JPS58168807A - Incinerator for sludge - Google Patents

Incinerator for sludge

Info

Publication number
JPS58168807A
JPS58168807A JP57052732A JP5273282A JPS58168807A JP S58168807 A JPS58168807 A JP S58168807A JP 57052732 A JP57052732 A JP 57052732A JP 5273282 A JP5273282 A JP 5273282A JP S58168807 A JPS58168807 A JP S58168807A
Authority
JP
Japan
Prior art keywords
sludge
incinerator
auxiliary fuel
dryer
temperature
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
JP57052732A
Other languages
Japanese (ja)
Other versions
JPH0256566B2 (en
Inventor
No Kubota
久保田 濃
Sumio Kawai
川合 純夫
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.)
Okawara Mfg Co Ltd
Original Assignee
Okawara Mfg Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Okawara Mfg Co Ltd filed Critical Okawara Mfg Co Ltd
Priority to JP57052732A priority Critical patent/JPS58168807A/en
Publication of JPS58168807A publication Critical patent/JPS58168807A/en
Publication of JPH0256566B2 publication Critical patent/JPH0256566B2/ja
Granted legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/001Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations

Abstract

PURPOSE:To prevent wearing of an incinerator and a dryer due to excessive feeding of auxiliary fuel, as well as to save the consumption of auxiliary fuel, by automatically introducting the auxiliary fuel so that its introducing rate is suitable to the amount of sludge. CONSTITUTION:A level gauge 10 is provided to a dry sludge tank 4. When the level gauge 10 for dry sludge in the tank 4 falls down lower than a predetermined level, the feeding speed of auxiliary fuel from a hopper 6 is increased by a controller 11. When the level is heightened, the introducing speed is slowed down. On the other hand, a temperature detector 12 is provided to the passage of exhaust gas, discharged from a dryer 1. When the temperature of the exhaust gas becomes lower than a predetermined temperature, the blast rate to an incinerator 2 is increased by increasing the opening of a flow-rate controller 9 by a controller 13, while the blast rate is decreased when the temperature of exhaust gas is high. With such an arrangement, wasteful consumption of auxuliary fuel can be prevented.

Description

【発明の詳細な説明】 本発明は水分の含有量が高く、低発熱量であるために自
燃することのできない汚泥を予備乾燥して焼却すゐ装置
に関し、特に脱水汚泥は、乾燥汚泥を焼却する際の排ガ
スを利用して予備乾燥するものであシ、且つ予備乾燥を
するのに不足する熱量は脱水汚泥に粉粒状の補助燃料を
添加することによって補なうものであることを特徴とす
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for pre-drying and incinerating sludge that cannot self-combust due to its high moisture content and low calorific value, and in particular for dewatered sludge. The method is characterized in that the exhaust gas from the dewatered sludge is used for pre-drying, and the amount of heat insufficient for pre-drying is compensated for by adding granular auxiliary fuel to the dehydrated sludge. It is something to do.

普通、有機質汚泥は、脱水し、予備乾燥したのち焼却し
て処分する。この場合、脱水汚泥を予備乾燥するに要す
る熱量は、予備乾燥した汚泥を焼却する際に発生する熱
を利用するのであるが、脱水汚泥には、70〜90%の
水分が含有しているため、汚泥中の再紙成分よ多発生す
る上記熱量によっては、脱水汚泥を可燃、状態にまるま
で乾燥させることはできないことがある。かような場合
に、汚泥中に木粉や粉炭などの可燃性粉粒体を補助燃料
として添加する方法が採られることがあるが、従来は、
補助燃料の適正な添加量、即ち、脱水汚泥を乾燥させる
に充分で最少の量を把握することができなかったので、
補助燃料を加剰に加えて、余剰の熱は水t−噴霧して冷
却するなどの方策が採られていたのであゐ。
Normally, organic sludge is dehydrated, pre-dried, and then incinerated for disposal. In this case, the amount of heat required to pre-dry the dehydrated sludge uses the heat generated when the pre-dried sludge is incinerated, but since dehydrated sludge contains 70 to 90% water. Depending on the amount of heat generated by the recycled paper components in the sludge, it may not be possible to dry the dehydrated sludge to a combustible state. In such cases, a method of adding combustible powder such as wood powder or powdered charcoal to the sludge as an auxiliary fuel is sometimes adopted, but conventionally,
It was not possible to determine the appropriate amount of auxiliary fuel to be added, that is, the minimum amount sufficient to dry the dehydrated sludge.
Measures were taken such as adding extra auxiliary fuel and cooling the excess heat by spraying water.

本発明は、上記した点に鑑みてなされたものであって、
汚泥に対して補助燃料を適正な添加量となる様に自動的
に添加し、こねによって補助燃料の消費量を節減すると
共に、補助燃料の過剰添加に基づく焼−や乾燥機の損耗
を抑制するものである。
The present invention has been made in view of the above points, and includes:
Auxiliary fuel is automatically added to the sludge in an appropriate amount, reducing the amount of auxiliary fuel consumed through kneading, and reducing wear and tear on the burner and dryer due to excessive addition of auxiliary fuel. It is something.

以下、本発明を図面に基づいて具体的に説明する。Hereinafter, the present invention will be specifically explained based on the drawings.

図中符号lは乾燥機、2は焼却炉である0乾燥機1は脱
水汚泥を可燃状部にまで予備乾燥するものであシ、焼却
炉2は乾燥された汚泥を焼却すると共に乾燥機lに対す
る熱風の供給源となるものであゐ。 乾燥機lは通常の
この種の乾燥機と変るところはないのでありて、−例と
して横形回転胴式乾燥機が用いられるO 符号3は乾燥
機lに脱水汚泥を供給するための汚泥供給ホッパーであ
る。 この供給ホツノ<3は乾燥機lに対して脱水汚泥
を遍尚な速度で供給することができる様に形成されてい
るものであって、−例として底部にスクリウが取付けら
れていて、このスクリウを回転させる仁とによ(′スク
リウ\の回転速度に対応した速度で脱水汚泥を供給する
0 脱水汚泥は乾燥IIl内で、#O述する焼却炉2か
ら送シ込まれる熱風と接触して所定の水分含有量になる
まで乾燥され、構外に排出されて、乾燥汚泥タンク4に
投入されるO一方、機外に排出され九高湿排ガスは排ガ
ス処理機器を経て大気中に放出されゐ。 符号6は汚泥
に補助燃料を添加するための添加ホッパであシ、図示は
しないが、添加量を自動調節することがで!!ゐ様に形
成されている・ 114、図では添加ホッパ6は補助燃
料を脱水汚泥と共に乾燥Illに投入する構成を示した
が、鳩舎によシ補助燃料を乾燥機lよシ排出されゐ乾燥
汚泥に添加する様に構成しても何ら差しつかえはない0
 添加ホッパ6を図の様に構成したのは補助燃料を脱水
汚泥に対する乾燥助材として利用[ して汚泥の乾燥効果を高める点にあみ。 即ち、脱水汚
泥が粘性を有していて乾燥411内でJll状になシ易
いときはこれを解きはぐすことが必要とされる。 この
様なときに、粉粒体補助燃料を脱水汚泥に混合すること
によ#J、乾燥機内では汚泥の分散効果が得られ、乾燥
しヤす(なゐ利点があシ、かつ、乾燥汚泥内部に粉粒体
補助燃料が抱き込まれた状態となりて乾燥機よ〉排出さ
れるので炉内での燃焼が均一に行なわれゐ8点もあゐ。
In the figure, symbol l is a dryer, and symbol 2 is an incinerator. Dryer 1 pre-dries dehydrated sludge to a combustible state. Incinerator 2 incinerates the dried sludge, and dryer l It serves as a source of hot air for the air. The dryer 1 is no different from a normal dryer of this type, and, for example, a horizontal rotary drum dryer is used. 3 is a sludge supply hopper for supplying dehydrated sludge to the dryer 1. It is. This supply hole <3 is formed so as to be able to supply dehydrated sludge to the dryer l at a uniform rate; The dehydrated sludge is supplied at a speed corresponding to the rotational speed of the screw.The dehydrated sludge is brought into contact with the hot air blown from the incinerator 2 in the dryer IIl. The sludge is dried to a predetermined moisture content, discharged outside the premises, and put into a dry sludge tank 4. On the other hand, the highly humid exhaust gas discharged outside the machine is discharged into the atmosphere through exhaust gas treatment equipment. Reference numeral 6 is an addition hopper for adding auxiliary fuel to the sludge.Although not shown in the figure, it is formed in such a way that the amount of addition can be automatically adjusted. Although the configuration is shown in which the auxiliary fuel is added to the dryer Ill along with the dehydrated sludge, there is no problem in constructing the pigeon coop so that the auxiliary fuel is added to the dried sludge discharged from the dryer Ill.
The reason why the addition hopper 6 is configured as shown in the figure is that the auxiliary fuel is used as a drying aid for the dehydrated sludge to enhance the drying effect of the sludge. That is, when the dehydrated sludge is viscous and easily forms into a Jll shape in the dryer 411, it is necessary to loosen it. In such cases, by mixing granular auxiliary fuel with dehydrated sludge, it is possible to obtain a dispersion effect on the sludge in the dryer and dry it. Since the powdered auxiliary fuel is trapped inside and discharged from the dryer, the combustion in the furnace is uniform, which resulted in 8 points.

 乾燥汚泥タンク4に投入され九補助燃料を含む乾燥汚
泥は供給ホッパ7に転送されて焼却炉2に投入される・
 焼却炉2は通常のこの種の粉粒体焼却炉と変るとζろ
はなく。
The dried sludge containing the 9 auxiliary fuel charged into the dry sludge tank 4 is transferred to the supply hopper 7 and then fed into the incinerator 2.
The incinerator 2 is different from a normal granular material incinerator of this type.

−例として流動層焼却炉が用いられる。 送風7アン8
から焼却炉2に供給される燃焼用空気量は、流量調節装
置9によりて調節される様に表りておn、t*焼却炉2
よ如排aS畜れる高温熱風は乾燥様lに導入されるII
K構成されている。 歯、焼却炉20焼却能力は乾燥様
lの乾燥に必要な熱量を発生させうるものであ如、少な
くともそれ以下でない様に形成されている0である0 
また、本装置が定常状態で運転されていると1は、脱水
汚泥は乾燥機IK対して一定の速度で投入されてお)、
補助燃料は汚泥に対して必要にして最少の混合率になる
様に(一定の速度で)添加されている◎ ところで、本装置は補助燃料の添加速度へ換言すれば脱
水汚泥に対する混合量は脱水汚泥に対して適正量になる
様に側索されているものである。 即ち、乾燥汚泥タン
ク4にはレベルゲージ10が備えられていて、これがタ
ンク4内の乾燥汚泥が所定のレベルよシ低下すると側音
装置Uによりて添加ホッパ6からの補助燃料の添加速度
を速めレベルが増加すると添加速度を遅くする様になっ
ている。 また、乾燥機lから排出される排ガスの排出
経路には温度検出*Uが備見られていて、排ガスotm
tが所定温度よシ低下したときは側索装置口によシ流量
調節装@9t)開腹を大きくして焼却炉2に対する送風
量を増加し、排ガスの温度が上昇したときは送風量を減
少させる0 伺ここでは、乾燥後の水分検出を排ガスの
温度検出におき換えたが%乾燥汚泥の温度穐〜或いは水
分を曹接検串する手法がとれる場合には何ら排ガス温度
検出にこだわゐ必賛はなく、畳は乾燥汚泥の含有水分が
高いと事は焼却炉への送風量を増やし、低い時社焼却炉
への送風量會減らすことがなされればよいのである。 
焼却炉zK社tた温度検出器14が備えられていて、炉
内温度が所定温度よ如低下したと事は側索装置11jl
によ如供給ホッパ7かもの乾燥汚泥の投入量を増加し、
所定温度より上昇し九ときは投入量を減少させて、焼却
炉2に対する空気の送入量O変化するに拘わらず炉内温
度を一定に保って、乾燥Sに対して一定温度の熱風が送
p込iれるIIK構成されているO更に、供給ホラパフ
に4レベルゲージ1@が備見られていて、ホッパ内01
1L燥汚泥が一定量以下になると乾燥汚泥タンク4内の
乾燥汚泥が供給ホーバフに送り込壕れゐ様に構成されて
いるO続いて、脱水汚泥に対して補助燃料の添加量を調
節する側索手順について説明するO先ず、装置は定常状
態で運転されているものとする。 この状態で、汚泥供
給ホッパ3から乾燥機lに常態よシも水分含有量の高い
脱水汚泥が投入されたとする。 すると、汚泥011有
水分の多い分だけ排ガスの温度が低下するC)e。
- As an example a fluidized bed incinerator is used. Air blower 7 an 8
The amount of combustion air supplied to the incinerator 2 from
High-temperature hot air is introduced into the drying process II.
It is composed of K. The incineration capacity of the incinerator 20 is such that it can generate the amount of heat necessary for drying the drying process, at least not less than 0.
In addition, when this device is operated in a steady state, (1) dehydrated sludge is fed into the dryer IK at a constant speed),
The auxiliary fuel is added to the sludge (at a constant rate) to achieve the minimum mixing ratio required.◎ By the way, this device is capable of adding the auxiliary fuel to the dehydrated sludge in terms of the addition rate. The sludge is lined with side ropes to keep the appropriate amount of sludge. That is, the dry sludge tank 4 is equipped with a level gauge 10, and when the dry sludge in the tank 4 drops below a predetermined level, the side sound device U speeds up the addition speed of auxiliary fuel from the addition hopper 6. As the level increases, the addition rate is slowed down. In addition, temperature detection *U is installed on the exhaust path of the exhaust gas discharged from the dryer l, and the exhaust gas otm
When t falls below a predetermined temperature, the flow rate adjustment device @9t) increases the amount of air blown to the incinerator 2 by increasing the abdominal opening, and decreases the amount of air blown when the temperature of the exhaust gas rises. Here, we replaced the moisture detection after drying with the temperature detection of the exhaust gas, but if the temperature of the dried sludge or the moisture can be measured on a skewer, there is no need to insist on detecting the exhaust gas temperature. There is no objection, and if the moisture content of the dried sludge on tatami mats is high, the amount of air blown to the incinerator should be increased, and if the amount of air blown to the incinerator is low, it should be reduced.
The incinerator is equipped with a temperature detector 14, and when the temperature inside the furnace falls below a predetermined temperature, the side cable device 11jl
Increase the amount of dried sludge input into the supply hopper 7,
When the temperature rises above a predetermined temperature, the input amount is reduced, and the temperature inside the furnace is kept constant regardless of the change in the amount of air fed into the incinerator 2, so that hot air at a constant temperature is sent to the dryer S. In addition, a 4-level gauge 1 is provided in the supply hollow puff, and 01 in the hopper is configured.
When the 1L dried sludge becomes less than a certain amount, the dried sludge in the dry sludge tank 4 is sent to the supply hose buff. First, it is assumed that the device is operating in a steady state. In this state, it is assumed that dehydrated sludge, which has a higher water content than normal, is fed into the dryer l from the sludge supply hopper 3. Then, the temperature of the exhaust gas decreases by the amount of water in the sludge 011 (C)e.

その温[0低下を温度検出器Uが検知し、側索装置11
3が作動して流量調節装msc+一度を大1くして焼却
炉2に対する空気O送入量を多くする。 すると、それ
に応じて炉内温度が低下するので、これ管温度検出器1
4で検知し、側索装@Utが作動して焼却炉2に対する
乾燥汚泥O投入量を増加し、而して炉内温度を上昇させ
ゐ・その結果、乾燥機lに供給畜れる熱量か増加する。
The temperature detector U detects the temperature [0 drop, and the side cable device 11
3 is activated and the flow rate adjustment device msc+1 is increased by 1 to increase the amount of air O fed into the incinerator 2. Then, the temperature inside the furnace decreases accordingly, so the tube temperature detector 1
4, the side cable system @Ut is activated to increase the amount of dried sludge O input to the incinerator 2, thereby increasing the temperature inside the furnace.As a result, the amount of heat supplied to the dryer 1 is increased. To increase.

 一方、乾燥機IK対して乾燥汚l!O投入量が増加す
ると、その分だけ乾燥汚泥メンタ4内の乾燥汚泥Oレベ
ルが低下するので、側索装置luが作動して補助燃料の
添加量を増加す、II。
On the other hand, compared to the dryer IK, there is dry dirt! When the O input amount increases, the dried sludge O level in the dry sludge mentor 4 decreases by that amount, so the side cable device lu operates to increase the amount of auxiliary fuel added. II.

一方、脱水汚泥0**水分が少ないときは、焼却炉2に
対する空気の送入量が減少し、乾燥汚泥の投入速度が遅
くなるので、乾燥汚泥タンク4内の乾燥汚泥のレベルが
上昇し、しかして補助燃料の添加量が減少する。
On the other hand, when the dehydrated sludge 0** water content is low, the amount of air fed into the incinerator 2 decreases and the input speed of dried sludge slows down, so the level of dried sludge in the dried sludge tank 4 increases, Therefore, the amount of auxiliary fuel added decreases.

かくして脱水汚泥O金高水分の変動するに脣じて補助燃
料の添加量が増減し、S<〜X汚渉には焼却処理するに
適当した補助燃料が混合1れ、補助燃料の無駄金焼却が
無(愈る0である0
In this way, the amount of auxiliary fuel added increases or decreases as the dehydrated sludge O gold and water content changes, and auxiliary fuel suitable for incineration is mixed with S<~X pollution, and waste of auxiliary fuel is incinerated. is nothing (0 that is 0 that fades)

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

図は本発明の一実施例を示す系統図であゐ。 The figure is a system diagram showing one embodiment of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 焼却炉と乾燥機とを備え、乾燥機には脱水汚泥と補助燃
料とを投入してこれを予備乾燥すると共に、乾燥物を焼
却して、生ずる燃焼ガスを乾燥機の乾燥用熱源として利
用する汚泥焼却装置において、乾燥機から排出される排
ガスの温度を検知して焼却炉に対する空気、の送入量を
調節する調節装置、焼却デの炉内温度を検知して焼却炉
に対する乾燥汚泥の供給量を調節して炉内温度を所定の
温度に制御する制御装置、乾燥汚泥タンク内の乾燥汚泥
のレベルを検知して補助燃料の添加量を制御する制御装
置を備えたことを特徴とする汚泥焼却装置。
Equipped with an incinerator and a dryer, the dryer is charged with dehydrated sludge and auxiliary fuel to pre-dry it, the dried material is incinerated, and the resulting combustion gas is used as a heat source for drying the dryer. In a sludge incinerator, a control device detects the temperature of exhaust gas discharged from the dryer and adjusts the amount of air fed into the incinerator, and a control device detects the temperature inside the incinerator and supplies dried sludge to the incinerator. Sludge comprising: a control device that adjusts the amount of auxiliary fuel to control the furnace temperature to a predetermined temperature; and a control device that detects the level of dried sludge in a dry sludge tank and controls the amount of auxiliary fuel added. Incinerator.
JP57052732A 1982-03-30 1982-03-30 Incinerator for sludge Granted JPS58168807A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57052732A JPS58168807A (en) 1982-03-30 1982-03-30 Incinerator for sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57052732A JPS58168807A (en) 1982-03-30 1982-03-30 Incinerator for sludge

Publications (2)

Publication Number Publication Date
JPS58168807A true JPS58168807A (en) 1983-10-05
JPH0256566B2 JPH0256566B2 (en) 1990-11-30

Family

ID=12923095

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57052732A Granted JPS58168807A (en) 1982-03-30 1982-03-30 Incinerator for sludge

Country Status (1)

Country Link
JP (1) JPS58168807A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62163799A (en) * 1986-01-14 1987-07-20 Okawara Mfg Co Ltd Method for incinerating high-water content sludge containing soluble inorganic substance
JPH0328615A (en) * 1989-06-24 1991-02-06 Takahashi Shoten:Kk Method and device therefor bean curd refuse incineration
US6055915A (en) * 1997-04-04 2000-05-02 Bickell; Roy A. Wood residue disposal system
JP2017089990A (en) * 2015-11-12 2017-05-25 株式会社大川原製作所 Drying facility and its operational method
JP2017187199A (en) * 2016-04-04 2017-10-12 川崎重工業株式会社 Wet biomass incineration system and operational method of wet biomass combustion furnace
JP2020151636A (en) * 2019-03-19 2020-09-24 メタウォーター株式会社 Method for incinerating dewatered sludge

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62163799A (en) * 1986-01-14 1987-07-20 Okawara Mfg Co Ltd Method for incinerating high-water content sludge containing soluble inorganic substance
JPH0328615A (en) * 1989-06-24 1991-02-06 Takahashi Shoten:Kk Method and device therefor bean curd refuse incineration
US6055915A (en) * 1997-04-04 2000-05-02 Bickell; Roy A. Wood residue disposal system
JP2017089990A (en) * 2015-11-12 2017-05-25 株式会社大川原製作所 Drying facility and its operational method
JP2017187199A (en) * 2016-04-04 2017-10-12 川崎重工業株式会社 Wet biomass incineration system and operational method of wet biomass combustion furnace
JP2020151636A (en) * 2019-03-19 2020-09-24 メタウォーター株式会社 Method for incinerating dewatered sludge

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