JPH0253120B2 - - Google Patents

Info

Publication number
JPH0253120B2
JPH0253120B2 JP56117941A JP11794181A JPH0253120B2 JP H0253120 B2 JPH0253120 B2 JP H0253120B2 JP 56117941 A JP56117941 A JP 56117941A JP 11794181 A JP11794181 A JP 11794181A JP H0253120 B2 JPH0253120 B2 JP H0253120B2
Authority
JP
Japan
Prior art keywords
exhaust gas
sludge
temperature hearth
supplied
dust
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 - Lifetime
Application number
JP56117941A
Other languages
Japanese (ja)
Other versions
JPS5820300A (en
Inventor
Sanemi Kimoto
Shojiro Sasaki
Muneharu Ueno
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.)
Osaka Gas Co Ltd
Original Assignee
Osaka Gas 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 Osaka Gas Co Ltd filed Critical Osaka Gas Co Ltd
Priority to JP11794181A priority Critical patent/JPS5820300A/en
Publication of JPS5820300A publication Critical patent/JPS5820300A/en
Publication of JPH0253120B2 publication Critical patent/JPH0253120B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、汚泥を、炭素系可燃物質によつて形
成した高温炉床に供給して、燃焼溶融させる方法
に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method of feeding sludge to a high-temperature hearth formed of carbon-based combustible material and burning and melting it.

上記方法は、近年極めて大量に発生する各種汚
泥を、十数分の1に体積減小させて埋立用地面等
において有利にした状態で、かつ、有害重金属が
溶出しない安全な状態で、さらに、近年コスト面
及び省資源面で問題の多い石油系燃料をほとんど
必要としない状態で処理でき、極めて有用な汚泥
処理方法である。
The above method reduces the volume of various types of sludge, which have been generated in extremely large quantities in recent years, to a tenth of a tenth, making it advantageous for use in landfill sites, etc., and in a safe state where no harmful heavy metals are eluted. This is an extremely useful sludge treatment method that can be treated with almost no need for petroleum-based fuels, which have recently been problematic in terms of cost and resource conservation.

従来、例えば特開昭55−142576号公報に示され
ているように、高温炉床型式の溶融炉では溶融処
理物を全て高温炉床の上方に投入しており、した
がつて、高温炉床からの燃焼排ガスに含まれるダ
ストを、サイクロンなどで回収して、高温炉床の
上方に汚泥と共に投入していた。
Conventionally, as shown in JP-A-55-142576, for example, in a high-temperature hearth type melting furnace, all of the melted material is charged above the high-temperature hearth. The dust contained in the combustion exhaust gas from the furnace was collected using a cyclone, etc., and was thrown into the upper part of the high-temperature hearth along with the sludge.

しかし、汚泥やダストは高温炉床から吹上がる
燃焼ガスによつて飛散されやすく、ダストを高温
炉床の上方に投入する方式では、大量発生するダ
ストが再飛散する確率が高くて、ダストの溶融処
理効率が悪くなりやすく、一層の改良の余地があ
つた。
However, sludge and dust are easily scattered by the combustion gas blowing up from the high-temperature hearth, and with the method of injecting dust above the high-temperature hearth, there is a high probability that a large amount of dust will be re-splattered and the dust will melt. Processing efficiency tends to deteriorate, and there is room for further improvement.

本発明の目的は、燃焼排ガスから回収したダス
トの溶融処理を効率良く実行できるようにする点
にある。
An object of the present invention is to enable efficient melting of dust collected from combustion exhaust gas.

本発明の特徴手段は、汚泥を、炭素系可燃物質
によつて形成した高温炉床に供給して、燃焼溶融
させる方法において、前記高温炉床からの燃焼排
ガスから回収したダストを、前記高温炉床の内部
に吹込んで溶融処理することにあり、その作用効
果は次の通りである。
A characteristic feature of the present invention is that in a method of supplying sludge to a high-temperature hearth formed of a carbon-based combustible material and burning and melting it, dust recovered from combustion exhaust gas from the high-temperature hearth is transferred to the high-temperature hearth. The purpose is to blow it into the bed for melting treatment, and its effects are as follows.

つまり、回収したダストを高温炉床の内部に周
部から吹込むと、ダストが燃焼ガスにより高温炉
床上方に吹上げられるには、高温炉床内の狭い曲
がつた〓間を長時間高温にされされて通過しなけ
ればならず、そのために、実際には、ダストのほ
とんど全量が高温炉床内で確実に溶融する。
In other words, when the collected dust is blown into the high-temperature hearth from the periphery, it takes a long time for the dust to be blown up above the high-temperature hearth by the combustion gas through the narrow curved spaces in the high-temperature hearth. The dust has to be passed through the dust, which in fact ensures that almost the entire amount of dust is melted in the hot hearth.

その結果、ダストの高温炉床からの再飛散を十
分かつ確実に抑制でき、燃焼排ガスから回収した
大量のダストの溶融処理を効率良く実行できる、
一段と優れた汚泥の溶融方法を確立できた。
As a result, re-entrainment of dust from the high-temperature hearth can be sufficiently and reliably suppressed, and a large amount of dust recovered from combustion exhaust gas can be efficiently melted.
We were able to establish an even better method for melting sludge.

次に、例示図により本発明の実施態様を説明す
る。
Next, embodiments of the present invention will be described with reference to illustrative figures.

第2図に示すように、キユポラタイプの溶融炉
1に、炭素系可燃物質から成る高温炉床2を形成
し、ホツパー3から高温炉床2に、ダンパー4
a,4bを交互に開閉して、汚泥を、炭素系可燃
物質と混合状態であるいは交互に供給し、炭素系
可燃物質と汚泥の充填層5を高温炉床2上に形成
し、そして、下方の第1羽口6から高温炉床2に
空気等の酸素含有ガスを供給して、高温炉床2の
上部において汚泥を、燃焼、溶融させ、そして、
燃焼排ガスを高温炉床2の上方に形成した上昇流
路7と高温炉床2の下部に接続した下部流路8と
に排出させるようにし、そして、溶融物を前記下
部流路8を通して溶融物取出し炉体9を取出すと
ともに、炉体9に取出した溶融物を第1及び第2
出口10a,10bから適宜回収させるように
し、そして、高温炉床2から発生した燃焼排ガス
を、充填層5を通過する際に生成される臭気成分
及び有害成分を燃焼分解させるよう、上昇流路7
内において、第2羽口11から供給される空気等
の酸素含有ガスによつて後燃焼させるようにして
ある。
As shown in FIG. 2, a high-temperature hearth 2 made of carbon-based combustible material is formed in a cupola type melting furnace 1, and a damper 4 is connected to the high-temperature hearth 2 from a hopper 3.
a and 4b are alternately opened and closed to supply sludge in a mixed state with carbon-based combustible material or alternately to form a packed layer 5 of carbon-based combustible material and sludge on high-temperature hearth 2, and then An oxygen-containing gas such as air is supplied from the first tuyere 6 to the high temperature hearth 2 to burn and melt the sludge in the upper part of the high temperature hearth 2, and
The combustion exhaust gas is discharged into an ascending passage 7 formed above the high-temperature hearth 2 and a lower passage 8 connected to the lower part of the high-temperature hearth 2, and the molten material is passed through the lower passage 8. At the same time as taking out the furnace body 9, the molten material taken out into the furnace body 9 is transferred to the first and second
The ascending flow path 7 is designed to recover the combustion exhaust gas from the high-temperature hearth 2 as appropriate from the outlets 10a and 10b, and to burn and decompose odor components and harmful components generated when the combustion exhaust gas generated from the high-temperature hearth 2 passes through the packed bed 5.
Inside the combustion chamber, after-combustion is performed using oxygen-containing gas such as air supplied from the second tuyere 11.

第1図及び第2図に示すように、上昇流路7か
らの燃焼排ガスを、炉頂部に接続した排ガスダク
ト12を介してダスト除去用サイクロン13に供
給し、サイクロン13からの燃焼排ガスを、ブロ
ワ14によつて第1、第2羽口6,11に送られ
る空気を予熱するために空気予熱器15に供給
し、空気予熱器15からの燃焼排ガスを、後述す
る乾燥処理後の排ガスを加温処理するための排ガ
ス予熱器16に供給し、排ガス予熱器16からの
燃焼排ガスを、SOxを水酸化ナトリウムや水酸化
マグネシウムの水溶液を用いて除去する洗浄器1
7に供給し、更に、洗浄器17からの燃焼排ガス
を、排風機18により電気集塵機19及び煙突
(図示せず)を通して大気中に放出させるように
してある。又、前記サイクロン13からの燃焼排
ガスの一部を、予め水分80%程度に脱水処理され
た汚泥が供給ポンプ20によつて供給される直接
接触加熱型の乾燥兼造粒機21に供給して、汚泥
を水分が50%〜65%になるように乾燥及び造粒処
理し、乾燥処理後の汚泥をコンベア装置等を用い
て順次溶融炉1におけるホツパー3に供給させる
ようにし、そして、乾燥処理後の排ガスを、冷却
器22に供給して脱湿処理し、脱湿処理後の排ガ
スを、排風機23によつて前記排ガス予熱器16
に供給して加温処理し、加温処理の排ガスを、供
給口24から前記高温炉床2の上方に供給して燃
焼脱臭処理させるようにしてある。
As shown in FIGS. 1 and 2, the combustion exhaust gas from the ascending passage 7 is supplied to the dust removal cyclone 13 through the exhaust gas duct 12 connected to the top of the furnace, and the combustion exhaust gas from the cyclone 13 is The air sent to the first and second tuyeres 6, 11 by the blower 14 is supplied to an air preheater 15 for preheating, and the combustion exhaust gas from the air preheater 15 is treated as the exhaust gas after a drying process to be described later. A cleaning device 1 that supplies an exhaust gas preheater 16 for heating treatment and removes SOx from the combustion exhaust gas from the exhaust gas preheater 16 using an aqueous solution of sodium hydroxide or magnesium hydroxide.
Furthermore, the combustion exhaust gas from the washer 17 is discharged into the atmosphere by an exhaust fan 18 through an electrostatic precipitator 19 and a chimney (not shown). Further, a part of the combustion exhaust gas from the cyclone 13 is supplied to a direct contact heating type drying/granulating machine 21 to which sludge that has been dehydrated to about 80% moisture is supplied by a supply pump 20. The sludge is dried and granulated to a moisture content of 50% to 65%, and the sludge after the drying process is sequentially supplied to the hopper 3 in the melting furnace 1 using a conveyor device, etc., and then the drying process is performed. The remaining exhaust gas is supplied to the cooler 22 for dehumidification treatment, and the exhaust gas after the dehumidification treatment is sent to the exhaust gas preheater 16 by the exhaust fan 23.
The heated exhaust gas is supplied from the supply port 24 above the high-temperature hearth 2 to undergo combustion deodorization treatment.

さらに詳述すると、汚泥を、前記高温炉床2に
供給する前に高温炉床2からの燃焼排ガスのうち
の一部との接触によつて熱交換効率の良い状態で
良好に乾燥させることができ、しかも、前記乾燥
処理において、水分が混入し、温度が低下し、臭
気成分が混入することになる乾燥処理後の排ガス
を、除湿、加温により燃焼し易い状態に調整する
ことによつて溶融炉1内の温度を不必要に低下さ
せる等のトラブルを回避させながら、既設の溶融
炉1を有効利用した経済面で有利な状態で良好に
燃臭脱臭処理させることができ、そのうえ、1200
℃以上の高温で且つ少量のダストが含まれる高温
炉床2からの燃焼排ガスを、乾燥処理後の排ガス
の混入によつてクリンカー発生を抑制すべく800
℃〜1050℃に冷却させることができ、さらに、前
記高温炉床2からの燃焼排ガスを、乾燥処理後の
排ガスの加熱処理に有効利用することによつて、
100℃〜250℃に冷却でき、換言すれば、大気中に
放出される燃焼排ガスの熱エネルギーを極力有効
に利用できるのである。
More specifically, before the sludge is supplied to the high-temperature hearth 2, it can be properly dried in a state with good heat exchange efficiency by contacting with a part of the combustion exhaust gas from the high-temperature hearth 2. Moreover, by dehumidifying and heating the exhaust gas after the drying process, in which moisture is mixed in, the temperature is lowered, and odor components are mixed in, the exhaust gas is adjusted to a state where it is easy to burn. While avoiding troubles such as unnecessarily lowering the temperature inside the melting furnace 1, it is possible to effectively deodorize combustion odors by effectively utilizing the existing melting furnace 1 in an economically advantageous condition.
The combustion exhaust gas from the high-temperature hearth 2, which is at a high temperature of 800℃ or higher and contains a small amount of dust, is mixed with the exhaust gas after drying to suppress clinker generation.
℃ ~1050℃, and furthermore, by effectively using the combustion exhaust gas from the high temperature hearth 2 for heating treatment of the exhaust gas after drying treatment,
It can be cooled to 100°C to 250°C, in other words, the thermal energy of the combustion exhaust gas released into the atmosphere can be used as effectively as possible.

又、第1図に示すように、前記サイクロン13
から乾燥兼造粒機21への燃焼排ガスの供給量を
変更設定する流量調節弁25を設け、もつて、供
給量が多過ぎた場合における溶融炉1内の温度が
下がり過ぎるトラブルを生じないように、且つ、
供給量が少な過ぎた場合における汚泥の乾燥が不
充分となるトラブルを生じないように、燃焼排ガ
スの供給量を調節できるようにし、又、前記排ガ
ス予熱器16へ供給される排風機23からの排ガ
スの一部を大気中に放出する状態と放出しない状
態とに切換可能で、且つ、放出量を変更調節可能
な弁26を設け、もつて、溶融炉1内の温度が異
常に低下した場合等において、排風機23からの
排ガスの一部を大気中に放出できるようにし、さ
らに、前記サイクロン13にて回収されたダスト
を第1羽口6に供給される酸素含有ガス中に供給
する供給路27を設け、もつて、ダストを自動的
に高温炉床2へ供給できるようにしてある。
Moreover, as shown in FIG. 1, the cyclone 13
A flow control valve 25 is provided to change and set the amount of combustion exhaust gas supplied from the dryer/granulator 21 to the dryer/granulator 21, so as to prevent the temperature inside the melting furnace 1 from falling too low when the amount of supply is too large. , and
In order to avoid problems such as insufficient drying of sludge when the supply amount is too small, the supply amount of combustion exhaust gas can be adjusted, and the exhaust gas from the exhaust fan 23 supplied to the exhaust gas preheater 16 can be If the temperature inside the melting furnace 1 drops abnormally by providing a valve 26 that can switch between releasing a part of the exhaust gas into the atmosphere and not releasing it into the atmosphere, and which can change and adjust the amount of exhaust gas released. etc., a part of the exhaust gas from the exhaust fan 23 is discharged into the atmosphere, and the dust collected by the cyclone 13 is further supplied into the oxygen-containing gas supplied to the first tuyere 6. A channel 27 is provided so that dust can be automatically supplied to the high temperature hearth 2.

尚、本発明は、下水汚泥、し尿性汚泥、工場排
水処理汚泥、浄水場汚泥、活性処理汚泥等の各種
汚泥を処理対象にできる。
The present invention can treat various types of sludge, such as sewage sludge, human waste sludge, factory wastewater treatment sludge, water purification plant sludge, and activated treatment sludge.

また、高温炉床2を形成する炭素系可燃物質と
しては、主としてコークスを用いるとよいが、無
煙炭等の練炭、黒鉛電極屑等の各種のものを利用
してもよい。
Further, as the carbon-based combustible material forming the high-temperature hearth 2, it is preferable to mainly use coke, but various materials such as briquettes such as anthracite coal, graphite electrode scraps, etc. may also be used.

又、上記の如く、炭素系可燃物質としてコーク
スを使用するに、溶融炉1へのコークス供給量
は、炉1へ供給される汚泥の水分および発熱量に
よつてきまり、一般に、汚泥重量100に対してコ
ークス重量3〜13である。そして、溶融炉1への
酸素含有ガス供給量は、一般に、炉1へ供給され
るコークスおよび汚泥の理論燃焼酸素含有ガス量
の1〜1.2倍である。
Furthermore, as mentioned above, when coke is used as the carbon-based combustible material, the amount of coke supplied to the melting furnace 1 depends on the water content and calorific value of the sludge supplied to the furnace 1, and generally, it is On the other hand, the coke weight is 3 to 13. The amount of oxygen-containing gas supplied to the melting furnace 1 is generally 1 to 1.2 times the theoretical combustion oxygen-containing gas amount of coke and sludge supplied to the furnace 1.

また、利用する溶融炉の具体的構成は、各種変
形可能である。第3図は、その一例を示し、高温
炉床2部分に対する側壁を、2重管構造に形成し
て水冷ジヤケツト28を構成したものである。
Furthermore, the specific configuration of the melting furnace used can be modified in various ways. FIG. 3 shows an example of this, in which the side wall for the two portions of the high-temperature hearth is formed into a double pipe structure to constitute a water-cooled jacket 28.

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

図面は本発明に係る汚泥の溶融方法の実施の態
様を例示し、第1図はブロツク線図、第2図は使
用する溶融炉の断面図、第3図は別構成の溶融炉
の断面図である。 2……高温炉床。
The drawings illustrate embodiments of the sludge melting method according to the present invention, with FIG. 1 being a block diagram, FIG. 2 being a sectional view of the melting furnace used, and FIG. 3 being a sectional view of a melting furnace with a different configuration. It is. 2...High temperature hearth.

Claims (1)

【特許請求の範囲】[Claims] 1 汚泥を、炭素系可燃物質によつて形成した高
温炉床2に供給して、燃焼溶融させる方法であつ
て、前記高温炉床2からの燃焼排ガスから回収し
たダストを、前記高温炉床2の内部に周部から吹
込んで溶融処理する汚泥の溶融方法。
1 A method in which sludge is supplied to a high-temperature hearth 2 formed of a carbon-based combustible material and burned and melted, the dust collected from the combustion exhaust gas from the high-temperature hearth 2 being fed to the high-temperature hearth 2. A method of melting sludge by blowing it into the interior of the sludge from the periphery.
JP11794181A 1981-07-28 1981-07-28 Sludge-melting method Granted JPS5820300A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11794181A JPS5820300A (en) 1981-07-28 1981-07-28 Sludge-melting method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11794181A JPS5820300A (en) 1981-07-28 1981-07-28 Sludge-melting method

Publications (2)

Publication Number Publication Date
JPS5820300A JPS5820300A (en) 1983-02-05
JPH0253120B2 true JPH0253120B2 (en) 1990-11-15

Family

ID=14724006

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11794181A Granted JPS5820300A (en) 1981-07-28 1981-07-28 Sludge-melting method

Country Status (1)

Country Link
JP (1) JPS5820300A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5535821A (en) * 1978-09-05 1980-03-13 Japan Organo Co Ltd Method of burning sludge
JPS55142576A (en) * 1979-04-23 1980-11-07 Oosakashi Treating method for waste material

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5535821A (en) * 1978-09-05 1980-03-13 Japan Organo Co Ltd Method of burning sludge
JPS55142576A (en) * 1979-04-23 1980-11-07 Oosakashi Treating method for waste material

Also Published As

Publication number Publication date
JPS5820300A (en) 1983-02-05

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