JPH1133599A - Carbonized sludge producing apparatus - Google Patents

Carbonized sludge producing apparatus

Info

Publication number
JPH1133599A
JPH1133599A JP9210030A JP21003097A JPH1133599A JP H1133599 A JPH1133599 A JP H1133599A JP 9210030 A JP9210030 A JP 9210030A JP 21003097 A JP21003097 A JP 21003097A JP H1133599 A JPH1133599 A JP H1133599A
Authority
JP
Japan
Prior art keywords
furnace
gas
sludge
drying
supplied
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
JP9210030A
Other languages
Japanese (ja)
Other versions
JP3787690B2 (en
Inventor
Makoto Terunuma
誠 照沼
Setsuya Morino
節也 森野
Mikihiko Ono
幹彦 大野
Haruki Takai
治樹 高井
Akira Kagohashi
章 籠橋
Akira Minowa
亮 美濃羽
Kazuaki Yamaguchi
一昭 山口
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.)
NIPPON GESUIDO JIGYODAN
Daido Steel Co Ltd
Takasago Industry Co Ltd
TYK Corp
Original Assignee
NIPPON GESUIDO JIGYODAN
Daido Steel Co Ltd
Takasago Industry Co Ltd
TYK Corp
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 NIPPON GESUIDO JIGYODAN, Daido Steel Co Ltd, Takasago Industry Co Ltd, TYK Corp filed Critical NIPPON GESUIDO JIGYODAN
Priority to JP21003097A priority Critical patent/JP3787690B2/en
Publication of JPH1133599A publication Critical patent/JPH1133599A/en
Application granted granted Critical
Publication of JP3787690B2 publication Critical patent/JP3787690B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Carbon And Carbon Compounds (AREA)
  • Drying Of Solid Materials (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To miniaturize an apparatus and to reduce equipment costs and running costs. SOLUTION: One end of a supply pipe 21 the other end of which is connected to the outlet 17a of a hot air generating furnace 17 is connected to the suction port 12a of a drying furnace 12, the drying gas generated in the furnace 17 is supplied to the drying furnace 12. One end of an exhaust gas pipe 27 the other end of which is connected to the exhaust port 33a of a carbonization furnace 26 is connected to the inlet 17b of the furnace 17, high temperature exhaust gas generated in the carbonization furnace 26 is supplied to the furnace 17. In other words, exhaust gas containing unburned gas from the carbonization furnace 26 is supplied to the furnace 17, and the unburned gas is burned completely to remove odors.

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】この発明は、炭化汚泥製造装
置に関し、更に詳細には、例えば下水処理施設の汚水処
理過程で発生する汚泥を、乾留により炭化して土壌改良
剤等として使用し得るようにする炭化汚泥製造装置に関
するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for producing carbonized sludge, and more particularly, to a method in which sludge generated in a sewage treatment process in a sewage treatment facility is carbonized by dry distillation and used as a soil conditioner or the like. The present invention relates to a carbonized sludge production apparatus.

【0002】[0002]

【従来の技術】一般家庭や事務所、デパート、レストラ
ン等から出る家庭汚水は、下水処理施設で汚水処理さ
れ、その過程で有機物を多量に含む汚泥が発生する。こ
の汚泥を乾燥した後に更に加熱して炭化し、得られた炭
化物を土壌改良剤や融雪剤等として使用することが行な
われている。汚泥を炭化処理する装置では、乾燥炉に汚
泥(所謂「脱水ケーキ」)を供給して所要の含水率まで乾燥
した後、この乾燥汚泥を炭化炉に供給して加熱処理する
ことにより、空隙・孔に富んだ炭化物を製造するよう構
成される。
2. Description of the Related Art Household sewage from general households, offices, department stores, restaurants and the like is treated in a sewage treatment facility, and in the process, sludge containing a large amount of organic matter is generated. After drying this sludge, it is further heated and carbonized, and the obtained carbide is used as a soil improving agent, a snow melting agent and the like. In an apparatus for carbonizing sludge, after supplying sludge (so-called “dehydrated cake”) to a drying furnace and drying it to a required moisture content, the dried sludge is supplied to a carbonizing furnace and subjected to a heat treatment, so that voids / It is configured to produce a porous carbide.

【0003】[0003]

【発明が解決しようとする課題】前記乾燥汚泥を炭化す
る炭化炉では、該乾燥汚泥を蒸し焼き状態とする乾留を
行ない、燃焼成分を揮発させて乾留ガスを発生させ、こ
の乾留ガスを燃焼させることで炭化炉の内部を乾留状態
に保持する構成が採用されている。この場合に、乾留ガ
スは炭化炉では完全に燃焼しないため、その燃焼しきれ
なかった未燃ガスを含む排気ガスには臭気が混じってお
り、これを直に外部に排出すると周囲環境を汚染して問
題となる。そこで、炭化炉における排気ガスの排気側に
脱臭炉を付設し、該炭化炉から排出される排気ガスに含
まれる未燃ガスを脱臭炉で完全に燃焼することで脱臭し
た後に、外部に排出するよう構成していた。しかるにこ
の場合は、付帯設備として脱臭炉が必要になるために設
備コストが嵩むと共に装置全体が大型化し、大きな設置
スペースが必要となる難点がある。また、脱臭炉で使用
される燃料等の費用が嵩み、全体のランニングコストが
高くなる欠点も指摘される。
In the carbonization furnace for carbonizing the dry sludge, dry distillation is performed to make the dry sludge in a steamed state, a combustion component is volatilized to generate a dry distillation gas, and the dry distillation gas is burned. A configuration is employed in which the inside of the carbonization furnace is kept in a dry distillation state. In this case, since the carbonized gas does not completely burn in the carbonization furnace, the exhaust gas containing unburned gas that has not been completely burned contains an odor.If this gas is discharged directly to the outside, the surrounding environment is polluted. Problem. Therefore, a deodorizing furnace is attached to the exhaust side of the exhaust gas in the carbonization furnace, and after the unburned gas contained in the exhaust gas discharged from the carbonization furnace is completely deodorized by being completely burned in the deodorizing furnace, it is discharged to the outside. It was configured as follows. However, in this case, since a deodorizing furnace is required as ancillary equipment, equipment costs are increased, and the entire apparatus is increased in size, and a large installation space is required. Further, it is pointed out that the cost of fuel and the like used in the deodorizing furnace increases, and that the overall running cost increases.

【0004】[0004]

【発明の目的】この発明は、従来の技術に係る炭化汚泥
製造装置に内在している前記欠点に鑑み、これを好適に
解決するべく提案されたものであって、装置の小型化を
図ると共に設備コストおよびランニングコストを低減し
得る炭化汚泥製造装置を提供することを目的とする。
SUMMARY OF THE INVENTION The present invention has been proposed in view of the above-mentioned drawbacks inherent in the conventional carbonized sludge production apparatus, and has been proposed to solve the problem suitably. It is an object of the present invention to provide a carbonized sludge production apparatus capable of reducing equipment costs and running costs.

【0005】[0005]

【課題を解決するための手段】前記課題を克服し、初期
の目的を達成するため、本発明に係る炭化汚泥製造装置
は、汚泥が供給される乾燥炉と、この乾燥炉に高温の乾
燥用気体を供給する熱風発生炉と、前記乾燥炉で乾燥さ
れた乾燥汚泥が供給され、この乾燥汚泥を炭化させる炭
化炉とから構成される炭化汚泥製造装置において、前記
炭化炉の内部に画成した燃焼室に、前記乾燥炉で乾燥さ
れた乾燥汚泥が供給される筒体を連通状態で配設し、該
筒体の内部で発生させた乾留ガスを燃焼室で燃焼させる
ようにし、前記炭化炉の燃焼室と前記熱風発生炉とを連
通接続し、該燃焼室で燃焼しきれなかった未燃ガスを含
む排気ガスを前記熱風発生炉に供給して燃焼させるよう
構成したことを特徴とする。
SUMMARY OF THE INVENTION In order to overcome the above-mentioned problems and to achieve the initial object, a carbonized sludge producing apparatus according to the present invention comprises a drying furnace to which sludge is supplied, and a high-temperature drying furnace in the drying furnace. In a carbonized sludge manufacturing apparatus comprising a hot air generating furnace for supplying gas and dry sludge dried in the drying furnace, and a carbonizing furnace for carbonizing the dried sludge, the inside of the carbonizing furnace is defined. In the combustion chamber, a cylinder to which the dried sludge dried in the drying furnace is supplied is disposed in communication with the combustion chamber, and the carbonization gas generated inside the cylinder is burned in the combustion chamber. The combustion chamber and the hot-air generating furnace are connected to each other, and exhaust gas containing unburned gas that has not been completely burned in the combustion chamber is supplied to the hot-air generating furnace for combustion.

【0006】[0006]

【発明の実施の形態】次に、本発明に係る炭化汚泥製造
装置につき、好適な実施例を挙げて、添付図面を参照し
ながら詳細に説明する。図1は、実施例に係る炭化汚泥
製造装置の概略構成を示すものであって、下水処理施設
からトラック等で運搬された汚泥(含水率が約80%の
脱水ケーキ)が貯留される受入ホッパ10に、モーノポ
ンプ(登録商標)等の定量供給装置11が接続されてい
る。この定量供給装置11は、ロータリキルン型式の乾
燥炉12に接続され、定量供給装置11から乾燥炉12
に所定量の汚泥を連続的に供給するよう構成される。乾
燥炉12は、図2および図3に示す如く、図示しない駆
動手段により所定方向に回転される円筒状の回転筒13
の軸方向一端に、スクリューコンベヤ14を内蔵した投
入ホッパ15が投入口13aを介して連通接続され、前
記定量供給装置11からの汚泥は投入ホッパ15に供給
された後にスクリューコンベヤ14を介して回転筒13
の内部に供給されるようになっている。また回転筒13
の内壁面に、周方向に離間して複数の持上げ棧16が配
設され、回転筒13に供給された汚泥は、該回転筒13
の回転に伴って持上げ棧16により底部側から頂部側へ
持上げられた後に自重で底部へ落下する工程を繰返しな
がら出口13bに向けて移動される。なお、汚泥が底部
に落下する過程で、後述の熱風発生炉17から供給され
る高温(例えば700℃程度)の乾燥用気体と接触して、
該汚泥の乾燥がなされる。
BEST MODE FOR CARRYING OUT THE INVENTION Next, an apparatus for producing carbonized sludge according to the present invention will be described in detail with reference to the accompanying drawings with reference to preferred embodiments. FIG. 1 shows a schematic configuration of a carbonized sludge manufacturing apparatus according to an embodiment, and a receiving hopper in which sludge (a dehydrated cake having a water content of about 80%) transported from a sewage treatment facility by a truck or the like is stored. 10 is connected to a fixed amount supply device 11 such as a Mono pump (registered trademark). The quantitative supply device 11 is connected to a rotary kiln type drying furnace 12, and is supplied from the quantitative supply device 11 to the drying furnace 12.
Is continuously supplied with a predetermined amount of sludge. As shown in FIGS. 2 and 3, the drying furnace 12 has a cylindrical rotating cylinder 13 that is rotated in a predetermined direction by driving means (not shown).
At one end in the axial direction, a charging hopper 15 having a screw conveyor 14 incorporated therein is connected through a charging port 13a. Cylinder 13
It is supplied inside. Rotating cylinder 13
A plurality of lifting members 16 are disposed on the inner wall surface of the rotating cylinder 13 at a distance from each other in the circumferential direction.
Is moved toward the outlet 13b while repeating the process of being lifted from the bottom side to the top side by the lifting ridge 16 with the rotation and falling to the bottom by its own weight. In the process of sludge falling to the bottom, it comes into contact with a high-temperature (for example, about 700 ° C.) drying gas supplied from a hot-air generating furnace 17 described below,
The sludge is dried.

【0007】前記回転筒13の内部には、当該回転筒1
3の軸中心から偏位した位置に回転軸18が回転自在に
配設され、該回転軸18は駆動モータ19によって所定
方向に回転されるよう構成される。この回転軸18に
は、図2に示す如く、軸方向に離間して複数の破砕撹拌
翼20が配設され、回転軸18の回転により一体的に回
転する破砕撹拌翼20で、前記持上げ棧16により底部
側から頂部側へ持上げられた後に自重で底部へ落下する
汚泥を細かく破砕するようになっている。なお、破砕撹
拌翼20の形状や配設数および回転軸18の回転数を変
更することにより、当該乾燥炉12で得られる乾燥汚泥
の粒度を任意に設定することができる。
[0007] Inside the rotary cylinder 13, the rotary cylinder 1
A rotation shaft 18 is rotatably disposed at a position deviated from the center of the shaft 3, and the rotation shaft 18 is configured to be rotated in a predetermined direction by a drive motor 19. As shown in FIG. 2, a plurality of crushing and stirring blades 20 are disposed on the rotating shaft 18 so as to be spaced apart from each other in the axial direction. The sludge that has been lifted from the bottom side to the top side and then falls to the bottom by its own weight after it is lifted by 16 is finely crushed. The particle size of the dried sludge obtained in the drying furnace 12 can be arbitrarily set by changing the shape and the number of the crushing and stirring blades 20 and the number of rotations of the rotary shaft 18.

【0008】前記乾燥炉12の吸気口12aには、熱風
発生炉17における乾燥用気体の出口17aに一端が接
続する供給管21の他端が接続されている。この熱風発
生炉17には、パイロットバーナ用のLPG、加熱バー
ナ用の灯油および燃焼空気が供給され、気体を所定温度
まで加熱して乾燥用気体を発生させ、この高温の乾燥用
気体を供給管21を介して乾燥炉12に供給するよう構
成してある。また乾燥炉12の排気口12bに第1戻し
管22の一端が接続され、この第1戻し管22の他端は
集塵機23の吸気口23aに接続されている。更に、集
塵機23の排気口23bに一端が接続する第2戻し管2
4は、前記熱風発生炉17における気体の入口17bに
接続する後述の排ガス管27に接続され、この第2戻し
管24に介挿した循環用ブロワ25を回転することによ
り、熱風発生炉17で発生した高温の乾燥用気体を乾燥
炉12に引込むと共に、前記集塵機23で塵埃の除去さ
れた処理後気体を排ガス管27および入口17bを介し
て熱風発生炉17に戻すよう構成される。
The other end of a supply pipe 21 having one end connected to the drying gas outlet 17a of the hot air generating furnace 17 is connected to the inlet 12a of the drying furnace 12. The hot air generating furnace 17 is supplied with LPG for a pilot burner, kerosene for a heating burner, and combustion air, heats the gas to a predetermined temperature to generate a drying gas, and supplies the high-temperature drying gas to a supply pipe. It is configured to supply to the drying furnace 12 through 21. One end of a first return pipe 22 is connected to an exhaust port 12 b of the drying furnace 12, and the other end of the first return pipe 22 is connected to an intake port 23 a of a dust collector 23. Further, a second return pipe 2 having one end connected to the exhaust port 23b of the dust collector 23
4 is connected to an exhaust gas pipe 27 described below which is connected to a gas inlet 17 b of the hot air generating furnace 17, and rotates a circulation blower 25 inserted in the second return pipe 24 so that the hot air generating furnace 17 The generated high-temperature drying gas is drawn into the drying furnace 12, and the processed gas from which dust has been removed by the dust collector 23 is returned to the hot-air generating furnace 17 via the exhaust gas pipe 27 and the inlet 17 b.

【0009】前記第2戻し管24には、図1に示す如
く、前記供給管21から分岐するバイパス管29が接続
される熱交換器30が介挿されている。またバイパス管
29における熱交換器30の出口側に排気用ブロワ31
が介挿され、該ブロワ31を回転することで供給管21
を流通する乾燥用気体の一部をバイパス管29に導入す
るよう構成してある。すなわち、前記乾燥炉12で熱交
換を行なって降温された処理後気体は、熱交換器30で
乾燥用気体と熱交換して所要温度まで昇温された後に、
前記熱風発生炉17に戻されるようになっている。な
お、乾燥炉12に供給される乾燥用気体の風量は、前記
循環用ブロワ25および排気用ブロワ31の回転を制御
すると共に、供給管21に介挿した調整弁46、第2戻
し管24に介挿した調整弁47およびバイパス管29に
介挿した調整弁48を調整することにより最適な状態に
保持される。
As shown in FIG. 1, a heat exchanger 30 to which a bypass pipe 29 branching from the supply pipe 21 is connected is inserted in the second return pipe 24. An exhaust blower 31 is provided at the outlet side of the heat exchanger 30 in the bypass pipe 29.
Is inserted, and the supply pipe 21 is rotated by rotating the blower 31.
Is introduced into the bypass pipe 29. That is, the post-treatment gas, which has undergone heat exchange in the drying furnace 12 and has been cooled, is heat-exchanged with the drying gas in the heat exchanger 30 and heated to the required temperature.
The heat is returned to the hot-air generating furnace 17. The flow rate of the drying gas supplied to the drying furnace 12 controls the rotation of the circulation blower 25 and the exhaust blower 31, and is transmitted to the adjustment valve 46 and the second return pipe 24 inserted in the supply pipe 21. By adjusting the interposed regulating valve 47 and the regulating valve 48 interposed in the bypass pipe 29, an optimum state is maintained.

【0010】前記乾燥炉12の出口13bに移送装置3
2が接続され、乾燥炉12で所要の含水率(約40%)ま
で乾燥された乾燥汚泥を移送装置32で炭化炉26に供
給するようになっている。この炭化炉26は、図4に示
す如く、炉本体33の内部に2基の相互に連通する炉体
34,34を備えている。また炭化炉26には、2基の
炉体34,34に貫通された円筒状の回転筒(筒体)37
が回転自在に支持され、駆動モータ38によって所定方
向に回転するよう構成されると共に、前記移送装置32
で移送された乾燥汚泥が投入口37aを介して供給され
る。この回転筒37には、炉体34の内部に画成された
燃焼室34aに連通する複数の乾留ガス供給管39が配
設され、回転筒37の内部で発生した乾留ガスが燃焼室
34aに噴出するようになっている。また炉体34の内
部に、複数の加熱源としての助燃バーナ40が配設さ
れ、該バーナ40によって回転筒37を加熱して、乾留
ガスを発生させ得る状態(蒸し焼き状態)とするよう構成
される。そして、乾留ガスが発生した以後においては、
回転筒37から燃焼室34aに噴出させた乾留ガスを燃
焼させることで、回転筒37の内部を乾留状態に保持す
るよう構成される。なお、炉体34には、パイロットバ
ーナ用のLPG、助燃バーナ用の灯油が供給されると共
に、回転筒37には乾留状態を維持するに足るだけの酸
素(空気)が供給されるようになっている。
The transfer device 3 is connected to the outlet 13b of the drying furnace 12
2 is connected, and the dried sludge dried to a required moisture content (about 40%) in the drying furnace 12 is supplied to the carbonization furnace 26 by the transfer device 32. As shown in FIG. 4, the carbonization furnace 26 includes two furnace bodies 34, 34 communicating with each other inside a furnace main body 33. The carbonizing furnace 26 has a cylindrical rotating cylinder (cylindrical body) 37 penetrated by two furnace bodies 34, 34.
Is rotatably supported, is configured to rotate in a predetermined direction by a drive motor 38, and the transfer device 32
The dried sludge transferred in the above is supplied through the inlet 37a. The rotary cylinder 37 is provided with a plurality of carbonized gas supply pipes 39 communicating with the combustion chamber 34a defined inside the furnace body 34, and the carbonized gas generated inside the rotary cylinder 37 is supplied to the combustion chamber 34a. It gushes out. Further, inside the furnace body 34, a plurality of auxiliary combustion burners 40 as a heating source are arranged, and the rotary cylinder 37 is heated by the burners 40 so as to be in a state in which a dry distillation gas can be generated (steaming state). You. And after the carbonization gas is generated,
By burning the carbonized gas spouted from the rotating cylinder 37 into the combustion chamber 34a, the inside of the rotating cylinder 37 is configured to be kept in a carbonized state. The furnace body 34 is supplied with LPG for a pilot burner and kerosene for an auxiliary burner, and the rotary cylinder 37 is supplied with enough oxygen (air) to maintain a dry distillation state. ing.

【0011】前記炉本体33に設けた排気口33aに一
端が接続された排ガス管27の他端は、前記熱風発生炉
17の入口17bに接続され、前記炉体34における燃
焼室34aでの燃焼により生じた高温の排気ガスは、排
ガス管27を介して熱風発生炉17に供給されるよう構
成される。すなわち、燃焼室34aで燃焼しきれなかっ
た未燃ガスを含む排気ガスを熱風発生炉17に供給し、
該未燃ガスを完全に燃焼させることで臭気を除去(脱臭)
するようにしてある。また、排ガス管27に供給用ブロ
ワ50が介挿され、該ブロワ50を回転制御することに
より、排気ガスの熱風発生炉17への供給量および炭化
炉26の内部圧力を調整するよう構成される。
The other end of the exhaust gas pipe 27, one end of which is connected to an exhaust port 33a provided in the furnace main body 33, is connected to the inlet 17b of the hot air generating furnace 17, and the combustion in the combustion chamber 34a of the furnace body 34 is performed. The high-temperature exhaust gas generated by the above is configured to be supplied to the hot-air generating furnace 17 via the exhaust gas pipe 27. That is, the exhaust gas containing the unburned gas that has not been completely burned in the combustion chamber 34a is supplied to the hot-air generating furnace 17,
Remove odor by completely burning the unburned gas (deodorization)
I have to do it. Further, a supply blower 50 is inserted into the exhaust gas pipe 27, and the rotation of the blower 50 is controlled to adjust the supply amount of the exhaust gas to the hot air generator 17 and the internal pressure of the carbonization furnace 26. .

【0012】前記炭化炉26に配設される回転筒37の
内壁面には、図5に示す如く、周方向に離間して複数の
持上げ棧42が配設され、回転筒37に供給された乾燥
汚泥は、該回転筒37の回転に伴って持上げ棧42によ
り底部側から頂部側へ持上げられた後に自重で底部へ落
下する工程を繰返しながら出口37bに向けて移動され
るようになっている。なお、前記持上げ棧42は必須の
要件ではなく、省略することも可能である。
As shown in FIG. 5, a plurality of lifting members 42 are provided on the inner wall surface of the rotary cylinder 37 disposed in the carbonization furnace 26 and are spaced apart in the circumferential direction. The dried sludge is lifted from the bottom side to the top side by the lifting member 42 along with the rotation of the rotary cylinder 37, and is then moved toward the outlet 37b while repeating the process of falling to the bottom by its own weight. . The lifting member 42 is not an essential requirement, and may be omitted.

【0013】[0013]

【実施例の作用】次に、前述した実施例に係る炭化汚泥
製造装置の作用につき説明する。前記熱風発生炉17で
発生した高温の乾燥用気体は、前記循環用ブロワ25の
運転によって出口17a、供給管21および吸気口12
aを介して乾燥炉12に吸引される。また、前記定量供
給装置11から乾燥炉12に連続的に供給される汚泥
(例えば含水率80%)は、回転筒13の回転によって前
記持上げ棧16により底部側から頂部側へ持上げられた
後に自重で底部へ落下する過程で、乾燥用気体に晒され
つつ出口13bに向けて移動されることで乾燥される。
また、回転軸18の回転により一体的に回転する破砕撹
拌翼20で、汚泥は所定の大きさに破砕される。
Next, the operation of the carbonized sludge manufacturing apparatus according to the above-described embodiment will be described. The high-temperature drying gas generated in the hot-air generating furnace 17 is supplied to the outlet 17 a, the supply pipe 21, and the intake port 12 by the operation of the circulation blower 25.
It is sucked into the drying furnace 12 through a. Further, sludge continuously supplied from the quantitative supply device 11 to the drying furnace 12
(For example, a water content of 80%) is lifted from the bottom side to the top side by the lifting member 16 by the rotation of the rotary cylinder 13 and then falls to the bottom by its own weight. It is dried by being moved.
Further, the sludge is crushed into a predetermined size by the crushing and stirring blades 20 which are integrally rotated by the rotation of the rotating shaft 18.

【0014】前記乾燥炉12で所要の含水率(例えば4
0%)まで乾燥された乾燥汚泥は、移送装置32を介し
て炭化炉26の回転筒37に供給される。この回転筒3
7の内部は、運転の初期には前記助燃バーナ40により
加熱されて乾留状態とされており、従って回転筒37に
供給された乾燥汚泥からは乾留ガスが発生し、このガス
が乾留ガス供給管39から燃焼室34aに噴出する。そ
して、燃焼室34aに乾留ガスが安定的に噴出されるよ
うになった後は、該乾留ガスを燃焼室34aで燃焼させ
ることで回転筒37の内部を乾留状態に保持し、これに
より内部の乾燥汚泥は炭化される。なお、乾留ガスの燃
焼により回転筒37の内部が乾留状態に保持される状態
となった以後は、前記助燃バーナ40を消してもよい。
In the drying furnace 12, a required water content (for example, 4
The dried sludge dried to 0%) is supplied to the rotary cylinder 37 of the carbonization furnace 26 via the transfer device 32. This rotating cylinder 3
The interior of 7 is heated and carbonized by the combustion burner 40 at the beginning of the operation, so that dry sludge gas is generated from the dry sludge supplied to the rotary cylinder 37, and this gas is supplied to the carbonization gas supply pipe. From 39, it blows out to the combustion chamber 34a. After the carbonized gas is stably jetted into the combustion chamber 34a, the inside of the rotary cylinder 37 is kept in a carbonized state by burning the carbonized gas in the combustion chamber 34a. The dried sludge is carbonized. Note that after the inside of the rotary cylinder 37 is kept in a carbonized state by the combustion of the carbonized gas, the auxiliary burner 40 may be turned off.

【0015】すなわち、乾燥炉12において汚泥を含水
率80%から40%まで乾燥させつつ破砕すると共に、
炭化炉26において回転筒37を回転させつつ乾燥汚泥
の炭化を行なうよう構成したので、細かな炭化物を製造
することができる。また回転軸18の回転数等を変更す
ることにより、任意の粒径の炭化物を製造することが可
能となる。例えば園芸等で用いられる土壌改良剤として
は、5mm程度のものが好適であり、このような粒径の
炭化物を後工程で破砕することなく得ることができる。
That is, the sludge is dried and crushed in the drying furnace 12 from a moisture content of 80% to 40%.
Since the dry sludge is carbonized while rotating the rotary cylinder 37 in the carbonization furnace 26, fine carbides can be produced. Further, by changing the number of revolutions of the rotating shaft 18 or the like, it is possible to produce carbide having an arbitrary particle size. For example, a soil improver used in horticulture or the like is preferably about 5 mm, and a carbide having such a particle size can be obtained without crushing in a later step.

【0016】前記乾燥炉12の内部で汚泥と熱交換して
降温された処理後気体は、前記排気口12bから排出さ
れて第1戻し管22を介して集塵機23に導入され、こ
こで塵埃が除去される。また集塵機23で塵埃が除去さ
れた処理後気体は、該集塵機23の排気口23bに接続
する第2戻し管24に排出される。第2戻し管24に配
設された熱交換器30を処理後気体が通過する過程で、
前記供給管21から分岐したバイパス管29を流通する
高温の乾燥用気体との間で熱交換が行なわれ、この昇温
された処理後気体が前記熱風発生炉17に入口17bを
介して戻される。そして、この熱風発生炉17に戻され
た処理後気体が燃焼されて所要温度まで昇温されること
で、乾燥用気体として再利用される。また、前記炭化炉
26から排出される高温の排気ガスは、前記排ガス管2
7を介して熱風発生炉17に供給され、ここで燃焼され
ることで脱臭がなされる。
The post-treatment gas, which has undergone heat exchange with sludge in the drying furnace 12 and has been cooled, is discharged from the exhaust port 12b and introduced into a dust collector 23 through a first return pipe 22, where dust is removed. Removed. The processed gas from which dust has been removed by the dust collector 23 is discharged to the second return pipe 24 connected to the exhaust port 23b of the dust collector 23. In the process in which the gas passes through the heat exchanger 30 disposed in the second return pipe 24 after the treatment,
Heat exchange is performed between the high-temperature drying gas flowing through the bypass pipe 29 branched from the supply pipe 21, and the heated gas after the processing is returned to the hot-air generating furnace 17 via the inlet 17 b. . Then, the post-processing gas returned to the hot-air generating furnace 17 is burned and heated to a required temperature, so that it is reused as a drying gas. The high-temperature exhaust gas discharged from the carbonization furnace 26 is supplied to the exhaust gas pipe 2.
The hot air is supplied to the hot-air generating furnace 17 through the humidifier 7, where it is burned and deodorized.

【0017】すなわち、乾燥用気体の一部を利用して昇
温させた処理後気体を熱風発生炉17に戻すと共に、炭
化炉26で発生した高温の排気ガスを熱風発生炉17に
供給するよう構成したことで、該熱風発生炉17での省
エネルギーを達成し得る。また、炭化炉26の燃焼室3
4aでは乾留ガスを完全に燃焼できないため、該炭化炉
26から排出される燃焼室34aで燃焼しきれなかった
未燃ガスを含む排気ガスには臭気が含まれているが、該
排気ガスを熱風発生炉17に供給して未燃ガスを完全に
燃焼させることで脱臭が行なわれる。従って、炭化炉2
6の排気側に別途脱臭炉を設ける必要はなく、設備コス
トを低減し得ると共に装置の小型化を図り得る。更に
は、熱風発生炉17で乾燥用気体の発生と排気ガスの脱
臭とを兼用させることにより、燃料費を低減することが
でき、ランニングコストを低く抑えることも可能とな
る。また実施例の装置では、乾燥炉12から排出される
処理後気体の脱臭も熱風発生炉17で行なわれる。
That is, the post-treatment gas heated by using a part of the drying gas is returned to the hot-air generating furnace 17, and the high-temperature exhaust gas generated in the carbonizing furnace 26 is supplied to the hot-air generating furnace 17. With this configuration, energy saving in the hot air generator 17 can be achieved. Further, the combustion chamber 3 of the carbonization furnace 26
4a, the carbonized gas cannot be completely burned, so that the exhaust gas containing unburned gas that cannot be completely burned in the combustion chamber 34a discharged from the carbonization furnace 26 contains an odor. Deodorization is performed by completely supplying the generator 17 with unburned gas and burning it. Therefore, carbonization furnace 2
It is not necessary to provide a separate deodorizing furnace on the exhaust side of 6, so that equipment costs can be reduced and the size of the apparatus can be reduced. Furthermore, by combining the generation of the drying gas and the deodorization of the exhaust gas in the hot-air generating furnace 17, the fuel cost can be reduced, and the running cost can be reduced. Further, in the apparatus of the embodiment, deodorization of the post-treatment gas discharged from the drying furnace 12 is also performed in the hot air generation furnace 17.

【0018】なお、実施例では乾燥炉および炭化炉をロ
ータリキルン型式とした場合につき説明したが、本願は
これに限定されるものでなく、各種の型式のものを採用
し得る。また、実施例では炭化炉における炉本体の内部
に分割された2基の炉体を配設した場合につき説明した
が、炉本体内の略全長に亘って1基の炉体を配設しても
よい。
In the embodiment, the case where the drying furnace and the carbonizing furnace are of a rotary kiln type has been described. However, the present invention is not limited to this, and various types can be adopted. In the embodiment, the case where two divided furnace bodies are provided inside the furnace body of the carbonization furnace has been described. However, one furnace body is provided over substantially the entire length inside the furnace body. Is also good.

【0019】[0019]

【発明の効果】以上に説明した如く、本発明に係る炭化
汚泥製造装置は、炭化炉から排出される未燃ガスを含む
排気ガスを熱風発生炉に供給し、該未燃ガスを完全に燃
焼させるよう構成したので、排気ガスの脱臭を独立した
脱臭炉を設けることなく行ない得る。すなわち、炭化炉
の排気側に別途脱臭炉を設ける必要はなく、設備コスト
を低減し得ると共に装置の小型化を図り得る。また、熱
風発生炉で乾燥用気体の発生と排気ガスの脱臭とを兼用
させることにより、燃料費を低減することができ、ラン
ニングコストを低く抑えることができる。
As described above, the apparatus for producing carbonized sludge according to the present invention supplies exhaust gas containing unburned gas discharged from the carbonizing furnace to the hot-air generating furnace and completely burns the unburned gas. With this configuration, the exhaust gas can be deodorized without providing an independent deodorizing furnace. In other words, there is no need to provide a separate deodorizing furnace on the exhaust side of the carbonizing furnace, so that equipment costs can be reduced and the size of the apparatus can be reduced. Further, by combining the generation of the drying gas and the deodorization of the exhaust gas in the hot-air generating furnace, the fuel cost can be reduced and the running cost can be reduced.

【0020】更には、炭化炉から排出される高温の排気
ガスを熱風発生炉に供給することで、当該熱風発生炉で
常に常温の空気を加熱して乾燥用気体を発生させるのに
比べて省エネルギーを図り得る。
Further, by supplying high-temperature exhaust gas discharged from the carbonizing furnace to the hot-air generating furnace, energy is saved as compared with the case where the room-temperature air is always heated in the hot-air generating furnace to generate the drying gas. Can be achieved.

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

【図1】本発明の好適な実施例に係る炭化汚泥製造装置
の概略構成図である。
FIG. 1 is a schematic configuration diagram of an apparatus for producing carbonized sludge according to a preferred embodiment of the present invention.

【図2】実施例に係る乾燥炉の概略構成を示す縦断正面
図である。
FIG. 2 is a vertical sectional front view showing a schematic configuration of a drying furnace according to an embodiment.

【図3】実施例に係る乾燥炉の概略構成を示す縦断側面
図である。
FIG. 3 is a vertical sectional side view showing a schematic configuration of a drying furnace according to an embodiment.

【図4】実施例に係る炭化炉の概略構成を示す縦断正面
図である。
FIG. 4 is a vertical sectional front view showing a schematic configuration of a carbonization furnace according to an example.

【図5】実施例に係る炭化炉の概略構成を示す縦断側面
図である。
FIG. 5 is a vertical sectional side view showing a schematic configuration of a carbonization furnace according to an example.

【符号の説明】[Explanation of symbols]

12 乾燥炉 17 熱風発生炉 26 炭化炉 34a 燃焼室 37 回転筒(筒体) 40 助燃バーナ(加熱源) 12 Drying furnace 17 Hot air generating furnace 26 Carbonization furnace 34a Combustion chamber 37 Rotating cylinder (cylindrical body) 40 Combustion burner (heating source)

───────────────────────────────────────────────────── フロントページの続き (71)出願人 390008431 高砂工業株式会社 岐阜県土岐市駄知町2321番地の2 (72)発明者 照沼 誠 神奈川県平塚市菫平12−12−2−607 (72)発明者 森野 節也 岐阜県各務原市緑苑南4丁目19番地 (72)発明者 大野 幹彦 岐阜県本巣郡北方町北方1717番地 (72)発明者 高井 治樹 愛知県尾張旭市吉岡町2−1−7 (72)発明者 籠橋 章 岐阜県土岐市駄知町2321番地の2 高砂工 業株式会社内 (72)発明者 美濃羽 亮 岐阜県土岐市駄知町2321番地の2 高砂工 業株式会社内 (72)発明者 山口 一昭 岐阜県土岐市駄知町2321番地の2 高砂工 業株式会社内 ──────────────────────────────────────────────────続 き Continued on the front page (71) Applicant 390008431 Takasago Industry Co., Ltd. 2321, 2321 Dachi-cho, Toki-shi, Gifu (72) Inventor Makoto Terunuma 12-12-607, Heihei-zuka, Kanagawa 12-12-607 (72) Invention Setsuya Morino 4-19, Rokuen-minami, Kakamigahara-shi, Gifu (72) Inventor Mikihiko Ohno 1717 north of Kitakata-cho, Motosu-gun, Gifu (72) Inventor Haruki Takai 2-1-7, Yoshiokacho, Owariasahi-shi, Owariasahi, Aichi Prefecture Inventor: Akira Kagohashi, 2231-2, Dachi-cho, Toki City, Gifu Prefecture, Japan 2 (72) Inventor Ryo Minoba, 2231-2, Dachi-cho, Toki City, Toki City, Gifu Prefecture 2 within Takasago Industry Co., Ltd. (72) Invention Person Kazuaki Yamaguchi 2231 Takachisago Industry Co., Ltd., Dachi-cho, Toki-shi, Gifu

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 汚泥が供給される乾燥炉(12)と、この乾
燥炉(12)に高温の乾燥用気体を供給する熱風発生炉(17)
と、前記乾燥炉(12)で乾燥された乾燥汚泥が供給され、
この乾燥汚泥を炭化させる炭化炉(26)とから構成される
炭化汚泥製造装置において、 前記炭化炉(26)の内部に画成した燃焼室(34a)に、前記
乾燥炉(12)で乾燥された乾燥汚泥が供給される筒体(37)
を連通状態で配設し、該筒体(37)の内部で発生させた乾
留ガスを燃焼室(34a)で燃焼させるようにし、 前記炭化炉(26)の燃焼室(34a)と前記熱風発生炉(17)と
を連通接続し、該燃焼室(34a)で燃焼しきれなかった未
燃ガスを含む排気ガスを前記熱風発生炉(17)に供給して
燃焼させるよう構成したことを特徴とする炭化汚泥製造
装置。
1. A drying furnace (12) to which sludge is supplied, and a hot-air generating furnace (17) for supplying a high-temperature drying gas to the drying furnace (12).
And, dried sludge dried in the drying furnace (12) is supplied,
In a carbonized sludge manufacturing apparatus comprising a carbonization furnace (26) for carbonizing the dried sludge, a combustion chamber (34a) defined inside the carbonization furnace (26) is dried in the drying furnace (12). Cylinder to which dried sludge is supplied (37)
The carbonized gas generated inside the cylinder (37) is burned in a combustion chamber (34a), and the combustion chamber (34a) of the carbonization furnace (26) and the hot air generation The furnace (17) is connected in communication, and the exhaust gas containing unburned gas that has not been completely burned in the combustion chamber (34a) is supplied to the hot air generating furnace (17) for combustion. Sludge production equipment.
【請求項2】 前記筒体(37)の内部を加熱源(40)により
乾留状態とすることで、前記乾燥汚泥から乾留ガスを発
生させるようにした請求項1記載の炭化汚泥製造装置。
2. The carbonized sludge production apparatus according to claim 1, wherein the inside of the cylindrical body (37) is carbonized by a heating source (40) to generate carbonized gas from the dried sludge.
JP21003097A 1997-07-17 1997-07-17 Carbonized sludge production equipment Expired - Fee Related JP3787690B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21003097A JP3787690B2 (en) 1997-07-17 1997-07-17 Carbonized sludge production equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP21003097A JP3787690B2 (en) 1997-07-17 1997-07-17 Carbonized sludge production equipment

Publications (2)

Publication Number Publication Date
JPH1133599A true JPH1133599A (en) 1999-02-09
JP3787690B2 JP3787690B2 (en) 2006-06-21

Family

ID=16582657

Family Applications (1)

Application Number Title Priority Date Filing Date
JP21003097A Expired - Fee Related JP3787690B2 (en) 1997-07-17 1997-07-17 Carbonized sludge production equipment

Country Status (1)

Country Link
JP (1) JP3787690B2 (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006088020A (en) * 2004-09-22 2006-04-06 Japan Sewage Works Agency Stabilizing treatment method for carbonized product
JP4600956B2 (en) * 2000-12-28 2010-12-22 東京瓦斯株式会社 Sludge treatment method and apparatus
CN105819650A (en) * 2015-01-07 2016-08-03 广州新致晟环保科技机械设备有限公司 Bottom drying-type sludge drying device and bottom drying-type sludge drying method
JP2018001127A (en) * 2016-07-06 2018-01-11 大同特殊鋼株式会社 Carbonization treatment facility of sludge
JP2018162914A (en) * 2017-03-24 2018-10-18 光夫 成瀬 Solid liquid separator
JP2019157114A (en) * 2018-03-13 2019-09-19 大同特殊鋼株式会社 Carbonization processing method and carbonization processor
CN111664455A (en) * 2020-04-20 2020-09-15 河南城建学院 Garbage disposal system
CN114234601A (en) * 2021-12-29 2022-03-25 江苏海洋大学 Soil moisture content is soil drying oven drying rack for measurement
CN114993003A (en) * 2022-06-02 2022-09-02 山东中鸿新能源科技有限公司 Heating device for preparing sodium ion battery anode material

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4600956B2 (en) * 2000-12-28 2010-12-22 東京瓦斯株式会社 Sludge treatment method and apparatus
JP2006088020A (en) * 2004-09-22 2006-04-06 Japan Sewage Works Agency Stabilizing treatment method for carbonized product
CN105819650A (en) * 2015-01-07 2016-08-03 广州新致晟环保科技机械设备有限公司 Bottom drying-type sludge drying device and bottom drying-type sludge drying method
JP2018001127A (en) * 2016-07-06 2018-01-11 大同特殊鋼株式会社 Carbonization treatment facility of sludge
JP2018162914A (en) * 2017-03-24 2018-10-18 光夫 成瀬 Solid liquid separator
JP2019157114A (en) * 2018-03-13 2019-09-19 大同特殊鋼株式会社 Carbonization processing method and carbonization processor
KR20190108065A (en) 2018-03-13 2019-09-23 다이도 토쿠슈코 카부시키가이샤 Carbonization treatment method and carbonization treatment equipment
CN111664455A (en) * 2020-04-20 2020-09-15 河南城建学院 Garbage disposal system
CN111664455B (en) * 2020-04-20 2022-11-08 河南城建学院 Garbage disposal system
CN114234601A (en) * 2021-12-29 2022-03-25 江苏海洋大学 Soil moisture content is soil drying oven drying rack for measurement
CN114993003A (en) * 2022-06-02 2022-09-02 山东中鸿新能源科技有限公司 Heating device for preparing sodium ion battery anode material
CN114993003B (en) * 2022-06-02 2023-08-18 山东中鸿新能源科技有限公司 Heating device for preparing positive electrode material of sodium ion battery

Also Published As

Publication number Publication date
JP3787690B2 (en) 2006-06-21

Similar Documents

Publication Publication Date Title
CN102476907B (en) Method of high-efficiency high-speed environmentally-friendly energy-saving sludge treatment system
KR101916958B1 (en) Apparatus and method for pyrolysis carbonizing of sludge
JP6000739B2 (en) Dry carbonization system
JPH1133599A (en) Carbonized sludge producing apparatus
JP4445148B2 (en) Sludge treatment method and apparatus
KR101364491B1 (en) Treatment device of sludge using oxidation dewatering and dry combustion
JP3811834B2 (en) Method and apparatus for carbonizing sludge
JPH11286684A (en) Continuous carbonization furnace
JPH1137656A (en) Sludge dryer
JP3840584B2 (en) Sludge carbonization equipment
CN207514925U (en) A kind of mud cake fluid bed anhydration and incineration stove
JP2004344710A5 (en)
KR19990048204A (en) Food waste treatment method and device
JP4470520B2 (en) Carbonization equipment for sludge containing organic matter
JP4597261B1 (en) Sludge carbide production equipment
JP3101811U (en) Dry carbonization equipment
KR20100040079A (en) Apparatus for drying and carbonating combustibile or organic waste
CN212713218U (en) High efficiency sludge drying burns device
KR102355850B1 (en) Direct heating type drying system for slug
JP2008212800A (en) Sludge treatment apparatus
JP2004043587A (en) Carbonzing device and method for manufacturing carbonized matter
JP3618280B2 (en) Waste carbonization and reduction equipment
JPH067799A (en) Transport and drying method by dehydrated cake pipeline
CN108298795A (en) A kind of sludge drying mechanism
KR102084665B1 (en) Drying and incineration of sludge using compressed air

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20040422

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20051124

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20051129

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20060124

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20060214

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20060314

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090407

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100407

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110407

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120407

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120407

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130407

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130407

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140407

Year of fee payment: 8

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees