JPH0914841A - Drying furnace, incineration furnace, and drying/ incineration furnace - Google Patents
Drying furnace, incineration furnace, and drying/ incineration furnaceInfo
- Publication number
- JPH0914841A JPH0914841A JP7188346A JP18834695A JPH0914841A JP H0914841 A JPH0914841 A JP H0914841A JP 7188346 A JP7188346 A JP 7188346A JP 18834695 A JP18834695 A JP 18834695A JP H0914841 A JPH0914841 A JP H0914841A
- Authority
- JP
- Japan
- Prior art keywords
- drying
- incinerator
- incineration
- furnace body
- heated
- 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.)
- Pending
Links
- 238000001035 drying Methods 0.000 title claims abstract description 90
- 239000010802 sludge Substances 0.000 claims abstract description 40
- 238000002485 combustion reaction Methods 0.000 claims abstract description 39
- 239000002699 waste material Substances 0.000 claims abstract description 36
- 239000000463 material Substances 0.000 claims description 31
- 239000000835 fiber Substances 0.000 claims description 17
- 239000000126 substance Substances 0.000 claims description 17
- 238000007664 blowing Methods 0.000 claims description 13
- 238000010438 heat treatment Methods 0.000 abstract description 9
- 238000000034 method Methods 0.000 abstract description 5
- 239000007789 gas Substances 0.000 description 33
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 15
- 229910052742 iron Inorganic materials 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
- 239000002440 industrial waste Substances 0.000 description 6
- 239000004744 fabric Substances 0.000 description 5
- 239000004753 textile Substances 0.000 description 5
- 239000000498 cooling water Substances 0.000 description 4
- 239000010791 domestic waste Substances 0.000 description 3
- 230000007723 transport mechanism Effects 0.000 description 3
- 239000000446 fuel Substances 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000007246 mechanism Effects 0.000 description 2
- 239000000155 melt Substances 0.000 description 2
- 229920002972 Acrylic fiber Polymers 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- NIXOWILDQLNWCW-UHFFFAOYSA-N acrylic acid group Chemical group C(C=C)(=O)O NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 230000012447 hatching Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 150000002505 iron Chemical class 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- NJPPVKZQTLUDBO-UHFFFAOYSA-N novaluron Chemical compound C1=C(Cl)C(OC(F)(F)C(OC(F)(F)F)F)=CC=C1NC(=O)NC(=O)C1=C(F)C=CC=C1F NJPPVKZQTLUDBO-UHFFFAOYSA-N 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 238000010992 reflux Methods 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- -1 that is Substances 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P70/00—Climate change mitigation technologies in the production process for final industrial or consumer products
- Y02P70/10—Greenhouse gas [GHG] capture, material saving, heat recovery or other energy efficient measures, e.g. motor control, characterised by manufacturing processes, e.g. for rolling metal or metal working
Landscapes
- Gasification And Melting Of Waste (AREA)
- Incineration Of Waste (AREA)
- Drying Of Solid Materials (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は乾燥炉、焼却炉及び乾燥
焼却炉に関する。特に繊維産業特有の産業廃棄物、その
中でも化学繊維を含む汚泥、糸屑、ウェス等の焼却に有
用な乾燥炉、焼却炉及び乾燥焼却炉に関する。FIELD OF THE INVENTION The present invention relates to a drying oven, an incinerator and a drying incinerator. In particular, the present invention relates to a drying furnace, an incinerator and a dry incinerator which are useful for incinerating industrial wastes peculiar to the textile industry, among them sludge, yarn waste, waste cloth and the like containing chemical fibers.
【0002】[0002]
【従来の技術】繊維産業は石川県の有力地場産業であ
る。繊維産業では、産業廃棄物として汚泥、糸屑、ウェ
ス等が発生する。従来これらは個々に焼却、埋立処分等
されて来た。2. Description of the Related Art The textile industry is a leading local industry in Ishikawa prefecture. In the textile industry, sludge, lint, waste, etc. are generated as industrial waste. Conventionally, these have been individually incinerated and landfilled.
【0003】[0003]
【発明が解決しようとする課題】廃棄物は焼却が最も好
ましい(有毒ガス等の問題が無い限り)。焼却はその物
質の燃焼可能な部分全てを滅失させ(気化させ)、その
容積を一番小さくしてしまうからである。灰にしてしま
えば腐敗等も起こりにくい。Incineration of the waste is most preferable (unless there is a problem of toxic gas, etc.). This is because incineration destroys (vaporizes) all the combustible parts of the substance, making it the smallest volume. If it is turned into ash, it will be less likely to decompose.
【0004】しかし上記繊維産業廃棄物はこの焼却処分
が困難な部類に属していた。即ち汚泥は、乾燥させ、適
当に助燃すれば燃焼可能ではあるが、従来これを効率良
く実行出来る装置は無かった。糸屑、ウェスについても
同じで、これらを人手を掛けないで効率良く焼却出来る
装置はなかった。特に化学繊維に係るもの、即ち化学繊
維を含む汚泥、糸屑、ウェス等は、加熱され溶けると火
格子の下に滴下して固まってしまう為、焼却は一層難し
かった。However, the above-mentioned textile industry waste belongs to the category where this incineration is difficult. That is, sludge can be burned if it is dried and appropriately supplemented with combustion, but there has been no device capable of efficiently performing this. The same applies to lint and waste, and there was no device that could incinerate them efficiently without manpower. In particular, those related to chemical fibers, that is, sludge, thread waste, waste cloth and the like containing chemical fibers are more difficult to incinerate because they are dripped and hardened under the grate when heated and melted.
【0005】本発明の目的は、廃棄物、特に有機汚泥に
ついて効率良く乾燥作業が出来る乾燥炉を提供すること
にある。本発明の他の目的は、廃棄物、特に化学繊維を
含むウェス、糸屑等について、効率良く焼却作業が出来
る焼却炉を提供することにある。本発明の他の目的は、
廃棄物、特に繊維産業廃棄物について、乾燥から焼却ま
で一貫して処理可能な乾燥焼却炉を提供することにあ
る。An object of the present invention is to provide a drying furnace capable of efficiently drying waste, especially organic sludge. It is another object of the present invention to provide an incinerator capable of efficiently incinerating wastes, particularly waste including chemical fibers, yarn wastes and the like. Another object of the present invention is to
It is an object of the present invention to provide a dry incinerator capable of consistently processing waste, particularly textile industry waste, from drying to incineration.
【0006】[0006]
【課題を解決するための手段】上記目的達成のため、請
求項1の乾燥炉では、回転する炉体を有し、該炉体は外
周が加熱される。請求項2の焼却炉では、火格子の下が
副焼却室とされ、該副焼却室には燃焼用空気を吹き込む
空気吹き込み手段が備えられ、前記火格子の間から落下
した被焼却物が前記吹き込まれた空気により前記副焼却
室内で燃焼する。請求項3の乾燥焼却炉では、乾燥部と
焼却部とを有し、前記乾燥部は回転する炉体を備え、該
炉体は外周が前記焼却部の排ガスで加熱される。請求項
4の乾燥焼却炉では、乾燥部と焼却部とを有し、前記乾
燥部は回転する炉体を備え、該炉体は外周が前記焼却部
の排ガスで加熱され、前記焼却炉は火格子の下が副焼却
室とされ、該副焼却室には燃焼用空気を吹き込む空気吹
き込み手段が備えられ、前記火格子の間から落下した被
焼却物は前記吹き込まれた燃焼空気により前記副焼却室
内で燃焼する。In order to achieve the above-mentioned object, the drying furnace of claim 1 has a rotating furnace body, and the outer circumference of the furnace body is heated. In the incinerator according to claim 2, below the grate is a sub incineration chamber, the sub incineration chamber is provided with air blowing means for blowing combustion air, and the incineration material dropped from between the grate is The blown air burns in the sub incineration chamber. In the dry incinerator of Claim 3, it has a drying part and an incineration part, The said drying part is equipped with the furnace body which rotates, The outer periphery of this furnace body is heated by the exhaust gas of the said incineration part. The dry incinerator according to claim 4, comprising a drying section and an incineration section, wherein the drying section includes a rotating furnace body, the outer periphery of the furnace body is heated by the exhaust gas of the incinerator, and the incinerator burns. Below the grate is a sub-incineration chamber, the sub-incineration chamber is provided with air blowing means for blowing combustion air, and the incineration material dropped between the grate is the sub-incineration by the blown combustion air. Burns indoors.
【0007】請求項5の乾燥炉では、請求項1にいう炉
体の外周が他の炉で発生した排ガスで加熱される。請求
項6の乾燥焼却炉では、請求項3又は請求項4にいう乾
燥部で乾燥された被乾燥物を前記焼却部に搬送する為の
搬送手段を備える。請求項7の乾燥炉では、請求項1又
は請求項5にいう炉体がその内部も加熱される。請求項
8の乾燥焼却炉では、請求項3、請求項4又は請求項6
にいう炉体がその内部も加熱される。In the drying furnace of claim 5, the outer periphery of the furnace body according to claim 1 is heated by the exhaust gas generated in another furnace. According to a sixth aspect of the dry incinerator, there is provided a conveying means for conveying the material to be dried that has been dried in the drying section according to the third or fourth aspect to the incineration section. In the drying furnace according to claim 7, the inside of the furnace body according to claim 1 or 5 is also heated. In the dry incinerator of claim 8, claim 3, claim 4 or claim 6
The inside of the furnace body is heated.
【0008】請求項9の乾燥炉では、請求項1、請求項
5、請求項7にいう炉体に被乾燥物として有機汚泥が投
入される。請求項10の乾燥焼却炉では、請求項3、請
求項4、請求項6又は請求項8にいう炉体に被乾燥物と
して有機汚泥が投入される。請求項11の焼却炉では、
化学繊維に係る廃棄物が請求項2にいう被焼却物とされ
る。請求項12の乾燥焼却炉では、化学繊維に係る廃棄
物が請求項3、請求項4、請求項6、請求項8又は請求
項10にいう被焼却物とされる。In the drying furnace according to claim 9, organic sludge is put into the furnace body according to claims 1, 5, and 7 as a material to be dried. In the dry incinerator of claim 10, organic sludge is put into the furnace body of claim 3, claim 4, claim 6 or claim 8 as a material to be dried. In the incinerator according to claim 11,
The waste related to the chemical fiber is the incineration object according to claim 2. In the dry incinerator according to the twelfth aspect, the waste related to the chemical fiber is the incineration object according to the third, fourth, sixth, eighth or tenth aspect.
【0009】[0009]
【作用】請求項1の乾燥炉では、炉体が外周から加熱さ
れ且つ回転される。外周からの加熱は炉体全体の十分な
温度上昇をもたらし、回転は被乾燥物を攪拌する。これ
ら十分な温度上昇と攪拌とが相俟って、乾燥効率は向上
し、順に投入していけば、順に乾燥して排出されていく
という、円滑な処理の流れが実現される。請求項2の焼
却炉では、火格子の下が副焼却室とされ、ここに燃焼用
空気が吹き込まれる。火格子の上には燃えている被焼却
物があり、その輻射熱でこの副焼却室も加熱されてい
る。従って火格子の間から被焼却物が落下しても、この
熱と吹き込まれた空気とによって燃焼が継続し、焼却が
円滑に継続する。In the drying furnace of the first aspect, the furnace body is heated from the outer circumference and rotated. The heating from the outer circumference brings about a sufficient temperature rise of the entire furnace body, and the rotation agitates the material to be dried. The sufficient temperature rise and the agitation are combined with each other to improve the drying efficiency and realize a smooth process flow in which the materials are sequentially dried and discharged if they are sequentially charged. In the incinerator according to the second aspect, below the grate is a sub-incinerator chamber, into which combustion air is blown. There is a burning material to be burned on the grate, and the radiant heat also heats this sub-incinerator. Therefore, even if the material to be incinerated falls from between the grate, combustion continues due to this heat and the blown air, and the incineration continues smoothly.
【0010】請求項3の乾燥焼却炉では、回転する炉体
の外周が焼却部の排ガスで加熱される。排ガスが熱源と
して利用されるので資源が節約される。また乾燥から焼
却へと円滑な作業の流れが形成される。請求項4の乾燥
焼却炉では、請求項2の焼却炉と同じく効率良い燃焼が
実現される。その排ガスで外周から炉体が加熱されるの
で、更に効率の良い乾燥が実現される。請求項5の乾燥
炉でも、炉体外周加熱に排ガスが有効利用される。In the dry incinerator of claim 3, the outer periphery of the rotating furnace body is heated by the exhaust gas of the incinerator. Resources are saved because the exhaust gas is used as a heat source. In addition, a smooth work flow is formed from drying to incineration. In the dry incinerator of claim 4, as in the incinerator of claim 2, efficient combustion is realized. Since the furnace body is heated from the outer periphery by the exhaust gas, more efficient drying is realized. Also in the drying furnace of claim 5, the exhaust gas is effectively used for heating the outer circumference of the furnace body.
【0011】請求項6の乾燥焼却炉では、乾燥された被
乾燥物が乾燥部から焼却部へいわば自動的に搬送され
る。乾燥処理、焼却処理が一連のものとして実行され、
一層円滑な廃棄物処理が行なわれる。請求項7の乾燥炉
又は請求項8の乾燥焼却炉では、その炉体の内部も加熱
される。外周、内周とも加熱される結果、乾燥能率は向
上し、いわば誰でも簡単に、時間を掛けないで廃棄物の
処理が出来る。In the dry incinerator of the sixth aspect, the dried material to be dried is automatically conveyed from the drying section to the incineration section. The drying process and incineration process are executed as a series,
Waste treatment will be carried out more smoothly. In the drying furnace of claim 7 or the drying incinerator of claim 8, the inside of the furnace body is also heated. As a result of heating both the outer circumference and the inner circumference, the drying efficiency is improved, and so to speak, anyone can easily dispose of waste without taking time.
【0012】請求項9の乾燥炉、請求項10の乾燥焼却
炉では、被乾燥物として有機汚泥が投入される。炉体は
高い乾燥効率を有し、特にこの処理に適しており、その
利点が遺憾なく発揮される。請求項11の焼却炉、請求
項12の乾燥焼却炉では、化学繊維に係る廃棄物が被焼
却物とされる。上記乾燥炉、乾燥焼却炉はこれに対して
も有効で、その利点が遺憾なく発揮される。特に被乾燥
物が有機汚泥であり、被焼却物がその乾燥後の有機汚泥
とウェス等であるという組合わせ(請求項10を引用し
た請求項12の乾燥焼却炉)は、助燃材が無くても非常
に安定した燃焼状態が維持されるものであり、効率、資
源の有効利用の点で最も有用である。In the drying furnace of claim 9 and the drying incinerator of claim 10, organic sludge is put in as a material to be dried. The furnace body has a high drying efficiency and is particularly suitable for this treatment, and its advantages are fully demonstrated. In the incinerator according to the eleventh aspect and the dry incinerator according to the twelfth aspect, the waste related to the chemical fiber is treated as the incineration target. The drying furnace and the drying incinerator are also effective for this, and their advantages are fully exhibited. In particular, the combination in which the material to be dried is organic sludge and the material to be incinerated is the organic sludge after drying and waste cloth (dry incinerator of claim 12 citing claim 10) does not have an auxiliary combustion material. Also maintains a very stable combustion state and is most useful in terms of efficiency and effective use of resources.
【0013】[0013]
【実施例】以下本発明の詳細を図示実施例に基いて説明
する。図1〜図12に乾燥焼却炉本体101を示す(以
下単に「本体」という)。図13に搬送機構102を示
す。図14に排出量制御の為の他の構造例(堰103)
を示す。図2は本体101の正面、図3及び図4は右側
面、図5は平面を表わす。なお図3及び図4は本来1枚
の図である。図3の蒸気逃がし筒11、直接排気筒12
及び煙突13を上部で切断し、次の図4とする。図1は
図5の(1)−(1)矢視で垂直断面を表わす。図6は
図3の(6)−(6)矢視で水平断面を表わす。図7及
び図8は、図6(7)−(7)矢視で垂直断面を表わ
す。これも本来は1枚の図で、図7が左側、図8が右側
である。DESCRIPTION OF THE PREFERRED EMBODIMENTS The details of the present invention will be described below with reference to the illustrated embodiments. 1 to 12 show a dry incinerator main body 101 (hereinafter simply referred to as "main body"). FIG. 13 shows the transport mechanism 102. FIG. 14 shows another example of the structure for controlling the discharge amount (weir 103).
Is shown. 2 shows the front of the main body 101, FIGS. 3 and 4 show the right side, and FIG. 5 shows the plane. It should be noted that FIGS. 3 and 4 are originally one sheet. The vapor escape tube 11 and the direct exhaust tube 12 of FIG.
And the chimney 13 is cut at the upper part to obtain the next FIG. FIG. 1 shows a vertical section taken along line (1)-(1) of FIG. FIG. 6 shows a horizontal section taken along line (6)-(6) of FIG. FIG. 7 and FIG. 8 show vertical cross sections as viewed in the direction of arrows (7)-(7) of FIG. This is also one sheet originally, and FIG. 7 is the left side and FIG. 8 is the right side.
【0014】図9は図8と同一矢視で回転ドラムを支持
するローラ46,ボルト49を取り除いて表わす。図1
0は図1と同じ矢視(図5(1)−(1))で乾燥部左
側壁15を取り除いて回転ドラム14及びローラ46等
を表わす。図11は図8の(11)−(11)矢視で垂
直断面を表わす。図12は図5(12)−(12)矢視
で、燃焼空気吹き込み用ノズル16の詳細を表わす。な
お何れかの図で説明をした部分は、他の図では同じ符号
を付すだけとし、必要以外再度の説明をしない。また解
像度の関係で、断面図では鉄板を1本の線で表わす(厚
みを表現しない。但し図7〜図12、図14では表
現)。また断面のうち微細なものは、ハッチングを省略
することがある。FIG. 9 is shown by removing the roller 46 and the bolt 49 for supporting the rotary drum in the same arrow view as FIG. FIG.
Reference numeral 0 indicates the rotary drum 14, the roller 46 and the like by removing the left side wall 15 of the drying portion in the same arrow view as in FIG. 1 (FIGS. FIG. 11 shows a vertical section taken along line (11)-(11) of FIG. FIG. 12 is a detailed view of the combustion air blowing nozzle 16 as viewed in the direction of arrows (12)-(12) of FIG. It should be noted that the portions described in any of the drawings are given the same reference numerals in the other drawings and will not be described again unless necessary. Further, due to the relation of resolution, the iron plate is represented by a single line in the cross-sectional view (thickness is not represented, but is represented in FIGS. 7 to 12 and 14). Further, hatching may be omitted for a fine cross section.
【0015】以下各図について順に説明をする。本体1
01は、焼却部21とこれに連設された乾燥部22の二
つのブロックから成る(図1〜図5参照)。これに再燃
焼筒23が連設され、これら全体がフレーム20上に載
置されている。焼却部21の内容積は凡そ1.5立方メ
ートルで、幅は1.2m、奥行1.1m、中央高さ約
1.4mほどであり、アクリルの廃棄ウェスを1時間あ
たり10Kg焼却可能である。乾燥部22は、回転ドラ
ム14の内容積が1.4立方メートルで、直径は1m、
長さは1.8mほどであり、アクリル繊維の有機質汚泥
を1時間あたり50Kg乾燥可能である。焼却部21は
水冷である。前後左右の各側壁31〜34と屋根35と
が鉄板の二重壁とされており、屋根35の上に配置され
たシスタンク26から右側壁34の下方に給水管27が
延伸され、これを通じて冷却水28が供給されている。The respective figures will be described below in order. Body 1
01 consists of two blocks, the incineration part 21 and the drying part 22 connected to this (refer to FIGS. 1-5). A re-combustion cylinder 23 is connected to this, and the whole of them is mounted on the frame 20. The internal volume of the incinerator 21 is approximately 1.5 cubic meters, the width is 1.2 m, the depth is 1.1 m, and the central height is approximately 1.4 m, and it is possible to incinerate 10 kg of waste acrylic waste cloth per hour. The drying unit 22 has an inner volume of the rotating drum 14 of 1.4 cubic meters and a diameter of 1 m,
The length is about 1.8 m, and 50 kg of organic sludge of acrylic fiber can be dried per hour. The incinerator 21 is water cooled. The front, rear, left and right side walls 31 to 34 and the roof 35 are double walls made of iron plate, and the water supply pipe 27 is extended from the cis tank 26 arranged on the roof 35 to the lower side of the right side wall 34, through which cooling is performed. Water 28 is supplied.
【0016】屋根35上には逃がしタンク25が配置さ
れている(図2〜図5参照)。その上部には蒸気逃がし
筒11が設けられている。逃がしタンク25の内部空間
は二重壁の内部空間と連通されており、焼却部21の熱
で冷却水が加熱され、それによって発生する水蒸気が逃
がし筒11から外界に放出されることで、焼却部21が
冷却される。なお各側壁の外側からもかなり熱が発散さ
れる。冷却水水位は逃がしタンク25の中間程度とされ
る。シスタンク26には不図示ボールタップが内蔵され
ていて、これに不図示水道管が接続されている。蒸発で
冷却水水位が低下すると、ボールタップが開き、不足分
の給水が行なわれる。An escape tank 25 is arranged on the roof 35 (see FIGS. 2 to 5). A vapor escape tube 11 is provided on the upper portion thereof. The internal space of the escape tank 25 communicates with the internal space of the double wall, the cooling water is heated by the heat of the incinerator 21, and the steam generated thereby is released from the escape tube 11 to the outside, so that it is incinerated. The part 21 is cooled. Note that considerable heat is also radiated from the outside of each side wall. The cooling water level is about the middle of the escape tank 25. The cis tank 26 has a ball tap (not shown) built therein, and a water pipe (not shown) is connected to the ball tap. When the water level of the cooling water drops due to evaporation, the ball tap opens and the shortage of water is supplied.
【0017】焼却部21は底29だけキャスター張り
(耐熱モルタル張り)である(図1、図3など参照)。
底29の少し上方には火格子支持用鉄パイプ30が4本
配置されている。鉄パイプ30の内部空間は左右の側壁
33,34の内部空間と連通されていて、ここにも冷却
水28が充填されている。火格子36はこの鉄パイプ3
0の上に置かれる。焼却部21の火室には燃焼空気吹き
込み用のノズル16が突出している(図6、図12等参
照)。これらは左右の側壁33,34を貫通して、鉄パ
イプ30の上方に左右から各4本、同じく鉄パイプ30
の下方に左右から各4本、そして手前側の側壁31の左
右を貫通して鉄パイプ30の下方に左右各1本、夫々突
出している。燃焼用空気は、屋根35の上に載置された
ブロワ24から供給される(図2〜図5等参照)。ここ
で取り込まれ加圧された空気は、アキュムレータ37で
緩衝され、供給管38を介して各ノズル16に供給され
る。Only the bottom 29 of the incineration section 21 is caster-cast (heat-resistant mortar-clad) (see FIGS. 1 and 3).
Four iron pipes 30 for supporting the grate are arranged slightly above the bottom 29. The inner space of the iron pipe 30 communicates with the inner spaces of the left and right side walls 33 and 34, and the cooling water 28 is also filled therein. The grate 36 is this iron pipe 3
Placed on top of 0. A nozzle 16 for blowing combustion air projects into the fire chamber of the incinerator 21 (see FIG. 6, FIG. 12, etc.). These penetrate the left and right side walls 33 and 34, and are located above the iron pipe 30, and each four from the left and right.
4 from the left and right, and 1 right and left respectively below the iron pipe 30 through the right and left sides of the side wall 31 on the front side. The combustion air is supplied from the blower 24 placed on the roof 35 (see FIGS. 2 to 5, etc.). The air taken in and pressurized here is buffered by the accumulator 37, and is supplied to each nozzle 16 via the supply pipe 38.
【0018】火格子36の上に位置するノズル16の先
端には、拡散板39が取着されている(図12)。この
拡散板39は鉄板を円形に切り抜いたもので、ノズル1
6から吹き出す空気を扇状に上方に又は下方に向かって
拡散させる。具体的には、右側一番手前のノズル16で
は上に向かって吹き出すように拡散板39が取り付けら
れ、次は下に向かって吹き出すように拡散板39が取り
付けられている。また左側は最初のものが下向きに空気
を吹き出すように取り付けられ、次のものが上向きに吹
き出すように取り付けられている。このように扇状に拡
散して噴出させると、燃焼が安定する。これにより従来
よりノズル径を太くして、いわばドッと空気を吹き込む
ことが出来る。従ってその分ノズル本数が少なくなり、
製作及びメンテナンスのコストが下がる。なお17は被
焼却物投入口、18は灰の取り出し口であり、この取り
出し口18に加熱用バーナ19が取着されている(図2
ほか)。A diffuser plate 39 is attached to the tip of the nozzle 16 located above the grate 36 (FIG. 12). The diffuser plate 39 is a steel plate cut out in a circular shape.
The air blown out from 6 is diffused upward or downward in a fan shape. Specifically, the rightmost frontmost nozzle 16 has the diffuser plate 39 attached so as to blow out upward, and the diffuser plate 39 is attached next so as to eject downward. The left side is attached so that the first one blows air downward and the next one is blown upward. Combustion is stabilized by diffusing in a fan shape and ejecting. As a result, the nozzle diameter can be made thicker than in the past, and so to speak, air can be blown in. Therefore, the number of nozzles decreases accordingly,
Manufacturing and maintenance costs are reduced. Reference numeral 17 is an incineration object inlet, and 18 is an ash outlet, and a heating burner 19 is attached to the outlet 18 (FIG. 2).
And others).
【0019】焼却部21の奥側側壁32には四角の大き
な開口42が設けられている。乾燥部22の手前側側壁
にも同じ大きさの開口43が設けられていて、これらが
突き合わされ、焼却部21の火室と乾燥部22の内部空
間とが連通されている。乾燥部22は各側壁、天井及び
床、何れもキャスター張りにされている。焼却部21は
水冷にしたが、こちらはそれよりは温度が低いのでキャ
スター張りとした。乾燥部22の内部空間の中央には、
開口を横向きにして回転ドラム14が配置されている
(図6ほか)。回転ドラム14は鉄製で、内部に攪拌羽
根44が突設されている(図1)。回転ドラム14の両
端にはリム45が外嵌固定されており(図6)、この部
分が左右2個づつのローラ46で回転自在に支承されて
いる(図7、図8)。左側のローラ46は張り出し架台
47に支持されている(図7)。右側の2個のローラ4
6は夫々2本のボルト49で支承されている(図8)。
ボルト49はローラ46の高さを変える為のもので、こ
れで回転ドラム14の右方向への傾きを調節する。傾き
を急にすれば回転ドラム14内での汚泥の滞留時間は短
くなり、緩めればその逆になる。なお図14に示すよう
に回転ドラム14の開口部に堰103を配置し、これを
矢印50の如く上下して隙間Gを調節し、乾燥汚泥の排
出量を制御しても良い。A large square opening 42 is provided on the rear side wall 32 of the incinerator 21. The opening 43 of the same size is also provided on the front side wall of the drying unit 22, and these are abutted against each other so that the fire chamber of the incineration unit 21 and the internal space of the drying unit 22 communicate with each other. Each of the side walls, ceiling and floor of the drying unit 22 is caster-cast. The incinerator 21 was water-cooled, but the temperature was lower than that, so casters were used. In the center of the internal space of the drying section 22,
The rotary drum 14 is arranged with the opening facing sideways (FIG. 6 and others). The rotary drum 14 is made of iron, and a stirring blade 44 is provided inside the rotary drum 14 (FIG. 1). A rim 45 is externally fitted and fixed to both ends of the rotary drum 14 (FIG. 6), and this portion is rotatably supported by two left and right rollers 46 (FIGS. 7 and 8). The roller 46 on the left side is supported by an overhanging mount 47 (FIG. 7). Right two rollers 4
6 are each supported by two bolts 49 (FIG. 8).
The bolt 49 is for changing the height of the roller 46, and adjusts the inclination of the rotary drum 14 to the right with this. If the inclination is made steep, the retention time of the sludge in the rotary drum 14 becomes short, and if it becomes loose, the opposite occurs. As shown in FIG. 14, the weir 103 may be arranged in the opening of the rotary drum 14, and the weir 103 may be moved up and down as shown by an arrow 50 to adjust the gap G to control the discharge amount of the dried sludge.
【0020】回転ドラム14の左側リム45の側面には
リング状にチェーン51が固定されている(図7)。乾
燥部22の左外側にはギヤードモータ52が配置されて
おり、その出力軸にチェーンスプロケット53が取着さ
れている。これがチェーン51と噛合し、回転ドラム1
4を回転させる。ギヤードモータ52の回転数を変えれ
ば回転ドラム14の回転数が変わる。乾燥部22の左側
壁15にはスクリューコンベア54が貫通されている
(図7、図13、図1ほか)。スクリューコンベア54
は回転ドラム14内に汚泥を投入する為のもので、先端
55は回転ドラム14の左側開口からやや中の位置まで
突出されている。スクリューコンベア54の取り込み口
56は汚泥受け入れバケット57の底部にある(図1
3)。バケット57に投入された汚泥はここから順次回
転ドラム14の中に送り込まれる。なお58はスクリュ
ー駆動用プーリーで、不図示Vベルトで駆動される。ス
クリュー59の回転数を変えることで、汚泥の投入量が
調節出来る。A ring-shaped chain 51 is fixed to the side surface of the left rim 45 of the rotary drum 14 (FIG. 7). A geared motor 52 is arranged on the left outer side of the drying section 22, and a chain sprocket 53 is attached to its output shaft. This meshes with the chain 51, and the rotary drum 1
Rotate 4. When the rotation speed of the geared motor 52 is changed, the rotation speed of the rotary drum 14 is changed. A screw conveyor 54 penetrates the left side wall 15 of the drying unit 22 (FIGS. 7, 13, and 1). Screw conveyor 54
Is for throwing sludge into the rotary drum 14, and the tip 55 is projected from the left opening of the rotary drum 14 to a position slightly inside. The intake 56 of the screw conveyor 54 is at the bottom of the sludge receiving bucket 57 (FIG. 1).
3). The sludge thrown into the bucket 57 is sequentially fed into the rotary drum 14 from here. Reference numeral 58 is a screw driving pulley, which is driven by a V belt (not shown). The amount of sludge input can be adjusted by changing the rotation speed of the screw 59.
【0021】乾燥部22の左側壁15にはバーナ61も
配置されている(図7)。バーナ61の吹き出し口62
は丁度回転ドラム14の左側開口の位置にある。その周
囲には四角の開口63が設けられている(図1)。これ
は再燃焼筒23から還流される排ガスの吹き出し口で、
この還流排ガスと前記バーナ61の発する高温ガスとが
回転ドラム14内に吹き込まれ、攪拌されている汚泥を
加熱、乾燥させる。回転ドラム14は外周から焼却部2
1の排ガスで加熱されており、またこのバーナ61の高
温ガスと還流排ガスとで内部から加熱される。内部、外
周双方からの加熱で、乾燥能力は著しく高められてい
る。また排ガスは再燃焼筒23で完全燃焼させたものが
還流再利用される。従って熱効率も高い。A burner 61 is also arranged on the left side wall 15 of the drying section 22 (FIG. 7). Air outlet 62 of burner 61
Is just at the position of the left opening of the rotating drum 14. A square opening 63 is provided around it (FIG. 1). This is the outlet of the exhaust gas recirculated from the reburning cylinder 23,
The recirculated exhaust gas and the high-temperature gas generated by the burner 61 are blown into the rotary drum 14 to heat and dry the agitated sludge. Rotating drum 14 is incinerated part 2 from the outer periphery
It is heated by the exhaust gas of No. 1 and is heated from the inside by the high temperature gas of the burner 61 and the recirculated exhaust gas. By heating from both inside and outside, the drying capacity is significantly enhanced. Further, the exhaust gas completely recycled in the reburning cylinder 23 is recycled for reuse. Therefore, the thermal efficiency is also high.
【0022】乾燥され、顆粒化或いは粉末化した汚泥は
回転ドラム14右側開口から排出される。乾燥部22の
右側壁の内面には、回転ドラム14の右側開口下半分を
囲むように、包囲壁64が突設されている(図11)。
包囲壁64の下側部分は、両側とも下方に延伸されてい
る。この部分には閉塞板66が取り付けられており、側
壁と協同してシュート65を形成する。シュート65の
下部開口67は張り出し架台48を貫通して乾燥部22
の右側下部に突出している(図8)。回転ドラム14か
ら排出される乾燥汚泥はここから第1コンベア69上に
落下する(図13)。乾燥汚泥は第1コンベア69で手
前に搬送される。そして第2コンベア70、第3コンベ
ア71を経て焼却部21に投入される。これら3つのコ
ンベア69〜71が搬送機構102を形成する。なお7
2,73は手動で乾燥汚泥を取り出す為の開口及びその
扉であり(図3)、74,75は底部に貯まる灰を取り
出す為の開口及びその扉である(図3、図1)。The dried, granulated or powdered sludge is discharged from the right opening of the rotary drum 14. On the inner surface of the right side wall of the drying section 22, a surrounding wall 64 is provided so as to surround the lower half of the right side opening of the rotary drum 14 (FIG. 11).
The lower part of the surrounding wall 64 extends downward on both sides. A closing plate 66 is attached to this portion and forms a chute 65 in cooperation with the side wall. The lower opening 67 of the chute 65 penetrates the overhanging pedestal 48 and passes through the drying section 22.
It projects to the lower right side of the (Fig. 8). The dried sludge discharged from the rotary drum 14 falls on the first conveyor 69 from here (FIG. 13). The dried sludge is conveyed to the front by the first conveyor 69. Then, it is put into the incinerator 21 via the second conveyor 70 and the third conveyor 71. These three conveyors 69 to 71 form the transport mechanism 102. 7
Reference numerals 2 and 73 are openings and doors for manually extracting the dried sludge (FIG. 3), and 74 and 75 are openings and doors for extracting the ash accumulated at the bottom (FIGS. 3 and 1).
【0023】乾燥部22奥側には排気用開口81が設け
られている(図1、図6ほか)。乾燥部22後方には再
燃焼筒23が配置されており、この奥側開口81は、ダ
クト82を介し再燃焼筒23の下部に接続されている。
乾燥部22の右側壁にも排気用の開口83が設けられて
いる(図8,図11)。この右側開口にはパイプ84と
直接排気筒12が接続されている(図2、図3ほか)。
パイプ84は再燃焼筒23の内部空間上部に接続されて
いる。その中間には再燃焼筒23側に向かってノズル4
1が設けられている。ブロワ86からこのノズル41に
空気が供給され(図5、図3)、この気流で排気が再燃
焼筒23側に誘引される。直接排気筒12は、煙突13
の中間点に接続されている(図4)。An exhaust opening 81 is provided on the inner side of the drying section 22 (FIGS. 1 and 6 and others). A reburning cylinder 23 is arranged behind the drying unit 22, and the rear side opening 81 is connected to a lower portion of the reburning cylinder 23 via a duct 82.
An opening 83 for exhaust is also provided on the right side wall of the drying unit 22 (FIGS. 8 and 11). The pipe 84 and the exhaust pipe 12 are directly connected to the right opening (FIGS. 2 and 3 and the like).
The pipe 84 is connected to the upper part of the internal space of the reburning cylinder 23. In the middle, the nozzle 4 is directed toward the reburning cylinder 23 side.
1 is provided. Air is supplied to the nozzle 41 from the blower 86 (FIGS. 5 and 3), and the exhaust gas is attracted to the reburning cylinder 23 side by this airflow. The direct stack 12 has a chimney 13
(Fig. 4).
【0024】パイプ84及び直接排気筒12には、中間
に、不図示流量調整用ダンパが挿入されている。排ガス
中の一酸化炭素、煤煙等の量は焼却物毎に異なる。そこ
でその性質に応じ、このダンパの開度を変え、再燃焼筒
23への流量と外部排出量とを調節する。これにより排
ガスが完全に燃焼し、公害が防止出来、且つ再循環の熱
量も増えて効率が上がる。再燃焼筒23には上部、下部
にバーナ87が2個取着されている(図1、図3、図
5)。これらからは再燃焼筒23内の円周方向に向けて
高温ガスが噴出されており、これによって再燃焼筒23
内部で反時計方向に排気ガスが渦を巻き、完璧な再燃焼
が実現される。そして再燃焼した排ガスは煙突13を経
て外部へ排出される。An unillustrated flow rate adjusting damper is inserted in the middle of the pipe 84 and the direct exhaust tube 12. The amount of carbon monoxide, soot, etc. in the exhaust gas differs depending on the incinerated material. Therefore, the opening degree of the damper is changed according to the property to adjust the flow rate to the reburning cylinder 23 and the external discharge amount. As a result, the exhaust gas is completely burned, pollution can be prevented, and the amount of heat for recirculation is increased to improve efficiency. Two burners 87 are attached to the upper and lower parts of the reburning cylinder 23 (FIGS. 1, 3, and 5). From these, high-temperature gas is ejected in the circumferential direction in the re-combustion cylinder 23.
Inside, the exhaust gas swirls counterclockwise, achieving perfect reburn. Then, the reburned exhaust gas is discharged to the outside through the chimney 13.
【0025】煙突13の中間には排ガス再循環パイプ8
8が接続されている。このパイプ88の途中には乾燥部
22側に向けてノズル89が配置されており(図5、図
1)、ブロワ91から供給された空気がここから吹き出
して、再燃焼筒23の高温排ガスを乾燥部22側へ誘引
する。なお92は保守用の開口で、再燃焼筒23内に堆
積した灰の除去に使用する。An exhaust gas recirculation pipe 8 is provided in the middle of the chimney 13.
8 are connected. A nozzle 89 is arranged in the middle of the pipe 88 toward the drying section 22 side (FIGS. 5 and 1), and the air supplied from the blower 91 blows out from this, and the high temperature exhaust gas of the reburning cylinder 23 is discharged. Attract to the drying unit 22 side. Reference numeral 92 is an opening for maintenance, which is used for removing ash accumulated in the reburning cylinder 23.
【0026】例えば化学繊維を含む汚泥と化学繊維のウ
ェスとを焼却する場合、焼却部21と乾燥部22の各バ
ーナ19,61に点火し、焼却部21及び乾燥部22を
加熱する。スクリューコンベア54、回転ドラム14を
回転させ、各コンベア68〜70も起動する。ブロワ2
4も起動して火格子36の上下に燃焼用空気を吹き込み
む。この状態で焼却部21に適宜量のウェスを投入す
る。ウェスは加熱され燃焼を開始する。そこで更に適宜
量のウェスを順次投入して、燃焼を盛んにしていく。燃
焼が進むと繊維が溶け、それらは火格子36の下に滴下
して、焼却部21の底29に溜まる。これらは火格子3
6上の燃焼による輻射で加熱される。火格子36の下に
は燃焼用空気が吹き込まれており、この為、この火格子
36の下が副焼却室となって、溶融物は燃焼を持続す
る。For example, when incinerating sludge containing chemical fibers and a waste of chemical fibers, the burners 19 and 61 of the incinerator 21 and the dryer 22 are ignited to heat the incinerator 21 and the dryer 22. The screw conveyor 54 and the rotary drum 14 are rotated, and the conveyors 68 to 70 are also activated. Blower 2
4 is also activated to inject combustion air above and below the grate 36. In this state, an appropriate amount of waste is put into the incinerator 21. The waste is heated and begins to burn. Therefore, an appropriate amount of waste is sequentially added to increase combustion. As the combustion progresses, the fibers melt and they drip under the grate 36 and collect on the bottom 29 of the incinerator 21. These are grate 3
6 is heated by radiation from combustion. Combustion air is blown into the bottom of the grate 36. Therefore, the bottom of the grate 36 serves as a sub-incinerator, and the melt continues burning.
【0027】汚泥はバケット57に投入する。スクリュ
ー59の回転で汚泥が順次回転ドラム14内に送り込ま
れる。そして回転ドラム14の回転で攪拌されながら、
その傾きで少しづつ右側開口に向かって移動して行く。
回転ドラム14は、バーナ61の高温ガス及び還流排ガ
スで内部から加熱され、また焼却部21の排ガスで外周
から加熱されている。従って回転ドラム14の右側開口
に到達する頃には、含有されていた水分が完全に蒸発
し、サラサラの顆粒状の粉末になる(そうなるように、
回転ドラム14の右側への傾き、回転数、汚泥投入量な
どを調節する)。乾燥された汚泥はシュート65から第
1コンベア68上に落下する。そして手前に運ばれて次
の第2コンベア69上に落下し、更に第3コンベア70
上に落下して焼却部21内に投入される。水分が完全に
無くなっており、また有機質の汚泥なので、投入後直ち
に燃焼し、焼却部21の燃焼は一層盛んになる。The sludge is put into the bucket 57. Sludge is sequentially fed into the rotary drum 14 by the rotation of the screw 59. While being stirred by the rotation of the rotary drum 14,
The slope gradually moves toward the right side opening.
The rotary drum 14 is heated from the inside by the high temperature gas of the burner 61 and the reflux exhaust gas, and is heated from the outer periphery by the exhaust gas of the incinerator 21. Therefore, by the time the right side opening of the rotary drum 14 is reached, the water contained therein is completely evaporated into a smooth, granular powder (as it happens,
Adjust the inclination of the rotating drum 14 to the right, the number of rotations, the amount of sludge input, etc.). The dried sludge falls from the chute 65 onto the first conveyor 68. Then, it is carried to the front and drops onto the next second conveyor 69, and then the third conveyor 70.
It falls on top and is thrown in incineration part 21. Since the water content is completely lost and it is an organic sludge, it burns immediately after being charged, and combustion in the incinerator 21 becomes more active.
【0028】汚泥の乾燥が良好な状態に保たれ、そして
火格子36上でのウェスの燃焼及び副焼却室93に滴下
した溶融物の燃焼が良好に持続する状態になったら、焼
却部21のバーナ19及び乾燥部22のバーナ61を止
める。火格子36の下へ空気が吹き込まれているのでそ
れでも十分に燃焼が持続する。これにより、産業廃棄物
たるウェス、それも従来焼却が難しかった化学繊維の焼
却が円滑に実行される。なお発明者らが試作、実験した
結果では、極めて良好な燃焼状態が維持されたが、汚泥
が殆んど無機質であるなど、燃焼状態が悪いときは、バ
ーナを点火し、助燃を行なうと良い。When the sludge is kept in a good dry state, and the combustion of the waste on the grate 36 and the combustion of the melt dropped in the sub-incinerator 93 are maintained well, the incinerator 21 of the incinerator 21 is heated. The burner 19 and the burner 61 of the drying unit 22 are stopped. Since air is blown into the bottom of the grate 36, the combustion is still sufficiently sustained. As a result, the waste, which is industrial waste, and the chemical fiber, which has been difficult to incinerate in the past, can be smoothly incinerated. It should be noted that, as a result of the trial production and experiment conducted by the inventors, an extremely good combustion state was maintained, but when the combustion state is poor such that the sludge is almost inorganic, it is better to ignite the burner to assist the combustion. .
【0029】変形例について述べる。乾燥部22のみ、
焼却部21のみを実施するようにしても良い。この場
合、乾燥部22の回転ドラム14の外周を加熱する熱源
は何でも良い。例えば汎用のバーナを熱源としたり、他
の焼却炉の排ガス、工場の種々の排ガス、例えば高炉の
排ガスなど、他の諸々の発熱源がこの為の熱源として利
用し得る。なおバーナのように新たに燃料代が掛かるも
のでなく、排ガスなど、費用の掛からないものを利用す
るのが好ましい。それで十分に効果が期待でき、エネル
ギーの節約になる。被乾燥物は汚泥に限らない。製紙廃
棄物その他、種々の湿潤した産業廃棄物、生活廃棄物
(家庭ごみ)に対する乾燥に関しても乾燥部22は有用
である。被焼却物も化学繊維に限らない。燃焼で溶融す
る性質のもの、例えばプラスチック等にも有用であり、
更には一般の産業廃棄物、生活廃棄物にも有用である。A modified example will be described. Only the drying unit 22,
You may make it implement only the incineration part 21. In this case, any heat source may be used to heat the outer circumference of the rotary drum 14 of the drying section 22. For example, a general-purpose burner may be used as a heat source, or exhaust gas of other incinerators, various exhaust gas of a factory, for example, exhaust gas of a blast furnace, and various other heat sources may be used as the heat source for this purpose. It should be noted that it is preferable to use an inexpensive fuel such as exhaust gas instead of a new fuel cost such as a burner. It can be fully effective and saves energy. The material to be dried is not limited to sludge. The drying unit 22 is also useful for drying papermaking waste and various other wet industrial waste and household waste (household waste). The materials to be incinerated are not limited to chemical fibers. It is also useful for things that melt when burned, such as plastic,
Furthermore, it is also useful for general industrial waste and household waste.
【0030】[0030]
【発明の効果】以上説明したように、請求項1の乾燥炉
では、回転する炉体を外周から加熱するようにした。従
って炉体全体の温度が十分に上昇し、効率良い乾燥が行
なえる。また従来の同種目的のものに比べ、炉長をかな
り短くすることが出来る。従って例えば実施例のよう
に、正面から見て横向きにし、焼却炉の後に配置するこ
となど、設置場所が少なくて済む。特に請求項5のよう
に、他の炉が発生する排ガスをこの乾燥炉の炉体外周加
熱に利用すると資源の節約にもなる。請求項2の焼却炉
では、火格子の下を副焼却室として、ここにも燃焼用空
気を吹き込むようにした。火格子の上で燃えている被焼
却物の輻射熱によって副焼却室も加熱される。そこに燃
焼用空気が吹き込まれることで、火格子の間から被焼却
物が落下してもここで完全に燃焼する。特に請求項11
のように被燃焼物が化学繊維である場合、従来はこれが
火格子の下に落下しても、底に溜まるなり固まるなりす
るだけで殆んど燃えなかったが、本発明のようにここに
空気を吹き込むことで、これと輻射熱とが有効に作用し
て燃焼が持続し、迅速、完全な焼却が為される。As described above, in the drying furnace of claim 1, the rotating furnace body is heated from the outer circumference. Therefore, the temperature of the entire furnace body is sufficiently increased, and efficient drying can be performed. Further, the furnace length can be considerably shortened as compared with the conventional one for the same purpose. Therefore, it is possible to reduce the number of installation places, for example, by arranging it horizontally when viewed from the front and arranging it after the incinerator as in the embodiment. In particular, when the exhaust gas generated by another furnace is used for heating the outer circumference of the furnace body of this drying furnace, the resource can be saved. In the incinerator according to the second aspect of the present invention, the sub-incinerator is provided below the grate, and the combustion air is blown into the sub-incinerator. The sub-incinerator chamber is also heated by the radiant heat of the incineration object burning on the grate. By blowing the combustion air into it, even if the material to be incinerated falls between the grate, it is completely burned here. In particular, claim 11
When the material to be burned is a chemical fiber like in the above, even if it hits the bottom of the grate in the past, it hardly burns as it accumulates at the bottom and hardens, but like the present invention, By injecting air, this and radiant heat effectively act to continue combustion, resulting in quick and complete incineration.
【0031】請求項3の乾燥焼却炉では、連設された焼
却部21の排ガスで、乾燥部の炉体外周が加熱されるよ
うにした。排ガスが熱源として利用されるので資源が節
約される。また乾燥処理と焼却処理とが連繋して実行出
来るようになる。請求項4の乾燥焼却炉では、請求項2
の焼却炉と同じく効率良い燃焼が実現され、その排ガス
によって乾燥部の炉体が外周から加熱される。従って一
層効率の高い乾燥処理が出来る。In the dry incinerator according to the third aspect, the exhaust gas of the incinerator 21 connected in series heats the outer periphery of the furnace body of the dryer. Resources are saved because the exhaust gas is used as a heat source. In addition, the drying process and the incineration process can be executed together. In the dry incinerator of claim 4, claim 2
As in the case of the incinerator, efficient combustion is realized, and the exhaust gas heats the furnace body in the drying section from the outer periphery. Therefore, a more efficient drying process can be performed.
【0032】請求項6の乾燥焼却炉では、乾燥部で乾燥
された被乾燥物が搬送手段で焼却部に搬送される。乾燥
処理、焼却処理が一連のものとして、いわば自動的に実
行可能となり、一層円滑な廃棄物処理が行なえる。請求
項7の乾燥炉又は請求項8の乾燥焼却炉では、炉体内部
も加熱されるようにした。外周、内周とも加熱される結
果、乾燥能率は更に向上し、いわば誰でも簡単に、しか
も時間を掛けないで産業廃棄物の処理が出来るようにな
る。請求項9の乾燥炉、請求項10の乾燥焼却炉では、
被乾燥物として有機汚泥が投入されるようにした。有機
汚泥は乾燥しにくいが、これら乾燥炉、乾燥焼却炉の乾
燥効率が大きく向上した為、これらでも迅速に乾燥、焼
却が出来る。In the dry incinerator of the sixth aspect, the material to be dried dried in the drying section is conveyed to the incineration section by the conveying means. As a series of drying and incineration processes, so to speak, they can be automatically executed, and smoother waste disposal can be performed. In the drying furnace of claim 7 or the drying incinerator of claim 8, the inside of the furnace body is also heated. As a result of heating both the outer circumference and the inner circumference, the drying efficiency is further improved, and so to speak, anyone can treat industrial waste easily and in a short time. In the drying furnace according to claim 9 and the drying incinerator according to claim 10,
Organic sludge was added as a material to be dried. Although organic sludge is difficult to dry, the drying efficiency of these drying furnaces and dry incinerators has been greatly improved, so even these can be quickly dried and incinerated.
【0033】請求項12の乾燥焼却炉では、請求項3、
4、6、8又は10の乾燥焼却炉が化学繊維に係る廃棄
物に適用される。これら各請求項の乾燥焼却炉では、外
周加熱を始めとする各構成により、それぞれの乾燥能
力、焼却能力が大幅に向上される。これにより特にこの
化学繊維に係る廃棄物の乾燥、焼却処理を迅速、且つ円
滑、効率的に実施することが出来る。特に被乾燥物が有
機汚泥であって、被焼却物がそれを乾燥した後のもの及
びウェスなどの組合わせであった場合(請求項10引用
の請求項12の乾燥焼却炉)、助燃材が無くても非常に
安定した燃焼ができ、種類の異なるものにも拘らず、そ
の一括処理が可能になる。According to the dry incinerator of claim 12, claim 3,
4, 6, 8 or 10 dry incinerators are applied to chemical fiber waste. In the dry incinerator of each of these claims, the drying capacity and the incineration capacity are greatly improved by the respective configurations including the heating of the outer circumference. As a result, in particular, the drying and incineration of the waste related to this chemical fiber can be carried out quickly, smoothly and efficiently. In particular, when the material to be dried is organic sludge and the material to be incinerated is a combination of the material after drying it and waste cloth (dry incinerator of claim 12 of claim 10), the auxiliary combustion material is Even without it, very stable combustion can be performed, and it is possible to carry out batch processing regardless of different types.
【図1】 図5(1)−(1)矢視で示す垂直断面図。FIG. 1 is a vertical sectional view taken along the line (1)-(1) of FIG.
【図2】 実施例の乾燥焼却炉本体等を示す正面図。FIG. 2 is a front view showing a dry incinerator main body and the like of an embodiment.
【図3】 実施例の乾燥焼却炉本体を示す右側面図(下
側)。FIG. 3 is a right side view (lower side) showing the dry incinerator main body of the embodiment.
【図4】 実施例の乾燥焼却炉本体を示す右側面図(上
側)。FIG. 4 is a right side view (upper side) showing the dry incinerator main body of the embodiment.
【図5】 実施例の乾燥焼却炉本体を示す平面図。FIG. 5 is a plan view showing a dry incinerator body of an example.
【図6】 図3の(6)−(6)矢視で示す水平断面
図。FIG. 6 is a horizontal sectional view taken along line (6)-(6) of FIG.
【図7】 図6(7)−(7)矢視で示す垂直断面図
(左側)。FIG. 7 is a vertical cross-sectional view (left side) shown by arrows in FIGS. 6 (7)-(7).
【図8】 図6(7)−(7)矢視で示す垂直断面図
(右側)。FIG. 8 is a vertical cross-sectional view (right side) shown by arrows in FIGS.
【図9】 図8と同一矢視で回転ドラム支持機構104
を取り除いて示す垂直断面図。9 is a rotary drum support mechanism 104 in the same direction as FIG.
The vertical sectional view which removes and shows.
【図10】 図1と同じ矢視で、乾燥部22の左側壁1
5を取り除いて回転ドラム14、支持機構等を表わす右
側面図。10 is a left side wall 1 of the drying unit 22 as viewed in the same direction as FIG.
5 is a right side view showing the rotary drum 14, a support mechanism, etc., with 5 removed. FIG.
【図11】 図8の(11)−(11)矢視で示す垂直
断面図。FIG. 11 is a vertical sectional view taken along line (11)-(11) of FIG.
【図12】 図5(12)−(12)矢視で示す燃焼空
気吹き込みノズル部分の詳細垂直断面図。FIG. 12 is a detailed vertical sectional view of a combustion air blowing nozzle portion as shown by arrows in FIGS. 5 (12)-(12).
【図13】 搬送機構を示す平面図。FIG. 13 is a plan view showing a transport mechanism.
【図14】 乾燥後汚泥排出量制御の為の他の構造例
(103)を示す右側面図。FIG. 14 is a right side view showing another structural example (103) for controlling the amount of discharged sludge after drying.
14 炉体(実施例では「回転ドラム」) 16 空気吹き込み手段(実施例ではノズル) 21 焼却炉(焼却部) 22 乾燥炉(乾燥部) 36 火格子 93 副焼却室 101 乾燥焼却炉 102 搬送手段(実施例では第1〜第3コンベア) 14 furnace body (“rotating drum” in the example) 16 air blowing means (nozzle in the example) 21 incinerator (incinerator) 22 drying oven (drying section) 36 grate 93 sub-incinerator 101 dry incinerator 102 transporting means (In the embodiment, the first to third conveyors)
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F26B 23/00 F26B 23/00 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location F26B 23/00 F26B 23/00 A
Claims (12)
熱されることを特徴とする乾燥炉。1. A drying furnace having a rotating furnace body, the outer circumference of which is heated.
室には燃焼用空気を吹き込む空気吹き込み手段が備えら
れ、前記火格子の間から落下した被焼却物が前記吹き込
まれた空気により前記副焼却室内で燃焼することを特徴
とする焼却炉。2. A sub-incineration chamber is provided below the grate, and an air blowing means for blowing combustion air is provided in the sub-incineration chamber, and an incineration object dropped from between the grate is blown into the sub-incineration chamber. An incinerator characterized by being combusted in the sub-incinerator chamber with air.
回転する炉体を備え、該炉体は外周が前記焼却部の排ガ
スで加熱されることを特徴とする乾燥焼却炉。3. A dry incinerator having a drying section and an incineration section, wherein the drying section includes a rotating furnace body, and the outer periphery of the furnace body is heated by the exhaust gas of the incinerator section.
回転する炉体を備え、該炉体は外周が前記焼却部の排ガ
スで加熱され、前記焼却炉は火格子の下が副焼却室とさ
れ、該副焼却室には燃焼用空気を吹き込む空気吹き込み
手段が備えられ、前記火格子の間から落下した被焼却物
は前記吹き込まれた燃焼空気により前記副焼却室内で燃
焼することを特徴とする乾燥焼却炉。4. A drying section and an incineration section, wherein the drying section includes a rotating furnace body, the outer periphery of the furnace body is heated by the exhaust gas of the incineration section, and the incinerator has a lower grate. The sub-incineration chamber is provided with an air blowing unit for blowing combustion air into the sub-incineration chamber, and the incineration material dropped from between the grate is burned in the sub-incineration chamber by the blown combustion air. A dry incinerator characterized by that.
スで加熱されることを特徴とする請求項1記載の乾燥
炉。5. The drying furnace according to claim 1, wherein the outer circumference of the furnace body is heated by exhaust gas generated in another furnace.
焼却部に搬送する搬送手段を備えたことを特徴とする請
求項3又は請求項4記載の乾燥焼却炉。6. The dry incinerator according to claim 3 or 4, further comprising a transfer unit that transfers the material to be dried that has been dried in the drying section to the incineration section.
特徴とする請求項1又は請求項5記載の乾燥炉。7. The drying furnace according to claim 1, wherein the inside of the furnace body is also heated.
特徴とする請求項3、請求項4又は請求項6記載の乾燥
焼却炉。8. The dry incinerator according to claim 3, wherein the inside of the furnace body is also heated.
泥であることを特徴とする請求項1、請求項5又は請求
項7記載の乾燥炉。9. The drying furnace according to claim 1, wherein the material to be dried put into the furnace body is organic sludge.
汚泥であることを特徴とする請求項3、請求項4、請求
項6又は請求項8記載の乾燥焼却炉。10. The dry incinerator according to claim 3, wherein the material to be dried put into the furnace body is organic sludge.
であることを特徴とする請求項2記載の焼却炉。11. The incinerator according to claim 2, wherein the material to be incinerated is waste related to chemical fibers.
であることを特徴とする請求項3、請求項4、請求項
6、請求項8又は請求項10記載の乾燥焼却炉。12. The dry incinerator according to claim 3, claim 4, claim 6, claim 8 or claim 10, wherein the material to be incinerated is waste related to chemical fibers.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7188346A JPH0914841A (en) | 1995-06-30 | 1995-06-30 | Drying furnace, incineration furnace, and drying/ incineration furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7188346A JPH0914841A (en) | 1995-06-30 | 1995-06-30 | Drying furnace, incineration furnace, and drying/ incineration furnace |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0914841A true JPH0914841A (en) | 1997-01-17 |
Family
ID=16222020
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7188346A Pending JPH0914841A (en) | 1995-06-30 | 1995-06-30 | Drying furnace, incineration furnace, and drying/ incineration furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0914841A (en) |
-
1995
- 1995-06-30 JP JP7188346A patent/JPH0914841A/en active Pending
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