JPS5915954B2 - Carbonization cracking method and equipment - Google Patents

Carbonization cracking method and equipment

Info

Publication number
JPS5915954B2
JPS5915954B2 JP50020403A JP2040375A JPS5915954B2 JP S5915954 B2 JPS5915954 B2 JP S5915954B2 JP 50020403 A JP50020403 A JP 50020403A JP 2040375 A JP2040375 A JP 2040375A JP S5915954 B2 JPS5915954 B2 JP S5915954B2
Authority
JP
Japan
Prior art keywords
carbonization
fluidized bed
sand
char
gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP50020403A
Other languages
Japanese (ja)
Other versions
JPS5196803A (en
Inventor
昇 梶本
記久男 荒木
義英 西本
哲夫 四方
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP50020403A priority Critical patent/JPS5915954B2/en
Publication of JPS5196803A publication Critical patent/JPS5196803A/en
Publication of JPS5915954B2 publication Critical patent/JPS5915954B2/en
Expired legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 本発明は乾留分解の方法およびその実施のための装置に
係り、特に固形廃棄物等を乾留分解し、油またはガスを
回収する方法およびその実施のための装置に関するもの
である。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method of carbonization cracking and an apparatus for carrying out the same, and more particularly to a method of carbonizing solid waste, etc. to recover oil or gas, and an apparatus for carrying out the same. It is.

固形状の廃棄物等を乾留分解し、これから油あるいはガ
スを回収する方法、特に産業廃棄物等を処理し、油脂分
あるいはガス等を回収する方法は省資源、資源の有効利
用等の観点から近年産業界の注目を集めている。
A method of carbonizing solid waste, etc. and recovering oil or gas from it, especially a method of treating industrial waste, etc. and recovering oil, fat, gas, etc., from the viewpoint of resource conservation and effective use of resources. In recent years, it has attracted attention from the industry.

これらの方法あるいは装置は、通常砂を流動媒体とし、
また空気を流動化ガスとして流動層型乾留炉内に供給し
、固形廃棄物を乾留分解するものである。
These methods or devices usually use sand as the fluidizing medium;
In addition, air is supplied as a fluidizing gas into a fluidized bed type carbonization furnace to decompose solid waste by carbonization.

従来この種の方法あるいは装置は、流動層型乾留炉と流
動層型焼却炉の二基から構成され、当該乾留炉と焼却炉
との間をパイプによって連絡し、オーバフロー(溢流)
によって上記の砂を循環させ、当該砂の顕熱を利用して
乾留、分解を行なっているものが多かった。
Conventionally, this type of method or apparatus consists of two units, a fluidized bed carbonization furnace and a fluidized bed incinerator, and the carbonization furnace and the incinerator are connected by a pipe to prevent overflow.
In many cases, the above-mentioned sand is circulated through the process, and carbonization and decomposition are performed using the sensible heat of the sand.

しかしながら以上に説明したような従来技術になる方法
あるいは装置の場合、先ず廃棄物を乾留するための熱源
としては、砂の顕熱のみでは不十分であり、補助的な燃
料を必要とすること、また第二に、前記の二基間を相互
にパイプによって連絡することは、現実に二基間に圧力
差があるためその圧力バランスの面でいろいろと面倒な
問題が生ずる、等の問題点がみられた。
However, in the case of the prior art method or device as explained above, firstly, the sensible heat of sand alone is insufficient as a heat source for carbonizing waste, and supplementary fuel is required; Secondly, connecting the two units mentioned above through pipes has problems, such as the fact that there is actually a pressure difference between the two units, which causes various troublesome problems in terms of pressure balance. It was seen.

また乾留処理の際に生ずる不燃物等を取出すために多量
のガスを必要とし、したがって乾留分解されて生成する
ガスが稀釈化され、副次製品としてのガスの品質が低下
するという問題がみられた。
In addition, a large amount of gas is required to remove incombustible materials generated during carbonization treatment, which causes the gas produced by carbonization to be diluted, resulting in a reduction in the quality of the gas as a by-product. Ta.

本発明は以上に説明したような従来技術にみられる問題
点に鑑みてなされたもので、上記の焼却炉から溢流排出
される熱媒体としての砂の上記乾留炉への供給をより容
易ならしめ、砂の有する顕熱の有効利用、固形廃棄物か
らの回収生成物の収率の増加、排出速度を自由に調整し
得ること等、固形廃棄物等の処理効率、処理方法の面で
大巾に改良、改善がなされた乾留分解方法およびその実
施のための装置を提供するものである。
The present invention has been made in view of the problems seen in the prior art as explained above, and it is possible to more easily supply sand as a heat medium discharged from the incinerator to the carbonization furnace. It has significant advantages in terms of solid waste processing efficiency and processing methods, such as effective use of the sensible heat of sand, increased yield of recovered products from solid waste, and ability to freely adjust the discharge rate. It is an object of the present invention to provide a carbonization cracking method and an apparatus for carrying out the method, which have been greatly improved and improved.

本発明になる乾留分解の方法および装置は、前記にも一
部説明したように、従来の二基式の構造を止めて乾留炉
の上部に直接焼却炉を設けて一基二段式として、当該焼
却炉から溢流排出される砂の上記乾留炉への供給をより
容易ならしめ、また上記乾留炉には溢流管を設けず、ス
クリューコンベヤに通じる排出管から、チャー、砂、不
燃物等の排出を行ない、かつ乾留ガスによって不燃物を
分別、分級し、チャーおよび砂を上記焼却炉へ気流輸送
することを骨子とするものである。
The method and apparatus for carbonization cracking according to the present invention, as partially explained above, replaces the conventional two-stage structure and installs an incinerator directly above the carbonization furnace to create a single-stage two-stage structure. This makes it easier to supply the sand overflowing from the incinerator to the carbonization furnace, and the carbonization furnace is not provided with an overflow pipe, and char, sand, and incombustible materials are removed from the discharge pipe leading to the screw conveyor. The main idea is to separate and classify incombustible materials using carbonized gas, and transport char and sand by air to the incinerator.

以下に添付の図面を参照しながら、本発明になる乾留分
解方法および装置についてさらに具体的に説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The carbonization cracking method and apparatus of the present invention will be described in more detail below with reference to the accompanying drawings.

第1図は本発明になる乾留分解方法およびその実施のた
めの装置を示す説明図である。
FIG. 1 is an explanatory diagram showing a carbonization cracking method according to the present invention and an apparatus for carrying out the method.

図において固形廃棄物等はホッパ2に貯留された後、ス
クリューコンベヤ3によって流動層型乾留炉1に供給さ
れる。
In the figure, solid waste and the like are stored in a hopper 2 and then supplied to a fluidized bed carbonization furnace 1 by a screw conveyor 3.

当該流動層型乾留炉1は、砂を熱媒体兼流動媒体とし、
限定された量の空気を流動化ガスとするものである。
The fluidized bed carbonization furnace 1 uses sand as a heat medium and a fluid medium,
A limited amount of air is used as the fluidizing gas.

また当該流動層型乾留炉1には空気供給配管7を通して
目皿板8の下部から制限された量の空気が供給され、当
該乾留炉1内の固形廃棄物の一部を燃焼し、当該炉内の
温度を450〜500℃に保持し、固形廃棄物等の乾留
熱分解を行なう。
In addition, a limited amount of air is supplied to the fluidized bed carbonization furnace 1 from the lower part of the perforated plate 8 through the air supply pipe 7, and a part of the solid waste in the carbonization furnace 1 is combusted. The temperature inside the reactor is maintained at 450 to 500°C, and solid waste, etc. is subjected to dry distillation thermal decomposition.

発生した乾留ガスはサイクロン11によって除塵された
後、油回収装置12によって油分を回収し、ガスは配管
13を通じてその一部または全部をブロワ14によって
吸引する。
After the generated carbonized gas is removed by a cyclone 11, oil is recovered by an oil recovery device 12, and part or all of the gas is sucked by a blower 14 through a pipe 13.

吸引されたガスは気流輸送管15を経て流動層型焼却炉
4内に供給され、当該ガス中に含まれる可燃性ガスが焼
却される。
The sucked gas is supplied into the fluidized bed incinerator 4 through the airflow transport pipe 15, and the combustible gas contained in the gas is incinerated.

一方、チャー、砂および不燃物等は排出管9から排出さ
れる。
On the other hand, char, sand, incombustibles, etc. are discharged from the discharge pipe 9.

当該排出管9の一端は上記目皿板8に開口し、別の一端
はスクリューコンベヤ10に通じており、上記不燃物等
の排出速度は当該スクリューコンベヤ100回転数によ
って調節される。
One end of the discharge pipe 9 opens into the perforated plate 8, and the other end communicates with the screw conveyor 10, and the discharge speed of the incombustibles etc. is adjusted by the 100 rotation speed of the screw conveyor.

上記スクリューコンベヤ10の他端は上記気流輸送管1
5に開口しているが、当該気流輸送管15中を経て排出
されるチャー、砂および不純物等は、同じく当該気流輸
送管15中を流れる乾留ガスによって分級される。
The other end of the screw conveyor 10 is the air flow transport pipe 1
The char, sand, impurities, etc. that are discharged through the air flow transport pipe 15 are classified by the carbonization gas that also flows through the air flow transport pipe 15.

すなわち、当該ガス流によって風力分級され、分級され
た不燃物等は不燃物排出管16から排出される。
That is, the gas flow performs wind classification, and the classified noncombustible materials are discharged from the noncombustible material discharge pipe 16.

一方、チャーおよび砂等は乾留ガスによって気流輸送さ
れ、上記流動層型焼却炉4内に供給される。
On the other hand, char, sand, and the like are transported in air by carbonization gas and supplied into the fluidized bed incinerator 4 .

当該流動層型焼却炉4内には空気供給配管17を経て十
分な量の空気が供給され、砂を流動媒体とし、また空気
を流動化ガスとしてチャーおよび可燃性ガス等が焼却あ
るいは燃焼される。
A sufficient amount of air is supplied into the fluidized bed incinerator 4 through the air supply pipe 17, and char, combustible gas, etc. are incinerated or combusted using sand as a fluidizing medium and air as a fluidizing gas. .

この際の燃焼温度は通常800〜850℃の程度である
The combustion temperature at this time is usually about 800 to 850°C.

一方、不燃物等はチャーおよび砂等から分別され、別途
排出される。
On the other hand, non-combustible materials are separated from char, sand, etc. and discharged separately.

流動媒体としての砂は、砂ホッパ5に常時貯留され、当
該砂ホッパ5からスクリューコンベヤ6によって上記流
動層型焼却炉4内に補充される。
Sand as a fluidizing medium is always stored in a sand hopper 5, and is replenished from the sand hopper 5 into the fluidized bed incinerator 4 by a screw conveyor 6.

当該焼却炉4には2個の仕切弁を介して上記乾留炉1に
通じる溢流管18が設けられ、上記熱媒体としての砂が
当該乾留炉1内に供給され、固形廃棄物等の乾留熱源の
一部として利用される。
The incinerator 4 is provided with an overflow pipe 18 that communicates with the carbonization furnace 1 through two gate valves, and sand as the heating medium is supplied into the carbonization furnace 1 to carbonize solid waste, etc. Used as part of the heat source.

したがって、上記乾留炉1内に供給される空気量が減少
し、固形廃棄物等の部分燃焼量が減少することにより、
乾留生成物の収率の増加が期待できる。
Therefore, the amount of air supplied into the carbonization furnace 1 is reduced, and the amount of partial combustion of solid waste, etc. is reduced, so that
An increase in the yield of carbonized products can be expected.

上記の流動層型焼却炉4内では、チャーおよび可燃性ガ
ス等が焼却あるいは燃焼されることは前記ですでに説明
したとおりであるが、この際発生する燃焼排ガス等は、
サイクロン19により除塵された後、熱交換器20によ
って熱回収され低カロリーの乾留ガスの熱量が回収され
ると同時に、ガス中の微量有害物質(アルデヒド、ケト
ン等)が燃焼処理され、外部に排出される。
As already explained above, char, combustible gas, etc. are incinerated or combusted in the fluidized bed incinerator 4, but the combustion exhaust gas etc. generated at this time is
After dust is removed by the cyclone 19, the heat is recovered by the heat exchanger 20, and the calorific value of the low-calorie carbonized gas is recovered, and at the same time, trace amounts of harmful substances (aldehydes, ketones, etc.) in the gas are combusted and discharged to the outside. be done.

一方空気はブロワ22、空気加熱器21を経て200〜
400℃程度の温度に予熱される。
On the other hand, the air passes through the blower 22 and air heater 21 to
It is preheated to a temperature of about 400°C.

この際、当該空気の温度は上記乾留炉1内に設置された
温度調節計23によって検知されるとともに、当該調節
計23と連動した流量調節弁24によってその流量の調
整が行なわれる。
At this time, the temperature of the air is detected by a temperature controller 23 installed in the carbonization furnace 1, and the flow rate is adjusted by a flow rate control valve 24 interlocked with the controller 23.

以上は詳細に説明したように、本発明になる固形廃棄物
等の乾留分解方法および装置は、従来技術になるものと
比較して砂の有する保有顕熱をより有効に利用し得るも
のであり、したがって処理の際に得られる回収生成物の
収率も増加し、乾留分解処理効率の面で大巾な向上が得
られた。
As described above in detail, the method and apparatus for carbonizing solid waste, etc. according to the present invention can utilize the sensible heat possessed by sand more effectively than the conventional technology. Therefore, the yield of recovered products obtained during the treatment also increased, resulting in a significant improvement in the efficiency of the carbonization cracking treatment.

また不燃物等の排出あるいは抜出しに特に排出用のガス
を必要とすることがなく、したがって乾留処理によって
生成された乾留ガスが稀釈化されず、副次製品としての
生成ガスの品質の面できわめて有利となった。
In addition, no special exhaust gas is required for discharging or extracting incombustibles, so the carbonized gas produced by carbonization is not diluted, and the quality of the produced gas as a by-product is extremely high. It was advantageous.

さらに不燃物等の排出速度、したがって滞留時間がスク
リューコンベヤの回転数によって任意に調整されるとい
う特徴がある。
A further feature is that the discharge rate of incombustibles, etc., and therefore the residence time, can be arbitrarily adjusted by the rotation speed of the screw conveyor.

以上のほか、従来の二基式乾留装置では砂の循環あるい
は圧力バランスの面でいろいろと問題が多いが、本発明
によればこれらの問題点も解消され、砂の循環もきわめ
て確実に行なわれるのみでなく、チャー、砂および不燃
物等がスクリューコンベヤによって排出されるため、前
記のように排出用のガスを特に必要とすることがない等
、得られる効果がきわめて大きい。
In addition to the above, conventional two-unit carbonization equipment has many problems in terms of sand circulation and pressure balance, but according to the present invention, these problems are solved and sand circulation is carried out extremely reliably. In addition, since char, sand, incombustibles, etc. are discharged by the screw conveyor, there is no need for any particular discharge gas as mentioned above, and other great effects can be obtained.

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

第1図は本発明になる固形廃棄物等の乾留分解方法の実
施のための装置の系統図である。 符号の説明、1・・・・・・流動層型乾留分解炉、2・
・・・・・固形廃棄物ホッパ、3.6.10・・・・・
・スクリューコンベヤ、4・・・・・・流動層型焼却炉
、5・・・・・・砂ホッパ、7,17・・・・・・空気
供給配管、8・・・・・・目皿板、9・・・・・・排出
管 11,19・・・・・・サイクロン、12・・・・
・・油回収装置、13・・・・・・ガス配管、14.2
2・・・・・・ブロワ、15・・・・・・気流輸送管、
16・・・・・・不燃物排出管、18・・・・・・溢流
管、20・・・・・・熱交換器、21・・・・・・空気
加熱器、23・・・・・・温度調節計、24・・・・・
・流量調節弁。
FIG. 1 is a system diagram of an apparatus for carrying out the method of carbonizing solid waste, etc. according to the present invention. Explanation of symbols, 1...Fluidized bed carbonization cracking furnace, 2.
...Solid waste hopper, 3.6.10...
・Screw conveyor, 4...Fluidized bed incinerator, 5...Sand hopper, 7, 17...Air supply piping, 8...Perforated plate , 9...Discharge pipe 11,19...Cyclone, 12...
...Oil recovery equipment, 13... Gas piping, 14.2
2... Blower, 15... Air flow transport pipe,
16...Incombustible material discharge pipe, 18...Overflow pipe, 20...Heat exchanger, 21...Air heater, 23...・・Temperature controller, 24・・・・
・Flow control valve.

Claims (1)

【特許請求の範囲】 1 固形廃棄物等の乾留分解方法において、流動層型乾
留分解炉の上部に直接生成チャーの流動層型焼却炉を設
けて一基二段式とし、かつ当該チャー、砂および不純物
等の排出をスクリューコンベヤによって実施するととも
に、当該コンベヤから排出される上記チャー、砂および
不純物等を生成乾留ガスによって上記流動層型焼却炉へ
気流輸送すると同時にその風力によって分別することを
特徴とする乾留分解方法。 2 流動層型乾留分解炉と、当該分解炉の上部に直接接
続された生成チャーの流動層型焼却炉と、上記乾留炉の
チャー、砂および不純物等の排出部に配備された回転速
度の調整自在であるスクリューコンベヤとを含んでなる
、上記特許請求の範囲第1項に記載の乾留分解方法を実
施するための装置。
[Scope of Claims] 1. In a carbonization method for solid waste, etc., a fluidized bed type incinerator for directly generated char is installed above a fluidized bed type carbonization furnace to form a single, two-stage system, and the char, sand, etc. and impurities, etc. are discharged by a screw conveyor, and the char, sand, impurities, etc. discharged from the conveyor are pneumatically transported to the fluidized bed incinerator by the produced carbonization gas, and at the same time are separated by the wind force. A carbonization decomposition method. 2 Adjustment of the rotational speed of a fluidized bed carbonization furnace, a fluidized bed incinerator for the produced char that is directly connected to the upper part of the cracking furnace, and a fluidized bed incinerator that is installed at the discharge section for char, sand, impurities, etc. of the carbonization furnace. An apparatus for carrying out the carbonization cracking method according to claim 1, comprising a screw conveyor, which is flexible.
JP50020403A 1975-02-20 1975-02-20 Carbonization cracking method and equipment Expired JPS5915954B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP50020403A JPS5915954B2 (en) 1975-02-20 1975-02-20 Carbonization cracking method and equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP50020403A JPS5915954B2 (en) 1975-02-20 1975-02-20 Carbonization cracking method and equipment

Publications (2)

Publication Number Publication Date
JPS5196803A JPS5196803A (en) 1976-08-25
JPS5915954B2 true JPS5915954B2 (en) 1984-04-12

Family

ID=12026047

Family Applications (1)

Application Number Title Priority Date Filing Date
JP50020403A Expired JPS5915954B2 (en) 1975-02-20 1975-02-20 Carbonization cracking method and equipment

Country Status (1)

Country Link
JP (1) JPS5915954B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0435792Y2 (en) * 1984-07-18 1992-08-25
JPH0442766Y2 (en) * 1985-03-26 1992-10-09

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0435792Y2 (en) * 1984-07-18 1992-08-25
JPH0442766Y2 (en) * 1985-03-26 1992-10-09

Also Published As

Publication number Publication date
JPS5196803A (en) 1976-08-25

Similar Documents

Publication Publication Date Title
US7214252B1 (en) Method and device for pyrolyzing and gasifying organic substances or substance mixtures
JP2003504454A5 (en)
RU2009140379A (en) METHOD OF HEAT PROCESSING OF MATERIAL (OPTIONS) AND INSTALLATION OF SEPARATION OF GRAIN MATERIAL
CA3113577A1 (en) Process of treating carbonaceous material and apparatus therefor
CN110882681A (en) Continuous regeneration method and system equipment for waste powdered activated carbon
CZ285991B6 (en) Heat treatment process of waste material and apparatus for making the same
RU2120460C1 (en) Method and apparatus for producing combustible gases from solid fuel, method and apparatus for treating raw phosphates
JPS5915954B2 (en) Carbonization cracking method and equipment
JP5864865B2 (en) Waste melting treatment method
US4563264A (en) Method of dry distillation of volatile substances from mineral matter containing same
EP0312742A2 (en) Process for the thermal treatment of organic or organically contaminated waste
US7063026B1 (en) Waste carbonizing and energy utilizing system
JP3913684B2 (en) Waste gasification and melting system
JP3702424B2 (en) Waste treatment method and treatment system
JPS599008B2 (en) Solid waste pyrolysis treatment equipment
JPS5893785A (en) Manufacture of pyrolytic gas and device for carrying out it
WO2004005428A1 (en) Coal drying and charring process
JPS6314165Y2 (en)
WO2021200519A1 (en) Carbonization product manufacturing facility and carbonization product manufacturing method
JPH10118614A (en) Process and device for exhausting pyrolysis gas in industrial waste thermal decomposition furnace
JP2006223961A (en) Method for separating char and noncombustible by means of fluidized layer
JPH039990A (en) Carbonization of organic solid
JP2965489B2 (en) Waste incineration method
JPH11322321A (en) Production of activated carbon and device therefor
JPH0960843A (en) Removing method of deposited matter in layer circulating fluidized bed combustion