JP4384378B2 - Organic waste drying apparatus and drying method - Google Patents

Organic waste drying apparatus and drying method Download PDF

Info

Publication number
JP4384378B2
JP4384378B2 JP2001248049A JP2001248049A JP4384378B2 JP 4384378 B2 JP4384378 B2 JP 4384378B2 JP 2001248049 A JP2001248049 A JP 2001248049A JP 2001248049 A JP2001248049 A JP 2001248049A JP 4384378 B2 JP4384378 B2 JP 4384378B2
Authority
JP
Japan
Prior art keywords
moisture
organic waste
vaporization container
pressure
container
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 - Lifetime
Application number
JP2001248049A
Other languages
Japanese (ja)
Other versions
JP2003053297A (en
Inventor
修一 吉田
昭光 平木
哲也 柳瀬
正巳 野々川
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.)
Metawater Co Ltd
Original Assignee
Metawater 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 Metawater Co Ltd filed Critical Metawater Co Ltd
Priority to JP2001248049A priority Critical patent/JP4384378B2/en
Publication of JP2003053297A publication Critical patent/JP2003053297A/en
Application granted granted Critical
Publication of JP4384378B2 publication Critical patent/JP4384378B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Landscapes

  • Drying Of Solid Materials (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、有機性廃棄物の乾燥方法および乾燥装置の改良に関するものである。
【0002】
【従来の技術】
従来、水分を含む有機性廃棄物を乾燥する方法および装置としては、対象物に熱風を接触させて水分を除去する、直接通風式乾燥が多用されている。また、対象物を加熱する手段が併用され、その熱源に、水蒸気や焼却装置の回収熱などが利用されている。
【0003】
これらの手段は、加熱下であるが常圧下で大量の空気によって水分を除去しようとするものであり、蒸発水分を含む大量の排ガスが発生することになる。さらに、有機性廃棄物を乾燥処理する場合、臭気成分の発生が避けられないので、この臭気成分が前記した大量の排ガスに混入する結果、大量の臭気含有ガスとして排出されるという問題があった。また、それを避けるためには、焼却炉による脱臭燃焼処理などを行う必要があった。
【0004】
【発明が解決しようとする課題】
本発明は、上記の問題点を解決するためになされたものであり、臭気含有ガスの発生量を最小限に抑えながら水分を含む有機性廃棄物を乾燥できる乾燥装置および乾燥方法を提供する。
【0005】
【課題を解決するための手段】
(第1発明)
上記の問題は、供給された有機性廃棄物を密閉状態で加熱し、含まれる水分を気化処理する金属製容器であって、上部には、有機性廃棄物供給フィーダに接続された供給手段と自動調圧機に接続されたガス排出手段を備え、内部には、攪拌手段を配設し、底部は、逆円錐形状に形成され、その下端部には、昇降操作される開閉栓を開くことにより水分気化容器の内圧と外部圧力との差圧を利用して乾燥物を排出する内容物排出手段を形成し、側壁部には、内部を加熱するための加熱手段を配設した水分気化容器を具備したことを特徴とする本発明の有機性廃棄物の乾燥装置によって解決することができる。
この有機性廃棄物の乾燥装置は、前記水分気化容器を複数併設して、時差運転可能とした形態に好ましく具体化され得る。
【0006】
(第2発明)
また、上記の問題は、次の工程を繰り返し行うことを特徴とする本発明の有機性廃棄物の乾燥方法によっても解決することができる。
(1)水分を含む有機性廃棄物を水分気化容器に供給して、該水分気化容器を閉鎖する廃棄物供給工程。(2)水分気化容器内の有機性廃棄物を100℃〜374℃の範囲に加熱し、水分を気化させるとともに、水分気化容器内部の圧力を処理温度における飽和蒸気圧以下になるように、水蒸気を排出して調整する加熱調圧工程。(3)水分気化の完了後、温度条件を維持して、水分気化容器内の水蒸気を排出して、内圧を乾燥物の排出に要する最小限の圧力まで減圧するガス放出工程。(4)水分気化容器底部の開閉栓を開き、水分気化容器の内圧と外部圧力との差圧を利用して乾燥物を排出する乾燥物排出工程。
【0007】
この有機性廃棄物の乾燥方法は、水分気化容器外に排出された乾燥物を貯留槽に収集するとともに、水分気化容器から排出した排ガスをコンデンサで冷却し、凝縮した水分はドレンタンクに収集して、水蒸気を除去した後の臭気ガス成分を触媒塔で処理する形態に好ましく具体化できる。
【0008】
【発明の実施の形態】
次に、本発明の有機性廃棄物の乾燥方法および乾燥装置に係る実施形態について、図1を参照しながら説明するが、先ず、第1発明である本発明の乾燥装置から説明する。
【0009】
(第1発明)
この乾燥装置は、供給された有機性廃棄物を密閉状態で加熱し気化処理する金属製水分気化容器1を中心にしたシステムであって、この水分気化容器1は、天井蓋部11、逆円錐形状の底部12を有する円筒形状の側壁部13から構成されている。
【0010】
そして、前記天井蓋部11には、被処理物である有機性廃棄物の供給フィーダ21に供給機22を介して接続された供給口14が設けられている。なお、この供給口14は、供給機22の下流の開閉弁23によって封止可能とされている。
【0011】
さらに、前記天井蓋部11には、自動弁41aを含む自動調圧機41に接続されたガス排出口15が備えられている。なお、水分気化容器から排出される水蒸気を主とする排ガスは、この自動調圧機41によって排出が制御される。そして、コンデンサ42に導かれ冷却され、凝縮した水分は下方のドレンタンク43に収集されるとともに、水分が除かれ通過した臭気成分を含むガス分は、触媒塔44に導かれて処理され、放出されるよう、排気系が設けられている。
【0012】
次に、水分気化容器1内部には、攪拌翼52を配設し、天井蓋部11に配設した攪拌モータ51によって回転させ、被処理物を攪拌可能としている。
また、水分気化容器1の側壁部13の外周には、内部を水の臨界温度である374℃までに加熱するための加熱ヒータ61が配設されている。図1では、底部斜面の外周にも加熱ヒータ61を配設している。この加熱ヒータ61には、電気抵抗加熱などの通常の加熱手段が適用される。
【0013】
また、水分気化容器1底部12は、前述の通り下方に縮径する逆円錐形状に形成され、その下端部には、外部から昇降操作される開閉栓71を備えた内容物排出口16が形成されている。そして、内容物排出口16は、シュート72を通じてフィーダタンク73に接続している。
【0014】
かくして、水分気化容器1内に供給された所定量の有機性廃棄物を、密閉状態で所定の温度に加熱し、その水分を気化処理することができる。そして、気化処理後の乾燥物は、水分気化容器外に排出され、一旦フィーダタンク73に貯められ、逐次に下方のコンベヤ74によって貯留槽75に収集されるよう、排出系が配設されている。
【0015】
本発明の有機性廃棄物の乾燥装置は、以上説明したように、前記水分気化容器1によって被処理物をバッチ処理する装置であるから、前記水分気化容器1の他に同様な水分気化容器1aを併設するように、複数台の水分気化容器を併設して、時差運転可能とすれば、需要に応じた処理能力の装置に設定できるなどの利点が得られる。
【0016】
(第2発明)
次に、以上説明した乾燥装置によって、本発明の有機性廃棄物の乾燥方法を説明すると、本発明は、次の工程(1)〜(4)を繰り返し行う点を特徴としている。
(1)廃棄物供給工程
供給フィーダ21中の水分を含む有機性廃棄物の所定量を、供給機22を介して供給口14から水分気化容器1に供給し、経路の開閉弁23を閉じて供給口14からの逆流を封止し、該水分気化容器1を閉鎖する。この場合、本発明では、有機性廃棄物の固形分濃度として最大20%の高濃度に脱水、濃縮処理した被処理物が適用可能である。また、常圧の水分気化容器1に有機性廃棄物を供給するので、特別な供給動力が必要でない利点がある。
【0017】
(2)加熱調圧工程
水分気化容器1内に供給された有機性廃棄物を加熱ヒータ61によって所定の温度、例えば100℃〜374℃の範囲に加熱して、有機性廃棄物が含む水分を気化させる。この場合、水分気化容器1内を予め所定の温度に加熱しておいて、その中に有機性廃棄物を供給して、加熱を促進するのがよい。さらに、水分気化容器1内下部に配設した攪拌翼52を攪拌モータ51によって回転させ、被処理物を攪拌することによって、内容物の解砕し水分気化を促進するのが好ましい。
【0018】
かくして、本発明では有機性廃棄物の含有水分が少ないので、昇温のためのエネルギも少なく済む利点が得られる。また、温度上昇にともない、容器内圧も上昇するが、処理温度における飽和蒸気圧以下、例えば、300℃、100気圧に保つように、ガス排出口15に接続された自動調圧機41の自動弁41aによって、発生した水蒸気の排出を調整するものとする。
【0019】
(3)ガス放出工程
前記の水分気化の終了後、好ましくはその温度条件を維持して、水分気化容器1内の発生水蒸気をガス排出口15から排出して、内圧を弱プラス圧まで減圧する。この場合、経路のバイパス弁41bを開閉して調整するのが好ましい。また、前記弱プラス圧の内圧は、後記の乾燥物の排出に要する最小限の圧力に設定すればよい。このようにして、水分気化容器内の水分を水蒸気として排出するので、内部には粉体化した乾燥物のみが残留することになり、その後の処理が容易になる利点が得られる。
本発明では、前記加熱調圧工程、ガス放出工程において、有機性廃棄物が含む水分を水蒸気の形態で排出するので、従来の乾燥機のような大量の乾燥用空気からなる排ガスを発生することがないという利点が得られる。
【0020】
(4)乾燥物排出工程
水分気化容器1底部の内容物排出口16に設けられている開閉栓71を開き、前記弱プラス圧の内圧を利用して粉体化した乾燥物を排出する。かくして、水分除去後の粉体化した乾燥物を内外の圧力差のみで取り出すことができるのである。排出された乾燥物は、シュート72を通じてフィーダタンク73に一時滞留させ、必要に応じて、コンベヤ74によって貯留槽75に集約するものとする。
【0021】
さらに、本発明の有機性廃棄物の乾燥方法では、水分気化容器1から排出した水蒸気をコンデンサ42で冷却し、コンデンサ42で凝縮した水分はドレンタンク43に収集する。かくして水分を除去したガスに含まれる臭気成分については、触媒塔44で処理するのが好ましい。このように、コンデンサで水分を除去すれば、臭気成分を含むガス量は、極く少量となるので、脱臭処理が容易になるという利点が得られる。
【0022】
また、本発明の有機性廃棄物の乾燥方法は、以上説明したように、前記水分気化容器1によって被処理物をバッチ処理するものであるから、前記水分気化容器1の他に同様な水分気化容器1aを併設するように、複数台を併設して、時差運転すれば、処理能力を適宜に増加させることができる利点が得られる。
【0023】
【発明の効果】
本発明の有機性廃棄物の乾燥方法および装置は、以上説明したように構成されているので、有機性廃棄物が含む水分を気化するに際して、乾燥用空気を使用しないので臭気含有ガスの発生量を最小限に制御するとともに、乾燥物を得ることができる。従って、臭気洩れが防止でき、脱臭処理も極めて容易になるという効果がある。さらに、排出水蒸気をコンデンサで凝縮すれば、臭気含有ガスの発生量をさらに減らすことが可能になるなどの優れた効果がある。よって本発明は、従来の問題点を解消した有機性廃棄物の乾燥方法および装置として、工業的価値はきわめて大なるものがある。
【図面の簡単な説明】
【図1】本発明を説明するための乾燥装置の要部フロー図。
【符号の説明】
1 水分気化容器、11 天井蓋部、12 底部、13 側壁部、14 供給口、15 ガス排出口、16 内容物排出口、21 供給フィーダ、22 供給機、23 開閉弁、41 自動調圧機、41a 自動弁、42 コンデンサ、43 ドレンタンク、44 触媒塔、51 攪拌モータ、52 攪拌翼、61 加熱ヒータ、71 開閉栓、72 シュート、73 フィーダタンク
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to an organic waste drying method and an improved drying apparatus.
[0002]
[Prior art]
Conventionally, as a method and apparatus for drying organic waste containing moisture, direct ventilation drying in which hot air is brought into contact with an object to remove moisture has been frequently used. In addition, a means for heating the object is used in combination, and steam, recovered heat of the incinerator, or the like is used as the heat source.
[0003]
These means are intended to remove moisture with a large amount of air under heating but under normal pressure, and a large amount of exhaust gas containing evaporated water is generated. Furthermore, when organic waste is dried, the generation of odor components is unavoidable, and as a result, the odor components are mixed into the above-described large amount of exhaust gas, resulting in a problem that the odor component is discharged as a large amount of odor-containing gas. . Moreover, in order to avoid it, it was necessary to perform the deodorizing combustion process by an incinerator.
[0004]
[Problems to be solved by the invention]
The present invention has been made to solve the above problems, and provides a drying apparatus and a drying method capable of drying organic waste containing moisture while minimizing the generation amount of odor-containing gas.
[0005]
[Means for Solving the Problems]
(First invention)
The above problem is a metal container that heats the supplied organic waste in a sealed state and vaporizes the contained water, and the upper part includes supply means connected to the organic waste supply feeder. and a gas discharge means connected to the self-intensifier, inside, arranged a stirring means, a bottom is formed in an inverted conical shape, in its lower end, by opening the shutoff cock being elevation operating A content discharge means for discharging dry matter is formed by utilizing the pressure difference between the internal pressure and the external pressure of the moisture vaporization container, and a moisture vaporization container provided with a heating means for heating the inside is provided on the side wall. The problem can be solved by the organic waste drying apparatus of the present invention.
This organic waste drying apparatus can be preferably embodied in a form in which a plurality of the water vaporization containers are provided so as to be capable of time difference operation.
[0006]
(Second invention)
Moreover, said problem can be solved also by the drying method of the organic waste of this invention characterized by repeating the following process.
(1) A waste supply step of supplying organic waste containing moisture to a moisture vaporization container and closing the moisture vaporization container. (2) The organic waste in the moisture vaporization container is heated to a range of 100 ° C. to 374 ° C. to vaporize the moisture, and the water vapor is adjusted so that the pressure inside the moisture vaporization container is equal to or lower than the saturated vapor pressure at the treatment temperature. Heating and adjusting process that discharges and adjusts. (3) A gas release step of maintaining the temperature condition and discharging the water vapor in the water vaporization container to reduce the internal pressure to the minimum pressure required for discharging the dry matter after the completion of the water vaporization. (4) A dry matter discharge step of opening the open / close stopper at the bottom of the moisture vaporization container and discharging the dry matter using a differential pressure between the internal pressure and the external pressure of the moisture vaporization container.
[0007]
In this organic waste drying method, dry matter discharged outside the moisture vaporization container is collected in a storage tank, exhaust gas discharged from the moisture vaporization container is cooled by a condenser, and condensed moisture is collected in a drain tank. Thus, the odor gas component after removing the water vapor can be preferably embodied in a form in which it is treated in the catalyst tower.
[0008]
DETAILED DESCRIPTION OF THE INVENTION
Next, an embodiment of the organic waste drying method and drying apparatus according to the present invention will be described with reference to FIG. 1. First, the drying apparatus according to the first invention will be described.
[0009]
(First invention)
This drying apparatus is a system centered on a metal moisture vaporization container 1 that heats and vaporizes the supplied organic waste in a sealed state. The moisture vaporization container 1 includes a ceiling lid 11 and an inverted cone. It is comprised from the cylindrical side wall part 13 which has the shape bottom part 12. As shown in FIG.
[0010]
The ceiling lid portion 11 is provided with a supply port 14 connected to a supply feeder 21 for organic waste, which is an object to be processed, through a feeder 22. The supply port 14 can be sealed by an on-off valve 23 downstream of the supply machine 22.
[0011]
Further, the ceiling lid portion 11 is provided with a gas discharge port 15 connected to an automatic pressure regulator 41 including an automatic valve 41a. Note that the automatic pressure regulator 41 controls the discharge of the exhaust gas mainly composed of water vapor discharged from the moisture vaporization container. Then, the condensed moisture is led to the condenser 42 and cooled, and the condensed moisture is collected in the lower drain tank 43, and the gas component including the odor component which is removed from the moisture is led to the catalyst tower 44 to be processed and discharged. An exhaust system is provided.
[0012]
Next, a stirring blade 52 is disposed inside the moisture vaporization container 1 and is rotated by a stirring motor 51 disposed in the ceiling lid portion 11 so that the workpiece can be stirred.
In addition, a heater 61 for heating the interior up to 374 ° C., which is the critical temperature of water, is disposed on the outer periphery of the side wall 13 of the moisture vaporization container 1. In FIG. 1, the heater 61 is also arranged on the outer periphery of the bottom slope. A normal heating means such as electric resistance heating is applied to the heater 61.
[0013]
Further, the bottom portion 12 of the water vaporization container 1 is formed in an inverted conical shape whose diameter is reduced downward as described above, and a content discharge port 16 having an opening / closing stopper 71 that is operated up and down from the outside is formed at the lower end portion thereof. Has been. The content discharge port 16 is connected to the feeder tank 73 through the chute 72.
[0014]
Thus, a predetermined amount of organic waste supplied into the moisture vaporization container 1 can be heated to a predetermined temperature in a sealed state to vaporize the moisture. The dried product after the vaporization process is discharged out of the moisture vaporization container, temporarily stored in the feeder tank 73 , and sequentially collected in the storage tank 75 by the lower conveyor 74. .
[0015]
As described above, the organic waste drying apparatus of the present invention is an apparatus that batch-processes the objects to be processed by the moisture vaporization container 1, and therefore, the moisture vaporization container 1a similar to the moisture vaporization container 1 is used. If a plurality of moisture vaporization containers are provided side by side so that the time difference operation is possible, an advantage can be obtained that the apparatus can be set to a processing capacity according to demand.
[0016]
(Second invention)
Next, the organic waste drying method of the present invention will be described using the drying apparatus described above. The present invention is characterized in that the following steps (1) to (4) are repeated.
(1) Waste supply step A predetermined amount of organic waste containing water in the supply feeder 21 is supplied from the supply port 14 to the moisture vaporization container 1 via the supply device 22, and the path opening / closing valve 23 is closed. The backflow from the supply port 14 is sealed, and the water vaporization container 1 is closed. In this case, in the present invention, an object to be processed that has been dehydrated and concentrated to a maximum concentration of 20% as the solid content concentration of the organic waste can be applied. In addition, since the organic waste is supplied to the moisture vaporizing container 1 at normal pressure, there is an advantage that no special supply power is required.
[0017]
(2) Heating and regulating step The organic waste supplied into the moisture vaporization container 1 is heated to a predetermined temperature, for example, in the range of 100 ° C. to 374 ° C. by the heater 61, and the moisture contained in the organic waste is reduced. Vaporize. In this case, it is preferable to heat the moisture vaporization container 1 to a predetermined temperature in advance and supply organic waste therein to promote heating. Furthermore, it is preferable to disintegrate the contents and promote moisture vaporization by rotating the agitating blades 52 disposed in the lower part of the moisture vaporizing container 1 by the agitating motor 51 and agitating the workpiece.
[0018]
Thus, in the present invention, since the organic waste contains less water, there is an advantage that less energy is required for raising the temperature. As the temperature rises, the internal pressure of the container also rises. However, the automatic valve 41a of the automatic pressure regulator 41 connected to the gas outlet 15 is maintained at a saturated vapor pressure or lower, eg, 300 ° C. and 100 atm. To adjust the discharge of the generated water vapor.
[0019]
(3) Gas release step After the above-described moisture vaporization is completed, preferably the temperature condition is maintained, and the generated water vapor in the moisture vaporization container 1 is discharged from the gas discharge port 15 to reduce the internal pressure to a weak positive pressure. . In this case, it is preferable to adjust by opening and closing the bypass valve 41b of the path. Further, the internal pressure of the weak positive pressure may be set to the minimum pressure required for discharging the dried material described later. In this way, since the water in the water vaporization container is discharged as water vapor, only the powdered dry matter remains in the interior, and the advantage of facilitating subsequent processing can be obtained.
In the present invention, the moisture contained in the organic waste is discharged in the form of water vapor in the heating and pressure adjusting step and the gas releasing step, so that an exhaust gas composed of a large amount of drying air like a conventional dryer is generated. The advantage is that there is no.
[0020]
(4) Dry matter discharge process The opening / closing stopper 71 provided in the content discharge port 16 at the bottom of the water vaporization container 1 is opened, and the dry matter pulverized is discharged using the internal pressure of the weak plus pressure. Thus, the powdered dried product after moisture removal can be taken out only by the pressure difference between the inside and outside. The discharged dry matter is temporarily retained in the feeder tank 73 through the chute 72 and is collected in the storage tank 75 by the conveyor 74 as necessary.
[0021]
Further, in the organic waste drying method of the present invention, the water vapor discharged from the water vaporization container 1 is cooled by the condenser 42, and the water condensed by the condenser 42 is collected in the drain tank 43. Thus, the odor component contained in the gas from which moisture has been removed is preferably treated in the catalyst tower 44. In this way, if moisture is removed by the capacitor, the amount of gas containing the odor component becomes extremely small, so that there is an advantage that the deodorization treatment is facilitated.
[0022]
Moreover, since the drying method of the organic waste of this invention batch-processes a to-be-processed object by the said water vaporization container 1, as demonstrated above, the same water vaporization besides the said water vaporization container 1 is carried out. If a plurality of units are installed side by side so that the container 1a is installed side by side, an advantage that the processing capacity can be appropriately increased can be obtained.
[0023]
【The invention's effect】
Since the organic waste drying method and apparatus according to the present invention are configured as described above, the amount of odor-containing gas generated is not used when drying the moisture contained in the organic waste. Is controlled to a minimum, and a dry product can be obtained. Therefore, odor leakage can be prevented and deodorizing treatment can be extremely facilitated. Furthermore, if the discharged water vapor is condensed by a condenser, there are excellent effects such as the generation amount of odor-containing gas can be further reduced. Therefore, the present invention has an extremely large industrial value as a method and apparatus for drying organic waste that has solved the conventional problems.
[Brief description of the drawings]
FIG. 1 is a main part flow diagram of a drying apparatus for explaining the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Moisture vaporization container, 11 Ceiling cover part, 12 Bottom part, 13 Side wall part, 14 Supply port, 15 Gas discharge port, 16 Content discharge port, 21 Supply feeder, 22 Supply machine, 23 On-off valve, 41 Automatic pressure regulator, 41a Automatic valve , 42 condenser, 43 drain tank, 44 catalyst tower, 51 stirring motor, 52 stirring blade, 61 heater, 71 open / close stopper, 72 chute, 73 feeder tank

Claims (4)

供給された有機性廃棄物を密閉状態で加熱し、含まれる水分を気化処理する金属製容器であって、上部には、有機性廃棄物供給フィーダに接続された供給手段と自動調圧機に接続されたガス排出手段を備え、内部には、攪拌手段を配設し、底部は、逆円錐形状に形成され、その下端部には、昇降操作される開閉栓を開くことにより水分気化容器の内圧と外部圧力との差圧を利用して乾燥物を排出する内容物排出手段を形成し、側壁部には、内部を加熱するための加熱手段を配設した水分気化容器を具備したことを特徴とする有機性廃棄物の乾燥装置。It is a metal container that heats the supplied organic waste in a sealed state and vaporizes the contained water. At the top, it is connected to a supply means connected to the organic waste supply feeder and an automatic pressure regulator. The gas discharge means is provided, the stirring means is disposed inside, the bottom is formed in an inverted conical shape, and the internal pressure of the moisture vaporization container is opened at the lower end by opening an opening / closing stopper that is operated up and down. The content discharge means for discharging the dry matter is formed using the differential pressure between the external pressure and the external pressure, and the moisture vaporization container provided with the heating means for heating the inside is provided on the side wall. Organic waste drying equipment. 前記水分気化容器を複数併設して、時差運転可能とした請求項1に記載の有機性廃棄物の乾燥装置。The organic waste drying apparatus according to claim 1, wherein a plurality of the water vaporization containers are provided side by side so that a time difference operation is possible. 次の工程を繰り返し行うことを特徴とする有機性廃棄物の乾燥方法。
(1)水分を含む有機性廃棄物を水分気化容器に供給して、該水分気化容器を閉鎖する廃棄物供給工程。
(2)水分気化容器内の有機性廃棄物を100℃〜374℃の範囲に加熱し、水分を気化させるとともに、水分気化容器内部の圧力を処理温度における飽和蒸気圧以下になるように、水蒸気を排出して調整する加熱調圧工程。
(3)水分気化の完了後、温度条件を維持して、水分気化容器内の水蒸気を排出して、内圧を乾燥物の排出に要する最小限の圧力まで減圧するガス放出工程。
(4)水分気化容器底部の開閉栓を開き、水分気化容器の内圧と外部圧力との差圧を利用して乾燥物を排出する乾燥物排出工程。
A method for drying organic waste, characterized by repeating the following steps.
(1) A waste supply step of supplying organic waste containing moisture to a moisture vaporization container and closing the moisture vaporization container.
(2) The organic waste in the moisture vaporization container is heated to a range of 100 ° C. to 374 ° C. to vaporize the moisture, and the water vapor is adjusted so that the pressure inside the moisture vaporization container is equal to or lower than the saturated vapor pressure at the treatment temperature. Heating and adjusting process that discharges and adjusts.
(3) A gas release step of maintaining the temperature condition and discharging the water vapor in the water vaporization container to reduce the internal pressure to the minimum pressure required for discharging the dry matter after the completion of the water vaporization.
(4) A dry matter discharge step of opening the open / close stopper at the bottom of the moisture vaporization container and discharging the dry matter using a differential pressure between the internal pressure and the external pressure of the moisture vaporization container.
水分気化容器外に排出された乾燥物を貯留槽に収集するとともに、水分気化容器から排出した排ガスをコンデンサで冷却し、凝縮した水分はドレンタンクに収集して、水蒸気を除去した後の臭気ガス成分を触媒塔で処理する請求項3に記載の有機性廃棄物の乾燥方法。  Oxidized gas after collecting the dry matter discharged outside the moisture vaporization container in a storage tank, cooling the exhaust gas discharged from the moisture vaporization container with a condenser, collecting the condensed moisture in a drain tank, and removing water vapor The method for drying organic waste according to claim 3, wherein the components are treated in a catalyst tower.
JP2001248049A 2001-08-17 2001-08-17 Organic waste drying apparatus and drying method Expired - Lifetime JP4384378B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001248049A JP4384378B2 (en) 2001-08-17 2001-08-17 Organic waste drying apparatus and drying method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001248049A JP4384378B2 (en) 2001-08-17 2001-08-17 Organic waste drying apparatus and drying method

Publications (2)

Publication Number Publication Date
JP2003053297A JP2003053297A (en) 2003-02-25
JP4384378B2 true JP4384378B2 (en) 2009-12-16

Family

ID=19077274

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001248049A Expired - Lifetime JP4384378B2 (en) 2001-08-17 2001-08-17 Organic waste drying apparatus and drying method

Country Status (1)

Country Link
JP (1) JP4384378B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109140966A (en) * 2018-08-29 2019-01-04 奉节县椿政生态农业发展有限公司 A kind of oil crops drying save set
CN112097478A (en) * 2020-09-24 2020-12-18 王化军 Bipyramid desiccator suitable for low heat sensitivity material
CN114636290B (en) * 2022-01-25 2023-04-18 武汉龙壹茶叶有限公司 Biological cake fertilizer drying device and method for drying biological cake fertilizer
CN114485091A (en) * 2022-02-24 2022-05-13 甘肃能源化工职业学院 Chemical raw material is with even drying device

Also Published As

Publication number Publication date
JP2003053297A (en) 2003-02-25

Similar Documents

Publication Publication Date Title
EP2398505B1 (en) Waste treatment autoclave to provide for steam-assisted drying
JP4386950B2 (en) Garbage disposal apparatus and garbage disposal method
KR970073757A (en) Garbage Disposal Equipment With Deodorizer
KR20050108306A (en) Heat treatment system using superheated steam
JP5504959B2 (en) Sludge carbonization equipment
JP2013154316A (en) Fermentation treatment method of organic waste and apparatus that executes the method
JP4384378B2 (en) Organic waste drying apparatus and drying method
KR20160073665A (en) Drying system and drying method for high water content materials
JPH11116966A (en) Heat treatment equipment of waste containing high water content
JP2006308162A (en) Superheated steam circulation type drying system
JP2004330082A (en) Waste treating method and its apparatus
JPH10211483A (en) Garbage treating apparatus and garbage treating method
JP4384377B2 (en) Hydrothermal treatment method for organic waste
KR19990074033A (en) Microwave Food Processing Device
JP3568262B2 (en) Garbage disposal equipment
JPH07120143A (en) Vacuum drier and vacuum drying method
JPH07243765A (en) Heating and drying device
KR100481030B1 (en) Non-odor sludge drying system using closed system
JP3560466B2 (en) Garbage disposal method and garbage disposal device
JPS6298185A (en) Garbage drying treater
JPH0835775A (en) Drying disposer for water-containing object
JP2006057885A (en) Drying device
JP3764042B2 (en) Waste dryer
JPH0429793A (en) Garbage treatment apparatus and method
JP2002186998A (en) Desiccating treatment apparatus of night soil

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070222

A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A712

Effective date: 20080331

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A821

Effective date: 20080514

RD02 Notification of acceptance of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7422

Effective date: 20080514

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20080604

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20090513

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20090522

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20090715

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20090814

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20090820

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

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20090915

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20090925

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

Free format text: PAYMENT UNTIL: 20121002

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Ref document number: 4384378

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

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

Free format text: PAYMENT UNTIL: 20121002

Year of fee payment: 3

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

Free format text: PAYMENT UNTIL: 20131002

Year of fee payment: 4

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term