JPH11319898A - Liquefying treatment of sewer sludge and its apparatus - Google Patents
Liquefying treatment of sewer sludge and its apparatusInfo
- Publication number
- JPH11319898A JPH11319898A JP10128786A JP12878698A JPH11319898A JP H11319898 A JPH11319898 A JP H11319898A JP 10128786 A JP10128786 A JP 10128786A JP 12878698 A JP12878698 A JP 12878698A JP H11319898 A JPH11319898 A JP H11319898A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- steam
- exhaust gas
- reaction tank
- 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.)
- Withdrawn
Links
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は下水汚泥の液状化処
理方法とその装置に関する。The present invention relates to a method and apparatus for liquefying sewage sludge.
【0002】[0002]
【従来の技術】図2に従来の下水汚泥液状化処理方法を
示す。従来の下水汚泥液状化処理方法は含水率98%の
濃縮汚泥15を遠心分離機16により脱水して、含水率
80%の固形物状の脱水汚泥17とし、その脱水汚泥1
7を圧入ピストン18により高温・高圧条件下(200
〜250℃、50〜70atm )である反応槽19へ圧入
する。反応槽19により脱水汚泥17を液状化した後、
熱交換器20により熱回収し、前段の反応槽19の熱源
とする。また熱回収した熱だけでは反応槽19の熱源と
して不十分な場合には加熱器21により熱媒体を加熱し
て反応槽19に必要な熱を供給する。2. Description of the Related Art FIG. 2 shows a conventional sewage sludge liquefaction treatment method. In the conventional sewage sludge liquefaction treatment method, a concentrated sludge 15 having a water content of 98% is dewatered by a centrifugal separator 16 to obtain a solid dewatered sludge 17 having a water content of 80%.
7 by the press-fitting piston 18 under high temperature and high pressure conditions (200
To 250 DEG C., 50 to 70 atm). After liquefaction of the dewatered sludge 17 by the reaction tank 19,
The heat is recovered by the heat exchanger 20 and used as a heat source for the reaction tank 19 in the preceding stage. If the recovered heat alone is not sufficient as a heat source for the reaction tank 19, the heating medium is heated by the heater 21 to supply necessary heat to the reaction tank 19.
【0003】次に熱交換器20により冷却した反応生成
物を減圧装置22により常温まで減圧した後、排ガス2
5と液状化汚泥23に分離し、排ガス25は排ガス処理
装置26により処理して処理ガス27として大気へ排出
し、生成した液状化汚泥23は貯留槽24へ貯留する。Next, the reaction product cooled by the heat exchanger 20 is depressurized to a normal temperature by a decompression device 22, and then the exhaust gas 2 is cooled.
5 and liquefied sludge 23, and the exhaust gas 25 is treated by an exhaust gas treatment device 26 and discharged to the atmosphere as a treatment gas 27, and the produced liquefied sludge 23 is stored in a storage tank 24.
【0004】[0004]
【発明が解決しようとする課題】以上のような処理方法
により液状化汚泥23を生成しているが、固形物状の脱
水汚泥17を反応槽19へ連続的に圧入することは困難
であり、詰まり等の問題も生じていた。本発明はかかる
従来技術の欠点に鑑み、反応槽への連続圧入の容易化を
図ると共に、該反応槽の詰まり等の問題の解消を図った
下水汚泥の液状化処理方法とその装置を提供することを
目的とする。Although the liquefied sludge 23 is produced by the above-mentioned treatment method, it is difficult to continuously press the solid dehydrated sludge 17 into the reaction tank 19, Problems such as clogging also occurred. The present invention, in view of the drawbacks of the prior art, provides a method and apparatus for liquefying sewage sludge which facilitates continuous press-fitting into a reaction tank and eliminates problems such as clogging of the reaction tank. The purpose is to:
【0005】[0005]
【課題を解決するための手段】請求項1記載の発明は、
かかる課題を達成する為に、下水濃縮汚泥を直接高温・
高圧条件下の反応槽に圧入し、該反応槽内で液状化した
後、まず蒸気発生温度以上の温度で排ガス及び水蒸気
と、液状化汚泥とに分離し、しかる後、該分離された排
ガス及び水蒸気を熱回収により蒸気発生温度以下に低下
させて排ガスのみを分離し、排ガス処理を行なうことを
特徴とする下水汚泥の液状化処理方法を提案する。この
場合、好ましくは請求項2記載のように前記排ガスと水
蒸気とを分離する際に得られた回収熱を前記反応槽の加
熱源とするのがよい。According to the first aspect of the present invention,
To achieve this task, concentrated sewage sludge is directly heated to high temperatures.
After pressurized into the reaction tank under high pressure conditions and liquefied in the reaction tank, first, at a temperature equal to or higher than the steam generation temperature, the exhaust gas and steam are separated into liquefied sludge, and then the separated exhaust gas and The present invention proposes a sewage sludge liquefaction treatment method characterized in that steam is reduced to a temperature equal to or lower than a steam generation temperature by heat recovery, and only exhaust gas is separated and subjected to exhaust gas treatment. In this case, it is preferable that the recovered heat obtained when separating the exhaust gas and the steam be used as a heating source for the reaction tank.
【0006】請求項3記載の発明は、前記請求項1記載
の発明を効果的に実施するための装置に関する発明で、
高温・高圧条件下で下水濃縮汚泥を反応させる反応槽
と、該反応槽に下水濃縮汚泥を圧入する圧入手段と、前
記反応槽に接続され、該反応槽内での反応により液状化
された汚泥を蒸気発生温度以上の温度で、排ガス及び水
蒸気と、液状化汚泥とに分離する第1の分離装置と、該
第1の分離装置で分離された排ガス及び水蒸気を熱回収
により蒸気発生温度以下に低下させて排ガスのみに分離
する第2の分離装置と、該第2の分離装置で分離された
排ガスを処理する排ガス処理装置と、からなることを特
徴とする。A third aspect of the present invention relates to an apparatus for effectively implementing the first aspect of the present invention.
A reaction tank for reacting the concentrated sewage sludge under high temperature and high pressure conditions, press-fitting means for injecting the concentrated sewage sludge into the reaction tank, and sludge connected to the reaction tank and liquefied by the reaction in the reaction tank At a temperature equal to or higher than the steam generation temperature, into a waste gas and water vapor, and a liquefied sludge; and a heat recovery of the waste gas and steam separated by the first separation device to a temperature below the steam generation temperature by heat recovery. It is characterized by comprising a second separation device for lowering and separating only exhaust gas, and an exhaust gas treatment device for treating the exhaust gas separated by the second separation device.
【0007】なお、後記実施例では、内部圧を第1の圧
力(常圧以上)に減圧して反応温度から、蒸気発生温度
以上の温度に、更に第1の圧力から常圧に減圧するとと
もに熱回収により蒸気発生温度以下に低下させている為
に、減圧装置と熱交換器を組合せて第1及び第2の分離
装置を構成しているが、これのみに限定されない。In the embodiment described below, the internal pressure is reduced to a first pressure (normal pressure or higher), the reaction temperature is reduced to a temperature equal to or higher than the steam generation temperature, and the first pressure is further reduced to normal pressure. Since the temperature is reduced to a temperature equal to or lower than the steam generation temperature by the heat recovery, the first and second separation devices are configured by combining the pressure reducing device and the heat exchanger, but the invention is not limited thereto.
【0008】かかる発明によれば、反応槽への供給原料
を固形物状の脱水汚泥から、スラリー状の濃縮汚泥に変
更したために、遠心分離機を削除できるとともに、脱水
汚泥からスラリー状の濃縮汚泥に変更することは反応槽
に供給試料を容易に供給できる。又、第1の分離装置で
は反応槽内での反応により液状化された汚泥を減圧等に
よる温度調整により水蒸気をガス側に移行させ、液状化
汚泥を得ることができる。According to this invention, since the feedstock to the reaction tank is changed from solid dehydrated sludge to slurry-type concentrated sludge, the centrifugal separator can be omitted, and slurry-like concentrated sludge can be removed from the dehydrated sludge. By changing to, the supply sample can be easily supplied to the reaction tank. Further, in the first separation device, the sludge liquefied by the reaction in the reaction tank is transferred to the gas side by adjusting the temperature by decompression or the like, and liquefied sludge can be obtained.
【0009】[0009]
【発明の実施の形態】以下、本発明を図に示した実施例
を用いて詳細に説明する。但し、この実施例に記載され
る構成部品の寸法、形状、その相対配置などは特に特定
的な記載がない限り、この発明の範囲をそれのみに限定
する趣旨ではなく単なる説明例に過ぎない。図1は本発
明の実施形態に係る下水汚泥液状化処理方法に関する構
成図である。図において、濃縮汚泥1を脱水せずにその
まま圧入ピストン2により高温・高圧条件下(200〜
250℃、50〜70atm )である反応槽3へ圧入し、
濃縮汚泥中の有機成分の低分子化を図る。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to an embodiment shown in the drawings. However, unless otherwise specified, dimensions, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the invention, but are merely illustrative examples. FIG. 1 is a configuration diagram relating to a sewage sludge liquefaction treatment method according to an embodiment of the present invention. In the figure, the concentrated sludge 1 is not dewatered and is directly used by the press-in piston 2 under high temperature and high pressure conditions (200 to
250 ° C., 50 to 70 atm).
Reduce the molecular weight of organic components in concentrated sludge.
【0010】次に減圧装置<1>4でガス側に水蒸気を
移行させるために減圧装置<1>4の内部温度を120
〜150℃になるように減圧装置<1>4の内部圧力を
常圧以上の所定正圧に調整して、(排ガス+水蒸気)5
と液状化汚泥10に分離した後、減圧装置<2>6と減
圧装置<3>11により(排ガス+水蒸気)5、液状化
汚泥10をそれぞれ常圧まで減圧する。Next, in order to transfer water vapor to the gas side by the decompression device <1> 4, the internal temperature of the decompression device <1> 4 is set to 120.
The internal pressure of the pressure reducing device <1> 4 is adjusted to a predetermined positive pressure equal to or higher than the normal pressure so that the temperature is reduced to 150 ° C.
Then, the liquefied sludge 10 and the liquefied sludge 10 are each depressurized to normal pressure by the decompression device <2> 6 and the decompression device <3> 11.
【0011】(排ガス+水蒸気)5は熱交換器7により
熱回収して蒸気発生温度以下に低下させて排ガスと水蒸
気を分離した後(水蒸気は水として回収して)、排ガス
のみを処理装置8により処理し、処理ガス9として放出
する。また液状化汚泥10も(排ガス+水蒸気)5と同様
に熱回収し、貯留槽12に保管する。それぞれの生成物
より熱交換器7、熱交換器13で回収した熱を反応槽3
の熱源として利用する。The (exhaust gas + steam) 5 is recovered by the heat exchanger 7 to reduce the temperature to below the steam generation temperature to separate the exhaust gas from the steam (the steam is recovered as water). And released as a processing gas 9. The liquefied sludge 10 also recovers heat in the same manner as the (exhaust gas + steam) 5 and stores it in the storage tank 12. The heat recovered from each product in heat exchangers 7 and 13 is transferred to reaction tank 3
Use as a heat source.
【0012】ここで回収した熱だけでは反応槽3の熱源
として不十分の場合には加熱器14により熱媒体を加熱
して反応槽3に必要とする熱を供給する。If the recovered heat alone is not sufficient as a heat source for the reaction tank 3, the heating medium is heated by the heater 14 to supply necessary heat to the reaction tank 3.
【0013】かかる実施形態によれば、液状化処理を行
なう反応槽3へ供給する汚泥形態を従来の固形物状の脱
水汚泥17からスラリー状の濃縮汚泥1とすることによ
り、遠心分離機16を省略でき、遠心分離機16に係る
イニシャルコスト、ランニングコストを削減できるだけ
でなく、反応槽3の内部が高圧であっても、原料の供給
が容易となり、下水汚泥の液状化に関して連続処理が可
能である。According to this embodiment, the sludge supplied to the reaction tank 3 for performing the liquefaction treatment is changed from the conventional solid-state dehydrated sludge 17 to the slurry-like concentrated sludge 1 so that the centrifugal separator 16 can be used. This can be omitted, and not only can the initial cost and running cost of the centrifuge 16 be reduced, but also the supply of raw materials becomes easy even when the inside of the reaction tank 3 is at a high pressure, and continuous treatment can be performed for liquefaction of sewage sludge. is there.
【0014】特にスラリー状の濃縮汚泥1を原料とした
場合、元々液状化状態であるため、反応槽3においては
液状化処理というよりも濃縮汚泥1中の有機成分の低分
子化であり、減圧装置<1>4において(水蒸気+排ガ
ス)5と液状化汚泥10に分離したときに初めて液状化
汚泥10が生成する。Particularly, when the concentrated sludge 1 in the form of slurry is used as a raw material, since the sludge is originally in a liquefied state, the organic component in the concentrated sludge 1 is reduced in the reaction tank 3 rather than in the liquefaction treatment. Liquefaction sludge 10 is generated only when (steam + exhaust gas) 5 and liquefaction sludge 10 are separated in device <1> 4.
【0015】また(水蒸気+排ガス)5と液状化汚泥1
0とに分離する減圧装置<1>4にて常圧まで減圧して
しまうと反応生成物が常温になり、反応生成物中の水が
液体として存在するため、分離した場合、液状化汚泥と
水が混在してしまう。そこで減圧装置<1>4では常圧
まで減圧せずに減圧装置<1>4の内部温度を120〜
150℃になるように減圧装置<1>4の内部圧力を調
整することにより、水を気体(水蒸気)としてガス側へ容
易に移行させ、(排ガス+水蒸気)5、と液状化汚泥10
に分離できる。Further, (steam + exhaust gas) 5 and liquefied sludge 1
If the pressure is reduced to normal pressure by the decompression device <1> 4, the reaction product becomes normal temperature, and water in the reaction product exists as a liquid. Water mixes. Therefore, the pressure reducing device <1> 4 does not reduce the pressure to the normal pressure, but raises the internal temperature of the pressure reducing device <1> 4 to 120 to
By adjusting the internal pressure of the pressure reducing device <1> 4 to 150 ° C., water is easily transferred to the gas side as gas (steam), and (exhaust gas + steam) 5 and liquefied sludge 10
Can be separated.
【0016】なお、本実施形態の場合、従来より減圧装
置が2台増加するが、減圧装置は動力は少なく、構造も
簡単なため、遠心分離機を省略した方が、イニシャルコ
スト、ランニングコストとも低減できる。In this embodiment, the number of decompression devices is increased by two compared to the conventional one. However, since the decompression device has less power and has a simple structure, it is better to omit the centrifugal separator in both initial cost and running cost. Can be reduced.
【0017】[0017]
【発明の効果】以上記載のごとく請求項1及び3記載の
発明によれば、反応槽への連続圧入の容易化を図ると共
に、該反応槽の詰まり等の問題の解消を図ることが出来
る。又、請求項2記載の発明によれば、前記夫々の分離
の際に回収した熱を反応槽へ供給して熱エネルギーの有
効利用を図れる。As described above, according to the first and third aspects of the present invention, continuous press-fitting into the reaction tank can be facilitated, and problems such as clogging of the reaction tank can be solved. According to the second aspect of the present invention, the heat recovered at the time of the respective separations is supplied to the reaction tank, so that the heat energy can be effectively used.
【図1】 本発明の実施例に係る下水汚泥液状化処理方
法に関する構成図である。FIG. 1 is a configuration diagram relating to a sewage sludge liquefaction treatment method according to an embodiment of the present invention.
【図2】 従来の下水汚泥液状化処理方法を示した構成
図である。FIG. 2 is a configuration diagram showing a conventional sewage sludge liquefaction treatment method.
1 濃縮汚泥 2 圧入ピストン 3 反応槽 4 減圧装置<1> 5 排ガス+水蒸気 6 減圧装置<2> 7,13 熱交換器 8 排ガス処理装置 9 処理ガス 10 液状化汚泥 11 減圧装置<3> 12 貯留槽 14 加熱器 REFERENCE SIGNS LIST 1 concentrated sludge 2 press-in piston 3 reaction tank 4 decompression device <1> 5 exhaust gas + steam 6 decompression device <2> 7, 13 heat exchanger 8 exhaust gas treatment device 9 process gas 10 liquefied sludge 11 decompression device <3> 12 storage Vessel 14 heater
Claims (3)
反応槽に圧入し、該反応槽内で液状化した後、まず蒸気
発生温度以上の温度で排ガス及び水蒸気と、液状化汚泥
とに分離し、しかる後、該分離された排ガス及び水蒸気
を熱回収により蒸気発生温度以下に低下させて排ガスの
みを分離し、排ガス処理を行なうことを特徴とする下水
汚泥の液状化処理方法。Claims: 1. Sewage concentrated sludge is directly injected into a reaction tank under high-temperature and high-pressure conditions and liquefied in the reaction tank. At first, at a temperature higher than the steam generation temperature, exhaust gas and steam are converted into liquefied sludge. A method for liquefaction treatment of sewage sludge, comprising separating the exhaust gas and water vapor to a temperature equal to or lower than the steam generation temperature by heat recovery to separate only the exhaust gas, and then subjecting the exhaust gas to waste gas treatment.
られた回収熱を前記反応槽の加熱源とすることを特徴と
する請求項1記載の下水汚泥の液状化処理方法。2. A sewage sludge liquefaction treatment method according to claim 1, wherein recovered heat obtained when the exhaust gas and steam are separated is used as a heating source for the reaction tank.
させる反応槽と、 該反応槽に下水濃縮汚泥を圧入する圧入手段と、 前記反応槽に接続され、該反応槽内での反応により液状
化された汚泥を蒸気発生温度以上の温度で排ガス及び水
蒸気と液状化汚泥とに分離する第1の分離装置と、 該第1の分離装置で分離された排ガス及び水蒸気を熱回
収により蒸気発生温度以下に低下させて排ガスのみに分
離する第2の分離装置と、 該第2の分離装置で分離された排ガスを処理する排ガス
処理装置と、 からなることを特徴とする下水汚泥の液状化処理装置。3. A reaction tank for reacting concentrated sewage sludge under high-temperature and high-pressure conditions, press-fitting means for injecting concentrated sewage sludge into the reaction tank, and a reaction tank connected to the reaction tank and reacting in the reaction tank. A first separation device that separates liquefied sludge into exhaust gas and water vapor and liquefied sludge at a temperature equal to or higher than the steam generation temperature, and generates steam by heat recovery of the exhaust gas and steam separated by the first separation device. Liquefaction treatment of sewage sludge, comprising: a second separation device that separates only exhaust gas by lowering the temperature to below the temperature, and an exhaust gas treatment device that treats the exhaust gas separated by the second separation device. apparatus.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10128786A JPH11319898A (en) | 1998-05-12 | 1998-05-12 | Liquefying treatment of sewer sludge and its apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10128786A JPH11319898A (en) | 1998-05-12 | 1998-05-12 | Liquefying treatment of sewer sludge and its apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH11319898A true JPH11319898A (en) | 1999-11-24 |
Family
ID=14993429
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10128786A Withdrawn JPH11319898A (en) | 1998-05-12 | 1998-05-12 | Liquefying treatment of sewer sludge and its apparatus |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH11319898A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103570200A (en) * | 2012-08-06 | 2014-02-12 | 吴俊斌 | Sludge liquefying and drying treatment system and method |
-
1998
- 1998-05-12 JP JP10128786A patent/JPH11319898A/en not_active Withdrawn
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103570200A (en) * | 2012-08-06 | 2014-02-12 | 吴俊斌 | Sludge liquefying and drying treatment system and method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP2366757B1 (en) | Pressure and temperature control system for at least one chemical reactor for treating biomass | |
US20100077765A1 (en) | High-Pressure Fluid Compression System Utilizing Cascading Effluent Energy Recovery | |
KR101871428B1 (en) | Apparatus for treating sewage sludge and method using the same | |
CN107200452B (en) | Device and method for microwave pyrolysis of sludge | |
CN111377579B (en) | Oil sludge treatment method | |
CN213835018U (en) | Vacuum thermal desorption device for petroleum oil sludge | |
JP2006281074A (en) | Organic sludge treatment method | |
JPH11319898A (en) | Liquefying treatment of sewer sludge and its apparatus | |
JP3318483B2 (en) | Supercritical water oxidation method of organic sludge and organic sludge supply device used for the method | |
CN112340962A (en) | Vacuum thermal desorption device for petroleum oil sludge and use method thereof | |
CN101817630A (en) | Pulse flashing deep dehydration method and device for sludge | |
JP4231739B2 (en) | Sludge recycling method | |
CN110304804B (en) | Sludge thermal conditioning and drying carbonization energy-saving system | |
JPH115100A (en) | Sewage sludge treatment system | |
JP2006061861A (en) | Apparatus and method for treating organic sludge | |
KR102505116B1 (en) | Solid Fuel Production and Energy Generation System using Hydrothermal Carbonization of Organic Waste and Method Therefor | |
JP2004237247A (en) | Treatment apparatus for water-containing slurry | |
KR102505123B1 (en) | Organic Waste Reduction and Biogas Production System combined with Hydrothermal Carbonization with Improved Energy Consumption Efficiency | |
JP3156894B2 (en) | Method and apparatus for treating organic sludge | |
KR20010023326A (en) | A method and an apparatus for upgrading a solid material | |
JPS6281491A (en) | Method of dehydrating brown coal | |
CN115196807B (en) | Treatment method for deacidifying and deaminizing coal chemical wastewater by strengthening waste heat recovery | |
JPH08206691A (en) | Treatment of sludge | |
JP2024073874A (en) | Gas supply system and power generation system | |
JPH11197698A (en) | Method and device for gasifying waste |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A300 | Withdrawal of application because of no request for examination |
Free format text: JAPANESE INTERMEDIATE CODE: A300 Effective date: 20050802 |