JPH039990A - Carbonization of organic solid - Google Patents
Carbonization of organic solidInfo
- Publication number
- JPH039990A JPH039990A JP1144093A JP14409389A JPH039990A JP H039990 A JPH039990 A JP H039990A JP 1144093 A JP1144093 A JP 1144093A JP 14409389 A JP14409389 A JP 14409389A JP H039990 A JPH039990 A JP H039990A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- organic matter
- solid organic
- hot gas
- packed bed
- 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
- 239000007787 solid Substances 0.000 title claims abstract description 80
- 238000003763 carbonization Methods 0.000 title description 8
- 239000000446 fuel Substances 0.000 claims abstract description 8
- 239000007788 liquid Substances 0.000 claims abstract description 7
- 239000005416 organic matter Substances 0.000 claims description 72
- 238000000197 pyrolysis Methods 0.000 claims description 56
- 238000000034 method Methods 0.000 claims description 19
- 238000002485 combustion reaction Methods 0.000 claims description 10
- 239000000945 filler Substances 0.000 claims description 3
- 238000010992 reflux Methods 0.000 claims 1
- 239000007789 gas Substances 0.000 abstract description 139
- 238000010438 heat treatment Methods 0.000 abstract description 10
- 239000000411 inducer Substances 0.000 abstract description 6
- 238000010000 carbonizing Methods 0.000 abstract description 3
- 238000004064 recycling Methods 0.000 abstract 1
- 239000002023 wood Substances 0.000 description 26
- 238000011282 treatment Methods 0.000 description 22
- 239000003610 charcoal Substances 0.000 description 11
- 238000009423 ventilation Methods 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 235000013311 vegetables Nutrition 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 239000000567 combustion gas Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000011368 organic material Substances 0.000 description 2
- 230000002250 progressing effect Effects 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 241001251054 Formica truncorum Species 0.000 description 1
- 241000519695 Ilex integra Species 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 239000003570 air Substances 0.000 description 1
- FFBHFFJDDLITSX-UHFFFAOYSA-N benzyl N-[2-hydroxy-4-(3-oxomorpholin-4-yl)phenyl]carbamate Chemical compound OC1=C(NC(=O)OCC2=CC=CC=C2)C=CC(=C1)N1CCOCC1=O FFBHFFJDDLITSX-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000003889 chemical engineering Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003780 insertion Methods 0.000 description 1
- 230000037431 insertion Effects 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 238000007790 scraping Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 239000002699 waste material 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
Landscapes
- Coke Industry (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、製炭用木材、木皮樹枝等木材の処理に伴う残
材又は木材加工残材等の木質、清掃処理された草木質残
渣、人口合成工程を経て製品化された有機物廃棄物等の
乾溜方法に関する。[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to wood for charcoal making, wood residues from wood processing such as bark and branches, wood processing residues, etc., vegetable residues after cleaning treatment, This article relates to a dry distillation method for organic waste, etc., which has been made into a product through an artificial synthesis process.
木炭製造のために木質の乾溜炭化を行う炭焼き装置は現
存しているが、その生産効率は低い。Charcoal burning equipment that performs dry distillation of wood to produce charcoal still exists, but its production efficiency is low.
一方、木材の残材や草木質残渣は、焼却される外に現在
実用化されている乾溜処理方法は殆んど工
見当らない0人■合成工程を経た有m物も又その熱処理
としては、最終製品化を目的とする化学工学的処理は別
として、乾溜過程を経るものもあっても実体としては焼
却処理に属するものが殆んどで、廃棄処理として焼却以
外には、乾溜処理してその処理物を再利用する例は殆ん
ど見られない。On the other hand, wood residues and vegetable residues are incinerated, and there is almost no dry distillation method currently in use. Aside from chemical engineering treatment for the purpose of final products, most of the items actually belong to incineration treatment, although some items go through the dry distillation process. There are almost no examples of reusing the processed materials.
上記従来の木炭製造用の炭焼き方式は、炉内に原料木材
を積み込み、一方の焚口から燃焼ガスを供給してその上
部空間を通って、他端の炉底近くに設けられた排気孔か
らそのガスが放出される間にこの熱ガスが緩徐に原料木
材に授熱して、その乾溜を進行させた上で、長時間(1
00〜150時間)かけて炭化が完了する。このように
、従来の炭焼き方式は非効率的な生産プロセスであるが
、更に次の問題点がある。In the conventional charcoal burning method for producing charcoal, raw wood is loaded into the furnace, combustion gas is supplied from one combustion port, passes through the upper space, and is released from the exhaust hole provided near the bottom of the furnace at the other end. While the gas is released, this hot gas slowly transfers heat to the raw material wood, and the dry distillation proceeds for a long period of time (1
00 to 150 hours) to complete carbonization. As described above, the conventional charcoal burning method is an inefficient production process, but it also has the following problems.
含水率の高い木質を急速乾燥すると激しい外亀裂が起る
。また、250°C〜300°C付近の乾溜域では内部
亀裂が生じ易い。従って、現在の炭焼き窯における炉内
堆積木材の加熱プロセスでは、炉内木材の堆積体の上方
及び側方を取巻く熱ガスが、ゆるやかにこの堆積体内部
の熱対流を促して、徐々に昇温が行われることを利用し
ているが、上記の亀裂発生を警戒して、その昇温速度が
著しく限定されることになっている。一方、焚口から供
給する熱ガス温度のコントロールが難しく、高過ぎれば
炉内木質乃至炭質の酸化を起し、低すぎれば昇温効率が
低くなるほかに、餅米を燃焼させて着火温度以下の中温
熱ガスを発生させることは容易ではないという掻作上の
難しさもある。When wood with a high moisture content is dried quickly, severe external cracks occur. Furthermore, internal cracks are likely to occur in the dry distillation region around 250°C to 300°C. Therefore, in the heating process of the wood piled up inside the furnace in the current charcoal kiln, the hot gas surrounding the top and sides of the pile of wood inside the furnace gently promotes thermal convection inside the pile, and the temperature gradually rises. However, due to the above-mentioned crack generation, the rate of temperature increase is significantly limited. On the other hand, it is difficult to control the temperature of the hot gas supplied from the fire pit; if it is too high, the wood or carbon in the furnace will oxidize, and if it is too low, the heating efficiency will be low, and the mochi rice will be burned and the temperature will drop below the ignition temperature. There is also the difficulty in scraping that it is not easy to generate medium-temperature gas.
一方、木質或いは草木質の乾溜を行って、その製品化或
いは処理後の排出物の利用を覗っても、その市場規模は
小さく、処理工程に要する設備費、処理費の極度の節減
が要求されるために、上記のように、これらの乾溜処理
は、古来からの炭焼き以外には殆んど実用例を見ない結
果に至っている。On the other hand, even if we look at dry distillation of wood or vegetable matter, commercialize it, or use the waste after treatment, the market size is small, and extreme reductions in equipment costs and treatment costs required for the treatment process are required. Therefore, as mentioned above, these dry distillation treatments have almost no practical application other than charcoal burning, which has been practiced since ancient times.
また、木質又は草木質の乾溜工程において発生する有機
分解ガスが装置外に放出される時の有色煙も問題であり
、これを処理しようとするとその処理の費用が問題とな
ってくる。Another problem is colored smoke when the organic decomposed gas generated in the process of dry distilling wood or plants is released outside the apparatus, and when attempting to treat this, the cost of treatment becomes an issue.
これらの理由によって、天然有機物の乾溜処理と同様に
合成有機物の乾溜処理も殆んど実用化されおらず、いづ
れも焼却処理の道を撰ぶ結果になっているのが現状であ
る。For these reasons, the dry distillation treatment of synthetic organic materials, as well as the dry distillation treatment of natural organic materials, has hardly been put into practical use, and the current result is that in either case, incineration is the preferred method of treatment.
本発明は、上記に鑑みなされたものであって、固形有機
物を循環ガスで加熱する方式を採用し、かつ、固形有機
物の加熱・乾燥の際に発生する放散ガスを利用した固形
有機物の乾溜方法を提供しようとするものである。The present invention has been made in view of the above, and is a method for dry distilling solid organic matter, which employs a method of heating solid organic matter with circulating gas and utilizes diffused gas generated during heating and drying of solid organic matter. This is what we are trying to provide.
本発明は、固形物の乾溜方法において、(D 固形有
機物を充填体とする充填層を構成し、この充填層内の充
填体の間隙に熱ガスを通して固形有機物の乾溜を行う乾
溜方法において、固形有a物を充填層内で一方向に移動
させ、熱ガスを固形有機物の移動方向と逆方向に流して
同固形有機物の加熱・乾溜を行なった上充填層より排出
し、同排出された熱ガス中に含まれる固形有機物からの
放散ガスを燃焼させた後に上記熱ガスとして充填層に還
流させることを特徴とする。The present invention provides a dry distillation method for solid matter (D) in which a packed bed containing solid organic matter is formed and hot gas is passed between the fillers in the packed bed to dry distill the solid organic matter. The organic matter is moved in one direction within the packed bed, and the hot gas is passed in the opposite direction to the direction of movement of the solid organic matter to heat and dry distill the solid organic matter, which is then discharged from the upper packed bed. The method is characterized in that the gas released from the solid organic matter contained in the gas is combusted and then refluxed to the packed bed as the above-mentioned hot gas.
(2)上記(1)の発明において、気体又は液体燃料を
燃焼するバーナに供給される空気噴流によって、上記充
填層から排出された熱ガスを吸引してバーナ内で固形有
機物からの放散ガスを燃焼させた上、熱ガスを充填層へ
還流させると共に、熱ガスの余剰分をバーナ内のガスの
運動エネルギによって外部に排出することを特徴とする
。(2) In the invention described in (1) above, the hot gas discharged from the packed bed is sucked by the air jet supplied to the burner that burns gas or liquid fuel, and the gas released from the solid organic matter is absorbed in the burner. After combustion, the hot gas is returned to the packed bed, and the surplus of the hot gas is discharged to the outside by the kinetic energy of the gas in the burner.
(3)上記(1)の発明において、充填層より排出され
固形有機物からの放散ガスが燃焼されたガスの一部を取
出して固形有機物を予熱することを特徴とする。(3) The invention according to (1) above is characterized in that a part of the gas discharged from the packed bed and in which the gas released from the solid organic matter is combusted is taken out to preheat the solid organic matter.
上記(1)の本発明では、被処理物の固形有機物を充填
体とする充填層へ供給された熱ガスは、固形有機物の連
続的又は間歇的な移動方向に対し逆方向に流れて、充填
体間の間隙を抜けて充填層から排出される。この間に、
この熱ガスからの給熱によって、固形有機物はその移動
の進行と共に昇温し、水蒸気、有機ガス等を放散し、こ
れらは、熱ガスに混入され、充填層から排出される。In the present invention described in (1) above, the hot gas supplied to the packed bed containing the solid organic matter of the object to be treated flows in the opposite direction to the direction of continuous or intermittent movement of the solid organic matter, and It passes through the gap between the bodies and is expelled from the packed bed. During this time,
With the heat supplied from the hot gas, the temperature of the solid organic matter increases as it moves, and releases water vapor, organic gas, etc., which are mixed with the hot gas and discharged from the packed bed.
充填層から排出された熱ガスは、再び充填層へ還流され
るが、その間において、熱ガス中に含まれる固形有機物
からの放散ガスが燃焼されて熱ガスの温度の回復が行な
われた上で、充填層へ還流され、固形有機物の加熱・乾
溜が行なわれる。このように、本発明(1)では、固形
有機物の加熱・乾溜によって放散されるガスを系外で燃
焼又は処理せずに、系内で燃焼処理して熱ガスの温度を
回復し、固形有機物の効果的な加熱・乾溜が行なわれる
。The hot gas discharged from the packed bed is returned to the packed bed, but during this time, the gas released from the solid organic matter contained in the hot gas is combusted, and the temperature of the hot gas is recovered. The solid organic matter is refluxed to the packed bed, where solid organic matter is heated and dry distilled. As described above, in the present invention (1), the gas released by heating and dry distillation of solid organic matter is not combusted or treated outside the system, but the temperature of the hot gas is recovered by combustion treatment within the system, and the temperature of the hot gas is recovered. Effective heating and dry distillation of
また、固形有機物の移動と熱ガスの流れは逆方向であり
、固形有機物は先づ比較的低温の熱ガスで加熱され、そ
の後更に高温の熱ガスによって加熱されるために、乾溜
度に応じた温度の熱ガスによって無理なく、かつ効率の
よい加熱が行なわれると共に、固形有機物の移動の終点
では、十分な乾溜がなされることになる。In addition, the movement of solid organic matter and the flow of hot gas are in opposite directions, and solid organic matter is first heated by relatively low-temperature hot gas and then further heated by high-temperature hot gas. The hot gas at the temperature provides reasonable and efficient heating, and at the end of the transfer of the solid organic matter, sufficient dry distillation is achieved.
なお、本発明において、固形有機物から放散されるガス
の燃焼に要する空気は、熱ガスの循環系の適宜の位置で
熱ガス中へ供給される。In the present invention, the air required for combustion of the gas emitted from the solid organic matter is supplied into the hot gas at an appropriate position in the hot gas circulation system.
上記(2)の本発明では、上記(1)の本発明において
、充填層から排出される熱ガスは、気体又は液体燃料を
燃焼する空気噴流によってバーナ内に吸引される。In the invention described in (2) above, in the invention described in (1) above, the hot gas discharged from the packed bed is drawn into the burner by an air jet that burns the gas or liquid fuel.
こによって、熱ガスの充填層内の流れが確保されること
になる。This ensures the flow of hot gas within the packed bed.
また、バーナ内で燃料の燃焼熱によって熱ガス中の放散
ガスが燃焼され、ガスの温度が上昇し、温度の上昇した
熱ガスが充填層に還流されて固形有機物の加熱・乾溜が
行なわれる。また更に、バーナにおける燃焼の結果生じ
た余剰の熱ガスは、バーナ内の空気噴流及びガス温度の
上昇によって生じたガスの運動エネルギによって外部へ
排出される。Furthermore, the diffused gas in the hot gas is combusted by the combustion heat of the fuel in the burner, the temperature of the gas rises, and the heated gas is returned to the packed bed to heat and dry distill the solid organic matter. Furthermore, the excess hot gas resulting from combustion in the burner is discharged to the outside by the kinetic energy of the gas generated by the air jet in the burner and the increase in gas temperature.
上記(3)の本発明では、上記(1)の本発明において
、固形有機物からの放散ガスが燃焼された後のガスの一
部を取出して固形有機物を予熱することによって、循環
される熱ガスの余剰分を利用して、充填層内で加熱・乾
溜される固形有機物を予め加熱することによって、熱効
率が向上する。In the present invention (3) above, in the present invention (1) above, the hot gas circulated by taking out a part of the gas after the gas emitted from the solid organic matter is combusted and preheating the solid organic matter. Thermal efficiency is improved by using the surplus to preheat the solid organic matter to be heated and dry distilled in the packed bed.
本発明の第一の実施例を、第1図によって説明する。 A first embodiment of the present invention will be described with reference to FIG.
本実施例は、被処理物としての固形有機物が処理工程中
に形状変化を起す場合又は固形有機物が強固で処理中に
破損を生じにくい場合等に適した固形有機物の乾溜方法
に係る。This embodiment relates to a method for dry distilling solid organic matter suitable for cases where the solid organic matter as a material to be treated changes its shape during the treatment process, or when the solid organic matter is strong and difficult to break during treatment.
1は乾溜処理室で、上蓋3、−下側の底蓋4及び底蓋4
の上方に設けられた締付はロッド6をもつシール板5を
具えている。ゴム等の固形有機物2は、上蓋3から乾溜
処理室1へ供給され、充填層を形成して後述するように
加熱・乾溜処理されながら下方へ移動し、下側の底蓋4
より取出されるようになっている。熱ガスは、ガス給気
口8がら乾溜処理室l内へ入り、充填層を形成する固形
有機物2の間隙を通って上方に流れ、ガス給気口8より
上方に設けられたガス排気ロアを通って乾溜処理室1か
ら排出される。排出された熱ガス中には、固形有機物2
から放散される水蒸気及び有機ガスが混入されている。1 is a dry distillation processing chamber, which includes an upper lid 3, a lower bottom lid 4, and a bottom lid 4.
The clamp provided above comprises a sealing plate 5 with a rod 6. The solid organic matter 2 such as rubber is supplied from the top lid 3 to the dry distillation processing chamber 1, forms a packed layer, and moves downward while being heated and dry distilled as described later, and is transferred to the bottom lid 4 on the lower side.
It is being taken out more and more. The hot gas enters the dry distillation processing chamber l through the gas supply port 8, flows upward through the gap between the solid organic matter 2 forming the packed bed, and passes through the gas exhaust lower provided above the gas supply port 8. and is discharged from the dry distillation treatment chamber 1. The discharged hot gas contains solid organic matter2.
water vapor and organic gases emitted from the water are mixed in.
排出された熱ガスは、バーナ9のガス吸入口13へ供給
される。同バーナ9の一端には、空気と気体又は液体燃
料の噴流管11を備え、インデューサ12及びその下流
側にガス放出開口15が噴流管11に対向して設けられ
、またガス放出開口15の下方にガス排出口14が設け
られている。上記ガス吸入口13は、インデューサ12
の上流側において、バーナ9に開口している。The discharged hot gas is supplied to the gas inlet 13 of the burner 9. One end of the burner 9 is provided with a jet pipe 11 for air and gas or liquid fuel, and an inducer 12 and a gas discharge opening 15 are provided downstream thereof facing the jet pipe 11. A gas exhaust port 14 is provided below. The gas inlet 13 is connected to the inducer 12
The burner 9 is opened on the upstream side of the burner 9 .
一方、加圧ファン10で加圧された空気は熱交換器18
を通って予熱された上、噴流管11へ供給され、気体又
は液体燃料と共に噴流管11からバーナ9内へ噴出され
、この際ガス吸入口13からバーナ9内へ熱ガスを吸引
し、熱ガス中の固形有機物からの放散ガス中の可燃分と
気体又は液体燃料が燃焼し、これによって熱ガスの温度
が上昇する。インデューサ12を通った熱ガスは、ガス
排出口14を経て上記乾溜処理室■のガス給気口8へ還
流し、上記のように下方へ移動する固形有機物2の隙間
を上方に向って流れ、固形有機物2をカウンターフロー
状態で効率よく加熱して乾溜させる。同熱ガスは、上記
したように、ガス排出ロアからバーナ9へ入って加熱さ
れ、乾溜処理室1へ循環する。乾溜処理学1内で下方に
移動中に加熱・乾溜された固形有機物2は、底蓋4より
取出される。On the other hand, the air pressurized by the pressurizing fan 10 is transferred to the heat exchanger 18.
The hot gas is preheated through the gas inlet 13 and then supplied to the jet pipe 11, and is ejected from the jet pipe 11 into the burner 9 together with gas or liquid fuel. The combustible content in the gas emitted from the solid organic matter therein and the gaseous or liquid fuel are combusted, thereby increasing the temperature of the hot gas. The hot gas that has passed through the inducer 12 flows back through the gas outlet 14 to the gas supply port 8 of the dry distillation processing chamber (2), and flows upward through the gap between the solid organic matter 2 moving downward as described above. , solid organic matter 2 is efficiently heated and dry distilled in a counterflow state. As described above, the isothermal gas enters the burner 9 from the gas discharge lower, is heated, and circulates to the dry distillation processing chamber 1. The solid organic matter 2 heated and dry distilled while moving downward in the dry distillation process 1 is taken out from the bottom lid 4.
一方・バーナ9の燃焼ガスの余剰分は、インデューサ1
2で増速されたバーナ9内のガスの運動エネルギーによ
って、噴流管11に対向するガス放出開口15へ押込ま
れ、熱交換器18でバーナ9へ入る空気を予熱する。熱
交換器18を出たガスは、予熱ガス給気口22を経て予
熱室20の下部へ入り、同予熱室20に収容された固形
有機物21を加熱した上、吸引ファン24に吸引されて
、予熱室20の上部の予熱ガス排気口23を経て外部へ
排出される。この外部へ排出されるガスは、固形有機物
より放散されたガスがバーナ9で燃焼されているために
、無害化されている。また、予熱室20で予熱された固
形有機物21は、予熱室20の底部のシール板26を開
くことによって予熱室20から取出され、乾溜処理室1
へ供給される。On the other hand, the excess combustion gas of burner 9 is transferred to inducer 1
The kinetic energy of the gas in the burner 9, accelerated at 2, forces it into the gas discharge opening 15 facing the jet tube 11 and preheats the air entering the burner 9 in a heat exchanger 18. The gas leaving the heat exchanger 18 enters the lower part of the preheating chamber 20 through the preheating gas supply port 22, heats the solid organic matter 21 contained in the preheating chamber 20, and is then sucked into the suction fan 24. The preheating gas is discharged to the outside through the preheating gas exhaust port 23 in the upper part of the preheating chamber 20. This gas discharged to the outside is rendered harmless because the gas released from the solid organic matter is burned in the burner 9. Further, the solid organic matter 21 preheated in the preheating chamber 20 is taken out from the preheating chamber 20 by opening the seal plate 26 at the bottom of the preheating chamber 20, and is removed from the dry distillation processing chamber 20.
supplied to
なお、30は、処理後の固形有機物2の仕上用の乾溜処
理室1への空気供給口である。また31は、乾溜処理室
1とバーナ9との間に配置された固形有機物からの放散
ガス中の有機分解ガスの冷却液化装置であり、乾溜分の
多い草木質等を処理する場合に、有機分解ガスを液化し
て再利用する目的等に用いられ、32は同冷却液化装置
31の冷却用ウォーターボックスである。33は、熱ガ
ス循環用の補助ファンであり、16.17.28はそれ
ぞれ乾溜処理室に入る熱ガスの温度、乾溜処理室内の温
度及び予熱室内の温度を検出する温度計であり、25は
予熱室への補給用空気の吸入管である。Note that 30 is an air supply port to the dry distillation processing chamber 1 for finishing the solid organic matter 2 after processing. Further, 31 is a cooling and liquefaction device for organic decomposed gas in the gas emitted from solid organic matter, which is disposed between the dry distillation processing chamber 1 and the burner 9. It is used for the purpose of liquefying and reusing cracked gas, and 32 is a cooling water box of the cooling liquefaction device 31. 33 is an auxiliary fan for hot gas circulation, 16, 17, and 28 are thermometers that detect the temperature of the hot gas entering the dry distillation treatment chamber, the temperature inside the dry distillation treatment chamber, and the temperature inside the preheating chamber, respectively; This is a suction pipe for supplying air to the preheating chamber.
以上説明したように、本実施例では、乾溜処理室1にお
いて、固形有機物2と熱ガスは互いに逆方向に移動して
効率良く固形有機物2の加熱・乾溜が行なわれる。また
固形有機物2の充填層を出た熱ガスは、バーナ9へ吸引
されて固形有機物2からの放散ガスを燃焼させると共に
昇温された上で乾溜処理室lへ還流して、固形有機物を
加熱・乾溜する。熱ガスは、以上の通り乾溜処理室1を
循環する閉鎖系を構成しているために、熱効率を向上さ
せることができる。As explained above, in this embodiment, the solid organic matter 2 and the hot gas move in opposite directions in the dry distillation processing chamber 1, so that the solid organic matter 2 is efficiently heated and dry distilled. In addition, the hot gas leaving the packed bed of solid organic matter 2 is sucked into the burner 9, burns the gas released from the solid organic matter 2, and is raised in temperature, and then refluxed to the dry distillation treatment chamber 1 to heat the solid organic matter.・Dry distillation. Since the hot gas constitutes a closed system in which it circulates through the dry distillation treatment chamber 1 as described above, thermal efficiency can be improved.
また、バーナ9における燃焼及び乾溜処理室lにおける
固形有機物2からのガスの放散に伴って生ずる熱ガスの
余剰分は、インデューサ12で増速されたバーナ9内の
ガスの運動エネルギによってガス放出開口15へ押し込
まれ、熱交換器18でバーナ9へ供給される空気を予熱
し、更に予熱室20において固形有機物21を予熱する
ことによって、熱回収が図られ、熱効率が向上する。更
に、予熱室20から外部へ排出されるガスは、バーナ9
によって、固形有機物2からの放散ガスが燃焼処理され
て無害化されており、環境上も問題を生ずることがない
。Further, the surplus of hot gas generated due to the combustion in the burner 9 and the dissipation of gas from the solid organic matter 2 in the dry distillation processing chamber 1 is released by the kinetic energy of the gas in the burner 9, which is accelerated by the inducer 12. By preheating the air forced into the opening 15 and supplied to the burner 9 in the heat exchanger 18, and further preheating the solid organic matter 21 in the preheating chamber 20, heat recovery is achieved and thermal efficiency is improved. Further, the gas discharged from the preheating chamber 20 to the outside is transferred to the burner 9.
As a result, the gas emitted from the solid organic matter 2 is burned and rendered harmless, and there is no problem with the environment.
また更に、本実施例では、バーナ9のガス放出開口15
下流の通気抵抗を調節することによって、熱ガスの循環
系内の圧力を外気以下に抑制することができ、これによ
って、乾溜処理室l内等の熱ガスの外部への逸散が防止
され、環境保全上の問題の発生を防ぐことができる。Furthermore, in this embodiment, the gas discharge opening 15 of the burner 9 is
By adjusting the downstream ventilation resistance, the pressure in the hot gas circulation system can be suppressed to below the outside air, thereby preventing hot gas from escaping to the outside, such as in the dry distillation processing chamber l. It is possible to prevent the occurrence of environmental conservation problems.
本発明の第二の実施例を、第2図によって説明する。A second embodiment of the present invention will be described with reference to FIG.
本実施例は、高級木炭の製造等処理される固形有機物の
破損、亀裂を防止する必要がある場合に適した固形有機
物の乾溜方法に係る。This embodiment relates to a dry distillation method for solid organic matter suitable for cases where it is necessary to prevent breakage and cracking of solid organic matter being processed, such as in the production of high-grade charcoal.
本実施例において、上記第1図に示す第一の実施例と同
一の部分は、第2図中同一の符号が付されており、その
説明を省略し、以下第一の実施例と異る部分について説
明する。In this embodiment, the same parts as in the first embodiment shown in FIG. 1 above are designated by the same reference numerals in FIG. Let me explain the parts.
40は、固形有機物である木材2を収容する容器であり
、その底部には通気板41とフォークリフトのフォーク
挿入部43が設けられている。乾溜処理室1は、上部に
ガス排出ロアが、下部にガス給気口8が設けられ、また
底部の通風+ff142a及び中部の通風板42bによ
って上下2段に仕切られている。Reference numeral 40 denotes a container for storing wood 2, which is a solid organic substance, and a ventilation plate 41 and a fork insertion part 43 of a forklift are provided at the bottom of the container. The dry distillation processing chamber 1 is provided with a gas discharge lower in the upper part and a gas supply port 8 in the lower part, and is partitioned into two upper and lower stages by the ventilation +ff 142a at the bottom and the ventilation plate 42b at the middle.
本実施例では、通風板42a、42b上に上下2個の容
器40をフォークリフトを用いて載置し、熱ガスを第一
実施例と同様に乾溜処理室1→バーナ9→乾溜処理室1
と循環させて、容器40内の木材2を加熱・乾溜させて
炭化し、木炭とする。In this embodiment, two upper and lower containers 40 are placed on the ventilation plates 42a and 42b using a forklift, and hot gas is passed through the dry distillation chamber 1→burner 9→dry distillation chamber 1 in the same manner as in the first embodiment.
The wood 2 in the container 40 is heated, dry distilled, and carbonized to produce charcoal.
本実施例においては、バーナ9から熱交換器18を通っ
たガスを、補給用空気の吸入管25の弁25との開度を
調整することによって空気で薄めて温度を下げた上予熱
室20へ導入し、同予熱室20内で木材21を緩徐に乾
燥し、150″C程度迄予熱を行ない、予熱された木材
21をシール板26を開いて取出して乾溜処理室1へ装
入する前に用意された予備の容器40に充填する。一方
乾溜処理室l内では下段の容器40内において木材の乾
溜が進み、上段の容器40内においても下段に遅れなが
ら木材の乾溜が進行している。下段の容器40内の木材
2の乾溜が適当な水準迄進行した時、前面の扉を開いて
下段の容器40を炭化仕上台44の上に移し替える。上
段の容器40を下段に移し替え、上記予熱処理を終えた
木材を収容した予備の容器40を上段へ装入する。In this embodiment, the gas that has passed through the heat exchanger 18 from the burner 9 is diluted with air by adjusting the opening degree of the replenishment air suction pipe 25 with the valve 25, and the temperature is lowered in the upper preheating chamber 20. The wood 21 is slowly dried in the preheating chamber 20 and preheated to about 150''C, and the preheated wood 21 is taken out by opening the seal plate 26 before being charged into the dry distillation treatment chamber 1. On the other hand, in the dry distillation processing chamber 1, dry distillation of wood is progressing in the lower container 40, and dry distillation of wood is also progressing in the upper container 40, lagging behind the lower container. When the dry distillation of the wood 2 in the lower container 40 has progressed to an appropriate level, the front door is opened and the lower container 40 is transferred onto the carbonization finishing table 44.The upper container 40 is transferred to the lower container. Then, the spare container 40 containing the wood that has been preheated is loaded into the upper stage.
この上で扉を閉めて乾溜処理室lは再び乾溜進行に入る
。一方炭化仕上台44上に据えられた容器40は、炭化
仕上台44の燃焼口45から乾溜仕上に必要な熱気ない
し空気の供給を受けて、より高温の炭化仕上に入る。こ
の際炭化仕上台44の内部に屑炭を投入し、炭化仕上に
おける製品酸化を抑制することもできる。After this, the door is closed and the dry distillation processing chamber 1 starts dry distillation again. On the other hand, the container 40 placed on the carbonization finishing table 44 receives hot air or air necessary for dry distillation finishing from the combustion port 45 of the carbonizing finishing table 44, and enters carbonization finishing at a higher temperature. At this time, it is also possible to put scrap charcoal inside the carbonization finishing table 44 to suppress product oxidation during carbonization finishing.
本実施例においては、第一の実施例と同様熱ガスは閉鎖
系をなしており、また余剰の熱ガスは熱交換器18、予
熱室20を通る際にその熱回収が行なわれるために、熱
効率が上昇する。また乾溜処理室1内では、上段で容器
40内の木質固形物を比較的低温の熱ガスによって加熱
・乾溜処理した後、容器40を下段へ移して、乾溜処理
室1内へ入る高温の熱ガスによって加熱・乾溜すること
によって、木材2はその乾溜程度に応じた温度の熱ガス
によって処理されることになり、効率のよい乾溜が行な
われると共に、木材2の象、激な温度変化を避けて、破
損・亀裂の発生を防止することができる。In this embodiment, as in the first embodiment, the hot gas forms a closed system, and the excess hot gas is recovered as it passes through the heat exchanger 18 and the preheating chamber 20. Thermal efficiency increases. In the dry distillation chamber 1, the wood solids in the container 40 are heated and dry distilled in the upper stage using relatively low-temperature hot gas, and then the container 40 is moved to the lower stage where high-temperature heat enters the dry distillation chamber 1. By heating and dry distilling the wood 2 with gas, the wood 2 is treated with hot gas at a temperature that corresponds to the degree of dry distillation, resulting in efficient dry distillation and avoiding drastic temperature changes. This can prevent damage and cracks from occurring.
また更に、木材は、予熱室20で低温のガスで乾燥・予
熱された上で、乾溜処理室1で加熱・乾溜処理を受ける
ために、熱効率を向上させることができ、また、破損・
亀裂のない乾溜を行なうことができる。Furthermore, since the wood is dried and preheated with low-temperature gas in the preheating chamber 20 and then heated and subjected to dry distillation treatment in the dry distillation treatment chamber 1, it is possible to improve thermal efficiency and prevent damage.
Dry distillation can be performed without cracks.
〔発明の効果]
以上説明したように、本発明は次の効果を奏することが
できる。[Effects of the Invention] As explained above, the present invention can have the following effects.
(1)固形有機物を加熱・乾溜する熱ガスの温度を同熱
ガス中の固形有機物からの放散ガスを燃焼させて回復し
た上、固形有機物の充填層へ循環還流させるために熱効
率が上昇する。(1) The temperature of the hot gas for heating and dry distilling the solid organic matter is recovered by burning the gas released from the solid organic matter in the isothermal gas, and the thermal efficiency is increased because the gas is circulated and refluxed to the packed bed of the solid organic matter.
(2)固形有機物の連続的又は間歇的移動方向と熱ガス
の流れの方向は逆であるために、固形有機物の乾溜変に
応じた温度の熱ガスによって、無理のない効率的な乾溜
が行なうことができる。(2) Since the direction of continuous or intermittent movement of solid organic matter and the flow direction of hot gas are opposite, the hot gas at a temperature corresponding to the dry distillation of solid organic matter allows for easy and efficient dry distillation. be able to.
(3)熱ガスはバーナの空気噴流によってバーナ内へ吸
引されることによって、熱ガスの流れが確保されると共
に、余剰の無害化されたガスをバーナ内のガスの運動エ
ネルギによって排出することができる。(3) Hot gas is drawn into the burner by the air jet of the burner, ensuring a flow of hot gas, and excess detoxified gas can be discharged by the kinetic energy of the gas in the burner. can.
(4)固形有機物からの放散ガスを燃焼したガスの一部
を取出して固形有機物を予熱することによって、余剰分
の熱ガスの熱を回収することができる。(4) By preheating the solid organic matter by extracting a part of the gas from the combustion of the gas released from the solid organic matter, the heat of the excess hot gas can be recovered.
第1図は本発明の第一の実施例の系統図、第2図は本発
明の第二の実施例の系統図である。
1・・・乾溜処理室、 2・・・固形有機物、7・
・・ガス排気口、
9・・・バーナ、
I2・・・インデエーサ、
15・・・ガス放出開口、
20・・・予熱室、
40・・・容器、
44・・・炭化仕上台。FIG. 1 is a system diagram of a first embodiment of the invention, and FIG. 2 is a system diagram of a second embodiment of the invention. 1... Dry distillation processing chamber, 2... Solid organic matter, 7.
...Gas exhaust port, 9...Burner, I2...Indeer, 15...Gas discharge opening, 20...Preheating chamber, 40...Container, 44...Carbonization finishing table.
Claims (3)
充填層内の充填体の間隙に熱ガスを通して固形有機物の
乾溜を行う乾溜方法において、固形有機物を充填層内で
一方向に移動させ、熱ガスを固形有機物の移動方向と逆
方向に流して同固形有機物の加熱・乾溜を行なった上充
填層より排出し、同排出された熱ガス中に含まれる固形
有機物からの放散ガスを燃焼させた後に上記熱ガスとし
て充填層に還流させることを特徴とする固形有機物の乾
溜方法。(1) In a dry distillation method in which a packed bed is formed with solid organic matter as a filler and hot gas is passed between the fillers in the packed bed to dry distill the solid organic matter, the solid organic matter is moved in one direction within the packed bed. The hot gas is then flowed in the opposite direction to the direction of movement of the solid organic matter to be discharged from the upper packed bed where the solid organic matter has been heated and dry distilled, and the gas released from the solid organic matter contained in the discharged hot gas is A method for dry distilling solid organic matter, which comprises refluxing the solid organic matter into a packed bed as the hot gas after combustion.
空気噴流によって、上記充填層から排出された熱ガスを
吸引してバーナ内で固形有機物からの放散ガスを燃焼さ
せた上、熱ガスを充填層へ還流させると共に、熱ガスの
余剰分をバーナ内のガスの運動エネルギによって外部に
排出することを特徴とする請求項(1)に記載の固形有
機物の乾溜方法。(2) An air jet supplied to a burner that burns gas or liquid fuel sucks in the hot gas discharged from the packed bed, burns the gas released from the solid organic matter in the burner, and then converts the hot gas into 2. The dry distillation method of solid organic matter according to claim 1, wherein the hot gas is refluxed to the packed bed and the surplus of the hot gas is discharged to the outside by the kinetic energy of the gas in the burner.
燃焼されたガスの一部を取出して固形有機物を予熱する
ことを特徴とする請求項(1)に記載の固形有機物の乾
溜方法。(3) The method for dry distilling solid organic matter according to claim (1), characterized in that the solid organic matter is preheated by taking out a part of the gas discharged from the packed bed and combusted to emit gas from the solid organic matter.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1144093A JPH039990A (en) | 1989-06-08 | 1989-06-08 | Carbonization of organic solid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1144093A JPH039990A (en) | 1989-06-08 | 1989-06-08 | Carbonization of organic solid |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH039990A true JPH039990A (en) | 1991-01-17 |
Family
ID=15354049
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1144093A Pending JPH039990A (en) | 1989-06-08 | 1989-06-08 | Carbonization of organic solid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH039990A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008144179A (en) * | 2007-11-30 | 2008-06-26 | Minoru Sakamoto | Container which is packed with charcoal material outside kiln, is brought in kiln, and burns charcoal |
| RU2525941C2 (en) * | 2009-05-01 | 2014-08-20 | Зеотек Инк. | Vehicle with liquid waste filtration system |
| US9702481B2 (en) | 2009-08-17 | 2017-07-11 | Dunan Microstaq, Inc. | Pilot-operated spool valve |
-
1989
- 1989-06-08 JP JP1144093A patent/JPH039990A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008144179A (en) * | 2007-11-30 | 2008-06-26 | Minoru Sakamoto | Container which is packed with charcoal material outside kiln, is brought in kiln, and burns charcoal |
| RU2525941C2 (en) * | 2009-05-01 | 2014-08-20 | Зеотек Инк. | Vehicle with liquid waste filtration system |
| US9702481B2 (en) | 2009-08-17 | 2017-07-11 | Dunan Microstaq, Inc. | Pilot-operated spool valve |
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