JPS638365B2 - - Google Patents

Info

Publication number
JPS638365B2
JPS638365B2 JP54159421A JP15942179A JPS638365B2 JP S638365 B2 JPS638365 B2 JP S638365B2 JP 54159421 A JP54159421 A JP 54159421A JP 15942179 A JP15942179 A JP 15942179A JP S638365 B2 JPS638365 B2 JP S638365B2
Authority
JP
Japan
Prior art keywords
ash
sludge
arc
arc 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.)
Expired
Application number
JP54159421A
Other languages
Japanese (ja)
Other versions
JPS5682317A (en
Inventor
Toshiharu Furukawa
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.)
Daido Steel Co Ltd
Original Assignee
Daido Steel 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 Daido Steel Co Ltd filed Critical Daido Steel Co Ltd
Priority to JP15942179A priority Critical patent/JPS5682317A/en
Publication of JPS5682317A publication Critical patent/JPS5682317A/en
Publication of JPS638365B2 publication Critical patent/JPS638365B2/ja
Granted legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Vertical, Hearth, Or Arc Furnaces (AREA)

Description

【発明の詳細な説明】 この発明は汚泥の処理方法に関する。[Detailed description of the invention] This invention relates to a method for treating sludge.

一般に下水汚泥、し尿汚泥などの各種の汚泥の
処理にあたつては、汚泥焼却炉により焼却し、得
られた焼却残渣である灰は散逸を防ぐため含水率
20〜30%となるように加湿後埋立処分している。
しかしこの埋立処分のために広大な用地を必要と
し、埋立後の灰の飛散や灰中の重合属類の溶出な
どの二次公害のおそれもあるので、灰をさらにア
ーク炉におけるアーク熱により溶融処理し、その
減容化や安定化をはかることが考えられる。すな
わち製鋼用等に使用されるエール式アーク炉を改
良し、炉内の溶融メタルと電極の間にアークを飛
ばし、この炉内に上記の灰を投入すれば、高温還
元性雰囲気中で熱分解をうけ灰中の有機物はガス
化し、無機物は溶融スラグとなり、金属類は一部
がガス化し他はスラグおよび溶融メタル中に分配
される。この方法により得られた溶融スラグは冷
却固化すればもとの灰に比較して半分以下に減容
され、重金属類の流出もないうえ、コンクリート
用骨材等に有効利用することもできる。ところが
一般に汚泥焼却炉としては第1図に示すような多
段床型焼却炉1が用いられ、投入口2より投入さ
れた汚泥脱水ケーキは予熱帯3において乾燥予熱
され、燃焼帯4においてバーナ5による助燃のも
とに燃焼後、灰となつて冷却帯6において冷風に
より冷却され灰出口7より炉外に排出され、さら
にこの灰は散逸防止や消火のための加湿及び自然
放熱により常温近くまで冷却されてしまう。従つ
てこの冷却後の灰をアーク炉に投入して溶融する
処理工程を採用すると、燃焼帯4通過直後に約
600〜800℃の高温であつた灰をわざわざ一旦冷却
してアーク熱により再加熱することになるため、
電力費がささみ不経済である。また仮に上記高温
の灰の有する顕熱が全部焼却炉における燃焼空気
の予熱に利用されたとしても、同一熱量の供給に
要する燃料費より電力費の方が大であるから、空
気予熱による燃料費の節約額より再加熱のための
電力費の増加分の方が大であるため不経済であ
る。
Generally, when treating various types of sludge such as sewage sludge and human waste sludge, they are incinerated in a sludge incinerator, and the resulting incineration residue, ash, has a high moisture content to prevent it from dissipating.
After humidifying the water to a level of 20 to 30%, it is disposed of in a landfill.
However, this landfill disposal requires a vast amount of land, and there is a risk of secondary pollution such as the scattering of the ash after the landfill and the elution of polymeric substances in the ash, so the ash is further melted using arc heat in an arc furnace. It is conceivable to treat it to reduce its volume and stabilize it. In other words, if you improve the Yale arc furnace used for steelmaking, etc., create an arc between the molten metal and the electrode, and put the ash into the furnace, thermal decomposition will occur in a high-temperature reducing atmosphere. The organic matter in the ash is gasified, the inorganic matter is turned into molten slag, and some of the metals are gasified and the rest are distributed into the slag and molten metal. When the molten slag obtained by this method is cooled and solidified, its volume is reduced to less than half that of the original ash, no heavy metals are released, and it can be effectively used as aggregate for concrete. However, in general, a multi-bed incinerator 1 as shown in Fig. 1 is used as a sludge incinerator, and the sludge dewatered cake fed through the inlet 2 is dried and preheated in a preheating zone 3, and then heated in a combustion zone 4 by a burner 5. After combustion under auxiliary combustion, the ash becomes ash, which is cooled by cold air in the cooling zone 6 and discharged from the furnace through the ash outlet 7.The ash is further cooled to near room temperature by humidification and natural heat radiation to prevent dissipation and extinguish fire. It will be done. Therefore, if a treatment process is adopted in which the cooled ash is put into an arc furnace and melted, approximately
The ash, which was at a high temperature of 600 to 800 degrees Celsius, has to be cooled down and then reheated using arc heat.
Electricity costs are low and it is uneconomical. Furthermore, even if all the sensible heat of the high-temperature ash was used to preheat the combustion air in the incinerator, the electricity cost would be greater than the fuel cost required to supply the same amount of heat, so the fuel cost due to air preheating would be higher than the fuel cost required to supply the same amount of heat. This is uneconomical because the increase in electricity costs for reheating is greater than the savings.

この発明は上記の点にかんがみてなされたもの
で、アーク炉における溶融用電力が少なくて済み
経済的に汚泥を溶融処理することができる汚泥の
処理方法を提供しようとするものである。
This invention has been made in view of the above-mentioned points, and it is an object of the present invention to provide a sludge treatment method that requires less electric power for melting in an arc furnace and can economically melt sludge.

しかしてこの発明は汚泥焼却炉により汚泥を焼
却し、得られた高温の焼却灰を強制冷却をおこな
うことなく直接密閉式のアーク炉内に投入して、
該アーク炉において電極と導電材との間に発生さ
せたアークのアーク熱により上記焼却灰を溶融処
理することを特徴とするものである。
However, in this invention, sludge is incinerated in a sludge incinerator, and the resulting high-temperature incinerated ash is directly charged into a closed-type arc furnace without forced cooling.
The method is characterized in that the incinerated ash is melted by the arc heat of an arc generated between an electrode and a conductive material in the arc furnace.

以下この発明方法を第2図に示す実施例にもと
づいて詳細に説明する。なお図中第1図と同一符
号を付した部分は第1図と同一部分を示す。
The method of this invention will be explained in detail below based on the embodiment shown in FIG. In addition, the parts in the figure with the same reference numerals as in FIG. 1 indicate the same parts as in FIG. 1.

すなわち、汚泥焼却炉としては予熱帯3と燃焼
帯4のみをそなえ、冷却帯をそなえていない多段
床型燃焼炉8を用い、燃焼帯4を通過して灰出口
9から排出された高温の灰を強制冷却することな
くコンベア10により搬送して直接に密閉式のア
ーク炉11内に投入する。コンベア10の周囲は
ダクト12で包囲し、さらにこのダクトを断熱材
13で被覆するとよい。これにより灰の自然放熱
量を低くおさえることができ、灰をより高温のま
まアーク炉に搬送できる。アーク炉11に投入さ
れた灰は電極14と炉底の溶融メタルや黒鉛など
の導電材15との間に発生するアークのアーク熱
により熱分解され、その有機物はガス化してダク
ト16より排出され、焼却炉にて燃料として使用
される。また無機物は溶融スラグ17となる。こ
の際、アーク炉11に投入される灰は600〜800℃
であるため灰溶融用の電力が少なくて済むのであ
る。発明者らの実験結果によると、たとえば加湿
により20〜30%の水分を含む常温の下水汚泥焼却
灰(試料A)、加湿してない常温の下水汚泥焼却
灰(試料B)、700℃の下水汚泥焼却灰(試料C)
をアーク炉に投入した場合、その溶融処理に要す
る電力量はそれぞれ試料A:0.672kWh、試料
B:0.453kWh、試料C:0.325kWh(いずれも灰
1Kg当り)であり、本発明方法の採用により溶融
用電力の大巾な削減を達成できることが判る。
In other words, the sludge incinerator is a multi-bed type combustion furnace 8 that is equipped with only a pre-heating zone 3 and a combustion zone 4 and has no cooling zone, and the high-temperature ash that passes through the combustion zone 4 and is discharged from the ash outlet 9 is used as a sludge incinerator. is conveyed by a conveyor 10 without being forcedly cooled and directly placed into a closed arc furnace 11. It is preferable to surround the conveyor 10 with a duct 12 and further cover this duct with a heat insulating material 13. This allows the amount of natural heat dissipation of the ash to be kept low, and the ash can be transported to the arc furnace while maintaining a higher temperature. The ash put into the arc furnace 11 is thermally decomposed by the arc heat of the arc generated between the electrode 14 and the conductive material 15 such as molten metal or graphite at the bottom of the furnace, and the organic matter is gasified and discharged from the duct 16. , used as fuel in incinerators. Further, the inorganic substance becomes molten slag 17. At this time, the ash fed into the arc furnace 11 is heated to a temperature of 600 to 800°C.
Therefore, less electricity is required for ash melting. According to the inventors' experimental results, for example, sewage sludge incineration ash at room temperature containing 20 to 30% moisture due to humidification (sample A), sewage sludge incineration ash at room temperature without humidification (sample B), and 700℃ sewage Sludge incineration ash (sample C)
When put into an arc furnace, the amount of electricity required for the melting process is 0.672 kWh for sample A, 0.453 kWh for sample B, and 0.325 kWh for sample C (all per 1 kg of ash). It can be seen that a large reduction in melting power can be achieved.

なお上記実施例において灰出口9の下方にアー
ク炉11を設置できる場合は、コンベア10を用
いることなく灰出口9から灰をダクト等を経てア
ーク炉11内へ直接落下させるようにしてもよ
い。
In the above embodiment, if the arc furnace 11 can be installed below the ash outlet 9, the ash may be directly dropped from the ash outlet 9 into the arc furnace 11 through a duct or the like without using the conveyor 10.

以上説明したように、この発明によれば汚泥焼
却炉により汚泥を焼却し、得られた高温の焼却灰
を強制空冷、水冷等の冷却をおこなうことなく直
接アーク炉に供給してアーク熱により溶融処理す
るので、汚泥の焼却、予熱等は電力に比べて安価
な助燃用燃料を用いて経済的におこなえるうえ、
アーク炉における溶融用電力が少なくて済み、燃
料と電力を有効に利用して経済的に汚泥を溶融処
理することができる。また焼却後の灰の冷却や加
湿のための装置が不要となり設備が簡素化され設
備費も安価で済む。
As explained above, according to the present invention, sludge is incinerated in a sludge incinerator, and the resulting high-temperature incinerated ash is directly supplied to an arc furnace without cooling such as forced air cooling or water cooling, and is melted by arc heat. Since sludge is treated, sludge incineration, preheating, etc. can be done economically using auxiliary combustion fuel, which is cheaper than electricity.
The electric power required for melting in the arc furnace is small, and sludge can be melted and processed economically by effectively using fuel and electric power. Additionally, equipment for cooling and humidifying the ash after incineration is not required, simplifying the equipment and reducing equipment costs.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来の汚泥焼却炉の略示縦断面図、第
2図はこの発明方法の実施に使用する装置の一例
を示す機器配置図である。 3……予熱帯、4……燃焼帯、8……多段床型
焼却炉、9……灰出口、10……コンベア、11
……アーク炉、14……電極、15……導電材、
17……溶融スラグ。
FIG. 1 is a schematic longitudinal cross-sectional view of a conventional sludge incinerator, and FIG. 2 is an equipment layout diagram showing an example of the apparatus used to carry out the method of the present invention. 3... Pre-heating zone, 4... Combustion zone, 8... Multi-bed incinerator, 9... Ash outlet, 10... Conveyor, 11
... Arc furnace, 14 ... Electrode, 15 ... Conductive material,
17... Molten slag.

Claims (1)

【特許請求の範囲】[Claims] 1 汚泥焼却炉により汚泥を焼却し、得られた高
温の焼却灰を強制冷却をおこなうことなく直接密
閉式のアーク炉内に投入して、該アーク炉におい
て電極と導電材との間に発生させたアークのアー
ク熱により上記焼却灰を溶融処理することを特徴
とする汚泥の処理方法。
1 The sludge is incinerated in a sludge incinerator, and the resulting high-temperature incinerated ash is directly charged into a closed arc furnace without forced cooling, and generated between the electrode and the conductive material in the arc furnace. A sludge treatment method characterized by melting the incineration ash using the arc heat of an electric arc.
JP15942179A 1979-12-08 1979-12-08 Processing method of refuse Granted JPS5682317A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15942179A JPS5682317A (en) 1979-12-08 1979-12-08 Processing method of refuse

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15942179A JPS5682317A (en) 1979-12-08 1979-12-08 Processing method of refuse

Publications (2)

Publication Number Publication Date
JPS5682317A JPS5682317A (en) 1981-07-06
JPS638365B2 true JPS638365B2 (en) 1988-02-22

Family

ID=15693371

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15942179A Granted JPS5682317A (en) 1979-12-08 1979-12-08 Processing method of refuse

Country Status (1)

Country Link
JP (1) JPS5682317A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
NO157876C (en) * 1985-09-23 1988-06-01 Sintef METHOD AND APPARATUS FOR IMPLEMENTING HEAT TREATMENT.

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5339668A (en) * 1976-09-22 1978-04-11 Hitachi Plant Eng & Constr Co Ltd Apparatus for treating sludge

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5339668A (en) * 1976-09-22 1978-04-11 Hitachi Plant Eng & Constr Co Ltd Apparatus for treating sludge

Also Published As

Publication number Publication date
JPS5682317A (en) 1981-07-06

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