JP2003171667A - Method for carbonization treatment of sludge or the like - Google Patents

Method for carbonization treatment of sludge or the like

Info

Publication number
JP2003171667A
JP2003171667A JP2001373879A JP2001373879A JP2003171667A JP 2003171667 A JP2003171667 A JP 2003171667A JP 2001373879 A JP2001373879 A JP 2001373879A JP 2001373879 A JP2001373879 A JP 2001373879A JP 2003171667 A JP2003171667 A JP 2003171667A
Authority
JP
Japan
Prior art keywords
sludge
rotary kiln
wall
shaped
water content
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.)
Granted
Application number
JP2001373879A
Other languages
Japanese (ja)
Other versions
JP4559678B2 (en
JP2003171667A6 (en
Inventor
Tetsushi Maekawa
哲志 前川
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.)
Mayekawa Manufacturing Co
Original Assignee
Mayekawa Manufacturing Co
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 Mayekawa Manufacturing Co filed Critical Mayekawa Manufacturing Co
Priority to JP2001373879A priority Critical patent/JP4559678B2/en
Publication of JP2003171667A publication Critical patent/JP2003171667A/en
Publication of JP2003171667A6 publication Critical patent/JP2003171667A6/en
Application granted granted Critical
Publication of JP4559678B2 publication Critical patent/JP4559678B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for treating a sludge or the like which can continuously carry out the carbonization treatment of an object like a sewage sludge having a high water content, being an indefinite shape, and having a high viscosity and, simultaneously, has remarkably suppressed fuel consumption. <P>SOLUTION: The method for treating a sludge comprises (1) kneading an ore powder with a water-containing indefinite-shaped sludge to reduce the water content, passing the kneaded mixture in this state through a molding machine to render the cross-sectional shape a definite form, making each shaped sludge in the surface state of non- adhering or non-bonding to one another, then continuously supplying the shaped sludge to the upstream portion of a cylindrical rotary kiln 1 having a spiral conveying wall 2 at the inner peripheral surface and an agitation wall 3 crossing the conveying wall 2 formed at a part of the conveying wall 2 while rotating the rotary kiln 1; (2) flaming the inside of the above rotary kiln 1 from its downstream portion and stopping flaming when the above sludge ignites; (3) sucking gas in the inside of the above rotary kiln 1 from its upstream portion, carrying out the treatment for rendering the gas harmless, and then exhausting the harmless gas; and (4) discharging a carbonized product of the above sludge from the lower portion of the rotary kiln 1 by carrying out the above operations (1) to (3). <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明はロータリキリンを利
用して、下水汚泥などの汚泥廃棄物を、きわめて省エネ
ルギ的にしかも連続的に炭化処理する方法に関するもの
である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for continuously carbonizing sludge waste such as sewage sludge by utilizing rotary giraffe.

【0002】[0002]

【従来の技術】一般に、ロータリキルンは、内面を耐火
性に仕上げた円筒体を水平よりわずかに傾斜させてゆる
い速度で回転させるとき、その下部側から円筒体の内部
に火炎を吹込む一方、上部側からセメント原料等の原料
を送入して当該原料を焼成するためのものとして公知で
ある。
2. Description of the Related Art In general, a rotary kiln blows a flame into the inside of a cylindrical body from its lower side when the cylindrical body whose inner surface is fire-resistant is tilted slightly from the horizontal and rotated at a slow speed. It is known as a material for feeding a raw material such as cement raw material from the upper side and firing the raw material.

【0003】近時、上記ロータリキリンを利用して可燃
性の廃棄物を処理する手法が提案されているが、提案さ
れている方法では下水汚泥のような含水率が高くしかも
不定形で粘性も高い処理対象を効率よく炭化処理するこ
とは殆どできないでいる。また、下水汚泥等の不定形の
処理物の場合は勿論、定形の廃棄物の処理においても、
ロータリキルンの下部側から内部に吹込む火炎は、処理
中に吹込みっぱなしであるため、その燃料コストが著し
く嵩むという難点がある。
Recently, there has been proposed a method of treating combustible wastes using the above-mentioned rotary giraffe, but the proposed method has a high water content such as sewage sludge and is amorphous and viscous. It is almost impossible to efficiently carbonize a high object to be treated. In addition, not only in the case of irregularly shaped products such as sewage sludge, but also in the treatment of regular waste materials,
The flame blown from the lower side of the rotary kiln into the inside of the rotary kiln is continuously blown during the treatment, so that the fuel cost thereof is significantly increased.

【0004】[0004]

【発明が解決しようとする課題】そこで本発明では、下
水汚泥のような含水率が高く不定形で粘性も高い対象を
連続的に炭化処理できるのみならず、その処理における
燃料消費を著しく抑制した汚泥等の処理方法を提供する
ことを、その課題とするものである。
Therefore, in the present invention, not only can an object such as sewage sludge having a high water content, an indefinite shape and a high viscosity be continuously carbonized, but the fuel consumption in the treatment can be significantly suppressed. It is an object of the present invention to provide a method for treating sludge and the like.

【0005】[0005]

【課題を解決するための手段】上記課題を解決すること
を目的としてなされた本発明方法の構成は、(イ)水分を
含有する不定形の汚泥に鉱石紛末を混練して含水率を低
下せしめこの状態で成形機を通し断面形状を定形化し、
定形化された各汚泥をそれら同士が接着乃至は粘着しな
い表面状態にしてから、当該定形化された汚泥を、内周
面に螺旋状の搬送壁と該搬送壁の一部に当該搬送壁を横
断する攪拌壁を形成した円筒状のロータリキルンの上方
に、当該ロータリキルンを回転させつつ所定の単位量で
連続的に供給する、(ロ)前記(イ)の状態におかれている
ロータリキルンの下方からこのロータリキルンの内部に
火炎を吹込み、該ロータリキルン内で前記汚泥が着火し
たら火炎の吹込みを止める、(ハ)前記(イ),(ロ)の状態
におかれるロータリキルンの上方から該ロータリキルン
の内部の気体を吸引し無害化処理して排気する、(ニ)前
記(イ)〜(ハ)の操作を行うことによりロータリキリンの
下部から前記汚泥の炭化物を排出させることを特徴とす
るものである。
Means for Solving the Problems The constitution of the method of the present invention aimed at solving the above-mentioned problems is (a) reducing the water content by kneading ore powder with an amorphous sludge containing water. In this state, pass through a molding machine to standardize the cross-sectional shape,
After making each of the standardized sludge a surface state in which they do not adhere or stick to each other, the standardized sludge is provided with a spiral transport wall on the inner peripheral surface and the transport wall on a part of the transport wall. Above the cylindrical rotary kiln having a transverse stirring wall, the rotary kiln is continuously supplied in a predetermined unit amount while rotating the rotary kiln. (B) The rotary kiln in the state of (a) above. A flame is blown into the rotary kiln from below, and when the sludge is ignited in the rotary kiln, the blow of the flame is stopped. (C) The rotary kiln in the above (a) and (b) states Suction the gas inside the rotary kiln from above, detoxify and exhaust it, (d) discharge the carbide of the sludge from the lower part of the rotary giraffe by performing the operations (a) to (c). It is characterized by.

【0006】本発明では、定形化された各汚泥同士が接
着乃至は粘着しない表面状態にするため、適宜の加熱手
段又は送風手段若しくは加熱送風手段を用いることによ
り、例えば、表面をほぼ乾燥状態にすることもできる。
[0006] In the present invention, in order to form a surface state in which the standardized sludges do not adhere or stick to each other, appropriate heating means or air blowing means or heating air blowing means is used, for example, the surface is made almost dry. You can also do it.

【0007】[0007]

【発明の実施の形態】次に本発明方法の実施の形態例に
ついて、図に拠り説明する。図1は本発明方法を実施す
るための炭化処理装置を模式的に示した一部を断面にし
た側面図、図2は図1に示した炭化処理装置における搬
送壁に、図1のものとは異なる攪拌壁を設けた搬送壁の
一部拡大斜視図、図3は図2に示した搬送壁を用い、図
1に示した装置で炭化処理をしている状態を示す筒体1
の断面図、図4は図3に示した状態から筒体1を回転さ
せた状態を示す筒体1の断面図である。
BEST MODE FOR CARRYING OUT THE INVENTION Next, an embodiment of the method of the present invention will be described with reference to the drawings. FIG. 1 is a side view with a partial cross section schematically showing a carbonization treatment apparatus for carrying out the method of the present invention, and FIG. 2 shows a transfer wall of the carbonization treatment apparatus shown in FIG. Is a partially enlarged perspective view of a transfer wall provided with different stirring walls, and FIG. 3 is a cylindrical body 1 showing a state in which the transfer wall shown in FIG. 2 is used and carbonization is performed by the apparatus shown in FIG.
4 is a cross-sectional view of the tubular body 1 showing a state in which the tubular body 1 is rotated from the state shown in FIG.

【0008】図において、1は長さ約10m程度、内径40
〜50cm程度の鋼管製の筒体で、ここでは所要の単位長さ
筒体の複数を、互に外フランジ状の継手において接続す
ることにより、一本の筒体1に形成している。
In the figure, 1 is a length of about 10 m and an inner diameter of 40
A tubular body made of a steel pipe having a length of about 50 cm, in which a plurality of required unit length tubular bodies are connected to each other through joints in the form of outer flanges to form a single tubular body 1.

【0009】2は前記筒体1の内面に、この筒体1の全
長に亘って螺旋をなすように設けた搬送壁で、筒体1の
全長における手前側(図の左方)の部分には、前記螺旋
状の搬送壁2による搬送路に、それを横断する方向で攪
拌壁3が設けられている。
Reference numeral 2 denotes a conveying wall provided on the inner surface of the cylindrical body 1 so as to form a spiral over the entire length of the cylindrical body 1, and at a front side (left side in the figure) of the entire length of the cylindrical body 1. Is provided with a stirring wall 3 in a direction traversing the conveying path formed by the spiral conveying wall 2.

【0010】4は前記筒体1の全長外面に設けた断熱層
であり、上記の筒体1〜断熱層4までの構成により、ロ
ータリキルン本体Kbを形成する。
Reference numeral 4 denotes a heat insulating layer provided on the outer surface of the entire length of the tubular body 1, and the rotary kiln body Kb is formed by the above-described configurations of the tubular body 1 to the heat insulating layer 4.

【0011】上記のロータリキルン本体Kbは、その長さ
方向の3箇所、具体的には、前後両端部と中央部分に、
それぞれ帯状環5を取付け、各環5の下部を回転自在の
支持ローラ6,7,8で支持すると共に、少なくともい
ずれか一つのローラを駆動ローラとしてモータ等により
回転させると、このロータリキルン本体Kbは、前記ロー
ラ6〜8の上で定位置回転する。なお、6a,7a,8aはロ
ーラ架台、BFはローラ架台6a〜8aを定置したベースフ
レームである。図示した例では、ロータリキルン本体Kb
は略水平姿勢に設けているが、下り勾配(図の右側が下
方)を付けて配置してもよい。
The rotary kiln body Kb is provided at three positions in its length direction, specifically, at the front and rear end portions and the central portion.
When the belt-like rings 5 are attached, and the lower portions of the rings 5 are supported by rotatable support rollers 6, 7, and 8, and at least one of the rollers is driven by a motor or the like, the rotary kiln body Kb Rotate in place on the rollers 6-8. In addition, 6a, 7a and 8a are roller mounts, and BF is a base frame on which the roller mounts 6a to 8a are fixed. In the illustrated example, the rotary kiln body Kb
Is provided in a substantially horizontal posture, but it may be arranged with a downward slope (the right side in the drawing is downward).

【0012】9は前記ロータリキルン本体Kbの下方側
(図の右方)に配置した火炎用のガスバーナで、バーナ
9の火炎噴射口9aを前記本体Kbの内部側に向けて設けて
いる。なお、ガスバーナ9の手前には炭化処理物を収容
する容器20を配置するピットPに形成されている。
Reference numeral 9 denotes a gas burner for flames arranged on the lower side (right side in the figure) of the rotary kiln body Kb, and the flame injection port 9a of the burner 9 is provided toward the inside of the body Kb. In front of the gas burner 9, a pit P is formed in which a container 20 for containing a carbonized product is arranged.

【0013】10は前記ロータリキルン本体Kbの上方側に
配置した処理対象の投入手段で、具体的にはコンベアや
シャッタ付きのホッパなどにより形成され、ロータリキ
ルン本体Kbの上方内部に処理すべき下水汚泥等の廃棄物
を、単位量/時間で連続的に供給できるように形成され
ている。
Numeral 10 is a means to be treated which is disposed on the upper side of the rotary kiln body Kb, and is specifically formed by a conveyor, a hopper with a shutter or the like, and is disposed inside the rotary kiln body Kb to be treated. It is formed so that waste such as sludge can be continuously supplied at a unit amount / hour.

【0014】11は前記投入手段10の手前側に配置した前
処理部であり、この前処理部11は成形部11aと表面乾燥
部11bとから構成されている。この成形部11aにおいて
は、処理対象が下水汚泥の場合には、図示しないが、当
該汚泥に鉱石粉末を混練するミキサーと、ミキサーで混
練したものを吐出ノズルから連続的に排出する機能を具
備した、例えばペレット成形機により形成する。また、
前処理部11は、ロータリキルン本体Kbの上方側に選択的
に、又は、並列的に配置される。前処理部11のうち表面
乾燥部11bにおいては、成形部11aで成形され定形化され
た汚泥を受け入れ、加熱手段又は送風手段により又は加
熱送風手段によりそれら汚泥の表面を乾燥状態にする。
そのような手段としては、例えばドラム式乾燥機が用い
られるが、同様の機能を有するものであれば他の加熱,
送風機器を使用することもできる。この表面乾燥部11b
において表面が乾燥された汚泥はベルトコンベアで投入
手段10へ搬送される。このように定形化された各汚泥の
表面を乾燥状態にするのは、汚泥が投入手段10に投入さ
れたとき、或は、ロータリキルン本体Kbの内部において
搬送されるとき互いに接着したり粘着したりしないよう
にするためであるが、表面を乾燥させる以外に、各汚泥
が接着したり粘着したりしない方法があれば、当然、そ
の方法を使用することができる。
Reference numeral 11 is a pretreatment section arranged on the front side of the charging means 10. The pretreatment section 11 is composed of a molding section 11a and a surface drying section 11b. In the forming unit 11a, when the treatment target is sewage sludge, although not shown, it has a mixer for kneading ore powder in the sludge, and a function of continuously discharging the mixture kneaded by the mixer from the discharge nozzle. , For example, by a pellet molding machine. Also,
The pretreatment unit 11 is selectively or in parallel arranged above the rotary kiln body Kb. In the surface drying section 11b of the pretreatment section 11, the sludge shaped and shaped by the shaping section 11a is received, and the surface of the sludge is dried by the heating means or the air blowing means or the heating air blowing means.
As such a means, for example, a drum type dryer is used, but if it has a similar function, other heating,
Blowers can also be used. This surface drying section 11b
The sludge, the surface of which has been dried, is conveyed to the charging means 10 by a belt conveyor. The surfaces of the sludges thus formed are dried so that the sludges adhere to each other or stick to each other when the sludge is thrown into the throwing means 10 or conveyed inside the rotary kiln body Kb. In order to prevent the sludge from coming off, if there is a method in which each sludge does not adhere or stick to each other in addition to drying the surface, that method can be naturally used.

【0015】12はロータリキルン本体Kbの上方の開口端
において、処理工程中にキルン内部に存在する気体を吸
引して無害化処理する排気処理手段であり、図には模式
的にブロック化して示している。このうち12aは、処理
対象によって生じることがある黒煙や異臭,悪臭を燃焼
処理するためのアフターバーナと燃焼室による燃焼ブロ
ック、12bはこの燃焼ブロック12aから出る排気を冷却す
る冷却ブロック、12cは、冷却された排気中のCl成分な
どを中和するための消石灰と、次のフィルタブロック内
の濾布の集塵効率を上げるための活性炭を充填した中和
ブロックで、この活性炭はロータリキルンで炭化処理し
た汚泥炭を粉砕したものを使用することができる。12d
は、排気中の灰や塵を濾過するフィルタブロックと冷却
手段としてのサイクロンなどによる吸引ブロックとから
なる濾過吸引ブロックである。
Reference numeral 12 denotes an exhaust treatment means for detoxifying the gas present inside the kiln during the treatment process at the upper open end of the rotary kiln body Kb, which is schematically shown as a block. ing. Of these, 12a is a combustion block by an afterburner and a combustion chamber for burning and processing black smoke, an offensive odor, and a bad odor that may be generated depending on the processing target, 12b is a cooling block for cooling the exhaust gas emitted from this combustion block 12a, and 12c is , A neutralization block filled with slaked lime to neutralize the Cl components in the cooled exhaust and activated carbon to increase the dust collection efficiency of the filter cloth in the next filter block.This activated carbon is a rotary kiln. It is possible to use crushed carbonized sludge. 12d
Is a filter suction block including a filter block for filtering ash and dust in the exhaust gas and a suction block such as a cyclone as cooling means.

【0016】以上により本発明方法を実施するロータリ
キルンを利用した炭化処理装置の一例を構成するので、
次にこの装置を使用した汚泥の炭化処理について説明す
る。
As described above, since an example of the carbonization apparatus utilizing the rotary kiln for carrying out the method of the present invention is constructed,
Next, carbonization treatment of sludge using this device will be described.

【0017】まず、前処理部11において、脱水した処理
すべき下水汚泥に鉱石粉末を3〜8体積%程度の比率で
混ぜ、全体を混練して汚泥の含水率を低げたものを練物
状のものと同様に、成形機から押出すことにより投入手
段10に供給する。
First, in the pretreatment section 11, ore powder is mixed with dehydrated sewage sludge to be treated at a ratio of about 3 to 8% by volume, and the whole is kneaded to reduce the water content of the sludge into a kneaded form. Similarly to the above, it is supplied to the charging means 10 by being extruded from the molding machine.

【0018】一方、ロータリキルン本体Kbに対しては、
前記処理対象の投入手段10による投入に先立ち、ローラ
6,7,8の中の駆動ローラを回転させることにより、
このキルン本体Kbに、搬送壁2による送り方向の回転を
与えつつ、バーナ9から火炎を吹込んで内部を予熱す
る。この予熱は20分間程度実行し、火炎の吹込みを行っ
ている状態のまま上記処理対象(汚泥)を前記投入手段
10からロータリキルン本体Kbの上方に連続的に投入す
る。
On the other hand, for the rotary kiln body Kb,
By rotating the driving rollers among the rollers 6, 7, and 8 prior to loading by the loading means 10 for processing,
The inside of the kiln body Kb is preheated by blowing flame from the burner 9 while being rotated in the feeding direction by the conveying wall 2. This preheating is performed for about 20 minutes, and the processing target (sludge) is treated with the charging means while the flame is being blown.
Continuously feed from above the rotary kiln body Kb from 10.

【0019】投入される汚泥は、ロータリキルン本体Kb
の回転によって、この内部の搬送壁2の作用でキルン本
体Kbの下方側へ順次送り込まれる。この送り込みにおい
ては、攪拌壁3が設けられている部分で、この壁3の作
用により汚泥がキルン本体Kbの天井側に持上げられて落
下する挙動を繰返し、乾燥が促進される。また、送り込
みの際には、バーナ9から火炎がキルン本体Kbの内部に
吹込まれているので、汚泥中の水分は忽ち蒸発し、ロー
タリキルン本体Kbの下流側に行くに従って汚泥自体の含
水率はほとんど無くなる。更に、排気処理手段12も、こ
の段階では既に駆動され、ロータリキルン本体Kbの内部
を吸引している。
The sludge to be charged is the rotary kiln body Kb.
Due to the rotation of the inside of the kiln main body Kb, it is sequentially fed by the action of the conveying wall 2 inside. In this feeding, in the portion where the agitation wall 3 is provided, the action of the wall 3 causes sludge to be repeatedly lifted up to the ceiling side of the kiln body Kb and dropped, thereby promoting drying. In addition, since the flame is blown into the kiln body Kb from the burner 9 at the time of feeding, the water content in the sludge will be evaporated and the water content of the sludge itself will decrease as it goes to the downstream side of the rotary kiln body Kb. It almost disappears. Further, the exhaust processing means 12 is already driven at this stage, and sucks the inside of the rotary kiln body Kb.

【0020】この結果、ロータリキルン本体Kbの内部に
投入され、当該本体Kbの回転によってその下部側に搬送
され下端部に到達した乾燥汚泥はその内部から放出され
る可燃性ガス成分が、前記バーナ9の火炎によって着火
する。本発明では、汚泥がこのようにしてそのガス成分
に着火したらバーナ9からの火炎の吹込みを停止する。
火炎の吹込みが停止されても前記ガス成分の燃焼状態は
変らないが、その着火部分はロータリキルン本体Kbの内
部を徐々に上方(処理物の投入側)に遡上し、例えば上
方の端部から2m〜3mくらいの箇所に定位(燃焼位置
F)して、そこで汚泥から放出される可燃性ガス成分の
燃焼が続く。このときのロータリキルン本体Kbの内部温
度は800℃〜830℃程度になる。
As a result, the dry sludge introduced into the rotary kiln main body Kb, conveyed to the lower side by the rotation of the main body Kb, and reaching the lower end of the rotary kiln main body Kb has a combustible gas component released from the inside thereof, and the burnable gas component is Ignite with a flame of 9. In the present invention, when the sludge thus ignites its gas component, the blowing of the flame from the burner 9 is stopped.
Even if the blowing of flame is stopped, the combustion state of the gas component does not change, but the ignited portion gradually goes up inside the rotary kiln body Kb to the upper side (the input side of the processed material), for example, the upper end. It is localized (combustion position F) at a position about 2 to 3 m from the section, and the combustion of the combustible gas component released from the sludge continues there. At this time, the internal temperature of the rotary kiln body Kb is about 800 ° C to 830 ° C.

【0021】上記のようにしてロータリキルン本体Kbの
内部においては汚泥内部から放出される可燃ガス成分が
燃焼するが、この燃焼による当該汚泥の炭化機構につい
て説明する。ロータリキルン本体Kbの内部における定位
置Fで、処理物M(汚泥)が燃焼しているように見える
のは、その処理物Mの内部から放出される可燃性ガスの
燃焼である。そして、この燃焼が定位置Fで持続される
のは、ロータリキルン本体Kbの内部においては、ロータ
リキルン本体Kbの回転によって前記定位置Fに順次上方
から送られて来る処理物たる汚泥が、丁度その位置Fで
汚泥内部から放出されている可燃ガスの燃焼条件が整う
からである。即ち、その可燃性ガスの燃焼に必要な酸素
はロータリキルン本体Kbの下方(下流)から常時供給
(排気処理手段12の吸引作用)されるが、供給される酸
素は殆んどこの定位置Fでの燃焼で消費されてしまい、
ロータリキリン本体Kb内では汚泥自体が燃焼するための
酸素が欠乏するからである。
As described above, the combustible gas component released from the inside of the sludge is combusted inside the rotary kiln body Kb, and the carbonization mechanism of the sludge due to this combustion will be described. At the fixed position F inside the rotary kiln body Kb, it seems that the processed material M (sludge) is burning because of the combustion of the combustible gas released from the inside of the processed material M. This combustion is maintained at the fixed position F because inside the rotary kiln body Kb, the sludge, which is the processed product, which is sequentially sent from above to the fixed position F by the rotation of the rotary kiln body Kb, is just This is because the combustion conditions of the combustible gas released from the inside of the sludge are adjusted at the position F. That is, the oxygen necessary for the combustion of the combustible gas is constantly supplied from below (downstream) the rotary kiln body Kb (suction action of the exhaust treatment means 12), but the oxygen supplied is almost at the fixed position F. Burned in, consumed
This is because oxygen for burning the sludge itself is deficient in the rotary giraffe body Kb.

【0022】この結果、ロータリキルン本体Kbの内部に
おいては、可燃性ガスが定位置Fで燃焼を持続すること
と、キルン本体Kbの内部は排気処理手段12の吸引作用を
受けていることによって、燃焼位置Fよりも上流側はほ
とんど無酸素乃至は酸欠状態となり、また、下流側にお
いても吸引される酸素は定位置Fでの燃焼に消費され
て、酸素欠乏乃至はその近似状態となる。その一方で、
前記定位置Fで持続される燃焼を熱源としてロータリキ
ルン本体Kbの内部は下方の端部(外気流入端)を除いて
は、800℃〜830℃程度に保持される。このような酸素環
境,温度環境におかれるロータリキルン本体Kbの内部を
搬送される処理物M(汚泥)は、それ自体が燃焼される
ことなく熱分解されてその炭化が進行するのである。回
転しているロータリキルン本体Kbの下端からは、炭化し
た汚泥がピットPの容器20に落下するので、そこで炭化
物が回収される。
As a result, the combustible gas continues to burn at the fixed position F inside the rotary kiln body Kb, and the inside of the kiln body Kb receives the suction action of the exhaust treatment means 12, The upstream side of the combustion position F is almost anoxic or oxygen-deficient, and the oxygen sucked in the downstream side is consumed for combustion at the fixed position F, and becomes oxygen-deficient or its approximate state. On the other hand,
With the combustion continued at the fixed position F as a heat source, the inside of the rotary kiln body Kb is maintained at about 800 ° C. to 830 ° C. except for the lower end portion (outside air inflow end). The treated material M (sludge) transported inside the rotary kiln body Kb in such oxygen environment and temperature environment is thermally decomposed without being burned, and its carbonization proceeds. From the lower end of the rotating rotary kiln body Kb, carbonized sludge drops into the container 20 in the pit P, and the carbide is recovered there.

【0023】なお、下水汚泥の場合は、含水率が季節に
より10%程度の変動があるため、前処理部11において定
形化され、表面が乾燥された汚泥であっても、それらの
内部の含水率は季節によって異なっている。しかしなが
ら、お互いに接着、粘着しない条件が整えられているの
で、含水率が変わっても、上記のロータリキルン本体Kb
内において同様に炭化処理される。即ち、含水率が少な
い場合はロータリキルン本体Kb内における燃焼条件が整
う定位置Fが上流側に移動(火炎が上流側に移動)し、
含水率が大きい場合は、乾燥時間が掛かるので、燃焼条
件が整う定位置Fが下流側に移動(火炎が下流側に移
動)する。このことは、汚泥が乾燥されて内部から放出
される可燃ガス成分の放出位置が含水率によりロータリ
キルン本体Kb内において上流側或は下流側に自動的に移
動することを意味している。
In the case of sewage sludge, since the water content varies by about 10% depending on the season, even if the sludge that is standardized in the pretreatment section 11 and the surface is dried, the water content inside them is increased. Rates vary according to the season. However, since the conditions are such that they do not adhere or stick to each other, even if the water content changes, the above rotary kiln body Kb
In the same manner, carbonization treatment is carried out. That is, when the water content is low, the fixed position F where the combustion conditions are set in the rotary kiln body Kb moves to the upstream side (the flame moves to the upstream side),
If the water content is large, it takes a long time to dry, so the fixed position F where the combustion conditions are adjusted moves to the downstream side (the flame moves to the downstream side). This means that the position where the sludge is dried and the flammable gas component released from the inside is automatically moved to the upstream side or the downstream side in the rotary kiln body Kb due to the water content.

【0024】上記のロータリキルン本体Kbの内部でのガ
ス燃焼、並びに、炭化現象により生じる当該本体Kb内の
気体の排気は、排気処理手段12に吸引されて、黒煙や臭
気は、その燃焼ブロック12aで処理され、またCl成分等
は冷却ブロック12bを通ってから次の中和ブロック12cで
浄化された上で濾過吸引ブロック12dから系外に放出さ
れる。
The exhaust gas of the gas inside the main body Kb caused by the gas combustion inside the rotary kiln main body Kb and the carbonization phenomenon is sucked into the exhaust processing means 12, and the black smoke and the odor are removed from the combustion block. After being treated by 12a, Cl components and the like pass through the cooling block 12b, are purified by the next neutralization block 12c, and are then discharged from the filtration suction block 12d to the outside of the system.

【0025】次に、図1に示した炭化処理装置のロータ
リキルン本体Kbの筒体1内における搬送壁2に、上記例
のものとは形状が異なる図2に示したような攪拌壁31を
設けた別例について説明する。この攪拌壁31は搬送壁2
の外周縁から内側に膨出形成した断面略半円弧状のもの
で、この攪拌壁31によれば、処理物Mが搬送壁2の内周
縁より内側に入り込むことがなく、前後の搬送壁2,2
の間で、処理物Mの表裏が反転し転がるように攪拌され
るので、燃えることなく好適に炭化される。即ち、加熱
された熱風は筒体1内における搬送壁2の内周縁の内側
を通るが、この内周縁より内側に処理物Mが入り込む
と、直接火炎が当たるため、予め処理物Mに鉱石を混合
させておかないと燃えてしまい、相当量が灰化されてし
まう。そこで、上記のように処理物Mが前後の搬送壁
2,2の間にあって、搬送壁2の内周縁より内側に入り
込むことがないように攪拌(図3、図4参照)すれば、
燃えることはなく、しかも前後の搬送壁2,2の間にお
ける酸素は処理物Mから排出される可燃性ガスの燃焼に
消費されるので、この搬送壁2,2の間は極めて酸素が
少ない状態になり、この状態において搬送壁2の内周縁
より内側を通る加熱された熱風により高温度に加熱され
ると、処理物Mから更に可燃性ガスが発生し、いわゆる
蒸し焼き状態となって炭化が促進される。従って、この
攪拌壁31を用いた場合は、処理物Mに予め鉱石を混合さ
せておく必要がないので、純度の高い炭化物が得られ
る。上記の攪拌壁31の形状は断面略半円形であるが、こ
れ以外に、上記と同様に処理物Mを攪拌できるのであれ
ば、断面略三角形状,断面略台形状,断面略山形状であ
ってもよく、また、上記断面略半円弧状の攪拌壁を含め
これらの攪拌壁の外面は、波形などによる凹凸面に形成
してもよい。なお、この例の炭化処理装置は勿論、図1
に示した炭化処理装置においても、均一な炭が得られる
ようにするためには、汚泥などの処理物Mの形状が整っ
ている必要がある。
Next, a stirring wall 31 as shown in FIG. 2 having a shape different from that of the above example is provided on the conveying wall 2 in the cylindrical body 1 of the rotary kiln body Kb of the carbonization apparatus shown in FIG. Another example will be described. This stirring wall 31 is the transfer wall 2
The semicircular arc-shaped cross section is formed to bulge inward from the outer peripheral edge of the conveying wall 2. The stirring wall 31 prevents the processed material M from entering the inner peripheral edge of the conveying wall 2, , 2
During this period, the front and back of the treated product M are inverted and agitated so as to roll, so that the treated product M is preferably carbonized without burning. That is, the heated hot air passes through the inner side of the inner peripheral edge of the transfer wall 2 in the cylindrical body 1. However, when the processed material M enters inside the inner peripheral edge, the flame directly hits the processed material M in advance. If they are not mixed, they will burn and a considerable amount will be incinerated. Therefore, as described above, if the processed material M is located between the front and rear transfer walls 2 and 2 and is agitated so as not to enter the inner peripheral edge of the transfer wall 2 (see FIGS. 3 and 4),
Since it does not burn, and the oxygen between the front and rear transfer walls 2 and 2 is consumed for the combustion of the combustible gas discharged from the processed material M, the oxygen between the transfer walls 2 and 2 is extremely low. In this state, when heated to a high temperature by the heated hot air that passes inside the inner peripheral edge of the transport wall 2, a flammable gas is further generated from the processed material M, and a so-called steamed state is produced, which promotes carbonization. To be done. Therefore, when this stirring wall 31 is used, it is not necessary to mix the ore with the processed material M in advance, and thus a carbide having high purity can be obtained. The shape of the stirring wall 31 is substantially semicircular in cross section, but in addition to this, if the processed material M can be stirred in the same manner as described above, it may be substantially triangular in cross section, substantially trapezoidal in cross section, or substantially mountain-shaped in cross section. Alternatively, the outer surfaces of these stirring walls, including the stirring wall having a substantially semicircular arc shape in cross section, may be formed into a corrugated surface. It should be noted that the carbonization apparatus of this example is of course shown in FIG.
Also in the carbonization treatment apparatus shown in (1), in order to obtain uniform charcoal, the shape of the treated matter M such as sludge needs to be adjusted.

【0026】[0026]

【発明の効果】本発明は以上の通りであって、汚泥のよ
うな含水率が高く、また不定形で粘性も高い汚泥のよう
な従来では炭化処理など考えられなかった廃棄物を、そ
れに鉱石紛末を混練して含水率を低下せしめこの状態で
成形機を通し断面形状を定形化し、内周面に螺旋状の搬
送壁と搬送壁を横断する攪拌壁を一部に形成した円筒状
のロータリキルンの上方に、当該ロータリキルンを回転
させつつ所定の単位量で連続的に供給するとき、ロータ
リキルンの下方からこのロータリキルンの内部に火炎を
吹込み、該ロータリキルン内で前記汚泥が着火したら火
炎の吹込みを止めると共に、ロータリキルンの上方から
該ロータリキルンの内部の気体を吸引し無害化処理して
排気することにより、ロータリキリンの下部から前記汚
泥の炭化物が連続的に取出されるようにしたので、至っ
て省エネルギ的に汚泥のような廃棄物を、効率よく連続
的に炭化処理することができるのである。従って、本発
明は特に最終処理に困窮している下水汚泥の処理方法と
してきわめて有用である。
EFFECTS OF THE INVENTION The present invention is as described above, and wastes which have not been considered such as carbonization treatment in the past, such as sludge, which has a high water content and which is amorphous and has high viscosity, are added to the ore. In order to reduce the water content by kneading the powder, the cross-sectional shape was standardized through a molding machine, and a cylindrical transfer wall and a stirring wall that crossed the transfer wall were formed in part on the inner peripheral surface. When the rotary kiln is continuously supplied in a predetermined unit amount above the rotary kiln while rotating, the flame is blown into the rotary kiln from below the rotary kiln, and the sludge is ignited in the rotary kiln. Then, while stopping the blowing of the flame, the gas inside the rotary kiln is sucked from above the rotary kiln to detoxify it and exhaust it. Since to be taken out, waste such as pretty energy saving manner sludge is the efficiency can be continuously carbonized. Therefore, the present invention is extremely useful as a method for treating sewage sludge, which is especially poor in final treatment.

【0027】また、本発明の炭化処理方法によれば、従
来の汚泥などを含水率が約70〜80%の脱水ケーキにして
焼却炉において焼却処理する方法と比べ、自燃式ゆえに
酸素の消費量が少なく、従って、CO2の大気中への排出
を35%も削減することができるという効果が得られる。
このことは燃焼のための空気の使用量を少なくできると
いうことになり、それ故、燃焼のための燃焼ブロックを
小型化できると共に、冷却ブロックや中和ブロック,濾
過吸引ブロックも同じく小型化することができるという
効果が得られる。
Further, according to the carbonization method of the present invention, compared with the conventional method in which sludge is made into a dehydrated cake having a water content of about 70 to 80% and incinerated in an incinerator, the amount of oxygen consumed is self-combustion. Therefore, it is possible to reduce the emission of CO 2 into the atmosphere by as much as 35%.
This means that the amount of air used for combustion can be reduced. Therefore, the combustion block for combustion can be downsized, and the cooling block, neutralization block, and filtration / suction block must also be downsized. The effect of being able to do is obtained.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明方法を実施するための炭化処理装置を模
式的に示した一部を断面にした側面図。
FIG. 1 is a side view with a partial cross section schematically showing a carbonization apparatus for carrying out the method of the present invention.

【図2】図1に示した炭化処理装置における搬送壁に、
図1のものとは異なる攪拌壁を設けた搬送壁の一部拡大
斜視図。
FIG. 2 shows a transfer wall in the carbonization apparatus shown in FIG.
The partially expanded perspective view of the conveyance wall which provided the stirring wall different from the thing of FIG.

【図3】図2に示した搬送壁を用い、図1に示した装置
で炭化処理をしている状態を示す筒体1の断面図。
FIG. 3 is a cross-sectional view of the tubular body 1 showing a state where carbonization is performed by the apparatus shown in FIG. 1 using the transfer wall shown in FIG.

【図4】図3に示した状態から筒体1を回転させた状態
を示す筒体1の断面図。
4 is a cross-sectional view of the tubular body 1 showing a state in which the tubular body 1 is rotated from the state shown in FIG.

【符号の説明】[Explanation of symbols]

1 筒体 2 搬送壁 3 攪拌壁 4 断熱層 5 帯状環 6,7,8 支持ローラ 9 ガスバーナ 9a 火炎噴射口 10 投入手段 11 前処理部 11a 成形部 11b 表面乾燥部 12 排気処理手段 12a 燃焼ブロック 12b 冷却ブロック 12c 中和ブロック 12d 濾過吸引ブロック Kb ロータリキルン本体 M 炭化処理物 1 cylinder 2 Transport wall 3 stirring wall 4 heat insulation layer 5 strip ring 6,7,8 Support roller 9 gas burner 9a Flame injection port 10 Input means 11 Pretreatment section 11a Molding part 11b Surface drying section 12 Exhaust treatment means 12a combustion block 12b cooling block 12c Neutralization block 12d filtration suction block Kb rotary kiln body M carbonized products

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 5/20 F23G 5/20 A 7/00 104 7/00 104A Fターム(参考) 3K061 AA07 AB02 AC02 BA05 CA01 DA03 DA17 DB14 GA05 KA02 KA16 3K065 AA07 AB02 AC02 BA05 CA03 CA04 4D059 AA03 BB05 BB14 BD01 BD11 BD22 BJ02 BK09 BK10 CB04 CC03 DA51 4H012 HA06 Front page continuation (51) Int.Cl. 7 Identification code FI theme code (reference) F23G 5/20 F23G 5/20 A 7/00 104 7/00 104A F term (reference) 3K061 AA07 AB02 AC02 BA05 CA01 DA03 DA17 DB14 GA05 KA02 KA16 3K065 AA07 AB02 AC02 BA05 CA03 CA04 4D059 AA03 BB05 BB14 BD01 BD11 BD22 BJ02 BK09 BK10 CB04 CC03 DA51 4H012 HA06

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 (イ) 水分を含有する不定形の汚泥に鉱
石紛末を混練して含水率を低下せしめこの状態で成形機
を通し断面形状を定形化し、定形化された各汚泥をそれ
ら同士が接着乃至は粘着しない表面状態にしてから、当
該定形化された汚泥を、内周面に螺旋状の搬送壁と該搬
送壁の一部に当該搬送壁を横断する攪拌壁を形成した円
筒状のロータリキルンの上方に、当該ロータリキルンを
回転させつつ所定の単位量で連続的に供給する、 (ロ) 前記(イ)の状態におかれているロータリキルンの
下方からこのロータリキルンの内部に火炎を吹込み、該
ロータリキルン内で前記汚泥が着火したら火炎の吹込み
を止める、 (ハ) 前記(イ),(ロ)の状態におかれるロータリキルン
の上方から該ロータリキルンの内部の気体を吸引し無害
化処理して排気する、 (ニ) 前記(イ)〜(ハ)の操作を行うことによりロータリ
キリンの下部から前記汚泥の炭化物を排出させることを
特徴とする汚泥の炭化処理方法。
(A) (1) Kneading ore powder to an amorphous sludge containing water to reduce the water content, and in this state, a cross-sectional shape is shaped through a molding machine, and each shaped sludge is A cylinder in which the shaped sludge is formed on its inner peripheral surface with a spiral conveying wall and a stirring wall that crosses the conveying wall at a part of the conveying wall after the surfaces are made to not adhere or stick to each other. Above the rotary kiln, the rotary kiln is continuously supplied in a predetermined unit amount while rotating, (b) From below the rotary kiln in the state of (a), the inside of this rotary kiln Blow a flame into the rotary kiln, and stop blowing the flame when the sludge ignites in the rotary kiln, (c) from above the rotary kiln in the conditions (a) and (b) above the inside of the rotary kiln. Inhale gas, detoxify and exhaust (D) A method for carbonizing sludge, which comprises discharging the carbide of the sludge from the lower part of the rotary giraffe by performing the operations of (a) to (c).
【請求項2】 定形化された汚泥は、加熱手段又は送風
手段若しくは加熱送風手段を用いて各汚泥同士が接着乃
至は粘着しない表面状態にする請求項1の汚泥の炭化処
理方法。
2. The method for carbonizing sludge according to claim 1, wherein the sludge that has been standardized is brought into a surface state in which the sludges are not adhered or adhered to each other by using a heating unit, a blowing unit, or a heating blowing unit.
【請求項3】 攪拌壁は断面略半円弧状で、搬送壁の外
周縁から内側に膨出形成したものである請求項1又は2
の汚泥の炭化処理方法。
3. The stirring wall has a substantially semi-circular cross section and is formed so as to bulge inward from the outer peripheral edge of the conveying wall.
Of sludge carbonization.
JP2001373879A 2000-12-07 2001-12-07 Sludge carbonization method Expired - Fee Related JP4559678B2 (en)

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JP2000372884 2000-12-07
JP2000372884 2000-12-07
JP2001373879A JP4559678B2 (en) 2000-12-07 2001-12-07 Sludge carbonization method

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* Cited by examiner, † Cited by third party
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JP2011189303A (en) * 2010-03-16 2011-09-29 Nishimatsu Constr Co Ltd Gasification treatment apparatus and soil treatment system
CN103911166A (en) * 2014-04-15 2014-07-09 石家庄新华能源环保科技股份有限公司 Semi-coke furnace capable of processing pulverized coal raw material
JP2017015336A (en) * 2015-07-02 2017-01-19 メタウォーター株式会社 Sludge drying method and sludge drying device
CN108033657A (en) * 2017-12-18 2018-05-15 北京城市排水集团有限责任公司 A kind of method for improving pyrolyzing sludge carbonization absorption property

Cited By (4)

* Cited by examiner, † Cited by third party
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JP2011189303A (en) * 2010-03-16 2011-09-29 Nishimatsu Constr Co Ltd Gasification treatment apparatus and soil treatment system
CN103911166A (en) * 2014-04-15 2014-07-09 石家庄新华能源环保科技股份有限公司 Semi-coke furnace capable of processing pulverized coal raw material
JP2017015336A (en) * 2015-07-02 2017-01-19 メタウォーター株式会社 Sludge drying method and sludge drying device
CN108033657A (en) * 2017-12-18 2018-05-15 北京城市排水集团有限责任公司 A kind of method for improving pyrolyzing sludge carbonization absorption property

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