JP6737561B1 - Subcritical water treatment device - Google Patents
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- JP6737561B1 JP6737561B1 JP2020073937A JP2020073937A JP6737561B1 JP 6737561 B1 JP6737561 B1 JP 6737561B1 JP 2020073937 A JP2020073937 A JP 2020073937A JP 2020073937 A JP2020073937 A JP 2020073937A JP 6737561 B1 JP6737561 B1 JP 6737561B1
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 54
- 238000006243 chemical reaction Methods 0.000 claims abstract description 50
- 238000010438 heat treatment Methods 0.000 claims abstract description 42
- 238000003756 stirring Methods 0.000 claims abstract description 13
- 239000000463 material Substances 0.000 claims description 4
- 238000010586 diagram Methods 0.000 abstract description 2
- 238000000605 extraction Methods 0.000 abstract description 2
- 239000002699 waste material Substances 0.000 description 8
- 239000000126 substance Substances 0.000 description 7
- 229920006395 saturated elastomer Polymers 0.000 description 6
- 239000005416 organic matter Substances 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 238000007790 scraping Methods 0.000 description 4
- 238000005452 bending Methods 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 3
- 239000002440 industrial waste Substances 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000010815 organic waste Substances 0.000 description 3
- PUKLDDOGISCFCP-JSQCKWNTSA-N 21-Deoxycortisone Chemical compound C1CC2=CC(=O)CC[C@]2(C)[C@@H]2[C@@H]1[C@@H]1CC[C@@](C(=O)C)(O)[C@@]1(C)CC2=O PUKLDDOGISCFCP-JSQCKWNTSA-N 0.000 description 2
- FCYKAQOGGFGCMD-UHFFFAOYSA-N Fulvic acid Natural products O1C2=CC(O)=C(O)C(C(O)=O)=C2C(=O)C2=C1CC(C)(O)OC2 FCYKAQOGGFGCMD-UHFFFAOYSA-N 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 239000002509 fulvic acid Substances 0.000 description 2
- 229940095100 fulvic acid Drugs 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000006864 oxidative decomposition reaction Methods 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000005431 greenhouse gas Substances 0.000 description 1
- 239000011810 insulating material Substances 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- MKTRXTLKNXLULX-UHFFFAOYSA-P pentacalcium;dioxido(oxo)silane;hydron;tetrahydrate Chemical compound [H+].[H+].O.O.O.O.[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O.[O-][Si]([O-])=O MKTRXTLKNXLULX-UHFFFAOYSA-P 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F27/00—Mixers with rotary stirring devices in fixed receptacles; Kneaders
- B01F27/60—Mixers with rotary stirring devices in fixed receptacles; Kneaders with stirrers rotating about a horizontal or inclined axis
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F27/00—Mixers with rotary stirring devices in fixed receptacles; Kneaders
- B01F27/60—Mixers with rotary stirring devices in fixed receptacles; Kneaders with stirrers rotating about a horizontal or inclined axis
- B01F27/70—Mixers with rotary stirring devices in fixed receptacles; Kneaders with stirrers rotating about a horizontal or inclined axis with paddles, blades or arms
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J3/00—Processes of utilising sub-atmospheric or super-atmospheric pressure to effect chemical or physical change of matter; Apparatus therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J3/00—Processes of utilising sub-atmospheric or super-atmospheric pressure to effect chemical or physical change of matter; Apparatus therefor
- B01J3/02—Feed or outlet devices therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J3/00—Processes of utilising sub-atmospheric or super-atmospheric pressure to effect chemical or physical change of matter; Apparatus therefor
- B01J3/04—Pressure vessels, e.g. autoclaves
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22B—METHODS OF STEAM GENERATION; STEAM BOILERS
- F22B3/00—Other methods of steam generation; Steam boilers not provided for in other groups of this subclass
- F22B3/08—Other methods of steam generation; Steam boilers not provided for in other groups of this subclass at critical or supercritical pressure values
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- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
- Mixers Of The Rotary Stirring Type (AREA)
Abstract
【課題】 大型化しても処理を均一に行える亜臨界水処理装置を提供する。【解決手段】加熱蒸気供給路4は遠隔操作バルブ6の下流側において分岐し、反応槽3の天井部の複数個所から加熱蒸気を反応槽3内に供給する。反応槽3内に供給される加熱蒸気は少なくとも2Mpa、300℃となっている。一方、循環路5は取出部9を避けて反応槽3の底面外側に沿ってラビリンス状に配置されている。循環路5を反応槽3内に設けると、攪拌装置との干渉を生じ、また被処理物の溜まり場が形成されるため、底面外側に配置する。【選択図】 図1PROBLEM TO BE SOLVED: To provide a subcritical water treatment device capable of performing uniform treatment even if the size is increased. SOLUTION: A heating steam supply path 4 branches downstream of a remote control valve 6 and supplies heating steam into the reaction tank 3 from a plurality of places on the ceiling of the reaction tank 3. The heating steam supplied into the reaction tank 3 is at least 2 MPa and 300°C. On the other hand, the circulation path 5 is arranged in a labyrinth shape along the outside of the bottom surface of the reaction tank 3 while avoiding the extraction section 9. When the circulation path 5 is provided in the reaction tank 3, it interferes with the stirring device and forms a pool for the object to be treated, so that the circulation path 5 is arranged outside the bottom surface. [Selection diagram]
Description
本発明は、亜臨界水を用いた有機系廃棄物などの処理装置に関する。 The present invention relates to a treatment device for organic waste using subcritical water.
有機系廃棄物を焼却炉や熱回収炉内において燃焼させて焼却処理すると、環境汚染の原因となる温暖化ガス、ダイオキシン、窒素酸化物などの有害物質が生成される場合がある。このため、超臨界水条件下(22.1MPa以上、374℃以上)の温度・圧力の超臨界水や亜臨界水条件下(1〜8MPa、100〜300℃)の亜臨界水を用いた処理方法が提案されている。 When organic waste is burned in an incinerator or heat recovery furnace to be incinerated, harmful substances such as greenhouse gases, dioxins, and nitrogen oxides, which cause environmental pollution, may be generated. Therefore, treatment using supercritical water having a temperature/pressure under supercritical water conditions (22.1 MPa or more and 374° C. or more) and subcritical water under subcritical water conditions (1-8 MPa, 100-300° C.) A method has been proposed.
100℃1気圧の水蒸気は飽和水蒸気であり、それに比較し高温高圧下の水蒸気は加熱蒸気(過熱水蒸気)であり、100℃1気圧の飽和水蒸気に比べてエンタルピーが高い。 Steam at 100° C. and 1 atmosphere is saturated steam, and steam under high temperature and high pressure is heated steam (superheated steam), and has a higher enthalpy than saturated steam at 100° C. and 1 atmosphere.
特許文献1には、重金属類を含む廃棄物の処理装置として、密閉容器、蒸気噴出手段、冷却手段及び分離回収手段とから構成され、前記密閉容器の内部に重金属類を含む廃棄物および処理中に少なくとも前記重金属類を結晶構造中に封じ込めるための5CaO・6SiO2・5H2O結晶(トバモライト)が形成されるのに十分な量のCa成分原料およびSiO2成分原料を収容するものが提案されている。
In
特許文献2には、廃棄物を高温高圧の蒸気を用いて処理する装置に連続して、処理された廃棄物と液体とを簡単な操作で分離して回収できる有機系廃棄物の処理装置が開示されている。
特許文献3には、フルボ酸の製造装置として、内部に木材チップである原料を収容する閉鎖空間を有する密閉容器と、密閉容器内に亜臨界水である高温高圧の蒸気を噴出する蒸気噴出手段と、密閉容器の底側に設けられ開閉機構を有する排出口と、排出口からの直接排出操作のみで処理された原料と液体とを分離して回収する分離回収手段を備えた構造が提案されている。
In
特許文献4には、産業廃棄物の加熱処理に用いる加熱蒸気(過熱水蒸気)を用いた加熱装置が開示されている。具体的には、流路を通過する被加熱物を加熱する加熱装置の上記流路として、電気抵抗率が100μΩ・cm以上である高抵抗素材からなり、外部が断熱層で被覆された中空状の発熱パイプの中空部が提案されている。 Patent Document 4 discloses a heating device using heated steam (superheated steam) used for heat treatment of industrial waste. Specifically, the flow path of the heating device for heating an object to be heated that passes through the flow path is made of a high resistance material having an electric resistivity of 100 μΩ·cm or more, and has a hollow shape whose outside is covered with a heat insulating layer. The hollow part of the heat generating pipe has been proposed.
特許文献5には、超臨界水又は亜臨界水による有機物質等の反応装置が開示されている。この反応装置は水蒸気を圧縮して超臨界水又は亜臨界水を得る手段と、この超臨界水又は亜臨界水を有機物等の被反応物質に接触させて化学反応を行なわせる手段と、この化学反応によって生じる生成物を含む水を膨張させて減圧させる手段とから構成される。
特許文献6には、超臨界水、亜臨界水、蒸気の少なくともいずれかを抽出して超臨界水を得て、この超臨界水を利用した蒸気プラントが開示されている。この蒸気プラントはボイラ給水系統と蒸気供給系統とを備え、ボイラ、ボイラ給水系統または蒸気供給系統のいずれかの部位より超臨界水、亜臨界水または蒸気を抽出して超臨界水を得る超臨界水取り出し装置と、この超臨界水取り出し装置によって得た超臨界水を溶媒とし、有機物を酸化分解処理する有機物分解反応タンクと、有機物の酸化分解処理により生成した処理済水を取り出す処理済水取り出し装置とを有する超臨界水有機物処理設備から構成される。 Patent Document 6 discloses a steam plant that uses supercritical water by extracting at least one of supercritical water, subcritical water, and steam to obtain supercritical water. This steam plant is equipped with a boiler water supply system and a steam supply system, and obtains supercritical water by extracting supercritical water, subcritical water or steam from any part of the boiler, the boiler water supply system or the steam supply system. Water removal device, organic matter decomposition reaction tank for oxidative decomposition of organic matter using supercritical water obtained by this supercritical water removal device as a solvent, and removal of treated water generated by oxidative decomposition of organic matter And a supercritical water organic matter treatment facility having a device.
上記した特許文献に開示される装置は、比較的小型(6m3以下)であれば、効率よく稼働する。しかしながら、大きな容量の反応槽とした場合、加熱蒸気が全体に行き渡らず、部分的に亜臨界水処理反応が進まず分解処理が不均一になりやすい。 The device disclosed in the above-mentioned patent document operates efficiently if it is relatively small (6 m 3 or less). However, in the case of a large-capacity reaction tank, the heating steam does not reach the whole, and the subcritical water treatment reaction does not proceed partially and the decomposition treatment tends to be non-uniform.
また、加熱蒸気が処理物に熱を奪われ、亜臨界水は飽和蒸気を経て温水となり、反応槽内に溜まってしまう問題がある。 Further, there is a problem that the heated steam removes heat from the processed material, and the subcritical water passes through the saturated steam to become hot water and accumulates in the reaction tank.
上記の課題を解消するため、亜臨界水よりも高温の加熱蒸気(高温高圧蒸気)は均一処理が難しいが、亜臨界水と組み合わせることで均一処理が可能になるという知見に基づいて本発明を成した。 In order to solve the above problems, it is difficult to uniformly treat heated steam (high-temperature high-pressure steam) having a temperature higher than that of subcritical water, but the present invention is based on the finding that uniform treatment is possible by combining with subcritical water. I made it.
具体的には、本発明に係る亜臨界水処理装置は、飽和蒸気を発生するボイラと、このボイラからの飽和蒸気を亜臨界水状態の加熱蒸気に変換する加熱蒸気発生装置と、この加熱蒸気発生装置からの加熱蒸気を反応槽の天井部から供給する加熱蒸気供給路と、前記反応槽の底面外側に沿って配置され前記加熱蒸気発生装置からの加熱蒸気を前記ボイラに戻す循環経路とから構成される。 Specifically, the subcritical water treatment apparatus according to the present invention is a boiler that generates saturated steam, a heating steam generator that converts saturated steam from this boiler into heating steam in a subcritical water state, and this heating steam. From the heating steam supply path for supplying the heating steam from the generator from the ceiling of the reaction tank, and the circulation path for returning the heating steam from the heating steam generator arranged along the outside of the bottom surface of the reaction tank to the boiler. Composed.
前記加熱蒸気供給路には、処理の間だけ加熱蒸気供給路を開とする遠隔操作バルブを設け、一方循環経路には常時加熱蒸気を流すことが好ましい。 It is preferable that the heating steam supply path is provided with a remote control valve that opens the heating steam supply path only during the treatment, while the heating steam is constantly supplied to the circulation path.
また反応槽の形状は両側面を閉じた横置き筒状をなし、この反応槽内には回転軸と攪拌羽根が収納され、攪拌羽根は順方向回転時には被処理物を攪拌し、逆方向回転時には被処理物を掻き出す構造とすることができる。 In addition, the shape of the reaction tank is a horizontal cylinder with both sides closed, and the rotation shaft and stirring blades are housed in this reaction tank.The stirring blades stir the object to be processed when rotating in the forward direction and rotate in the reverse direction. Sometimes, the structure can be such that the object to be processed is scraped out.
本発明によれば、反応槽を大型化しても廃棄物などの被処理物によって局所的に加熱蒸気の熱が奪われて水になりにくく、反応槽全体で分解反応が均一に行われる。また、反応槽を大型化できるので、1日当たりの廃棄物の処理量を大幅に増やすことができる。 According to the present invention, even if the reaction tank is upsized, the heat of the heated steam is locally removed by the object to be treated such as waste, and the water is unlikely to become water, so that the decomposition reaction is uniformly carried out in the entire reaction tank. In addition, since the reaction tank can be upsized, the amount of waste processed per day can be significantly increased.
特に、反応槽の底面外側面から循環経路内を流れる加熱蒸気で反応槽内を常時加熱することで、反応槽内全体の温度を均一に維持でき、また処理時のみに反応槽の天井部から加熱蒸気を供給すればよいので熱効率が向上する。 In particular, by constantly heating the inside of the reaction tank with the heating steam flowing from the outside of the bottom surface of the reaction tank in the circulation path, it is possible to maintain a uniform temperature throughout the reaction tank, and from the ceiling of the reaction tank only during processing. Since it suffices to supply heated steam, thermal efficiency is improved.
また、反応槽内に配置する攪拌装置の羽根構造として、順方向回転時には被処理物を攪拌し、逆方向回転時には被処理物を掻き出す構造とすることで、反応槽の形状を中央部が大径のラグビーボール形状とせず、単純な筒状としても、内部に処理対象物や処理後物質が残りにくい。 In addition, the blade structure of the stirring device placed in the reaction tank is such that the object to be processed is stirred when rotating in the forward direction and is scraped out when rotating in the reverse direction, so that the shape of the reaction tank has a large central part. Even if it is not a rugby ball shape with a diameter but a simple tubular shape, it is difficult for the object to be treated or the substance after treatment to remain inside.
以下に本発明の実施例を添付図面を参照しつつ説明する。
亜臨界水処理装置は亜臨界水状態(1〜2MPa、100〜250℃)の蒸気を発生するボイラ1と、このボイラ1からの亜臨界水を更に高温高圧の加熱蒸気に変換する加熱蒸気発生装置2と、この加熱蒸気発生装置2からの加熱蒸気を反応槽3の天井部から供給する加熱蒸気供給路4と、前記反応槽3の底面外側に沿って配置され前記加熱蒸気発生装置2からの加熱蒸気を前記ボイラ1に戻す循環路5から構成される。又、ボイラ1に飽和蒸気と過熱蒸気を生成する装置が付加することは厭わない。
Embodiments of the present invention will be described below with reference to the accompanying drawings.
The subcritical water treatment device is a
前記加熱蒸気供給路4と循環路5には遠隔操作バルブ6、7が設けられ、遠隔操作バルブ6は廃棄物を分解処理する間だけ開とし、遠隔操作バルブ7は長時間装置を停止する以外は常時開とし、反応槽3の全体の温度を一定以上に保っている。
Remotely operated
反応槽3は全体形状が両側端を閉じた筒状をなし、上部には産業廃棄物などの被処理物の投入部8が設けられ、底部には反応後の被処理物の取出部9が設けられている。取出部9はドレインの排出部も兼ねる。
The
加熱蒸気供給路4は遠隔操作バルブ6の下流側において分岐し、反応槽3の天井部の複数個所から加熱蒸気を反応槽3内に供給する。反応槽3内に供給される加熱蒸気は少なくとも2Mpa、300℃となっている。
The heating steam supply path 4 branches off on the downstream side of the remote control valve 6 and supplies the heating steam into the
循環路5は遠隔操作バルブ7の下流側において分岐し、取出部9を避けて反応槽3の底面外側に沿ってラビリンス状に配置されている。ボイラ1への還流側は、バルブ7より下部に位置し、ウォーターハンマー現象を防ぐ構造になっている。循環路5を反応槽3内に設けると、攪拌装置との干渉を生じ、また被処理物の溜まり場が形成されるため、底面を二重構造とし、この中に断熱材とともに配置する。ただし、熱放射(伝熱)効率を高めるため、反応槽3の表面との距離はできるだけ小さくし、接触させてもよい。加えて、熱交換を高めるため、ラジエーター構造にしても良い。
The
反応槽3内には攪拌装置10が配置されている。攪拌装置10は反応槽3の中心部に挿入される回転軸11に所定間隔で支持ロッド12を取付け、この支持ロッド12の先端にスプリング13を介して屈曲プレート14を取付けている。
A stirring
図5に示すように屈曲プレート14は攪拌部15と掻取部16からなり、掻取部16の外側面がスプリング13の弾発力で反応槽3の内面に押し付けられる。そして、順方向に回転する時には被処理物は反応槽3内で攪拌され、逆方向に回転する時には、被処理物は掻き出される。
As shown in FIG. 5, the
例えば、図1において、攪拌装置10を右側の攪拌装置10と左側の攪拌装置10に分け、それぞれの攪拌装置10の屈曲プレート14の向きを逆にする(攪拌部15と掻取部16の向きを逆にする)ことで、攪拌と掻取を効果的に行うことができる。
For example, in FIG. 1, the
以上において、循環路5内を流れる加熱蒸気によって、反応槽3全体が均一に加熱された状態で、産業廃棄物などの被処理物を投入部8から反応槽3内に投入し、同時に遠隔操作バルブ6を開として、加熱蒸気供給路4から反応槽3内に加熱蒸気(亜臨界水)を供給する。
In the above, while the
反応槽3内の被処理物は攪拌され、1〜8MPa、100〜300℃の条件下で低分子化される。
例えば、都市ごみは水熱分解されて堆肥となり、魚残渣や家畜からはアミノ酸が生産され、木材は飼料となりフルボ酸が生産される。
The substance to be treated in the
For example, municipal waste is hydrothermally decomposed into compost, amino acids are produced from fish residues and livestock, and wood is used as feed to produce fulvic acid.
1…ボイラ、2…加熱蒸気発生装置、3…反応槽、4…加熱蒸気供給路、5…循環路、6、7…遠隔操作バルブ、8…被処理物の投入部、9…被処理物の取出部、10…攪拌装置、11…回転軸、12…支持ロッド、13…スプリング、14…屈曲プレート、15…攪拌部、16…掻取部。
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