JPH04313615A - Method for adjusting basicity of incineration ash in incineration ash-melting furnace - Google Patents
Method for adjusting basicity of incineration ash in incineration ash-melting furnaceInfo
- Publication number
- JPH04313615A JPH04313615A JP7989391A JP7989391A JPH04313615A JP H04313615 A JPH04313615 A JP H04313615A JP 7989391 A JP7989391 A JP 7989391A JP 7989391 A JP7989391 A JP 7989391A JP H04313615 A JPH04313615 A JP H04313615A
- Authority
- JP
- Japan
- Prior art keywords
- basicity
- incinerated ash
- incineration ash
- melting furnace
- 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
Links
- 238000002844 melting Methods 0.000 title claims abstract description 42
- 238000000034 method Methods 0.000 title claims abstract description 12
- 230000008018 melting Effects 0.000 claims abstract description 39
- 238000000197 pyrolysis Methods 0.000 claims description 18
- 238000000354 decomposition reaction Methods 0.000 claims description 2
- 239000000446 fuel Substances 0.000 abstract description 11
- 239000003795 chemical substances by application Substances 0.000 abstract description 8
- 238000005979 thermal decomposition reaction Methods 0.000 abstract description 4
- 239000000155 melt Substances 0.000 abstract description 2
- 239000002699 waste material Substances 0.000 abstract description 2
- 239000010802 sludge Substances 0.000 description 12
- 239000000463 material Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 238000010586 diagram Methods 0.000 description 5
- 238000002156 mixing Methods 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 229910052681 coesite Inorganic materials 0.000 description 1
- 239000004035 construction material Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 229910052906 cristobalite Inorganic materials 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 238000010309 melting process Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 229910052682 stishovite Inorganic materials 0.000 description 1
- 229910052905 tridymite Inorganic materials 0.000 description 1
Landscapes
- Gasification And Melting Of Waste (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は被溶融物である焼却灰の
塩基度調整方法に関し、より詳しくは焼却灰を溶融する
焼却灰溶融炉に要する燃費を削減し得るようにした焼却
灰溶融炉における焼却灰の塩基度調整方法に関するもの
である。[Industrial Application Field] The present invention relates to a method for adjusting the basicity of incinerated ash, which is a material to be melted, and more specifically to an incinerated ash melting furnace that can reduce the fuel consumption required for an incinerated ash melting furnace that melts incinerated ash. The present invention relates to a method for adjusting the basicity of incinerated ash.
【0002】0002
【従来の技術】周知のように、都市ごみ、汚泥、産業廃
棄物等の被焼却物は焼却炉により焼却処理されるが、被
焼却物の焼却によって生じた焼却灰は焼却灰溶融炉によ
る溶融処理によって減容化、安定化されたのちに建設資
材等に有効利用され、あるいは埋め立て処理される。[Prior Art] As is well known, materials to be incinerated such as municipal waste, sludge, and industrial waste are incinerated in an incinerator, but incineration ash produced by incineration of materials to be incinerated is melted in an ash melting furnace. After the volume is reduced and stabilized through treatment, it can be used effectively as construction materials, etc., or it can be disposed of in landfills.
【0003】ところで、焼却灰の溶融処理には焼却灰の
塩基度(CaO/SiO2 )が極めて重要な意味を持
つ。つまり、焼却灰の塩基度が適性であると焼却灰の溶
流点が低くなり、焼却灰溶融炉に要する熱エネルギ−の
削減効果、つまり燃費に関して経済的に極めて有利にな
るからである。By the way, the basicity (CaO/SiO2) of the incinerated ash has an extremely important meaning in the melting process of the incinerated ash. In other words, if the basicity of the incinerated ash is appropriate, the melting point of the incinerated ash will be low, and the effect of reducing the thermal energy required for the incinerated ash melting furnace, that is, it will be extremely advantageous economically in terms of fuel consumption.
【0004】例えば、塩基度と汚泥焼却灰の溶流点との
関係は、その関係線図(無機系汚泥焼却灰を白丸印で、
また有機系汚泥焼却灰を黒丸印でそれぞれ示す)の図3
に示すように、1.0程度以下の範囲において汚泥焼却
灰の溶流点が最も低くなることが示されている。For example, the relationship between the basicity and the melting point of sludge incineration ash is shown in the relationship diagram (inorganic sludge incineration ash is marked with a white circle,
In addition, organic sludge incineration ash is indicated by black circles) in Figure 3.
As shown in , it has been shown that the melting point of sludge incineration ash is lowest in the range of about 1.0 or less.
【0005】そのため、焼却灰溶融炉に連通する焼却灰
の空気輸送供給ラインに塩基度調整剤の添加ラインを連
通させ、この添加ラインから塩基度調整剤を供給し、こ
れを輸送中の焼却灰に混入して焼却灰の塩基度を調整す
ることによって、焼却灰の溶流点の低温化を図っている
。[0005] Therefore, an addition line for a basicity regulator is connected to an incineration ash pneumatic transport supply line that communicates with an incineration ash melting furnace, and the basicity regulator is supplied from this addition line. By mixing it into the incineration ash to adjust the basicity of the incineration ash, the melting point of the incineration ash is lowered.
【0006】なお、塩基度調整剤の添加量を決定するた
めには、焼却灰の塩基度を知る必要があるが、その灰分
中のSiO2 はJISM8214により、またCaO
はJISM8221により測定する周知の方法が採用さ
れている。[0006] In order to determine the amount of basicity regulator added, it is necessary to know the basicity of the incinerated ash.
A well-known method of measuring according to JISM8221 is adopted.
【0007】[0007]
【発明が解決しようとする課題】ところが、焼却灰溶融
炉に入る少し前の焼却灰に塩基度調整剤が添加されるた
め、焼却灰と塩基度調整剤とが十分に混合されず、焼却
灰に塩基度調整剤を添加したにも関わらず焼却灰の溶流
点が低下しないことがあって、焼却灰溶融炉に要する熱
エネルギ−の削減に寄与しないことが多々あった。However, since the basicity regulator is added to the incinerated ash shortly before it enters the incinerated ash melting furnace, the incinerated ash and the basicity regulator are not sufficiently mixed, and the incinerated ash becomes Even though a basicity regulator was added to the incinerated ash, the melting point of the incinerated ash was not lowered, and it often did not contribute to reducing the thermal energy required for the incinerated ash melting furnace.
【0008】従って、本発明は焼却灰と塩基度調整剤と
を良好に混合することにより、焼却灰溶融炉に要する燃
費を削減することのできる焼却灰溶融炉における焼却灰
の塩基度調整方法の提供を目的とする。Therefore, the present invention provides a method for adjusting the basicity of incinerated ash in an incinerated ash melting furnace, which can reduce the fuel consumption required for the incinerated ash melting furnace by properly mixing incinerated ash and a basicity regulator. For the purpose of providing.
【0009】[0009]
【課題を解決するための手段】本発明は焼却灰と塩基度
調整剤とをより均一に混合させることが塩基度の調整に
有効であることから上記課題を解決したものであって、
従って本発明に係る焼却灰溶融炉における焼却灰の塩基
度調整方法の要旨は、焼却灰溶融炉に供給される流動床
式熱分解炉で分解焼却されて生じる被焼却物の焼却灰の
溶流点を低下させるために、この焼却灰に塩基度調整剤
を添加する焼却灰溶融炉における焼却灰の塩基度調整方
法において、前記塩基度調整剤を流動床式熱分解炉に供
給することを特徴とする。[Means for Solving the Problems] The present invention has solved the above problems because mixing the incinerated ash and the basicity regulator more uniformly is effective in adjusting the basicity.
Therefore, the gist of the method for adjusting the basicity of incinerated ash in an incinerated ash melting furnace according to the present invention is that the incinerated ash of the incinerated material produced by decomposition and incineration in the fluidized bed pyrolysis furnace is supplied to the incinerated ash melting furnace. A method for adjusting the basicity of incinerated ash in an incinerated ash melting furnace in which a basicity regulator is added to the incinerated ash in order to reduce the basicity of the incinerated ash, characterized by supplying the basicity regulator to a fluidized bed pyrolysis furnace. shall be.
【0010】0010
【作用】本発明に係る焼却灰溶融炉における焼却灰の塩
基度調整方法によれば、塩基度調整剤を流動床式熱分解
炉に供給するので、流動床式熱分解炉で生じる焼却灰に
塩基度調整剤が随伴する時間が従来より長時間になる。[Operation] According to the method for adjusting the basicity of incinerated ash in an incinerated ash melting furnace according to the present invention, since the basicity regulator is supplied to the fluidized bed type pyrolysis furnace, the incinerated ash produced in the fluidized bed type pyrolysis furnace is The time for which the basicity regulator is present is longer than before.
【0011】[0011]
【実施例】以下、本発明の一実施例を、焼却灰溶融炉を
備えた被焼却物処理設備の系統を示すブロック図の図1
と、焼却灰溶融炉の炉壁温度と焼却灰処理量の関係線図
の図2を参照しながら、汚泥焼却灰の場合を例として説
明する。[Embodiment] An embodiment of the present invention will be described below with reference to FIG.
The case of sludge incinerated ash will be described as an example with reference to FIG. 2, which is a diagram showing the relationship between the furnace wall temperature of the incinerated ash melting furnace and the amount of incinerated ash processed.
【0012】図1に示す符号1は流動床式熱分解炉で、
この流動床式熱分解炉1に投入された汚泥は熱分解・焼
却されるが、焼却により生じた焼却灰は流動床式熱分解
炉1からサイクロン2に送給され、次いでサイクロン2
から連通する空気輸送供給ライン3を通して焼却灰溶融
炉4に供給され、ここで溶融処理されてスラグとなって
焼却灰溶融炉4から排出される。Reference numeral 1 shown in FIG. 1 is a fluidized bed type pyrolysis furnace.
The sludge put into the fluidized bed pyrolysis furnace 1 is thermally decomposed and incinerated, and the incineration ash produced by the incineration is sent from the fluidized bed pyrolysis furnace 1 to the cyclone 2, and then to the cyclone 2.
The incinerated ash is supplied to the incinerated ash melting furnace 4 through the pneumatic transport supply line 3 communicating with the incinerated ash, where it is melted and turned into slag, which is discharged from the incinerated ash melting furnace 4.
【0013】一方、流動床式熱分解炉1で汚泥の熱分解
により生じた未燃ガスを含む排ガスはサイクロン2から
2次燃焼室5に送られて完全燃焼され、これにより生じ
た燃焼排ガスは空気予熱器6,6a、排ガス処理装置7
を経て煙突8から大気中に排出されるようになっている
。On the other hand, the exhaust gas containing unburned gas generated by the thermal decomposition of sludge in the fluidized bed type pyrolysis furnace 1 is sent from the cyclone 2 to the secondary combustion chamber 5 and completely combusted, and the combustion exhaust gas generated thereby is Air preheater 6, 6a, exhaust gas treatment device 7
It is then discharged into the atmosphere from a chimney 8.
【0014】また、空気予熱器6で予熱された空気は流
動床式熱分解炉1及び2次燃焼室5に、空気予熱器6a
で予熱された空気は焼却灰溶融炉4にそれぞれ送給され
、汚泥を熱分解させ、排ガスを完全燃焼させ、焼却灰を
溶融する熱源となる燃料を燃焼させる働きをする。即ち
、以上は従来の被焼却物処理設備と全く同構成である。Furthermore, the air preheated by the air preheater 6 is supplied to the fluidized bed type pyrolysis furnace 1 and the secondary combustion chamber 5 through the air preheater 6a.
The preheated air is sent to the incinerated ash melting furnace 4, where it serves to thermally decompose the sludge, completely combust the exhaust gas, and combust the fuel that becomes the heat source for melting the incinerated ash. That is, the configuration described above is exactly the same as the conventional incineration material processing equipment.
【0015】そして、従来の被焼却物処理設備では焼却
灰に塩基度調整剤を添加する添加ライン3a(破線で示
す)が空気輸送供給ライン3に連通させていたが、本実
施例では流動床式熱分解炉1に添加ライン1aを連通さ
せて、この添加ライン1aから塩基度調整剤を流動床式
熱分解炉1に供給するようにした。In the conventional incineration material processing equipment, the addition line 3a (indicated by a broken line) for adding a basicity regulator to the incinerated ash was connected to the pneumatic transport supply line 3, but in this embodiment An addition line 1a was connected to the pyrolysis furnace 1, and the basicity regulator was supplied to the pyrolysis furnace 1 through the addition line 1a.
【0016】以下、この実施例の作用態様を説明すると
、添加ライン1aから流動床式熱分解炉1に塩基度調整
剤が供給されるので、流動床式熱分解炉1で熱分解・燃
焼して生じた汚泥の焼却灰に塩基度調整剤が随伴して互
いに混じり合いながらサイクロン2から空気輸送供給ラ
イン3を通して焼却灰溶融炉4に供給される。The mode of operation of this embodiment will be explained below. Since the basicity regulator is supplied from the addition line 1a to the fluidized bed type pyrolysis furnace 1, it is thermally decomposed and burned in the fluidized bed type pyrolysis furnace 1. The incinerated ash of the sludge generated by the sludge is supplied from the cyclone 2 to the incinerated ash melting furnace 4 through the pneumatic transport supply line 3 while being mixed with the basicity adjusting agent.
【0017】このように、従来よりも塩基度調整剤が焼
却灰に随伴する時間が長くなり、そしてサイクロン2や
空気輸送供給ライン3において攪拌されるので、焼却灰
と塩基度調整剤とが均一に混合されるようになった。[0017] In this way, the time for the basicity adjuster to accompany the incinerated ash is longer than in the past, and since it is stirred in the cyclone 2 and the pneumatic transport supply line 3, the incinerated ash and the basicity adjuster are uniformly distributed. now mixed into
【0018】因みに、焼却灰と塩基度調整剤の混合の差
による効果の差を図2に基づいて説明する。なお、図2
は本実施例による場合を白丸印で示し、また従来の場合
を黒丸印で示したもので、何れも燃料の使用量は同量で
ある。Incidentally, the difference in effect due to the difference in the mixing of the incinerated ash and the basicity regulator will be explained based on FIG. 2. In addition, Figure 2
The case according to this embodiment is shown by a white circle, and the conventional case is shown by a black circle, and the amount of fuel used is the same in both cases.
【0019】同図によれば、燃料は同使用量であるにも
関わらず、本実施例の方が従来より焼却灰溶融炉4の炉
壁温度が高温度になっている。これは、溶流点の低下効
果が大きくなると焼却灰溶融炉4の炉壁に付着するスラ
グの層厚が薄くなることを物語っている。換言すれば、
従来と同等の焼却灰溶融炉内温度を確保するのに少ない
燃料で良いことを示唆するものである。According to the figure, although the amount of fuel used is the same, the furnace wall temperature of the incinerated ash melting furnace 4 is higher in this embodiment than in the conventional case. This indicates that the thickness of the slag layer adhering to the furnace wall of the incinerated ash melting furnace 4 becomes thinner as the effect of lowering the melting point increases. In other words,
This suggests that less fuel is needed to maintain the same internal temperature of the incinerated ash melting furnace as in the past.
【0020】このように、塩基度調整剤を添加する位置
を前工程に移すだけなので設備費増を来すことなく、焼
却灰と塩基度調整剤がより均一にかつ確実に混合される
ので焼却灰溶融炉4に要する燃費を確実に削減すること
が可能になる。[0020] In this way, since the position where the basicity adjuster is added is simply moved to the previous process, there is no increase in equipment costs, and the incineration ash and the basicity adjuster are mixed more uniformly and reliably. It becomes possible to reliably reduce the fuel consumption required for the ash melting furnace 4.
【0021】[0021]
【発明の効果】以上詳述したように、従来の焼却灰の塩
基度調整方法では、焼却灰と塩基度調整剤との混合不良
により塩基度調整剤の添加効果を期待し得ない場合があ
った。しかしながら、本発明に係る焼却灰の塩基度調整
方法によれば、塩基度調整剤を流動床式熱分解炉に供給
するようにしたので、流動床式熱分解炉で生じる焼却灰
に塩基度調整剤が随伴する時間が従来より長時間になる
ために焼却灰と塩基度調整剤がより確実に混合されるよ
うになる結果、焼却灰溶融炉に要する燃費の削減に対し
て極めて多大な効果を期待することができる。[Effects of the Invention] As detailed above, in the conventional method for adjusting the basicity of incinerated ash, the effect of adding the basicity adjusting agent may not be expected due to poor mixing of the incinerated ash and the basicity adjusting agent. Ta. However, according to the method for adjusting the basicity of incinerated ash according to the present invention, since the basicity regulator is supplied to the fluidized bed pyrolysis furnace, the basicity of the incinerated ash produced in the fluidized bed pyrolysis furnace is adjusted. Since the time that the agent is accompanied by the agent is longer than before, the incinerated ash and basicity adjuster can be mixed more reliably, which has an extremely large effect on reducing the fuel consumption required for the incinerated ash melting furnace. You can expect it.
【図1】焼却灰溶融炉を備えた被焼却物処理設備の系統
を示すブロック図である。FIG. 1 is a block diagram showing a system of incineration material processing equipment equipped with an incineration ash melting furnace.
【図2】焼却灰溶融炉の炉壁温度と焼却灰処理量の関係
線図である。FIG. 2 is a relationship diagram between the furnace wall temperature of the incinerated ash melting furnace and the amount of incinerated ash processed.
【図3】塩基度と汚泥焼却灰の融点との関係線図である
。FIG. 3 is a relationship diagram between basicity and melting point of sludge incineration ash.
1…流動床式熱分解炉 1a…添加ライン 2…サイクロン 3…空気輸送供給ライン 4…焼却灰溶融炉 5…2次燃焼室 6,6a…空気予熱器 7…排ガス処理装置 8…煙突 a…塩基度調整剤 1...Fluidized bed pyrolysis furnace 1a...Addition line 2...Cyclone 3...Pneumatic transportation supply line 4... Incineration ash melting furnace 5...Secondary combustion chamber 6, 6a...Air preheater 7...Exhaust gas treatment device 8...Chimney a...Basicity regulator
Claims (1)
分解炉で分解焼却されて生じる被焼却物の焼却灰の溶流
点を低下させるために、この焼却灰に塩基度調整剤を添
加する焼却灰溶融炉における焼却灰の塩基度調整方法に
おいて、前記塩基度調整剤を流動床式熱分解炉に供給す
ることを特徴とする焼却灰溶融炉における焼却灰の塩基
度調整方法。Claim 1: In order to lower the melting point of the incinerated ash produced by decomposition and incineration in the fluidized bed pyrolysis furnace supplied to the incinerated ash melting furnace, a basicity regulator is added to the incinerated ash. A method for adjusting the basicity of incinerated ash in an incinerated ash melting furnace, wherein the basicity adjusting agent is supplied to a fluidized bed type pyrolysis furnace.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7989391A JPH04313615A (en) | 1991-04-12 | 1991-04-12 | Method for adjusting basicity of incineration ash in incineration ash-melting furnace |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7989391A JPH04313615A (en) | 1991-04-12 | 1991-04-12 | Method for adjusting basicity of incineration ash in incineration ash-melting furnace |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04313615A true JPH04313615A (en) | 1992-11-05 |
Family
ID=13702953
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP7989391A Pending JPH04313615A (en) | 1991-04-12 | 1991-04-12 | Method for adjusting basicity of incineration ash in incineration ash-melting furnace |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04313615A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5653182A (en) * | 1993-04-15 | 1997-08-05 | Has Holding As | Method for neutralizing waste |
JP2008196711A (en) * | 2006-09-07 | 2008-08-28 | Kobelco Eco-Solutions Co Ltd | Melting device for incineration ash |
JP2016153809A (en) * | 2016-05-02 | 2016-08-25 | 株式会社クボタ | Radioactive cesium separation/concentration method and radioactive cesium separation/concentration apparatus |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5860114A (en) * | 1981-10-05 | 1983-04-09 | Kubota Ltd | Melting method for refuse |
JPS6038079A (en) * | 1983-08-10 | 1985-02-27 | Kawasaki Heavy Ind Ltd | Method and equipment for high temperature melting treatment of waste material |
-
1991
- 1991-04-12 JP JP7989391A patent/JPH04313615A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5860114A (en) * | 1981-10-05 | 1983-04-09 | Kubota Ltd | Melting method for refuse |
JPS6038079A (en) * | 1983-08-10 | 1985-02-27 | Kawasaki Heavy Ind Ltd | Method and equipment for high temperature melting treatment of waste material |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5653182A (en) * | 1993-04-15 | 1997-08-05 | Has Holding As | Method for neutralizing waste |
JP2008196711A (en) * | 2006-09-07 | 2008-08-28 | Kobelco Eco-Solutions Co Ltd | Melting device for incineration ash |
JP2016153809A (en) * | 2016-05-02 | 2016-08-25 | 株式会社クボタ | Radioactive cesium separation/concentration method and radioactive cesium separation/concentration apparatus |
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