルミナ(At203 : 95〜
97%。Next, alumina (At203: 95~
97%.
5i02:z−3%、 CaO: 1−2%)および珪
砂(SiO2: 97.8 % +At203:15%
、 pz2o3: 0.04)を用いた場合の実施f1
4について示す。被焼却物(食品廃液汚泥)の性状ル
は概下記の通りである。5i02:z-3%, CaO: 1-2%) and silica sand (SiO2: 97.8% + At203: 15%
, pz2o3: 0.04)
4 will be shown. The properties of the incinerated material (food waste liquid sludge) are approximately as follows.
上述のように珪砂を用いた場合は約70時間で焼結し、
運転不能となったがアルミナを流動媒体として用いた場
合は焼結現象も発生せず長時間の連続運転が可能である
ことが実証された。As mentioned above, when using silica sand, sintering takes about 70 hours,
Although operation became impossible, it was demonstrated that continuous operation for a long time was possible without sintering when alumina was used as the fluidizing medium.
図面は本発明に係る被焼却物を焼却処理する流動床焼却
炉の要部断面図である。The drawing is a sectional view of a main part of a fluidized bed incinerator for incinerating materials to be incinerated according to the present invention.
Claims (1)
アルミニウムを主成分とする流動媒体とともに焼却処理
することを特徴きする廃棄物の流動焼却方法。1. A method for fluidized waste incineration, which comprises incinerating waste containing alkali metals or alkaline earth metals together with a fluidized medium containing aluminum oxide as a main component.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1243583A JPS59138804A (en) | 1983-01-28 | 1983-01-28 | Method of fluidized combustion of waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1243583A JPS59138804A (en) | 1983-01-28 | 1983-01-28 | Method of fluidized combustion of waste |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS59138804A true JPS59138804A (en) | 1984-08-09 |
Family
ID=11805210
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1243583A Pending JPS59138804A (en) | 1983-01-28 | 1983-01-28 | Method of fluidized combustion of waste |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS59138804A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1987005089A1 (en) * | 1986-02-14 | 1987-08-27 | Ebara Corporation | Fluidized-bed method for burning combustible materials |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS493482A (en) * | 1972-04-26 | 1974-01-12 | ||
JPS4933699U (en) * | 1972-06-21 | 1974-03-25 | ||
JPS50139577A (en) * | 1974-04-24 | 1975-11-07 | ||
JPS5469699A (en) * | 1977-11-08 | 1979-06-04 | Energy Inc | Method of processing waste |
-
1983
- 1983-01-28 JP JP1243583A patent/JPS59138804A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS493482A (en) * | 1972-04-26 | 1974-01-12 | ||
JPS4933699U (en) * | 1972-06-21 | 1974-03-25 | ||
JPS50139577A (en) * | 1974-04-24 | 1975-11-07 | ||
JPS5469699A (en) * | 1977-11-08 | 1979-06-04 | Energy Inc | Method of processing waste |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1987005089A1 (en) * | 1986-02-14 | 1987-08-27 | Ebara Corporation | Fluidized-bed method for burning combustible materials |
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