JPH0578727B2 - - Google Patents
Info
- Publication number
- JPH0578727B2 JPH0578727B2 JP12747887A JP12747887A JPH0578727B2 JP H0578727 B2 JPH0578727 B2 JP H0578727B2 JP 12747887 A JP12747887 A JP 12747887A JP 12747887 A JP12747887 A JP 12747887A JP H0578727 B2 JPH0578727 B2 JP H0578727B2
- Authority
- JP
- Japan
- Prior art keywords
- grate
- drying
- combustion
- gas
- exhaust gas
- 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
- 239000007789 gas Substances 0.000 claims description 83
- 238000001035 drying Methods 0.000 claims description 59
- 238000002485 combustion reaction Methods 0.000 claims description 50
- 239000000463 material Substances 0.000 claims description 35
- 238000007664 blowing Methods 0.000 claims description 30
- 239000000567 combustion gas Substances 0.000 claims description 8
- 238000009423 ventilation Methods 0.000 description 7
- 238000007599 discharging Methods 0.000 description 5
- 238000003756 stirring Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 238000007670 refining Methods 0.000 description 3
- 239000010802 sludge Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 208000005156 Dehydration Diseases 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 239000010800 human waste Substances 0.000 description 2
- 230000006698 induction Effects 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000000861 blow drying Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 230000001771 impaired effect Effects 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 238000010926 purge Methods 0.000 description 1
- 238000012797 qualification Methods 0.000 description 1
- 230000003134 recirculating effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
Landscapes
- Incineration Of Waste (AREA)
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、屎尿や下廃水等の各種汚泥を予備脱
水処理をした所謂脱水ケーキのような高含水率の
物質の焼却に利用されるものであり、焼却炉外に
於ける予備乾燥等を一切必要とすることなしに、
高含水率の被焼却物質をそのまま効率よく焼却で
きるようにした階段式焼却炉に関するものであ
る。[Detailed Description of the Invention] (Industrial Application Field) The present invention is used to incinerate materials with high moisture content such as so-called dehydrated cakes obtained by preliminary dehydration of various sludges such as human waste and sewage water. Therefore, there is no need for any preliminary drying outside the incinerator.
This invention relates to a step-type incinerator that can efficiently incinerate materials with high moisture content to be incinerated as they are.
(従来の技術)
従来の階段式焼却炉は、通常第6図に示す如
く、ほぼ同一形状の固定火格子30と可動火格子
31とを交互に階段状に配列し、各固定火格子3
0を炉本体へ支持固定すると共に、各可動火格子
31を取付金物32を介して連結杆33へ取付
け、滑台34上へ滑動自在に支持した前記連結杆
33を、駆動装置35によつて前後方向へ一定の
ピツチで滑動させると共に、押込通風機36から
空気ダクト37、各ホツパ38、両火格子30,
31間に設けた間隙を通して、火床上面へ燃焼用
空気を供給する構成となつている(特開昭59−
183212号)。(Prior Art) As shown in FIG. 6, a conventional stepped incinerator usually has fixed and movable grates 30 and movable grates 31 of approximately the same shape arranged in a stair-like manner alternately.
0 is supported and fixed to the furnace body, each movable grate 31 is attached to a connecting rod 33 via a mounting hardware 32, and the connecting rod 33, which is slidably supported on a slide 34, is driven by a drive device 35. While sliding at a constant pitch in the front-back direction, the air duct 37 from the forced draft fan 36, each hopper 38, both grates 30,
The structure is such that combustion air is supplied to the upper surface of the fire bed through the gap provided between the holes.
No. 183212).
而して、脱水ケーキ等の被焼却物を焼却炉内へ
供給すると、可動火格子31の動きと火格子間の
落差によつて、被焼却物は順次撹拌されながら前
方へ移動し、その間に高温燃焼されることにな
る。 When the material to be incinerated, such as dehydrated cake, is fed into the incinerator, the material to be incinerated is sequentially stirred and moved forward due to the movement of the movable grate 31 and the head difference between the grate, and during that time, It will be burned at a high temperature.
しかし、含水率が60〜65%を越える脱水ケーキ
等の高含水率の被焼却物をそのまま焼却炉内へ投
入した様な場合には、各火格子30,31が略同
一形状であつて落差に変化がないうえ、被焼却物
に対する撹拌作用が可動火格子31の動きと火格
子落差のみに依存しているため、被焼却物が火格
子の上面を完全に覆つてしまう状態となり、送気
が火格子の下方から行なわれていることとも相俟
つて、通気性が著しく悪化する。その結果、必然
的に燃焼状態が不安定となり、脱水ケーキ等の高
含水率の物質は効率よく焼却できないという問題
がある。 However, in the case where materials to be incinerated with a high moisture content such as dehydrated cake with a moisture content exceeding 60 to 65% are directly put into the incinerator, each grate 30, 31 has approximately the same shape and the head There is no change in the amount of material to be incinerated, and since the stirring effect on the material to be incinerated depends only on the movement of the movable grate 31 and the height of the grate, the material to be incinerated completely covers the top surface of the grate, and the air supply is interrupted. Coupled with the fact that this is done from below the grate, ventilation is significantly impaired. As a result, the combustion state inevitably becomes unstable, and there is a problem that substances with a high water content such as dehydrated cake cannot be incinerated efficiently.
一方、階段式焼却炉は、火格子上で約1200℃前
後の高温燃焼を行なうことが可能であり、その結
果、焼却灰を有効利用が可能な半溶融状のクリン
カーとして排出することが出来る。この焼却灰の
性状の良さを利用すると共に、脱水ケーキ等の効
率的な焼却を図るため、予かじめ焼却炉外に於い
て、焼却炉の排熱回収により発生した蒸気等を用
いて被焼却物を乾燥させ、この予備乾燥した被焼
却物を階段式焼却炉で高温燃焼させるシステムが
開発・実施されている。 On the other hand, a stepped incinerator is capable of high-temperature combustion of around 1200°C on the grate, and as a result, the incinerated ash can be discharged as semi-molten clinker that can be used effectively. In order to take advantage of the good properties of this incinerated ash and to efficiently incinerate dehydrated cakes, etc., incineration is done in advance outside the incinerator using steam generated by recovering the exhaust heat of the incinerator. A system has been developed and implemented in which materials are dried and the pre-dried materials to be incinerated are burned at high temperatures in a stepped incinerator.
しかし、上記システムに於いても、焼却炉プラ
ントのシステム構成が複雑になり過ぎると共に、
運転者にボイラ技士等の資格が必要となるため、
中小規模の焼却炉プラントにあつては、管理体制
上に様々な問題が生ずることになる。 However, even in the above system, the system configuration of the incinerator plant becomes too complicated, and
Since the operator must have qualifications such as boiler engineer,
In the case of small and medium-sized incinerator plants, various problems arise in terms of management systems.
(発明が解決しようとする問題点)
本発明は、従前の階段式焼却炉を用いた脱水ケ
ーキ等の高含水率物質の焼却に於ける上述の如き
問題、即ち被焼却物質を直接焼却炉へ投入する
場合には、火格子上面が被焼却物質によつて完全
に覆われてしまい、通気が阻害されて燃焼が不安
定になること、被焼却物を予かじめ予備乾燥す
る場合には、プラントの構成が複雑になつて運転
管理に手数がかかること等の問題を解決せんとす
るものであり、階段式焼却炉の乾燥火床部の構造
等に改良を加えることにより、脱水ケーキ等の高
含水率物質を直接焼却炉内へ供給し、焼却灰の性
状の良さを生かしつつ、これを高効率で安定焼却
し得るようにした階段式焼却炉を提供するもので
ある。(Problems to be Solved by the Invention) The present invention solves the above-mentioned problems in the incineration of high moisture content materials such as dehydrated cakes using conventional step incinerators, that is, the materials to be incinerated are sent directly to the incinerator. When charging, the top surface of the grate will be completely covered with the material to be incinerated, which will obstruct ventilation and make combustion unstable.If the material to be incinerated is pre-dried in advance, This project aims to solve problems such as complicated plant configurations that require time-consuming operation management, and by making improvements to the structure of the drying grate of stepped incinerators, it is possible to reduce the amount of dehydrated cake, etc. To provide a step-type incinerator that can supply a high moisture content substance directly into the incinerator and incinerate it stably with high efficiency while taking advantage of the good properties of incinerated ash.
(問題点を解決するための手段)
本件発明は、脱水ケーキ等の高含水率の被焼却
物質を焼却する乾燥火床部と燃焼火床部を備えた
階段式焼却炉に於いて、前記乾燥火床部を、可動
火格子と固定火格子から成る乾燥用火床と、該乾
燥用火床の上方にその移動方向と交又状に配設し
たガス吹込管とから形成すると共に、高温の乾燥
用排ガスを前記ガス吹込管の通気孔から被焼却物
質内へ噴出することを、発明の基本構成とするも
のである。(Means for Solving the Problems) The present invention provides a step-type incinerator equipped with a drying grate and a combustion grate for incinerating materials with a high moisture content such as dehydrated cake. The fire bed section is formed of a drying fire bed consisting of a movable grate and a fixed grate, and a gas blowing pipe disposed above the drying fire bed in a direction perpendicular to the direction of movement of the drying fire bed. The basic structure of the invention is to blow drying exhaust gas into the material to be incinerated from the vent hole of the gas blowing pipe.
(作用)
プツシヤにより乾燥火床部3へ送り込まれてき
た高含水率の被焼却物質は、乾燥用火床22上に
積層され、可動火格子22aの作動と、比較的大
きく設定された火格子落差によつて、順次下方へ
移動して行く。(Function) The materials to be incinerated with a high moisture content sent to the drying grate 3 by the pusher are stacked on the drying grate 22, and the movable grate 22a and the relatively large grate are stacked on the drying grate 22. It gradually moves downward depending on the head.
乾燥用火床22の上方に横設したガス吹込管2
3は、被焼却物質の積層内に潜り込んだ状態とな
つており、該ガス吹込管23の存在により、下方
へ移動する被焼却物質の層が上・下に分割され、
所謂撹拌作用を受けることになる。 Gas blowing pipe 2 installed horizontally above the drying fire bed 22
3 is in a state that it has sunk into the stack of materials to be incinerated, and due to the presence of the gas blowing pipe 23, the layer of materials to be incinerated moving downward is divided into upper and lower layers,
This results in a so-called stirring action.
また、ガス吹込管23からは、被焼却物質の層
内へ高温で且つ低酸素濃度の乾燥用排ガスが噴出
され、これによつて被焼却物質の加熱及び発生蒸
気の排出等が行なわれ、乾燥が一層促進されるこ
とになる。 Further, from the gas blowing pipe 23, a high temperature and low oxygen concentration drying exhaust gas is blown into the layer of the material to be incinerated, thereby heating the material to be incinerated and discharging the generated steam. will be further promoted.
尚、乾燥火床部3に於いては、乾燥用火床22
の下方からも燃焼排ガスSの一部が被焼却物質内
へ送気されており、ガス吹込管23からの高温の
乾燥用排ガスと相俟つて、その乾燥が行なわれ
る。 In addition, in the drying grate part 3, the drying grate 22
A part of the combustion exhaust gas S is also fed into the material to be incinerated from below, and is dried together with the high temperature drying exhaust gas from the gas blowing pipe 23.
含水率が60〜65%以上の被焼却物質は、乾燥火
床部3を通過する間に、含水率が40〜55%位いま
で乾燥され、その後、燃焼火床部4へ送り込まれ
て、ここで順次高温燃焼されて行く。 The materials to be incinerated with a moisture content of 60 to 65% or more are dried while passing through the drying grate section 3 until the moisture content reaches about 40 to 55%, and then sent to the combustion grate section 4. Here, it is sequentially burned at high temperatures.
(実施例)
以下、第1図乃至第5図に基づいて本発明の実
施例を説明する。(Example) Hereinafter, an example of the present invention will be described based on FIGS. 1 to 5.
第1図は、本発明に係る階段式焼却炉を用いた
焼却プラントの系統概要図であり、図に於いて1
は炉本体の最上部に設けた投入ホツパ、2はプツ
シヤ、3は乾燥火床部、4は燃焼火床部、5及び
6はホツパ、7及び8はリドリングコンベア、9
は調質混合機、10はスラグ出口、11は、乾燥
火床部3の上方に設けた循環ガス排出用の煙道、
12は燃焼火床部4の上方に設けた燃焼ガス排出
用の煙道である。 FIG. 1 is a schematic system diagram of an incineration plant using a stepped incinerator according to the present invention.
2 is a pusher, 3 is a drying grate, 4 is a combustion grate, 5 and 6 are hoppers, 7 and 8 are retard conveyors, 9
10 is a refining mixer; 10 is a slag outlet; 11 is a flue for discharging circulating gas provided above the drying grate 3;
Reference numeral 12 denotes a flue for discharging combustion gas provided above the combustion grate 4.
また13は、1次ガスエアヒータ、14は2次
ガスエアヒータ、15は高温乾燥用排ガスの循環
フアン、16は燃焼用空気フアン、17は乾燥用
燃焼排ガスの循環フアン、18は誘引フアン、1
9は循環ガス吹込ダクト、20は燃焼用空気吹込
ダクト、21は燃焼排ガス吹込ダクトである。 Further, 13 is a primary gas air heater, 14 is a secondary gas air heater, 15 is a circulation fan for high-temperature drying exhaust gas, 16 is a combustion air fan, 17 is a circulation fan for drying combustion exhaust gas, 18 is an induction fan, 1
9 is a circulating gas blowing duct, 20 is a combustion air blowing duct, and 21 is a combustion exhaust gas blowing duct.
炉本体内に配設されたストーカ装置は、乾燥火
床部3と燃焼火床部4とから構成されており、又
前記乾燥火床部3は、第2図乃至第4図に示す如
く、乾燥用火床22とその上方に配設したガス吹
込管23とから形成されている。 The stoker device disposed within the furnace main body is composed of a drying grate 3 and a combustion grate 4, and the drying grate 3 has two main parts, as shown in FIGS. 2 to 4. It is formed from a drying fire bed 22 and a gas blowing pipe 23 arranged above it.
前記乾燥用火床22は、断面略〓形の可動火格
子22aと同形状の固定火格子22bとから形成
されており、各火格子22a,22bには、その
床面に通気孔24が、またその前面に通気孔25
が夫々形成されている。該両通気孔24,25か
らは、後述する如く、燃焼排ガス吹込ダクト21
からのO2濃度が6〜8%程度の燃焼排ガスSが
噴出される。 The drying grate 22 is formed of a movable grate 22a having a substantially square cross section and a fixed grate 22b having the same shape, and each grate 22a, 22b has a ventilation hole 24 in its floor surface. There are also 25 ventilation holes on the front.
are formed respectively. From both the vent holes 24 and 25, a combustion exhaust gas blowing duct 21 is connected as described later.
A combustion exhaust gas S having an O 2 concentration of about 6 to 8% is ejected.
前記可動火格子22a及び固定火格子22b
は、その前面が約95〜150mmの高さLに形成され
ており、後述する燃焼用火床22の火格子とは、
その高さ寸法が著しく異なつている。 The movable grate 22a and the fixed grate 22b
The front surface is formed at a height L of approximately 95 to 150 mm, and the grate of the combustion grate 22, which will be described later, is
Their height dimensions differ significantly.
前記ガス吹込管23は、両火格子22a,22
bの床面から約80〜120mm位い上方に位置して、
可動火格子22aの移動方向と直交状に配設され
ており、これには複数の通気孔26が穿設されて
いる。当該ガス吹込管23は、第3図に示す如
く、炉壁部に設けたガスダクト19aに支持固設
されており、ガスダクト19a内へ圧送されてき
たO2濃度が約8〜10%程度の高温の乾燥用排ガ
ス(循環排ガス)Gが通気孔26を通して脱水ケ
ーキ等の高含水率の被焼却物質K内へ放出され
る。 The gas blowing pipe 23 has both fire grates 22a, 22
Located about 80 to 120 mm above the floor of b,
It is disposed perpendicular to the moving direction of the movable grate 22a, and a plurality of ventilation holes 26 are bored therein. As shown in FIG. 3, the gas blowing pipe 23 is supported and fixed to a gas duct 19a provided on the furnace wall, and the O 2 concentration pumped into the gas duct 19a is at a high temperature of about 8 to 10%. The drying exhaust gas (circulating exhaust gas) G is discharged through the vent hole 26 into the incinerated material K having a high moisture content such as a dehydrated cake.
尚、本実施例では、乾燥火床部3の上方に設け
た循環ガス排出用煙道から取り出した排ガスG
を、加熱昇温してガス吹込管23へ供給している
が、燃焼火床部4の上方に配設した燃焼ガス排出
用煙道12から取り出した燃焼排ガスSを、ガス
吹込管23へ供給するようにしてもよい。 In this embodiment, the exhaust gas G taken out from the circulating gas exhaust flue provided above the drying grate 3 is
The combustion exhaust gas S taken out from the flue 12 for discharging combustion gas disposed above the combustion grate section 4 is supplied to the gas blowing pipe 23 after heating and raising the temperature. You may also do so.
一方、前記燃焼火床部4を構成する燃焼用火床
27は、第5図に示す如き断面〓形の可動火格子
27aと固定火格子27bとから形成されてい
る。前記両火格子27a,27bの前面には複数
個の通気孔28が穿設されており、これを通して
燃焼用空気Aが噴出される。 On the other hand, the combustion grate 27 constituting the combustion grate section 4 is formed of a movable grate 27a and a fixed grate 27b, each having a square cross section as shown in FIG. A plurality of ventilation holes 28 are provided in the front surfaces of both the fire grates 27a and 27b, through which the combustion air A is blown out.
尚、燃焼火床部4即ち燃焼用火床27を形成す
る各火格子27a,27bの前面の高さL′は、約
95〜100mm程度に選定されており、前記乾燥用火
床22の火格子22a,22bに比較して、その
高さ寸法が著しく小さくなつている。 The height L' of the front surface of each grate 27a, 27b forming the combustion grate 4, that is, the combustion grate 27, is approximately
The height is selected to be about 95 to 100 mm, and the height dimension is significantly smaller than that of the grate 22a, 22b of the drying grate 22.
次に、本件階段式焼却炉の作動について説明す
る。 Next, the operation of the stepped incinerator will be explained.
被焼却物質、例えば、屎尿汚泥や下廃水汚泥、
上水汚泥、低質汚泥等の各種汚泥を予備脱水処理
した後の水分が60〜65%以上の脱水ケーキK(以
下高水分ケーキと呼ぶ)は、投入ホツパ1からプ
ツシヤ2によつて乾燥火床部3へ供給され、乾燥
用火床22の上に一定の厚みのケーキ層が形成さ
れる。 Materials to be incinerated, such as human waste sludge and sewage sludge,
Dehydrated cake K (hereinafter referred to as high moisture cake) with a moisture content of 60 to 65% or more after pre-dehydration treatment of various sludges such as clean water sludge and low-quality sludge is transferred from input hopper 1 to pusher 2 on a drying bed. 3, and a cake layer of a constant thickness is formed on the drying grate 22.
乾燥用火床22の上方には、ケーキ層K内に潜
り込んだ状態でガス吹込管23が配設されてお
り、該ガス吹込管23からは、1次ガスヒータ1
3に於いて500℃〜600℃に予熱された高温の乾燥
用排ガス(循環排ガスG)が、ケーキ層K内へ噴
出され、その乾燥が行なわれる。即ち、乾燥用火
床22上のケーキ層Kは、可動火格子22aの動
きと比較的大きな火格子落差によつて、前方下段
へ順次送られて行くが、火格子22a,22bの
段差が大きいことと、高温の循環排ガスGを噴出
するガス吹込管23が存在することにより、ケー
キ層Kが上・下に分割され、所謂撹拌作用を受け
ると共に、ケーキ層K内へ高温の循環ガスGが供
給されることにより、その乾燥が一層促進される
ことになる。 A gas blowing pipe 23 is disposed above the drying fire bed 22 so as to be hidden inside the cake layer K, and from the gas blowing pipe 23, the primary gas heater 1 is connected.
In step 3, the high temperature drying exhaust gas (circulated exhaust gas G) preheated to 500°C to 600°C is ejected into the cake layer K to dry it. That is, the cake layer K on the drying grate 22 is sequentially sent to the lower front stage due to the movement of the movable grate 22a and the relatively large grate drop, but the step difference between the grate 22a and 22b is large. In addition, due to the existence of the gas blowing pipe 23 that blows out the high temperature circulating exhaust gas G, the cake layer K is divided into upper and lower parts, receives a so-called stirring action, and the high temperature circulating gas G is introduced into the cake layer K. By supplying it, the drying will be further accelerated.
前記高温の乾燥用排ガス(循環排ガスG)は、
循環フアン15によつて循環ガス排出用道11か
ら200〜300℃位いの温度で1次ガスエアヒータ1
3へ送られ、ここで500℃〜600℃に加熱された
後、循環ガス吹込ダクト19を通して乾燥火床部
3の前記ガス吹込管23へ供給されて行く。 The high temperature drying exhaust gas (circulated exhaust gas G) is
The primary gas air heater 1 is heated at a temperature of about 200 to 300°C from the circulating gas discharge path 11 by the circulation fan 15.
3, where it is heated to 500° C. to 600° C., and then supplied to the gas blowing pipe 23 of the drying grate 3 through the circulating gas blowing duct 19.
又、乾燥火床部3に於ける前記高温循環排ガス
Gの吹込みの補助として、2次ガスエアヒータ1
4の出口から分岐排出した排ガスSが、排ガス吹
込ダクト21を通して排ガス循環フアン17によ
り、乾燥用火床22の下方から送気されている。
この排ガスSの吹込みにより、ケーキ層Kの通気
性が一層改善されると共に、ケーキ層K内で発生
した蒸気が効率よく層外へパージされることにな
る。 In addition, a secondary gas air heater 1 is used to assist in blowing the high temperature circulating exhaust gas G into the drying grate 3.
Exhaust gas S branched out from the outlet of No. 4 is sent from below the drying fire bed 22 through an exhaust gas blowing duct 21 by an exhaust gas circulation fan 17.
By blowing in the exhaust gas S, the air permeability of the cake layer K is further improved, and the steam generated within the cake layer K is efficiently purged to the outside of the layer.
一方、乾燥用火床22からの落下物は、ホツパ
5を介してリドリングコンベア7上に集められ、
調質混合機9へ送られる。そして、ここで高水分
ケーキKと混合され、その水分調整が行なわれ
る。尚、この際に、所謂熱交ダストやサイクロン
ダスト等を適宜に混合することも可能である。 On the other hand, the falling objects from the drying grate 22 are collected on the ridgling conveyor 7 via the hopper 5,
It is sent to the refining mixer 9. Then, it is mixed with the high moisture cake K to adjust its moisture content. At this time, it is also possible to appropriately mix so-called heat exchanger dust, cyclone dust, etc.
前記乾燥火床部3で予備乾燥された高水分ケー
キKは、最終的には40〜55%の水分にまで乾燥さ
れた後、燃焼火床部4へ送り込まれる。尚、乾燥
火床部3と燃焼火床部4とは、やや大きな落差を
有しているものの、階段状ストーカとしては一連
のものであり、ケーキ層Kは連続的に下方へ移送
されて行く。 The high moisture cake K pre-dried in the drying grate section 3 is finally dried to a moisture content of 40 to 55%, and then sent to the combustion grate section 4. Although the drying grate section 3 and the combustion grate section 4 have a somewhat large head difference, they are a series of stepped stokers, and the cake layer K is continuously transferred downward. .
燃焼火床部4に於いては、燃焼用火床27の下
方から、燃焼用空気吹込ダクト20を通して燃焼
用空気Aが供給されており、これによつて前記ケ
ーキKが燃焼を開始する。尚、前記空気Aは、燃
焼用空気フアン16によつて2次ガスエアヒータ
14へ送られ、ここで150°〜250℃に予熱されて
いる。 In the combustion grate section 4, combustion air A is supplied from below the combustion grate 27 through a combustion air blowing duct 20, whereby the cake K starts to burn. Note that the air A is sent to the secondary gas air heater 14 by the combustion air fan 16, where it is preheated to 150° to 250°C.
前記燃焼火床部4で発生した燃焼排ガスSは、
800°〜1000℃の高温ガスであり、その結果臭気成
分は殆んど酸化分解されてしまつている。燃焼ガ
ス排出用煙道12から排出された燃焼排ガスS
は、1次ガスエアヒータ13へ送られ、ここで乾
燥用排ガス(循環排ガス)G側へ熱回収されて
250°〜350℃の温度になり、更に、2次ガスエア
ヒータ14へ送られて燃焼用空気A側へ熱回収さ
れ、約200〜250℃の温度になつて大気中へ排出さ
れて行く。 The combustion exhaust gas S generated in the combustion grate section 4 is
It is a high temperature gas of 800° to 1000°C, and as a result, most of the odor components have been oxidized and decomposed. Combustion exhaust gas S discharged from the flue 12 for exhausting combustion gas
is sent to the primary gas air heater 13, where the heat is recovered to the drying exhaust gas (circulated exhaust gas) G side.
The temperature reaches 250° to 350°C, and is further sent to the secondary gas air heater 14, where the heat is recovered to the combustion air A side, and the temperature reaches about 200° to 250°C, where it is discharged into the atmosphere.
焼却炉内に於いては、前記乾燥火床部3で発生
した蒸発水分相当量がガス量の増加となるが、循
環排ガス量を一定とすると、その増加分が燃焼火
床部4の上部を通過し、燃焼ガス排出用煙道12
から排出されて行く。 In the incinerator, the amount of evaporated moisture generated in the drying grate 3 increases the amount of gas, but if the amount of circulating exhaust gas is constant, the increase increases the amount of gas generated in the upper part of the combustion grate 4. through which a flue 12 for exhausting combustion gases
It is discharged from.
前記増加分の排ガスの抽気は、誘引フアン18
の入口側に設けたダンパ装置29を、焼却炉内部
が若干負圧(−5〜−10mmAq)になるよう自動
制御することにより行なわれる。又、前記抽気ガ
スには、NH3やH2S等の臭気成分が含まれてい
るが、燃焼ガス排出用煙道12から排出される前
に燃焼火床部4の上部の高温度域を通過するた
め、その殆んどはここで酸化分解されることにな
る。尚、必要に応じて排ガス処理装置(図示省
略)を設置してもよいことは勿論である。 The increased amount of exhaust gas is extracted by the induction fan 18.
This is done by automatically controlling a damper device 29 provided on the inlet side of the incinerator so that the inside of the incinerator has a slightly negative pressure (-5 to -10 mmAq). Moreover, the bleed gas contains odor components such as NH 3 and H 2 S, but the high temperature region in the upper part of the combustion grate section 4 is heated before being discharged from the flue 12 for exhausting combustion gas. Most of it will be oxidized and decomposed here. It goes without saying that an exhaust gas treatment device (not shown) may be installed if necessary.
燃焼火床部4で燃焼が進行し、燃焼用火床27
上に生成した焼却灰は、スラグ出口10から順次
炉外へ排出され、従前の階段式焼却炉と同様の手
段によつて処理されて行く。又、燃焼用火床27
からホツパ6内へ落下した微量の灰は、リドリン
グコンベア8によつて調質混合機9へ返送され、
高水分ケーキKの水分調整に利用される。 Combustion progresses in the combustion grate section 4, and the combustion grate 27
The incineration ash produced above is sequentially discharged out of the furnace from the slag outlet 10 and is processed by the same means as in the conventional step-type incinerator. Also, combustion grate 27
A small amount of ash that has fallen into the hopper 6 is returned to the refining mixer 9 by the riddling conveyor 8.
It is used to adjust the moisture content of high moisture cake K.
(発明の効果)
本発明では、乾燥用火床を構成する可動火格子
及び固定火格子の落差を、燃焼用火床の火格子よ
りも大きくすると共に、乾燥用火床の床面上の適
宜位置に、可動火格子の移動方向と交又状にガス
吹込管を配設し、高含水率の被焼却物の内部へ高
温で且つ酸素濃度の低い乾燥用排ガスを噴出する
構成としている。その結果、乾燥火床部を積層状
になつて下降する被焼却物は、ガス吹込管によつ
て下方へ移動する際に上・下に分割されることに
なり、所謂被焼却物の撹拌が行なわれる。(Effects of the Invention) In the present invention, the height difference between the movable grate and the fixed grate constituting the drying grate is made larger than that of the grate of the combustion grate, and A gas blowing pipe is disposed at a position intersecting with the moving direction of the movable grate, and is configured to blow out drying exhaust gas having a high temperature and low oxygen concentration into the interior of the material to be incinerated which has a high moisture content. As a result, the material to be incinerated descending in a layered manner through the drying firebed is divided into upper and lower parts as it moves downward by the gas blowing pipe, making it difficult to stir the material to be incinerated. It is done.
また、ガス吹込管から直接被焼却物内へ噴出さ
れた高温の乾燥用排ガスは、効率的にその保有熱
を被焼却物に与えると共に、発生した蒸気を被焼
却物外ヘパージすることになり、極めて効率的な
被焼却物の乾燥が可能になる。 In addition, the high-temperature drying exhaust gas that is blown directly into the material to be incinerated from the gas blowing pipe efficiently imparts its retained heat to the material to be incinerated, and purges the generated steam outside of the material to be incinerated. This allows extremely efficient drying of incinerated materials.
上述の如く、本件発明によれば、含水率の高い
脱水ケーキ等を直接炉内へ供給することにより、
これを安定且つ効率よく焼却することが出来ると
共に、焼却灰は骨材等として利用可能であり、優
れた実用的効用を奏するものである。 As described above, according to the present invention, by directly feeding a dehydrated cake etc. with a high moisture content into the furnace,
This can be stably and efficiently incinerated, and the incinerated ash can be used as aggregate, etc., and has excellent practical utility.
第1図は本件発明に係る階段式焼却炉の全体系
統図である。第2図は、乾燥火床部の部分断面概
要図であり、第3図はガス吹込管の取付状態を示
す斜面図である。第4図は、乾燥火床部を形成す
る火格子の一部を示す斜面図であり、第5図は燃
焼火床部を形成する火格子の一部を示す斜面図で
ある。第6図は、従前の階段式焼却炉の概要図で
ある。
3……乾燥火床部、4……燃焼火床部、11…
…循環ガス排出用煙道、12……燃焼ガス排出用
煙道、22……乾燥用火床、22a……可動火格
子、22b……固定火格子、23……ガス吹込
管、26……通気孔、27……燃焼用火床、27
a……可動火格子、27b……固定火格子、G…
…循環排ガス、S……燃焼排ガス、K……高含水
率の被焼却物。
FIG. 1 is an overall system diagram of a step-type incinerator according to the present invention. FIG. 2 is a schematic partial cross-sectional view of the drying grate, and FIG. 3 is a perspective view showing how the gas blowing pipe is attached. FIG. 4 is a perspective view showing a part of the grate forming the drying grate, and FIG. 5 is a perspective view showing a part of the grate forming the combustion grate. FIG. 6 is a schematic diagram of a conventional stepped incinerator. 3...Drying grate part, 4...Combustion grate part, 11...
... Flue for exhausting circulating gas, 12... Flue for discharging combustion gas, 22... Drying bed, 22a... Movable grate, 22b... Fixed grate, 23... Gas blowing pipe, 26... Ventilation hole, 27... Combustion grate, 27
a...Movable grate, 27b...Fixed grate, G...
...Recirculating exhaust gas, S...Combustion exhaust gas, K...Incineration material with high moisture content.
Claims (1)
する乾燥火床部3と焼却火床部4を備えた階段式
焼却炉に於いて、前記乾燥火床部3を、可動火格
子22aと固定火格子22bから成る乾燥用火床
22と、該乾燥用火床22の上方にその移動方向
と交又状に配設したガス吹込管23とから形成す
ると共に、高温の乾燥用排ガスを前記ガス吹込管
23の通気孔26から被焼却物質内へ噴出する構
成とした階段式焼却炉。 2 乾燥用排ガスを、乾燥火床部3の上方に設け
た循環ガス排出用煙道11から排出して、燃焼火
床部4の上方に設けた燃焼ガス排出用煙道12か
らの燃焼排ガスSにより加熱昇温した循環排ガス
Gとした特許請求の範囲第1項に記載の階段式焼
却炉。 3 乾燥用排ガスを、燃焼火床部4の上方に設け
た燃焼ガス排出用煙道12からの燃焼排ガスSと
した特許請求の範囲第1項に記載の階段式焼却
炉。[Scope of Claims] 1. In a stepped incinerator equipped with a drying grate section 3 and an incineration grate section 4 for incinerating materials to be incinerated with high moisture content such as dehydrated cake, the drying grate section 3 is , a drying grate 22 consisting of a movable grate 22a and a fixed grate 22b, and a gas blowing pipe 23 disposed above the drying grate 22 in a direction perpendicular to the direction of movement of the drying grate 22. A step-type incinerator configured to blow out drying exhaust gas from the vent hole 26 of the gas blowing pipe 23 into the material to be incinerated. 2. The drying exhaust gas is discharged from the circulating gas exhaust flue 11 provided above the drying grate 3, and the combustion exhaust gas S is discharged from the combustion gas exhaust flue 12 provided above the combustion grate 4. The step-type incinerator according to claim 1, wherein the circulating exhaust gas G is heated and heated by. 3. The step-type incinerator according to claim 1, in which the drying exhaust gas is the combustion exhaust gas S from the combustion gas discharge flue 12 provided above the combustion grate 4.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12747887A JPS63294414A (en) | 1987-05-25 | 1987-05-25 | Tiered type incinerator |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12747887A JPS63294414A (en) | 1987-05-25 | 1987-05-25 | Tiered type incinerator |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS63294414A JPS63294414A (en) | 1988-12-01 |
JPH0578727B2 true JPH0578727B2 (en) | 1993-10-29 |
Family
ID=14960931
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP12747887A Granted JPS63294414A (en) | 1987-05-25 | 1987-05-25 | Tiered type incinerator |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS63294414A (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4000973C1 (en) * | 1990-01-16 | 1991-02-28 | Teset Thermo-Energie-System Entsorgungs-Technologie, Weismes/Waimes, Be | |
AU2004237886B2 (en) * | 1999-05-21 | 2007-10-25 | Barlow Projects, Inc. | Improved mass fuel combustion system |
JP2000154909A (en) * | 2000-01-01 | 2000-06-06 | Worldwide Patent Licensing Co Llc | Method and system for incinerating bulk refuse and liquid containing hydrocarbon |
JP6685601B2 (en) * | 2016-06-28 | 2020-04-22 | 株式会社タクマ | Sludge treatment method and sludge treatment device |
-
1987
- 1987-05-25 JP JP12747887A patent/JPS63294414A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS63294414A (en) | 1988-12-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US5937772A (en) | Reburn process | |
JPS5911545B2 (en) | Portland cement production and waste utilization | |
CN102192590A (en) | Biomass whirlwind hot blast stove | |
US4771711A (en) | Furnace | |
JP2006242490A (en) | Stoker-type incinerator and its operation method | |
JP3582710B2 (en) | Combustion method of stoker type incinerator and stoker type incinerator | |
JPH0578727B2 (en) | ||
JP2007155301A (en) | Incinerator and incineration object incineration method by direct heating carbonization gasification method | |
CN212644614U (en) | Combustion device of garbage incinerator | |
JP2003166706A (en) | Combustion method and combustion device of stoker type incinerator | |
JP2003322321A (en) | Combustion method for stoker type refuse incinerator and stoker type refuse incinerator | |
CA1304991C (en) | Incinerator | |
JP5876264B2 (en) | Waste treatment equipment | |
JP2643720B2 (en) | Method and apparatus for reducing emitted pollutants in flue gas | |
JP7105469B2 (en) | incinerator | |
JPH07233921A (en) | Refuse incinerator | |
JP3372526B2 (en) | Waste treatment method and apparatus | |
JPS5823072Y2 (en) | garbage incinerator | |
SU1089358A2 (en) | Installation for incinerating waste | |
GB1484188A (en) | Sludge incinerating plant | |
CN118816212A (en) | H-shaped dry and wet sludge mixed incinerator and incineration method | |
JP3995237B2 (en) | Operation method of waste incinerator | |
JP2779145B2 (en) | Smokeless and odorless incinerator | |
WO2003093728A1 (en) | Method of operating waste incinerator and waste incinerator | |
JP2002106819A (en) | Circulating fluidized bed combustion apparatus and its combustion method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
LAPS | Cancellation because of no payment of annual fees |