JP2002113348A - Treating apparatus of organic waste from animal and vegetable residue by hydrothermal reaction - Google Patents
Treating apparatus of organic waste from animal and vegetable residue by hydrothermal reactionInfo
- Publication number
- JP2002113348A JP2002113348A JP2000309175A JP2000309175A JP2002113348A JP 2002113348 A JP2002113348 A JP 2002113348A JP 2000309175 A JP2000309175 A JP 2000309175A JP 2000309175 A JP2000309175 A JP 2000309175A JP 2002113348 A JP2002113348 A JP 2002113348A
- Authority
- JP
- Japan
- Prior art keywords
- organic waste
- raw material
- hydrothermal
- hydrothermal reactor
- water
- 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
- 239000010815 organic waste Substances 0.000 title claims abstract description 35
- 238000001027 hydrothermal synthesis Methods 0.000 title abstract description 19
- 235000013311 vegetables Nutrition 0.000 title abstract 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 61
- 238000010438 heat treatment Methods 0.000 claims abstract description 25
- 239000002699 waste material Substances 0.000 claims abstract description 3
- 238000012545 processing Methods 0.000 claims description 14
- 238000007254 oxidation reaction Methods 0.000 claims description 12
- 230000003647 oxidation Effects 0.000 claims description 10
- 230000001590 oxidative effect Effects 0.000 claims description 4
- 230000003247 decreasing effect Effects 0.000 abstract 1
- 239000002994 raw material Substances 0.000 description 56
- 239000007788 liquid Substances 0.000 description 29
- 238000000354 decomposition reaction Methods 0.000 description 11
- 239000000126 substance Substances 0.000 description 9
- 239000002002 slurry Substances 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 239000008399 tap water Substances 0.000 description 5
- 235000020679 tap water Nutrition 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- 230000001105 regulatory effect Effects 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000001877 deodorizing effect Effects 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 238000010335 hydrothermal treatment Methods 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 150000001247 metal acetylides Chemical class 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 238000006864 oxidative decomposition reaction Methods 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000009284 supercritical water oxidation Methods 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、生ゴミ等の動植物
残渣である有機性廃棄物を水熱反応で処理するための水
熱反応による動植物残渣等有機性廃棄物処理装置に関す
るものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for treating organic waste such as animal and plant residues by hydrothermal reaction for treating organic waste such as garbage and the like as animal and plant residues by hydrothermal reaction.
【0002】[0002]
【従来の技術】従来、生ゴミ等の動植物残渣は、専門業
者により、回収,焼却,埋め立てという方法などで処理
されていたが、近年各種ゴミ処理装置が開発されてい
る。2. Description of the Related Art Conventionally, animal and plant residues, such as garbage, have been treated by specialists by methods such as collection, incineration, and landfilling. In recent years, various types of refuse treatment apparatuses have been developed.
【0003】例えば、特開平10−328699号公報
には、含水有機廃棄物を超臨界水酸化反応にて酸化分解
することが開示されている。For example, JP-A-10-328699 discloses that hydrous organic waste is oxidatively decomposed by a supercritical water oxidation reaction.
【0004】しかし、超臨界による分解方法では、含水
有機廃棄物の圧力・温度を超臨界状態まで上げて、酸化
分解と処理能力の増大を図っているが、条件が厳しい
分、配管等の腐食の問題も大きくなる。[0004] However, in the decomposition method using supercritical fluid, the pressure and temperature of hydrated organic waste are raised to a supercritical state to increase oxidative decomposition and treatment capacity. The problem becomes bigger.
【0005】そこで、本発明者は、先に特願平11−3
30000号(発明の名称;水熱反応による動植物残渣
処理装置)にて、有機性廃棄物を亜臨界圧状態にして水
熱反応させ、その後、水熱反応で分解された有機性廃棄
物を酸化処理することを提案した。Accordingly, the present inventor has previously disclosed in Japanese Patent Application No. Hei 11-3
In No. 30,000 (Title of Invention; Apparatus for treating animal and plant residues by hydrothermal reaction), the organic waste is subjected to a hydrothermal reaction under a subcritical pressure state, and then the organic waste decomposed by the hydrothermal reaction is oxidized. Proposed to be processed.
【0006】この先願の基本的構成を図3により説明す
る。The basic configuration of the prior application will be described with reference to FIG.
【0007】図3において、原料タンク60からの原料
が原料供給ライン61に供給されると共に上水タンク6
2からの上水が原料供給ライン61に供給され、原料と
水とが混合され、昇圧ポンプ63で亜臨界圧状態まで昇
圧され、熱交換器64で予熱されたのち、水熱反応器6
5の循環ライン66に供給され、循環ライン66に接続
した循環ポンプ67で、水熱反応器65からの水熱処理
液と共に水熱反応器65に繰り返し循環されて水熱反応
がなされ、その後、ライン68から後処理装置に排出さ
れて無機化される。In FIG. 3, a raw material from a raw material tank 60 is supplied to a raw material supply line 61 and a raw water tank 6 is supplied.
2 is supplied to the raw material supply line 61, the raw material and water are mixed, the pressure is raised to a subcritical pressure state by the booster pump 63, and the water is preheated by the heat exchanger 64.
5 is circulated to the hydrothermal reactor 65 together with the hydrothermal treatment liquid from the hydrothermal reactor 65 by the circulating pump 67 connected to the circulating line 66 and connected to the circulating line 66 to perform the hydrothermal reaction. From 68, it is discharged to a post-processing device and mineralized.
【0008】[0008]
【発明が解決しようとする課題】この先願の発明におい
ては、水熱反応器65は、二重管等の熱交換器で形成さ
れ、原料スラリーを内側のチューブに流し、外管内に熱
媒油を流して熱交換するため、熱媒油と原料スラリーの
温度差を大きく取ると、原料スラリーがチューブ内で焦
げ付くため、焦げ付き防止を配慮した形式とする必要が
ある。In the invention of the prior application, the hydrothermal reactor 65 is formed by a heat exchanger such as a double tube, in which the raw material slurry flows into the inner tube, and the heat transfer oil is contained in the outer tube. When the temperature difference between the heating medium oil and the raw material slurry is large, the raw material slurry is scorched in the tube, so that it is necessary to take into consideration the prevention of scorching.
【0009】このため、温度差を小さくし、その分、伝
熱面積を大きくし、更に、原料スラリーの供給量に対す
るスラリーの循環量を数10倍と大きくして熱伝達効率
を高め、焦げ付きを防止しつつ、原料スラリーを水熱条
件の300℃まで加熱するようにしている。For this reason, the temperature difference is reduced, the heat transfer area is increased accordingly, and the circulation amount of the slurry relative to the supply amount of the raw material slurry is increased to several tens of times, so that the heat transfer efficiency is increased and the scorch is prevented. While preventing this, the raw material slurry is heated to the hydrothermal condition of 300 ° C.
【0010】しかしながら、多量の原料スラリーを、亜
臨界圧まで昇圧した状態で、水熱反応器65での伝熱面
積を大きとることは、水熱反応器65が大型となり、し
かも熱媒負荷や昇圧ポンプ63と循環ポンプ67の負荷
も大きくなり、全体にコストが高くなる問題がある。However, increasing the heat transfer area in the hydrothermal reactor 65 in a state in which a large amount of the raw material slurry is raised to a subcritical pressure requires an increase in the size of the hydrothermal reactor 65, and in addition to the load of the heat medium. There is a problem that the load on the boosting pump 63 and the circulation pump 67 also increases, and the cost increases as a whole.
【0011】そこで、本発明の目的は、上記課題を解決
し、水熱反応器での伝熱面積を低減できる動植物残渣等
有機性廃棄物処理装置を提供することにある。Accordingly, an object of the present invention is to solve the above problems and to provide an apparatus for treating organic waste such as animal and plant residues, which can reduce the heat transfer area in a hydrothermal reactor.
【0012】[0012]
【課題を解決するための手段】上記目的を達成するため
に、請求項1の発明は、動植物残渣等の有機性廃棄物
を、亜臨界状態まで昇圧・加熱して水熱反応させる水熱
反応器と、該水熱反応器に予め水熱条件まで加熱・加圧
した亜臨界水を有機性廃棄物と共に水熱反応器に供給す
る亜臨界水供給手段とを備えた水熱反応による動植物残
渣等有機性廃棄物処理装置である。Means for Solving the Problems In order to achieve the above object, the invention of claim 1 provides a hydrothermal reaction in which organic wastes such as animal and plant residues are pressurized and heated to a subcritical state and subjected to a hydrothermal reaction. Animal and plant residues by hydrothermal reaction, comprising: a reactor and subcritical water supply means for supplying subcritical water heated and pressurized in advance to the hydrothermal condition to the hydrothermal reactor together with organic waste to the hydrothermal reactor. An organic waste treatment device.
【0013】請求項2の発明は、亜臨界水供給手段は、
上水タンクとその上水タンクの上水を昇圧する昇圧ポン
プと昇圧された上水を約100〜300℃程度に加熱す
る加熱手段とからなり、他方、水熱反応器には、有機性
廃棄物を水熱反応器に繰り返し循環する循環ラインが接
続され、上記加熱手段が循環ラインに接続される請求項
1記載の動植物残渣等有機性廃棄物処理装置である。According to a second aspect of the present invention, the subcritical water supply means includes:
It consists of a water tank, a pressure pump for increasing the pressure of the water in the water tank, and a heating means for heating the pressurized water to about 100 to 300 ° C. The apparatus for treating organic waste such as animal and plant residues according to claim 1, wherein a circulation line for circulating the material repeatedly to the hydrothermal reactor is connected, and the heating means is connected to the circulation line.
【0014】請求項3の発明は、循環ラインには、分解
され減圧された有機性廃棄物残渣を、酸化する酸化槽が
接続される請求項2記載の動植物残渣等有機性廃棄物処
理装置である。According to a third aspect of the present invention, there is provided an apparatus for treating organic waste such as animal and plant residues according to the second aspect, wherein an oxidation tank for oxidizing the decomposed and decompressed organic waste residues is connected to the circulation line. is there.
【0015】[0015]
【発明の実施の形態】以下、本発明の好適実施の形態を
添付図面に基づいて詳述する。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will be described below in detail with reference to the accompanying drawings.
【0016】図1は、本発明の基本的構成を示す概略図
である。FIG. 1 is a schematic diagram showing a basic configuration of the present invention.
【0017】原料タンク10には、生ゴミ等の動植物残
渣からなる有機性廃棄物の原料が収容され、その原料が
原料供給ライン15に接続した昇圧ポンプ16で水の亜
臨界圧(約10MPa)まで昇圧され、水熱反応器25
に接続した循環ライン26に供給される。The raw material tank 10 contains raw materials for organic wastes such as garbage and other animal and plant residues, and the raw materials are supplied to a sub-critical pressure of water (about 10 MPa) by a booster pump 16 connected to a raw material supply line 15. Up to 25
Is supplied to a circulation line 26 connected to
【0018】水熱反応器25は、詳細は後述するが、二
重管等の熱交換器からなり、その内管に原料が供給さ
れ、外管内に熱媒油が供給されて熱交換され、内管に循
環ライン26が接続される。循環ライン26には、循環
ポンプ31が接続され、その吸込側に原料供給ライン1
5が接続される。The hydrothermal reactor 25 comprises a heat exchanger such as a double tube, which will be described in detail later. The raw material is supplied to the inner tube, and the heat transfer oil is supplied to the outer tube to exchange heat. The circulation line 26 is connected to the inner pipe. A circulation pump 31 is connected to the circulation line 26, and the raw material supply line 1 is connected to a suction side thereof.
5 is connected.
【0019】この循環ポンプ31の吸込側には、亜臨界
水供給手段19が接続される。The sub-critical water supply means 19 is connected to the suction side of the circulation pump 31.
【0020】亜臨界水供給手段19は、上水タンク12
と、上水タンク12からの上水を亜臨界圧まで昇圧する
昇圧ポンプ17と、その昇圧ポンプ17のライン18a
に接続され、昇圧された上水を100〜300℃程度に
加熱する加熱手段19aとから構成される。The subcritical water supply means 19 includes the water tank 12
Pump 17 for increasing the pressure of the water from the water tank 12 to a subcritical pressure, and a line 18a of the pressure pump 17
And heating means 19a for heating pressurized tap water to about 100 to 300 ° C.
【0021】この加熱手段19aは、後述する処理液の
熱を用いて予熱する熱交換器42と、その予熱された上
水を、水熱条件である約300℃まで加熱する温水ボイ
ラ18からなり、その温水ボイラ18からのライン18
aが循環ポンプ31の吐出側に接続される。The heating means 19a comprises a heat exchanger 42 for preheating by using the heat of the processing liquid, which will be described later, and a hot water boiler 18 for heating the preheated tap water to about 300 ° C., which is a hydrothermal condition. , Line 18 from the hot water boiler 18
a is connected to the discharge side of the circulation pump 31.
【0022】また、水熱反応器25の出口側の循環ライ
ン26には、分解物ライン33が接続され、水熱反応器
25での分解物が、後述するように減圧された後、酸化
槽22へ供給されて無機化される。A decomposed product line 33 is connected to the circulation line 26 on the outlet side of the hydrothermal reactor 25. The decomposed product in the hydrothermal reactor 25 is decompressed as described later, and It is supplied to 22 and mineralized.
【0023】この図1において、原料供給ライン15か
らは、有機性廃棄物のみの原料が水熱反応器25に供給
され、その有機性廃棄物と混合する水は、温水ボイラ1
8からなる亜臨界水供給手段19で別途供給すること
で、水熱反応器25は、原料分のみの昇温を受け持てば
良く伝熱面を大幅に削減することが可能となる。In FIG. 1, raw material containing only organic waste is supplied from a raw material supply line 15 to a hydrothermal reactor 25, and water mixed with the organic waste is supplied to a hot water boiler 1.
By separately supplying the subcritical water supply means 19 comprising the hydrothermal reactor 8, the hydrothermal reactor 25 only needs to handle the temperature rise of the raw material alone, and the heat transfer surface can be greatly reduced.
【0024】次に、図2により、本発明の全体構成を説
明する。Next, the overall configuration of the present invention will be described with reference to FIG.
【0025】図2において、10は、生ゴミ等の動植物
残渣からなる有機性廃棄物の原料11が収容される原料
タンク、12は亜臨界水による水熱反応を行うための上
水タンク、13は苛性ソーダ等が収容された薬液タン
ク、14は動植物残渣の処理後の処理液を貯留する処理
液タンクである。In FIG. 2, reference numeral 10 denotes a raw material tank for storing an organic waste raw material 11 consisting of animal and plant residues such as garbage, 12 denotes a water supply tank for performing a hydrothermal reaction with subcritical water, 13 Reference numeral denotes a chemical solution tank containing caustic soda and the like, and reference numeral 14 denotes a processing liquid tank for storing a processing liquid after processing animal and plant residues.
【0026】原料タンク10には、原料供給ライン15
が接続され、その原料供給ライン15に昇圧ポンプ16
が接続される。The raw material tank 10 has a raw material supply line 15
Is connected, and a boosting pump 16
Is connected.
【0027】上水タンク12には、昇圧ポンプ17が接
続され、その昇圧ポンプ17に、熱交換器42と温水ボ
イラ18からなる加熱手段19aが接続されて亜臨界水
供給手段19が構成され、その温水ボイラ18からの亜
臨界水供給ライン18aが原料供給ライン15の有機性
廃棄物と共に水熱反応器25に供給されるようになって
いる。A booster pump 17 is connected to the water supply tank 12, and a heating means 19a comprising a heat exchanger 42 and a hot water boiler 18 is connected to the booster pump 17 to constitute a subcritical water supply means 19. The subcritical water supply line 18 a from the hot water boiler 18 is supplied to the hydrothermal reactor 25 together with the organic waste in the raw material supply line 15.
【0028】また原料タンク10には、薬液タンク13
に接続された薬液供給ライン20が接続され、そのライ
ン20に薬液ポンプ21が接続される。The raw material tank 10 includes a chemical solution tank 13.
Is connected to a chemical solution supply line 20, and a chemical solution pump 21 is connected to the line 20.
【0029】原料供給ライン15には、二重管式の熱交
換器24が接続され、さらに原料供給ライン15が水熱
反応器25の循環ライン26に接続される。A double tube heat exchanger 24 is connected to the raw material supply line 15, and the raw material supply line 15 is connected to a circulation line 26 of the hydrothermal reactor 25.
【0030】水熱反応器25には、熱媒循環ライン27
が接続され、その熱媒循環ライン27には、熱媒循環ポ
ンプ28と熱媒加熱器29が接続される。The hydrothermal reactor 25 has a heating medium circulation line 27
The heating medium circulation line 27 is connected to a heating medium circulation pump 28 and a heating medium heater 29.
【0031】水熱反応器25は、二重管等で構成され、
内管30内を原料が流れ、外管32と内管30間に熱媒
が流れるようになっている。The hydrothermal reactor 25 comprises a double tube or the like,
The raw material flows inside the inner tube 30, and the heat medium flows between the outer tube 32 and the inner tube 30.
【0032】循環ライン26は、水熱反応器25の内管
30の出口と入口を結び、その間に循環ポンプ31が接
続されて構成される。The circulation line 26 connects the outlet and the inlet of the inner tube 30 of the hydrothermal reactor 25, and is constituted by connecting a circulation pump 31 therebetween.
【0033】この循環ポンプ31の吐出側の循環ライン
26に、原料供給ライン15と亜臨界水供給手段19が
接続されるが、原料供給ライン15と亜臨界水供給手段
19は、図1で説明したように循環ポンプ31の吸込側
に接続してもよい。The material supply line 15 and the subcritical water supply means 19 are connected to the circulation line 26 on the discharge side of the circulation pump 31. The material supply line 15 and the subcritical water supply means 19 will be described with reference to FIG. As described above, it may be connected to the suction side of the circulation pump 31.
【0034】この循環ポンプ31の吸込側の循環ライン
26より分岐して分解ライン33が接続され、その分解
ライン33に熱交換器24が接続され、その下流に酸化
槽22が接続される。The circulating pump 31 branches off from the circulating line 26 on the suction side, is connected to a decomposition line 33, the heat exchanger 24 is connected to the decomposition line 33, and the oxidation tank 22 is connected downstream thereof.
【0035】この熱交換器24と酸化槽22間の分解物
ライン33にはトリムクーラ34と背圧調整弁35が接
続される。A trim cooler 34 and a back pressure regulating valve 35 are connected to a decomposition line 33 between the heat exchanger 24 and the oxidation tank 22.
【0036】酸化槽22には、供給された分解物を燃焼
させて酸化するための酸化剤供給ライン36が接続さ
れ、その出口に気液分離器23が接続されると共にその
液相側排出ライン37に、酸化された分解物の一部を酸
化槽22に戻す戻しライン39とポンプ40とが接続さ
れる。The oxidizing tank 22 is connected to an oxidizing agent supply line 36 for burning and oxidizing the supplied decomposition product, and the outlet thereof is connected to the gas-liquid separator 23 and the liquid-side discharge line. A return line 39 for returning a part of the oxidized decomposition product to the oxidation tank 22 and a pump 40 are connected to 37.
【0037】気液分離器23の気相側排出ライン50に
は凝縮器38,分離ポット51,背圧調整弁52が接続
され、分離ポット51と気液分離器23間には、分離ポ
ット51により分離された凝縮水を気液分離器23に戻
すライン53が接続される。A condenser 38, a separation pot 51, and a back pressure adjusting valve 52 are connected to the gas-phase side discharge line 50 of the gas-liquid separator 23, and a separation pot 51 is provided between the separation pot 51 and the gas-liquid separator 23. A line 53 for returning the condensed water separated by the process to the gas-liquid separator 23 is connected.
【0038】液相側排出ライン37には、戻しライン3
9と分岐して、処理液を処理液タンク14に戻す排出ラ
イン41が接続され、その排出ライン41に、上水を加
熱するための加熱手段19aとしての熱交換器42が接
続され、背圧調整弁43が接続され、その背圧調整弁4
3で常圧に戻された処理液が処理液タンク14に戻され
るようになっている。The liquid-side discharge line 37 has a return line 3
9, a discharge line 41 for returning the processing liquid to the processing liquid tank 14 is connected, and the discharge line 41 is connected to a heat exchanger 42 as a heating means 19a for heating clean water. The regulating valve 43 is connected, and its back pressure regulating valve 4
The processing liquid returned to normal pressure in step 3 is returned to the processing liquid tank 14.
【0039】処理液タンク14は、その上部に分解ガス
排気ライン44が接続され、また下部に下水ライン45
が接続される。分解排気ライン44には、活性炭などか
らなる脱臭装置46が接続されまた下水ライン45に
は、その液の一部を原料タンク10に戻すライン47と
ポンプ48が接続される。The processing liquid tank 14 has a decomposition gas exhaust line 44 connected to its upper part, and a sewage line 45 formed to its lower part.
Is connected. The decomposition exhaust line 44 is connected to a deodorizing device 46 made of activated carbon or the like, and the sewage line 45 is connected to a line 47 for returning a part of the liquid to the raw material tank 10 and a pump 48.
【0040】また、原料タンク10でガス化したガスは
ガスライン49にて排気ライン44に接続される。The gas gasified in the raw material tank 10 is connected to the exhaust line 44 via a gas line 49.
【0041】なお、トリムクーラ34と凝縮器38は、
図示していないが冷水塔などからの冷水wが供給され、
そのトリムクーラ34と凝縮器38で冷却後の冷水wは
冷水塔で空冷されて再度トリムクーラ34と凝縮器38
に供給されるようになっている。The trim cooler 34 and the condenser 38 are
Although not shown, cold water w from a cold water tower or the like is supplied,
The chilled water w cooled by the trim cooler 34 and the condenser 38 is air-cooled by the cooling water tower, and is again cooled by the trim cooler 34 and the condenser 38.
It is supplied to.
【0042】また、原料タンク10に供給された原料1
1の水分が少ない場合、ライン51より上水タンク12
の上水が適宜供給されるようになっている。The raw material 1 supplied to the raw material tank 10
In the case where the water content is low, the water tank 12
Water is supplied as appropriate.
【0043】次に、図2における動植物残渣等の有機性
廃棄物の処理を説明する。Next, the treatment of organic waste such as animal and plant residues in FIG. 2 will be described.
【0044】有機性廃棄物である原料11を原料タンク
10に投入し、その原料タンク10内に薬液タンク13
からの薬液を、薬液ポンプ21にて薬液ライン20を介
して原料タンク10内に導入してポンプ搬送可能な状態
とする。この場合、上水タンク12からライン51にて
上水を供給して、原料の粘度を調整する。A raw material 11, which is an organic waste, is charged into a raw material tank 10, and a chemical solution tank 13 is placed in the raw material tank 10.
Is introduced into the raw material tank 10 through the chemical liquid line 20 by the chemical liquid pump 21 so that the liquid can be pumped. In this case, tap water is supplied from the tap water tank 12 through the line 51 to adjust the viscosity of the raw material.
【0045】原料タンク10内で調整された原料は、昇
圧ポンプ16にて亜臨界圧まで昇圧され、原料供給ライ
ン15を通じて熱交換器24に供給され、そこで、水熱
反応器25からの分解物と熱交換して加熱された後、循
環ライン26を介して水熱反応器25に供給される。The raw material adjusted in the raw material tank 10 is boosted to a subcritical pressure by a booster pump 16 and supplied to a heat exchanger 24 through a raw material supply line 15 where the decomposed product from a hydrothermal reactor 25 Then, after being heated by exchanging heat, it is supplied to the hydrothermal reactor 25 through the circulation line 26.
【0046】これと同時に、亜臨界水供給手段19よ
り、すなわち上水タンク12の上水を昇圧ポンプ17に
て亜臨界圧まで昇圧し、これを加熱手段19aで、すな
わち熱交換器42にて、気液分離器23で気液分離され
た処理液と熱交換して予熱すると共に温水ボイラ18に
て、100〜300℃まで加熱して略亜臨界水とし、こ
の亜臨界水を循環ライン26を介して水熱反応器25に
供給する。At the same time, the pressure of the subcritical water supply means 19, that is, the water in the water tank 12 is raised to a subcritical pressure by the pressure increasing pump 17, and this is heated by the heating means 19a, that is, by the heat exchanger 42. The pre-heating is performed by exchanging heat with the processing liquid separated by the gas-liquid separator 23, and the heated sub-critical water is heated to 100 to 300 ° C. by the hot water boiler 18 to make the sub-critical water substantially circulating line 26. To the hydrothermal reactor 25 via
【0047】このように、原料と別個に亜臨界水を製造
し、これを水熱反応器25に供給することで、水熱反応
器25では、原料を水熱反応に必要な分だけ加熱すれば
よいため、その伝熱面積を少なくすることが可能とな
り、また熱媒と原料の温度差も大きくする必要がなくな
り、焦げ付きの問題も解消できる。As described above, by producing subcritical water separately from the raw material and supplying it to the hydrothermal reactor 25, the hydrothermal reactor 25 heats the raw material by an amount required for the hydrothermal reaction. Therefore, the heat transfer area can be reduced, the temperature difference between the heat medium and the raw material does not need to be increased, and the problem of burning can be solved.
【0048】水熱反応器25内では、供給された亜臨界
状態(300℃、10MPa)にされた亜臨界水にて、
有機性廃棄物は、炭化水素、H2 等に分解される。この
水熱反応においては、原料を循環ライン26で繰り返し
水熱反応器25に循環することで、液の流速を確保して
水熱反応器25内での伝熱を促進させる。また原料には
苛性ソーダ等の薬液を混入しているため、原料の分解が
促進される。In the hydrothermal reactor 25, the supplied subcritical water (300 ° C., 10 MPa) is used to supply
Organic waste, hydrocarbon is decomposed into H 2 and the like. In this hydrothermal reaction, the raw material is repeatedly circulated through the circulation line 26 to the hydrothermal reactor 25 to secure the flow rate of the liquid and promote heat transfer in the hydrothermal reactor 25. Further, since the raw material contains a chemical solution such as caustic soda, the decomposition of the raw material is promoted.
【0049】この後、分解処理した原料は、分解ライン
33より熱交換器24に排出されて加熱された後、トリ
ムクーラ34を通して冷却され、背圧調整弁35で減圧
されたのち、酸化槽22に供給され、そこで、可燃分や
未反応の炭化物などが燃焼酸化され、気液分離器23を
通り、一部は戻しライン39にて再度酸化槽22に戻さ
れて未酸化分が再度酸化される。Thereafter, the cracked raw material is discharged from the cracking line 33 to the heat exchanger 24 and heated, then cooled through the trim cooler 34, reduced in pressure by the back pressure regulating valve 35, and then transferred to the oxidation tank 22. Then, the combustibles and unreacted carbides are burned and oxidized there, pass through the gas-liquid separator 23, and a part is returned to the oxidation tank 22 again in the return line 39, and the unoxidized components are oxidized again. .
【0050】このように分解後の原料と、水熱反応器2
5に供給する原料を熱交換させて熱回収を行うことで、
熱媒加熱器29での熱媒供給量を少なくできる。The raw material thus decomposed and the hydrothermal reactor 2
By performing heat recovery by exchanging heat with the raw material supplied to 5,
The heating medium supply amount in the heating medium heater 29 can be reduced.
【0051】その後、酸化後の分解原料は、気液分離器
23で気液分離され、液分の処理液は、排出ライン41
を通り、熱交換器42で、上水を加熱して冷却され、背
圧調整弁43で大気圧まで下げられた後、処理液タンク
14に排出される。Thereafter, the oxidized decomposed material is separated into gas and liquid by the gas-liquid separator 23, and the treated liquid is separated into a discharge line 41.
Then, the tap water is heated and cooled in the heat exchanger 42, lowered to the atmospheric pressure by the back pressure adjusting valve 43, and then discharged to the processing liquid tank 14.
【0052】また気液分離器23で分離されたガス分
は、気相側排出ライン50から凝縮器38に導入されて
冷却され、分離ポット51に供給され、凝縮液分は、ラ
イン53にて気液分離器23に戻され、ガス分は、背圧
調整弁52で減圧されて、処理液タンク14に供給され
る。The gas separated by the gas-liquid separator 23 is introduced into the condenser 38 from the gas-phase discharge line 50 and cooled, and is supplied to the separation pot 51. The gas is returned to the gas-liquid separator 23, and the gas component is reduced in pressure by the back pressure adjusting valve 52 and supplied to the processing liquid tank 14.
【0053】処理液タンク14では、ガス分は、排気ラ
イン44より脱臭装置46を通して排気され、液分は、
下水ライン45から排水される。In the processing liquid tank 14, a gas component is exhausted from an exhaust line 44 through a deodorizing device 46.
Drained from the sewage line 45.
【0054】このように、本発明においては、従来の超
臨界処理に比べて反応温度、圧力を緩和することで、原
料の分解能力(CODの低減)では低下するが、配管等
の腐食の問題を軽減することが可能となる。また分解能
力が低減した分は、水熱反応処理後に酸化槽22で酸化
反応プロセスにより酸化処理を行うことで、結果として
十分な分解能力が得られる。As described above, in the present invention, by reducing the reaction temperature and pressure as compared with the conventional supercritical treatment, the decomposition ability of raw materials (reduction of COD) is reduced, but the problem of corrosion of piping and the like is reduced. Can be reduced. In addition, a sufficient decomposition ability can be obtained as a result of performing the oxidation treatment by the oxidation reaction process in the oxidation tank 22 after the hydrothermal reaction treatment.
【0055】さらに、水熱反応管25にて分解を行う
際、原料と別個に亜臨界水を供給することで、水熱反応
管25の伝熱面積の大幅な低減が可能となり、水熱反応
管25の焦げ付きを防止しつつ、熱媒の負荷を低減する
ことができる。Further, when decomposing in the hydrothermal reaction tube 25, by supplying subcritical water separately from the raw material, the heat transfer area of the hydrothermal reaction tube 25 can be greatly reduced, and the hydrothermal reaction The load of the heat medium can be reduced while preventing the tube 25 from sticking.
【0056】[0056]
【発明の効果】以上要するに本発明によれば、有機性廃
棄物のみの原料を通して水熱反応器に供給し、その有機
性廃棄物と混合する水は、温水ボイラからなる亜臨界水
供給手段で別途供給することで、水熱反応器は、原料分
のみの昇温を受け持てば良く伝熱面を大幅に削減するこ
とが可能となる。In summary, according to the present invention, the organic waste alone is supplied to the hydrothermal reactor through the raw material, and the water mixed with the organic waste is supplied to the subcritical water supply means comprising a hot water boiler. By supplying it separately, the hydrothermal reactor only needs to handle the temperature rise of the raw material, and the heat transfer surface can be significantly reduced.
【0057】また、亜臨界での水熱反応とその後の酸化
反応の二段階で原料を処理することで、有機性廃棄物の
下水放出が可能となる。また、CO2 の放出や有害物発
生もなく、廃棄物処分場が不要となる等の効果を発揮す
る。Further, by treating the raw material in two stages of a subcritical hydrothermal reaction and a subsequent oxidation reaction, it is possible to discharge sewage of organic waste. In addition, there is no emission of CO 2 and no harmful substances are generated, and the effects of eliminating the need for a waste disposal site are exhibited.
【図1】本発明の一実施の形態を示す基本概略構成を示
す図である。FIG. 1 is a diagram showing a basic schematic configuration showing an embodiment of the present invention.
【図2】本発明の一実施の形態を示す全体構成を示す図
である。FIG. 2 is a diagram showing an overall configuration showing an embodiment of the present invention.
【図3】先願の発明の概略構成を示す図である。FIG. 3 is a diagram showing a schematic configuration of the invention of the prior application.
10 原料タンク 18 温水ボイラ 19 亜臨界水供給手段 19a 加熱手段 22 酸化槽 25 水熱反応器 Reference Signs List 10 raw material tank 18 hot water boiler 19 subcritical water supply means 19a heating means 22 oxidation tank 25 hydrothermal reactor
Claims (3)
状態まで加圧・加熱して水熱反応させる水熱反応器と、
該水熱反応器に予め水熱条件まで加熱・昇圧した亜臨界
水を有機性廃棄物と共に水熱反応器に供給する亜臨界水
供給手段とを備えたことを特徴とする水熱反応による動
植物残渣等有機性廃棄物処理装置。1. A hydrothermal reactor for hydrothermally reacting an organic waste such as animal and plant residues to a subcritical state by pressurizing and heating the waste.
Sub-critical water supply means for supplying sub-critical water heated and pressurized to hydrothermal conditions in advance to the hydrothermal reactor together with organic waste to the hydrothermal reactor Organic waste treatment equipment such as residue.
上水タンクの上水を昇圧する昇圧ポンプと昇圧された上
水を約100〜300℃程度に加熱する加熱手段とから
なり、他方、水熱反応器には、有機性廃棄物を水熱反応
器に繰り返し循環する循環ラインが接続され、上記加熱
手段が循環ラインに接続される請求項1記載の動植物残
渣等有機性廃棄物処理装置。2. The sub-critical water supply means comprises a water tank, a booster pump for increasing the pressure of the water in the water tank, and a heating means for heating the boosted water to about 100 to 300 ° C. The organic waste such as animal and plant residues according to claim 1, wherein a circulation line for repeatedly circulating the organic waste to the hydrothermal reactor is connected to the hydrothermal reactor, and the heating means is connected to the circulation line. Processing equipment.
機性廃棄物残渣を、酸化する酸化槽が接続される請求項
2記載の動植物残渣等有機性廃棄物処理装置。3. The apparatus for treating organic waste such as animal and plant residues according to claim 2, wherein an oxidation tank for oxidizing the organic waste residues decomposed and decompressed is connected to the circulation line.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000309175A JP2002113348A (en) | 2000-10-10 | 2000-10-10 | Treating apparatus of organic waste from animal and vegetable residue by hydrothermal reaction |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000309175A JP2002113348A (en) | 2000-10-10 | 2000-10-10 | Treating apparatus of organic waste from animal and vegetable residue by hydrothermal reaction |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2002113348A true JP2002113348A (en) | 2002-04-16 |
Family
ID=18789384
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP2000309175A Pending JP2002113348A (en) | 2000-10-10 | 2000-10-10 | Treating apparatus of organic waste from animal and vegetable residue by hydrothermal reaction |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005081332A (en) * | 2003-09-11 | 2005-03-31 | Osaka Industrial Promotion Organization | Method for treating waste originated from plant |
JP2005262177A (en) * | 2004-03-22 | 2005-09-29 | Ngk Insulators Ltd | High-temperature high-pressure treatment apparatus for organic waste |
JP2005270816A (en) * | 2004-03-25 | 2005-10-06 | Ngk Insulators Ltd | High temperature, high pressure treatment apparatus for organic waste |
JP2007291065A (en) * | 2006-02-15 | 2007-11-08 | Kenji Yamamoto | Method for producing polyphenol, vanillin, protocatechuic acid and vanillic acid |
-
2000
- 2000-10-10 JP JP2000309175A patent/JP2002113348A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005081332A (en) * | 2003-09-11 | 2005-03-31 | Osaka Industrial Promotion Organization | Method for treating waste originated from plant |
JP2005262177A (en) * | 2004-03-22 | 2005-09-29 | Ngk Insulators Ltd | High-temperature high-pressure treatment apparatus for organic waste |
JP2005270816A (en) * | 2004-03-25 | 2005-10-06 | Ngk Insulators Ltd | High temperature, high pressure treatment apparatus for organic waste |
JP2007291065A (en) * | 2006-02-15 | 2007-11-08 | Kenji Yamamoto | Method for producing polyphenol, vanillin, protocatechuic acid and vanillic acid |
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