JP2011072948A - Waste treatment method and waste treatment apparatus - Google Patents

Waste treatment method and waste treatment apparatus Download PDF

Info

Publication number
JP2011072948A
JP2011072948A JP2009228750A JP2009228750A JP2011072948A JP 2011072948 A JP2011072948 A JP 2011072948A JP 2009228750 A JP2009228750 A JP 2009228750A JP 2009228750 A JP2009228750 A JP 2009228750A JP 2011072948 A JP2011072948 A JP 2011072948A
Authority
JP
Japan
Prior art keywords
organic waste
waste
water
condensed water
chemical substance
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.)
Granted
Application number
JP2009228750A
Other languages
Japanese (ja)
Other versions
JP5630682B2 (en
Inventor
Taisuke Araki
泰輔 荒木
So Kadono
壮 門野
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.)
Sumitomo Osaka Cement Co Ltd
Original Assignee
Sumitomo Osaka Cement 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 Sumitomo Osaka Cement Co Ltd filed Critical Sumitomo Osaka Cement Co Ltd
Priority to JP2009228750A priority Critical patent/JP5630682B2/en
Publication of JP2011072948A publication Critical patent/JP2011072948A/en
Application granted granted Critical
Publication of JP5630682B2 publication Critical patent/JP5630682B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a waste treatment method and a waste treatment apparatus, which can suppress a remaining of a water-soluble chemical substance in a treated material after an organic waste containing the water-soluble chemical substance is treated. <P>SOLUTION: The waste treatment method includes contacting the organic waste having the water-soluble chemical substance with saturated steam of 150°C or higher in a sealed reactor to decompose the organic waste. While condensate water formed by a condensation of the saturated steam on the surface of the organic waste is separated from the organic waste, the organic waste is decomposed. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、有機性廃棄物を水蒸気を用いて処理する廃棄物処理方法及び廃棄物処理装置に関する。   The present invention relates to a waste treatment method and a waste treatment apparatus for treating organic waste with water vapor.

近年、環境保全や資源の有効利用を図る観点から、廃棄物(産業廃棄物や一般廃棄物等)を適当な方法で処理し、得られた処理物を様々な用途で使用する試みがなされている。例えば、生ゴミ、食品残渣、家畜の糞尿等からなる有機性廃棄物を高温の飽和水蒸気と接触させて分解した後、分解された有機性廃棄物を加熱して乾燥することで付着した飽和水蒸気の凝縮水を蒸発させ、乾燥した処理物を燃料として使用する試みがされている(特許文献1参照)。   In recent years, from the viewpoint of environmental protection and effective use of resources, attempts have been made to treat waste (industrial waste, general waste, etc.) by an appropriate method, and use the obtained treatment for various purposes. Yes. For example, organic waste consisting of garbage, food residues, livestock manure, etc. is decomposed by contacting with high-temperature saturated steam, and then the decomposed organic waste is heated and dried to adhere to saturated steam Attempts have been made to evaporate the condensed water and use the dried processed product as fuel (see Patent Document 1).

上記のような処理方法によれば、密閉された反応容器内で有機性廃棄物が高温の飽和水蒸気によって加熱されて加水分解されるため、細粉化された処理物を得ることができると共に、有機性廃棄物の燃焼を伴わないため、有機性廃棄物が元来保有する熱量を減少させることなく有機性廃棄物を細粒化させることができる。このため、得られた処理物は、良質な燃料として使用することができ、例えば、セメントを製造する際に用いられる焼成炉や各種ボイラー等の燃焼設備の燃料として使用することができる。   According to the treatment method as described above, the organic waste is heated and hydrolyzed by high-temperature saturated steam in a sealed reaction vessel, so that a finely ground treatment product can be obtained, Since the organic waste is not burned, the organic waste can be made fine without reducing the amount of heat originally held by the organic waste. For this reason, the obtained processed material can be used as a high-quality fuel, for example, it can be used as a fuel for combustion equipment such as a firing furnace or various boilers used when producing cement.

特開2007−136312号公報JP 2007-136312 A

しかしながら、上記のような方法では、処理物に付着した凝縮水には、有機性廃棄物に含有されていた水溶性の化学物質が溶け出しているため、処理物を乾燥させることによって水溶性の化学物質が濃縮されて高濃度で処理物中に残存することとなる。   However, in the method as described above, since the water-soluble chemical substance contained in the organic waste is dissolved in the condensed water adhering to the treated product, the water-soluble chemical substance is dissolved by drying the treated product. The chemical substance is concentrated and remains in the processed material at a high concentration.

そして、このような処理物を燃料として用いた場合、残存する化学物質の影響によって燃焼設備の劣化を促進させてしまったり、損傷させてしまったりする場合がある。特に、食品残渣等からなる有機性廃棄物には塩素化合物が含有されているものが多いため、上記のような方法では、処理物中に塩素成分が濃縮されて高濃度で残存することとなり、燃焼設備を腐食させてしまう場合がある。   When such a processed product is used as a fuel, deterioration of the combustion facility may be accelerated or damaged due to the influence of the remaining chemical substances. In particular, organic waste consisting of food residues and the like contains many chlorine compounds, so in the above method, the chlorine component is concentrated in the treated product and remains at a high concentration. The combustion equipment may be corroded.

また、焼成炉の燃料として用いた場合、残存する化学物質がセメント中に含有される虞があり、セメントの品質低下を招く要因となる場合もある。   Further, when used as a fuel for a firing furnace, residual chemical substances may be contained in the cement, which may cause a deterioration in the quality of the cement.

そこで、本発明は、このような従来技術の問題点に鑑みてなされたものであり、水溶性の化学物質を含有する有機性廃棄物を処理した後の処理物中に前記水溶性の化学物質が残存するのを抑制することができる廃棄物処理方法及び廃棄物処理装置を提供することを目的とする。   Therefore, the present invention has been made in view of such problems of the prior art, and the water-soluble chemical substance is contained in a treated product after treating an organic waste containing a water-soluble chemical substance. An object of the present invention is to provide a waste treatment method and a waste treatment apparatus that can suppress the remaining of the waste.

本発明にかかる廃棄物処理方法は、水溶性の化学物質を含有する有機性廃棄物を密閉された反応容器内で150℃以上の飽和水蒸気と接触させて有機性廃棄物を分解する廃棄物処理方法であって、前記有機性廃棄物の表面に飽和水蒸気が凝縮して形成された凝縮水を有機性廃棄物から分離させつつ有機性廃棄物を分解することを特徴とする。   The waste treatment method according to the present invention is a waste treatment method in which an organic waste containing a water-soluble chemical substance is brought into contact with saturated steam at 150 ° C. or higher in a sealed reaction vessel to decompose the organic waste. The method is characterized in that the organic waste is decomposed while separating the condensed water formed by condensation of saturated water vapor on the surface of the organic waste from the organic waste.

斯かる構成の廃棄物処理方法によれば、前記温度の飽和水蒸気と有機性廃棄物との接触によって、有機性廃棄物は、加水分解されて細粒化されると共に、有機性廃棄物の表面には飽和水蒸気の凝縮水が形成される。斯かる凝縮水には、有機性廃棄物中の水溶性の化学物質が溶出しているため、凝縮水を有機性廃棄物から分離させることで、細粒化された有機性廃棄物(以下、処理物と記す)中に水溶性の化学物質が残存するのを抑制することができる。   According to the waste treatment method having such a configuration, the organic waste is hydrolyzed and finely divided by the contact between the saturated water vapor at the temperature and the organic waste, and the surface of the organic waste In this, condensed water of saturated water vapor is formed. In such condensed water, water-soluble chemical substances in the organic waste are eluted, so by separating the condensed water from the organic waste, The water-soluble chemical substance can be prevented from remaining in the treated product).

本発明にかかる廃棄物処理装置は、水溶性の化学物質を含有する有機性廃棄物を密閉された反応容器内で150℃以上の飽和水蒸気と接触させて有機性廃棄物を分解する廃棄物処理装置であって、前記反応容器は、内部に配置された有機性廃棄物の下方領域に、有機性廃棄物の表面に凝縮する飽和水蒸気の凝縮水を回収する凝縮水回収空間が形成されるように有機性廃棄物を支持する廃棄物支持手段を備えることを特徴とする。   The waste treatment apparatus according to the present invention is a waste treatment method in which an organic waste containing a water-soluble chemical substance is brought into contact with saturated steam at 150 ° C. or higher in a sealed reaction vessel to decompose the organic waste. In the reaction vessel, a condensed water recovery space for recovering condensed water of saturated water vapor condensed on the surface of the organic waste is formed in a lower region of the organic waste disposed therein. And a waste supporting means for supporting organic waste.

斯かる構成によれば、反応容器が廃棄物支持手段を備え、該廃棄物支持手段によって、有機性廃棄物の下方領域に凝縮水回収空間が形成されることで、凝縮水回収空間に凝縮水を滴下させて回収することができ、処理物と凝縮水とを容易に分離することができる。これにより、処理物と凝縮水との接触が防止され、処理物中に水溶性の化学物質が残存するのを抑制することができる。   According to such a configuration, the reaction container includes the waste support means, and the condensed water recovery space is formed in the lower region of the organic waste by the waste support means, so that the condensed water is contained in the condensed water recovery space. Can be recovered by dropping, and the treated product and condensed water can be easily separated. Thereby, a contact with a processed material and condensed water is prevented, and it can suppress that a water-soluble chemical substance remains in a processed material.

また、本発明にかかる廃棄物処理装置は、前記廃棄物支持手段が有機性廃棄物を載置可能に構成された載置部を備え、該載置部には、前記凝縮水回収空間に連通する貫通孔が形成されていることが好ましい。   In the waste treatment apparatus according to the present invention, the waste support means includes a placement portion configured to be capable of placing organic waste, and the placement portion communicates with the condensed water recovery space. It is preferable that a through hole is formed.

斯かる構成によれば、前記廃棄物支持手段が有機性廃棄物を載置する載置部を備え、該載置部に貫通孔が形成されていることで、有機性廃棄物を下方から確実に支持した状態で処理することができると共に、貫通孔を通じて凝縮水を確実に凝縮水回収空間に送ることができる。また、回収された凝縮水と処理物との間に載置部が存在するため、凝縮水と処理物とを確実に分離することができる。   According to such a configuration, the waste support means includes the mounting portion on which the organic waste is placed, and the through-hole is formed in the placing portion, so that the organic waste can be reliably seen from below. And the condensed water can be reliably sent to the condensed water recovery space through the through hole. Moreover, since a mounting part exists between the collect | recovered condensed water and a processed material, condensed water and a processed material can be isolate | separated reliably.

以上のように、本発明によれば、水溶性の化学物質を含有する有機性廃棄物を処理した後の処理物中に前記水溶性の化学物質が残存するのを抑制することができる。   As mentioned above, according to this invention, it can suppress that the said water-soluble chemical substance remains in the processed material after processing the organic waste containing a water-soluble chemical substance.

(a)は、本実施形態に係る廃棄物処理装置を側方から見た際の一部断面図、(b)は、(a)のX−X断面図。(A) is a fragmentary sectional view at the time of seeing the waste disposal apparatus concerning this embodiment from the side, (b) is XX sectional drawing of (a). 実施例において、有機性廃棄物を処理する際の圧力容器内を示した図。The figure which showed the inside of the pressure vessel at the time of processing organic waste in an Example.

以下、本発明にかかる実施形態について、図1を参照しながら説明する。   Hereinafter, an embodiment according to the present invention will be described with reference to FIG.

本実施形態にかかる廃棄物処理装置1は、有機性廃棄物Aの処理に用いられるものである。具体的には、廃棄物処理装置1は、生ゴミ、食品残渣、家畜の糞尿、プラスチック、有機性汚泥等からなる有機性廃棄物Aを処理対象とするものである。具体的には、廃棄物処理装置1は、有機性廃棄物Aを高温高圧下の飽和水蒸気と接触させることによって分解するものである。   The waste treatment apparatus 1 according to this embodiment is used for the treatment of organic waste A. Specifically, the waste treatment apparatus 1 is intended for treating organic waste A composed of raw garbage, food residues, livestock manure, plastic, organic sludge, and the like. Specifically, the waste treatment apparatus 1 decomposes the organic waste A by bringing it into contact with saturated steam under high temperature and high pressure.

前記廃棄物処理装置1は、有機性廃棄物Aを内部に配置可能に構成された反応容器2と、該反応容器2の内部に水蒸気を供給する水蒸気供給手段3と、前記反応容器2内の有機性廃棄物Aを撹拌する撹拌手段4とを備えている。   The waste treatment apparatus 1 includes a reaction vessel 2 configured to be able to arrange organic waste A therein, a water vapor supply means 3 for supplying water vapor into the reaction vessel 2, Stirring means 4 for stirring the organic waste A is provided.

前記反応容器2は、密閉可能に構成されると共に、内部が高圧となった状態を維持可能に構成されている。また、反応容器2は、筒状(本実施形態では、円筒状)に形成された容器本体2aと、該容器本体2aの端部を閉塞する閉塞蓋2bとから構成されている。本実施形態では、容器本体2aは、一端部が閉塞された状態となっており、他端部が前記閉塞蓋2bによって閉塞されるように構成されている。   The reaction vessel 2 is configured to be hermetically sealed and configured to be able to maintain a state in which the inside is at a high pressure. Moreover, the reaction container 2 is comprised from the container main body 2a formed in the cylinder shape (this embodiment cylindrical shape), and the obstruction | occlusion lid 2b which obstruct | occludes the edge part of this container main body 2a. In the present embodiment, the container body 2a is configured such that one end is closed and the other end is closed by the closing lid 2b.

閉塞蓋2bは、容器本体2aに対して着脱可能、或いは、開閉可能に構成され、容器本体2aから閉塞蓋2bを取り外したり、閉塞蓋2bを開いたりすることで、容器本体2aの他端部を開口させることが可能となっている。また、容器本体2aの閉塞された一端部には、前記撹拌手段4が容器本体2aの内外を貫通するように取り付けられている。また、本実施形態では、反応容器2は、筒状の容器本体2aの軸が略水平となるように配置されている。なお、以下の説明において、反応容器2の「上」「下」とは、前記軸が略水平となる状態での「上」「下」を意味する。   The closing lid 2b is configured to be detachable from the container main body 2a or to be opened and closed. The other end of the container main body 2a is removed by removing the closing lid 2b from the container main body 2a or opening the closing lid 2b. Can be opened. Further, the stirring means 4 is attached to one end of the container body 2a that is closed so as to penetrate the inside and outside of the container body 2a. Moreover, in this embodiment, the reaction container 2 is arrange | positioned so that the axis | shaft of the cylindrical container main body 2a may become substantially horizontal. In the following description, “upper” and “lower” of the reaction vessel 2 mean “upper” and “lower” when the axis is substantially horizontal.

また、反応容器2(具体的には、容器本体2a)は、有機性廃棄物Aを反応容器2の内部に供給する供給部2cと、前記飽和水蒸気が凝縮した凝縮水Bを外部へ排出する排出部2dとを備えている。前記供給部2cは、反応容器2(具体的には、容器本体2a)の上側に位置するように形成されている。一方、排出部2dは、反応容器2(具体的には、容器本体2a)の下側に位置するように形成されている。   In addition, the reaction vessel 2 (specifically, the vessel body 2a) discharges the condensed water B in which the saturated water vapor is condensed and the supply unit 2c for supplying the organic waste A to the inside of the reaction vessel 2 to the outside. And a discharge part 2d. The supply part 2c is formed so as to be positioned above the reaction container 2 (specifically, the container body 2a). On the other hand, the discharge part 2d is formed to be positioned below the reaction vessel 2 (specifically, the vessel body 2a).

また、反応容器2は、内部に配置された有機性廃棄物Aの下方領域に凝縮水Bを回収する凝縮水回収空間2fが形成されるように構成されている。具体的には、反応容器2は、内部に配置された有機性廃棄物Aの下方領域に凝縮水回収空間2fが形成されるように、有機性廃棄物Aを支持する廃棄物支持手段2eを備えている。本実施形態では、廃棄物支持手段2eは、有機性廃棄物Aを載置可能に構成された載置部2eからなり、該載置部2eには、凝縮水回収空間2fに連通する貫通孔が形成されている。   The reaction vessel 2 is configured such that a condensed water recovery space 2f for recovering the condensed water B is formed in a lower region of the organic waste A disposed inside. Specifically, the reaction container 2 includes a waste support means 2e that supports the organic waste A so that a condensed water recovery space 2f is formed in a lower region of the organic waste A disposed inside. I have. In the present embodiment, the waste support means 2e includes a mounting portion 2e configured to be capable of mounting the organic waste A, and the mounting portion 2e has a through hole communicating with the condensed water recovery space 2f. Is formed.

具体的には、載置部2eは、複数の貫通孔が形成された網目状の形状を有し、該貫通孔から有機性廃棄物Aが抜け落ちないように構成されている。本実施形態では、載置部2eは、網目状の金属素材(パンチングメタル)を用いて形成されている。また、本実施形態では、載置部2eは、前記パンチングメタルが面状に形成されて、反応容器2の内部の下側、具体的には、撹拌手段4よりも下側に、容器本体2aとの間に間隔を空けて配置されている。これにより、容器本体2aと載置部2eとの間に凝縮水回収空間2fが形成される。該凝縮水回収空間2fは、反応容器2の軸に沿って容器本体2aの一端部と他端部との間に形成される。また、凝縮水回収空間2fは、前記排出部2dと連通するように形成される。   Specifically, the placing portion 2e has a mesh shape in which a plurality of through holes are formed, and is configured so that the organic waste A does not fall out from the through holes. In the present embodiment, the placement portion 2e is formed using a net-like metal material (punching metal). Further, in the present embodiment, the mounting portion 2e is formed such that the punching metal is formed into a planar shape, and the container main body 2a is located below the inside of the reaction vessel 2, specifically, below the stirring means 4. It is arranged with a space between. Thereby, the condensed water collection | recovery space 2f is formed between the container main body 2a and the mounting part 2e. The condensed water recovery space 2 f is formed between one end and the other end of the container body 2 a along the axis of the reaction container 2. The condensed water recovery space 2f is formed so as to communicate with the discharge part 2d.

前記水蒸気供給手段3は、反応容器2内に所定温度の水蒸気を供給し、反応容器2内の圧力が飽和水蒸気圧となるように構成されている。反応容器2内の飽和水蒸気の温度としては150℃以上であり、200〜235℃とすることが好ましい。この際の反応容器2内の圧力(飽和水蒸気圧)は、1.65〜3.29MPa(15〜33気圧)となることが好ましい。   The steam supply means 3 is configured to supply steam at a predetermined temperature into the reaction vessel 2 so that the pressure in the reaction vessel 2 becomes a saturated water vapor pressure. The temperature of the saturated water vapor in the reaction vessel 2 is 150 ° C. or higher, preferably 200 to 235 ° C. At this time, the pressure in the reaction vessel 2 (saturated water vapor pressure) is preferably 1.65 to 3.29 MPa (15 to 33 atm).

前記攪拌手段4は、有機性廃棄物Aを攪拌する攪拌羽根4aと、該攪拌羽根4aが連結された回転軸4bとから構成されている。前記攪拌羽根4aは、回転軸4bに複数連結されている。また、回転軸4bは、反応容器2を貫通するように配置されている。具体的には、回転軸4bは、容器本体2aの閉塞された一端部を貫通するように反応容器2の軸に沿って(本実施形態では、略水平に)配置されている。また、回転軸4bの一端部(具体的には、反応容器2の外側に位置する端部)には、回転軸4bをその長手方向を軸に回転させる回転手段4cが取り付けられている。そして、回転軸4bが回転することにより、複数の攪拌羽根4aが有機性廃棄物Aに接触して有機性廃棄物Aを撹拌し、有機性廃棄物Aが反応容器2内の飽和水蒸気と均一に接触するように構成されている。   The stirring means 4 includes a stirring blade 4a for stirring the organic waste A, and a rotating shaft 4b to which the stirring blade 4a is connected. A plurality of the stirring blades 4a are connected to the rotating shaft 4b. Moreover, the rotating shaft 4b is arrange | positioned so that the reaction container 2 may be penetrated. Specifically, the rotation shaft 4b is arranged along the axis of the reaction vessel 2 (substantially horizontally in the present embodiment) so as to penetrate the closed one end portion of the vessel body 2a. A rotating means 4c for rotating the rotating shaft 4b around its longitudinal direction is attached to one end of the rotating shaft 4b (specifically, the end located outside the reaction vessel 2). Then, by rotating the rotating shaft 4b, the plurality of stirring blades 4a come into contact with the organic waste A to stir the organic waste A, and the organic waste A is uniform with the saturated water vapor in the reaction vessel 2. It is comprised so that it may contact.

次に、廃棄物処理装置1が有機性廃棄物Aを分解する機構について説明する。供給部2cから反応容器2内に供給された有機性廃棄物Aは、前記攪拌手段4(具体的には、攪拌羽根4a)によって撹拌され、反応容器2内の飽和水蒸気と接触する。反応容器2内は、前記温度の飽和水蒸気で満たされて前記圧力となっており、有機性廃棄物Aが飽和水蒸気との接触によって加水分解されて細粒化される。この際、有機性廃棄物Aには、飽和水蒸気が凝縮して凝縮水Bが付着することとなる。具体的には、有機性廃棄物Aが飽和水蒸気によって加熱される際に、飽和水蒸気の熱を奪うため、飽和水蒸気が凝縮し、有機性廃棄物Aに付着することとなる。該凝縮水Bには、細粒化された有機性廃棄物Aから水溶性の化学物質(例えば、塩化物等)が溶出する。   Next, a mechanism in which the waste treatment apparatus 1 decomposes the organic waste A will be described. The organic waste A supplied from the supply unit 2c into the reaction vessel 2 is stirred by the stirring means 4 (specifically, the stirring blade 4a) and comes into contact with saturated water vapor in the reaction vessel 2. The inside of the reaction vessel 2 is filled with saturated steam at the above temperature and is at the pressure, and the organic waste A is hydrolyzed and finely divided by contact with saturated steam. At this time, saturated water vapor condenses and the condensed water B adheres to the organic waste A. Specifically, when the organic waste A is heated by the saturated water vapor, the saturated water vapor is deprived of heat, so that the saturated water vapor condenses and adheres to the organic waste A. In the condensed water B, water-soluble chemical substances (for example, chlorides) are eluted from the finely divided organic waste A.

化学物質が溶解した凝縮水Bは、廃棄物支持手段2e(パンチングメタル)の貫通孔を通って凝縮水回収空間2fに滴下されて回収される。この際、反応容器2内の水蒸気量が減少するため、水蒸気供給手段3から水蒸気が供給されて、反応容器2内の圧力が維持される。この状態において反応容器2内では、飽和水蒸気と凝縮水Bとの間で気液平衡が維持されている。そして、有機性廃棄物Aが十分に細粒化された後、排出部2dから凝縮水Bを排出し、細粒化された有機性廃棄物Aを冷却した後、乾燥する。これにより、水溶性の化学物質の含有量の少ない処理物となる。   The condensed water B in which the chemical substance is dissolved is dropped and recovered through the through hole of the waste support means 2e (punching metal) into the condensed water recovery space 2f. At this time, since the amount of water vapor in the reaction vessel 2 decreases, water vapor is supplied from the water vapor supply means 3 to maintain the pressure in the reaction vessel 2. In this state, vapor-liquid equilibrium is maintained between the saturated water vapor and the condensed water B in the reaction vessel 2. Then, after the organic waste A is sufficiently finely divided, the condensed water B is discharged from the discharge portion 2d, and the finely divided organic waste A is cooled and dried. Thereby, it becomes a processed material with little content of a water-soluble chemical substance.

以上のように、本実施形態に係る廃棄物処理装置1によれば、水溶性の化学物質を含有する有機性廃棄物Aを処理した後の処理物中に前記水溶性の化学物質が残存するのを抑制することができる。   As described above, according to the waste treatment apparatus 1 according to the present embodiment, the water-soluble chemical substance remains in the treated product after treating the organic waste A containing the water-soluble chemical substance. Can be suppressed.

即ち、前記温度の飽和水蒸気と有機性廃棄物Aとの接触によって、有機性廃棄物Aの表面に凝縮した凝縮水Bに有機性廃棄物A中の水溶性の化学物質が溶出し、凝縮水Bを有機性廃棄物Aから分離して回収することで、細粒化された有機性廃棄物A(処理物)中に水溶性の化学物質が残存するのを抑制することができる。これにより、水溶性の化学物質を除去する工程を行なうことなく処理物を燃料として利用することができる。   That is, the water-soluble chemical substance in the organic waste A elutes into the condensed water B condensed on the surface of the organic waste A by the contact of the saturated water vapor with the temperature and the organic waste A, and the condensed water By separating and recovering B from the organic waste A, it is possible to suppress the remaining water-soluble chemical substance in the finely divided organic waste A (processed product). Thereby, a processed material can be utilized as a fuel, without performing the process of removing a water-soluble chemical substance.

また、凝縮水回収空間2fが形成されることで、凝縮水回収空間2fに凝縮水Bを滴下させて回収することができ、処理物と凝縮水Bとを容易に分離することができる。これにより、処理物と凝縮水Bとの接触が防止され、処理物中に水溶性の化学物質が残存するのを抑制することができる。   Further, by forming the condensed water recovery space 2f, the condensed water B can be dropped and recovered in the condensed water recovery space 2f, and the processed product and the condensed water B can be easily separated. Thereby, a contact with a processed material and the condensed water B is prevented, and it can suppress that a water-soluble chemical substance remains in a processed material.

また、載置部(廃棄物支持手段)2eに貫通孔が形成されていることで、有機性廃棄物Aを下方から確実に支持した状態で処理することができると共に、貫通孔を通じて凝縮水Bを確実に凝縮水回収空間2fに送ることができる。また、回収された凝縮水Bと処理物との間に載置部2eが存在するため、凝縮水Bと処理物とを確実に分離できる。   In addition, since the through-hole is formed in the mounting portion (waste support means) 2e, the organic waste A can be treated in a state of being reliably supported from below, and the condensed water B is passed through the through-hole. Can be reliably sent to the condensed water recovery space 2f. Moreover, since the mounting part 2e exists between the collect | recovered condensed water B and a processed material, the condensed water B and a processed material can be isolate | separated reliably.

以下、本発明の実施例について説明する。   Examples of the present invention will be described below.

<処理装置>
図2に示すように、反応容器として200mLの圧力容器20を用い、内部に水Cを15g導入した。また、圧力容器20の内部に廃棄物支持手段として全体が1mmメッシュの金属素材で形成された金属容器20eを配置した。該金属容器20eは、前記水Cの水面から上方に離れた位置でサンプルAを載置可能に構成されている。
<Processing device>
As shown in FIG. 2, a 200 mL pressure vessel 20 was used as a reaction vessel, and 15 g of water C was introduced therein. In addition, a metal container 20e formed entirely of a 1 mm mesh metal material is disposed inside the pressure container 20 as waste support means. The metal container 20e is configured such that the sample A can be placed at a position away from the water surface of the water C.

<実施例1>
食品由来の有機性廃棄物から3〜5gのサンプルAを採取して前記金属容器20eに載置した後、圧力容器20を密閉した。そして、斯かる圧力容器20を電気炉内に配置し、圧力容器20内の温度が150℃となるまで約1時間かけて昇温して10分間保持した。この際、圧力容器20内は、150℃の水蒸気によって飽和状態となっており、飽和水蒸気圧は、0.49MPa(約4.8気圧)となっている。
<Example 1>
After 3 to 5 g of sample A was collected from the organic waste derived from food and placed on the metal container 20e, the pressure container 20 was sealed. Then, the pressure vessel 20 was placed in an electric furnace, heated up for about 1 hour until the temperature in the pressure vessel 20 reached 150 ° C., and held for 10 minutes. At this time, the inside of the pressure vessel 20 is saturated with water vapor at 150 ° C., and the saturated water vapor pressure is 0.49 MPa (about 4.8 atm).

その後、電気炉から圧力容器20を取出し、直ちに水蒸気を抜いて100℃まで空冷してサンプルAを取り出し、105℃で乾燥して処理物を得た。   Thereafter, the pressure vessel 20 was taken out from the electric furnace, immediately after removing water vapor and air-cooled to 100 ° C., sample A was taken out and dried at 105 ° C. to obtain a processed product.

上記方法による処理を3つのサンプルAで行い、得られた処理物について水溶性の化学物質の含有量の測定(塩素濃度の測定)を行なった。測定結果については、最大値、最小値、平均値についてのみ下記表1に示す。なお、塩素濃度の測定は、JIS R5202 ポルトランドセメントの化学分析方法(21.塩素の定量方法、21.2.電位差滴定方法)に基づいて行なった。   The treatment by the above method was performed on three samples A, and the content of the water-soluble chemical substance (measurement of chlorine concentration) was measured for the obtained processed product. About a measurement result, it shows in following Table 1 only about a maximum value, a minimum value, and an average value. The chlorine concentration was measured based on the chemical analysis method of JIS R5202 Portland cement (21. Chlorine determination method, 21.2. Potentiometric titration method).

<実施例2>
実施例1とは異なる食品由来の有機性廃棄物から3〜5gのサンプルAを採取して前記金属容器20eに載置した後、圧力容器20を密閉した。そして、斯かる圧力容器20を電気炉内に配置し、圧力容器20内の温度が235℃となるまで約1時間かけて昇温して10分間保持した。この際、圧力容器20内は、235℃の水蒸気によって飽和状態となっており、飽和水蒸気圧は、3.04MPa(約30気圧)となっている。
<Example 2>
After collecting 3 to 5 g of sample A from food-derived organic waste different from Example 1 and placing it on the metal container 20e, the pressure container 20 was sealed. Then, the pressure vessel 20 was placed in an electric furnace, heated up for about 1 hour until the temperature in the pressure vessel 20 reached 235 ° C., and held for 10 minutes. At this time, the inside of the pressure vessel 20 is saturated by steam at 235 ° C., and the saturated steam pressure is 3.04 MPa (about 30 atm).

その後、電気炉から圧力容器20を取出し、直ちに水蒸気を抜いて100℃まで空冷してサンプルAを取り出し、105℃で乾燥して処理物を得た。   Thereafter, the pressure vessel 20 was taken out from the electric furnace, immediately after removing water vapor and air-cooled to 100 ° C., sample A was taken out and dried at 105 ° C. to obtain a processed product.

上記方法による処理を5つのサンプルAで行い、得られた処理物について実施例1と同様に水溶性の化学物質の含有量の測定(塩素濃度の測定)を行なった。測定結果については、下記表1に示す。   The treatment by the above method was performed on five samples A, and the content of the water-soluble chemical substance (measurement of chlorine concentration) was measured in the same manner as in Example 1 for the obtained processed product. The measurement results are shown in Table 1 below.

<比較例1>
実施例1と同じ有機性廃棄物から3〜5gのサンプルを2つ採取して未処理のまま実施例1と同一条件で水溶性の化学物質の含有量の測定を行なった。測定結果については、下記表1に示す。
<Comparative Example 1>
Two 3 to 5 g samples were collected from the same organic waste as in Example 1, and the content of water-soluble chemical substances was measured under the same conditions as in Example 1 without treatment. The measurement results are shown in Table 1 below.

<比較例2>
実施例2と同じ有機性廃棄物から3〜5gのサンプルを3つ採取して未処理のまま実施例1と同一条件で水溶性の化学物質の含有量の測定を行なった。測定結果については、下記表1に示す。
<Comparative Example 2>
Three 3 to 5 g samples were collected from the same organic waste as in Example 2, and the content of water-soluble chemical substances was measured under the same conditions as in Example 1 without treatment. The measurement results are shown in Table 1 below.

Figure 2011072948
Figure 2011072948

<まとめ>
実施例及び比較例を比較すると、実施例の方が塩素濃度が低いことが認められる。これは、上記方法で有機性廃棄物を処理することで、有機性廃棄物の表面に付着した飽和水蒸気の凝縮水に有機性廃棄物中の塩素成分が溶出し、斯かる凝縮水が塩素成分と共に金属容器20eを通って有機性廃棄物の下方に滴下されて回収されるため、塩素を含んだ凝縮水を有機性廃棄物から分離させることができるためである。
以上のように、有機性廃棄物を高温の飽和水蒸気で処理する際に、有機性廃棄物の表面に凝縮する凝縮水を有機性廃棄物から分離しつつ処理することで、処理後の有機性廃棄物に塩素(水溶性の化学物質)が残存するのを抑制することができる。
<Summary>
When comparing the example and the comparative example, it is recognized that the chlorine concentration in the example is lower. This is because the chlorine component in the organic waste is eluted in the saturated water vapor condensed water adhering to the surface of the organic waste by treating the organic waste by the above method, and the condensed water becomes the chlorine component. At the same time, it is dropped and recovered below the organic waste through the metal container 20e, so that the condensed water containing chlorine can be separated from the organic waste.
As described above, when treating organic waste with high-temperature saturated steam, the condensed water condensed on the surface of the organic waste is treated while being separated from the organic waste. It is possible to suppress chlorine (water-soluble chemical substance) from remaining in the waste.

1…廃棄物処理装置、2…反応容器、2a…容器本体、2b…閉塞蓋、2c…供給部、2d…排出部、2e…廃棄物支持手段、載置部、2f…凝縮水回収空間、3…水蒸気供給手段、4…撹拌手段、4a…攪拌羽根、4b…回転軸、4c…回転手段、20…圧力容器、20e…金属容器、A…有機性廃棄物、B…凝縮水、C…水   DESCRIPTION OF SYMBOLS 1 ... Waste processing apparatus, 2 ... Reaction container, 2a ... Container main body, 2b ... Closure lid, 2c ... Supply part, 2d ... Discharge part, 2e ... Waste support means, mounting part, 2f ... Condensate recovery space, DESCRIPTION OF SYMBOLS 3 ... Steam supply means, 4 ... Agitation means, 4a ... Agitation blade, 4b ... Rotating shaft, 4c ... Rotation means, 20 ... Pressure vessel, 20e ... Metal container, A ... Organic waste, B ... Condensed water, C ... water

Claims (3)

水溶性の化学物質を含有する有機性廃棄物を密閉された反応容器内で150℃以上の飽和水蒸気と接触させて有機性廃棄物を分解する廃棄物処理方法であって、
前記有機性廃棄物の表面に飽和水蒸気が凝縮して形成される凝縮水を有機性廃棄物から分離させつつ有機性廃棄物を分解することを特徴とする廃棄物処理方法。
A waste treatment method for decomposing organic waste by bringing organic waste containing a water-soluble chemical substance into contact with saturated steam at 150 ° C. or higher in a sealed reaction vessel,
A waste treatment method comprising decomposing an organic waste while separating condensed water formed by condensation of saturated water vapor on the surface of the organic waste from the organic waste.
水溶性の化学物質を含有する有機性廃棄物を密閉された反応容器内で150℃以上の飽和水蒸気と接触させて有機性廃棄物を分解する廃棄物処理装置であって、
前記反応容器は、内部に配置された有機性廃棄物の下方領域に、有機性廃棄物の表面に凝縮する飽和水蒸気の凝縮水を回収する凝縮水回収空間が形成されるように有機性廃棄物を支持する廃棄物支持手段を備えることを特徴とする廃棄物処理装置。
A waste treatment apparatus for decomposing organic waste by bringing organic waste containing a water-soluble chemical substance into contact with saturated steam at 150 ° C. or higher in a sealed reaction vessel,
The organic waste is formed so that a condensed water recovery space for recovering condensed water of saturated water vapor condensed on the surface of the organic waste is formed in a lower region of the organic waste disposed therein. A waste treatment apparatus comprising waste support means for supporting the waste.
前記廃棄物支持手段は、有機性廃棄物を載置可能に構成された載置部を備え、該載置部には、前記凝縮水回収空間に連通する貫通孔が形成されていることを特徴とする請求項2に記載の廃棄物処理装置。   The waste support means includes a mounting portion configured to be capable of mounting organic waste, and the mounting portion is formed with a through hole communicating with the condensed water recovery space. The waste disposal apparatus according to claim 2.
JP2009228750A 2009-09-30 2009-09-30 Waste treatment method and waste treatment apparatus Active JP5630682B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2009228750A JP5630682B2 (en) 2009-09-30 2009-09-30 Waste treatment method and waste treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2009228750A JP5630682B2 (en) 2009-09-30 2009-09-30 Waste treatment method and waste treatment apparatus

Publications (2)

Publication Number Publication Date
JP2011072948A true JP2011072948A (en) 2011-04-14
JP5630682B2 JP5630682B2 (en) 2014-11-26

Family

ID=44017520

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2009228750A Active JP5630682B2 (en) 2009-09-30 2009-09-30 Waste treatment method and waste treatment apparatus

Country Status (1)

Country Link
JP (1) JP5630682B2 (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000246231A (en) * 1998-12-28 2000-09-12 Kobe Steel Ltd Method and apparatus for purifying solid substance containing organic halogen compound
JP2002113444A (en) * 2000-07-31 2002-04-16 Ishikawajima Harima Heavy Ind Co Ltd Organic-based waste treatment apparatus and method and reactor for vapor decomposition
JP2005193141A (en) * 2004-01-07 2005-07-21 Ishikawajima Harima Heavy Ind Co Ltd Organic solid treatment apparatus
JP2005230726A (en) * 2004-02-20 2005-09-02 Ishikawajima Harima Heavy Ind Co Ltd Steam-treatment apparatus
JP2007112880A (en) * 2005-10-19 2007-05-10 National Univ Corp Shizuoka Univ Device for conversion into fuel and method for producing fuel

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000246231A (en) * 1998-12-28 2000-09-12 Kobe Steel Ltd Method and apparatus for purifying solid substance containing organic halogen compound
JP2002113444A (en) * 2000-07-31 2002-04-16 Ishikawajima Harima Heavy Ind Co Ltd Organic-based waste treatment apparatus and method and reactor for vapor decomposition
JP2005193141A (en) * 2004-01-07 2005-07-21 Ishikawajima Harima Heavy Ind Co Ltd Organic solid treatment apparatus
JP2005230726A (en) * 2004-02-20 2005-09-02 Ishikawajima Harima Heavy Ind Co Ltd Steam-treatment apparatus
JP2007112880A (en) * 2005-10-19 2007-05-10 National Univ Corp Shizuoka Univ Device for conversion into fuel and method for producing fuel

Also Published As

Publication number Publication date
JP5630682B2 (en) 2014-11-26

Similar Documents

Publication Publication Date Title
US20090311766A1 (en) Apparatus and method for hydrolyzing biological material
WO2008089937A3 (en) Microwave integrated soxhlet
CN106319202A (en) Method for preparing rhodium chloride hydrate from oxo synthesis waste rhodium catalyst
GB2269601A (en) Electrochemical separation of contaminant metal from scrap graphite
JP2010137156A (en) Device for removing isopropyl alcohol from paper element
CN106053175B (en) The simple and easy method of carbide in a kind of extractor tool steel
JP5630682B2 (en) Waste treatment method and waste treatment apparatus
JP2016097322A (en) Organic waste treatment apparatus and organic waste treatment method
CN1181711A (en) Method for treatment of halogen-containing waste material
EA200900402A1 (en) METHOD OF CLEANING OF POLLUTED METAL WASTE AND DEVICE FOR ITS IMPLEMENTATION
JP2018111090A (en) Cleaning method of biomass and method of manufacturing solid fuel
RU2221614C2 (en) Decontamination method for materials including hazardous substances of without combustion thereof (variants)
JP5246401B2 (en) Contaminated soil treatment equipment
JP5383582B2 (en) Detoxification method for PCB mixed insulating oil
RU2521165C2 (en) Removal of oil from oiled iron/steel chips and scale of rolling process slimes
JP5725764B2 (en) Volume reduction treatment system for PCB contaminants and volume reduction treatment method
JP2004283819A (en) Method for treating dioxin contaminated incineration ash
JP2000239435A (en) Treatment of plastic mixed waste
JP5425718B2 (en) Sludge removal method
JP4227944B2 (en) Waste liquid waste gas treatment equipment
Oehlenschlager et al. Critical Review on the Suitability of Different Decomposition Procedures for the Analysis of Trace Metals in Biota
JP5058302B2 (en) Scale removal method
JP2004351307A (en) Apparatus for separating and extracting shell-meat extract, shell-meat, and shell
JP2000239434A (en) Process for treating plastic mixture waste
JP2023069446A (en) Heat treatment device

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20120227

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20121225

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20130201

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20130401

RD04 Notification of resignation of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7424

Effective date: 20130806

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20140110

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20140311

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: 20140912

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20140925

R150 Certificate of patent or registration of utility model

Ref document number: 5630682

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150