JP2006167634A - Treating method and treating system of sludge - Google Patents

Treating method and treating system of sludge Download PDF

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JP2006167634A
JP2006167634A JP2004364937A JP2004364937A JP2006167634A JP 2006167634 A JP2006167634 A JP 2006167634A JP 2004364937 A JP2004364937 A JP 2004364937A JP 2004364937 A JP2004364937 A JP 2004364937A JP 2006167634 A JP2006167634 A JP 2006167634A
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sludge treatment
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JP4526373B2 (en
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Osamu Yamada
修 山田
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JIPANGU ENERGY KK
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    • 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
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Abstract

<P>PROBLEM TO BE SOLVED: To divide sludge water into solid matter and steam at once. <P>SOLUTION: In this sludge treating method, a jet gas burner blows jet gas flame against the sludge water in a treating furnace to perform ultra-high temperature heating of the sludge water in an instant. Thus moisture and low melting point materials are evaporated, a dust collector divides evaporated gas into solid and gas, further the separated gas is divided into gaseous hydrogen and non-permeated gas via a separation membrane. The non-permeated gas is treated and obtained clean gas is discharged to the external world. The solid separated by the dust collector is collected and the solid matter such as non-sublimated metal remaining in the treating furnace is recovered. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

この発明は、生活廃水汚泥その他有害物を含んだ汚泥を処理することを目的とした汚泥処理方法及び処理システムに関する。   The present invention relates to a sludge treatment method and a treatment system for treating domestic wastewater sludge and other sludge containing harmful substances.

従来の一般的に採用されている汚泥処理は、汚泥を乾燥させ、含水率を下げた後、焼却している。   In the conventional sludge treatment generally adopted, the sludge is dried and incinerated after the moisture content is lowered.

また、ダイオキシンで汚染された地盤の表層に対して、原位置で熱分解処理する技術が提案されている。   In addition, a technique for thermally decomposing the surface layer of the ground contaminated with dioxin in situ has been proposed.

更に、廃棄物焼却炉にブラウンガスを導入して、廃棄物を高温燃焼する技術も開示されている。
特開2004−243157号 特開2000−39123号
Furthermore, a technique for introducing a brown gas into a waste incinerator and burning the waste at a high temperature is also disclosed.
JP 2004-243157 A JP 2000-39123 A

前記従来採用されている技術は、汚泥を乾燥させ然る後、焼却するので、処理工程が二段階となり、処理設備及びランニングコストが厖大となる問題点があった。   The technique employed in the prior art has a problem in that since the sludge is dried and then incinerated, the treatment process is in two stages, and the treatment equipment and running cost are enormous.

また引用文献1、2の発明は、共に水分含有量の少ない土壌については有効に機能する可能性があるが、例えば、水分90%以上というような汚泥については、そのまま採用することはできない問題点があった。   In addition, the inventions of the cited documents 1 and 2 may function effectively for soil having a low water content, but for example, sludge with a moisture content of 90% or more cannot be used as it is. was there.

更に、特許文献1においては、ブラウンガスバーナーの使用が記載されているが、水分の多い汚泥に使用した場合の処理技術が記載されていない。   Furthermore, Patent Document 1 describes the use of a brown gas burner, but does not describe a treatment technique when used for sludge with a lot of moisture.

この発明は、処理炉に収容した汚泥に、ゼットガスバーナーから、ゼットガス炎を吹きつけることにより、水分及び低融点物質を瞬時に気化することができるので、汚泥を連続的に処理することができる。   In this invention, moisture and a low-melting-point substance can be instantly vaporized by blowing a jet gas flame from a jet gas burner to the sludge accommodated in the treatment furnace, so that the sludge can be treated continuously. .

またゼットガス炎は、閉空間で発生するので、その熱量は全部有効に利用され、効率がきわめて良好である。前記ゼットガスは、水素ガスと酸素ガスの混合気体であるから、外部から酸素の給送がなくとも、自分の持っている酸素で十分目的を達成することができる。   Further, since the zet gas flame is generated in a closed space, all the heat is effectively used and the efficiency is very good. Since the zet gas is a mixed gas of hydrogen gas and oxygen gas, even if there is no supply of oxygen from the outside, the objective can be sufficiently achieved with the oxygen that the user has.

またセラミックスなどの耐熱触媒を使用する場合には、水分の一部がゼットガスに変えられる。例えば、2000℃〜3000℃のセラミックス触媒に水を衝突させると、水は水蒸気になると共に、水蒸気の一部は水素ガスと酸素ガスに変化するが、この場合にも水素ガスと酸素ガスの割合は、燃焼に必要な割合を保っているので、過不足なく完全燃焼することになる。   In addition, when using a heat-resistant catalyst such as ceramics, a part of the water can be changed to a jet gas. For example, when water collides with a ceramic catalyst of 2000 ° C. to 3000 ° C., the water becomes water vapor, and part of the water vapor changes into hydrogen gas and oxygen gas. In this case as well, the ratio of hydrogen gas to oxygen gas Since the ratio required for combustion is maintained, complete combustion is achieved without excess or deficiency.

即ち方法の発明は、処理炉中の汚泥水にゼットガスバーナーからゼットガス炎を吹きつけて、瞬時に超高温加熱し、水分及び低融点物質を気化させ、前記蒸発気体は、集塵機で気体と固体を分離し、分離気体は、分離膜を介して水素ガスと、未透過ガスとに分離し、未透過ガスを処理してクリーン気体を外界へ放出し、前記集塵機で分離した固体を集め、前記処理炉に残った未昇華金属その他の固形物を回収することを特徴とした汚泥処理方法であり、ゼットガスは、水を電気分解して生成した水素ガスと酸素ガスをそのまま混合して混合ガスとするものであり、分離膜は水素ガス透過膜であって、分離器内を二分するように張設してあり、透過膜の一側に排気を導き、他側に水素ガスの出口を設けたものである。   That is, the invention of the method is to blow a jet gas flame from a jet gas burner to the sludge water in the treatment furnace, instantaneously heat it to ultra high temperature to vaporize moisture and low melting point substance, and the evaporated gas is gas and solid by a dust collector. The separation gas is separated into hydrogen gas and non-permeated gas through a separation membrane, the non-permeated gas is processed to release clean gas to the outside, and the solid separated by the dust collector is collected. A sludge treatment method characterized by recovering unsublimated metal and other solids remaining in a treatment furnace. Zet gas is a mixture of hydrogen gas and oxygen gas generated by electrolyzing water and mixed gas. The separation membrane is a hydrogen gas permeable membrane, and is stretched so as to bisect the inside of the separator. The exhaust gas is led to one side of the permeable membrane, and the hydrogen gas outlet is provided on the other side. Is.

次にシステムの発明は、汚泥水にゼットガス炎を吹きつけて焼却処理する処理手段と、処理手段により生じた排気の集塵手段と、その気体の処理をする分離手段と、ガス処理器及び固形物処理手段とを組み合せたことを特徴とする汚泥処理システムであり、処理手段は、処理炉にゼットガスバーナーと、汚泥給送手段と、排気手段とを組み合せたものであり、分離手段は、槽内に分離膜を張設し、分離膜の一側に排気を供給し、他側に水素ガスの出口を設けたものであり、集塵手段は、サイクロンとしたものである。   Next, the invention of the system includes a processing means for incinerating sludge water with a jet gas flame, a dust collecting means for exhaust gas generated by the processing means, a separation means for processing the gas, a gas processor and a solid It is a sludge treatment system characterized by combining a material treatment means, the treatment means is a combination of a treatment furnace with a jet gas burner, a sludge feed means, and an exhaust means, and a separation means is A separation membrane is stretched in the tank, exhaust is supplied to one side of the separation membrane, and an outlet for hydrogen gas is provided on the other side. The dust collecting means is a cyclone.

更に、処理手段は、処理炉の下部に耐熱性触媒ロストルを設置し、該耐熱触媒ロストルの下面部へゼットガスバーナーからゼットガス炎を吹きつけ、前記処理炉の上部から前記ロストルの上面に向けて、加圧汚泥の噴射手段を設けたものであり、加圧汚泥の噴射手段は、ポンプ移送としたものである。   Further, the processing means installs a heat-resistant catalyst rooster at the lower part of the processing furnace, blows a jet gas flame from the jet gas burner to the lower surface portion of the heat-resistant catalyst rooster, from the upper part of the processing furnace toward the upper surface of the rooster. The pressurized sludge injection means is provided, and the pressurized sludge injection means is pumped.

前記発明におけるゼットガスは、水を電気分解して生成した水素ガスと酸素ガスを、そのまま混合したガスであって、ブラウンガスの特性と近似している。   The jet gas in the present invention is a gas obtained by mixing hydrogen gas and oxygen gas generated by electrolyzing water as it is, and approximates the characteristics of brown gas.

そこでゼットガスバーナーでゼットガスを汚泥に吹きつけると、火炎は瞬時に2000℃〜4000℃に昇温するので、水は勿論のこと、低融点物質は悉くガス化(昇華)し、重金属その他の未昇華物が残留するので、夫々分離処理し、有用物として再使用する。そこで排気中の固形物を分離し、ついで水素ガスを分離した後、残余のガスを処理して外界へ放出すれば、全処理を終了する。   Therefore, when the jet gas is blown onto the sludge with a jet gas burner, the flame instantly rises to 2000 ° C to 4000 ° C, so that water as well as low-melting-point substances are gasified (sublimated), and heavy metals and other unexposed Since the sublimate remains, it is separated and reused as a useful product. Therefore, after separating the solid matter in the exhaust gas and then separating the hydrogen gas, if the remaining gas is treated and released to the outside, the entire process is completed.

この発明で使用するゼットガス炎を汚泥水に照射すると、超高温(1000℃〜4000℃)となり、総ての物を溶解するけれども、他物に移るおそれはない。またゼットガス自体が酸素を保有しているので、空気のない場所でも燃焼を継続する。更にゼットガスは表1のような特性を持っている。

Figure 2006167634
When sludge water is irradiated to the sludge water used in the present invention, it becomes an extremely high temperature (1000 ° C. to 4000 ° C.), and all things are dissolved, but there is no risk of moving to other things. Also, since the zet gas itself contains oxygen, it will continue to burn even in places where there is no air. Furthermore, zet gas has the characteristics shown in Table 1.
Figure 2006167634

前記のように、ゼットガスは、化石燃料又は化石ガスに比し特性を有するので、目的物を目的温度に加熱し、しかも公害物を出さないので、汚泥処理などに最適である。   As described above, zet gas has characteristics as compared with fossil fuel or fossil gas, and therefore heats the target product to the target temperature and does not emit pollutants, so it is optimal for sludge treatment.

この発明は、水を電気分解して生成したゼットガスを使用して汚泥を加熱蒸発させるので、加熱熱量はクリーンであって有害ガスの生成されるおそれはない効果がある。   In the present invention, since sludge is heated and evaporated by using a zet gas generated by electrolyzing water, the amount of heat of heating is clean, and there is an effect that no harmful gas is generated.

また排気中に有毒ガスが含まれているとしても、分離後処理するので、外界へ有害ガスが放出されるおそれがないなどの効果がある。   Further, even if toxic gas is contained in the exhaust, since it is processed after separation, there is an effect that no harmful gas is released to the outside.

またこの発明によれば、汚泥が完全に処理され、廃棄物は0に近くなる。   Moreover, according to this invention, sludge is processed completely and a waste becomes close to zero.

この発明は、処理炉中へ汚泥を供給し、汚泥の上部から、ゼットガス炎を吹きつけて、重金属などの比重の大きい物質以外は昇華させるので、容易に分離することができる。ついで固気分離し(例えばサイクロン使用)、ついで水素を分離した後、残余のガスを処理すれば、クリーン気体となるので、汚泥処理に関し、外界を汚染するおそれはない。また重金属などは分類して再使用することができる。   According to the present invention, sludge is supplied into the treatment furnace, and a jet gas flame is blown from the top of the sludge to sublimate substances other than those having a high specific gravity such as heavy metals, and therefore can be easily separated. Next, solid gas separation is performed (for example, using a cyclone), and then hydrogen is separated, and then the remaining gas is treated to form a clean gas. Therefore, there is no risk of contaminating the outside environment with respect to sludge treatment. Heavy metals can be classified and reused.

前記におけるゼットガスは、クリーンガスであるから、全体としてクリーンに処理されることになり、従来問題視されていたような環境破壊のおそれは皆無である。   Since the zet gas in the above is a clean gas, it will be processed cleanly as a whole, and there is no fear of environmental destruction that has been regarded as a problem in the past.

この発明の実施例を図1について説明すると、処理炉へ汚泥水(例えば水分90%以上の砂の混合した汚泥水)に給送すると共に、処理炉へ設置した複数のゼットガスバーナーからゼットガスに点火すると共に吹きつける。   An embodiment of the present invention will be described with reference to FIG. 1. The sludge water (for example, sludge water mixed with 90% or more of water) is fed to the treatment furnace, and from a plurality of jet gas burners installed in the treatment furnace to the jet gas. Ignite and blow.

この場合に汚泥は、瞬時に2500℃位に昇温し、水及び低温気化物(例えば2000℃以下で昇華する物)は悉く気化し、吸引器に吸引されて、集塵機に送られる。この集塵機は例えばサイクロンであって、気体と固形物を自動的に分離するものである。   In this case, the sludge is instantly heated to about 2500 ° C., and water and a low-temperature vaporized substance (for example, sublimated at 2000 ° C. or less) are vaporized, sucked into the suction device, and sent to the dust collector. This dust collector is, for example, a cyclone and automatically separates gas and solid matter.

前記のようにして、固気を分離したならば、分離膜によって水素を分離し、残余の排気は、ガス処理筒で処理し、無害化気体のみを外界へ放出する。   When the solid gas is separated as described above, hydrogen is separated by the separation membrane, and the remaining exhaust gas is treated by the gas treatment cylinder, and only the harmless gas is discharged to the outside.

気体と分離した固形物は、例えば昇華しなかった金属類又はセラミックスその他の無機物であるが、金属類は夫々分別して再使用し、その他の無機物(例えば砂、石、その他のセラミックス類)は溶解後、水砕又は風砕により小粒化(例えば1mm〜5mm)し、建材などの骨材又はブロックの材料に使用する。   Solids separated from gas are, for example, metals that have not been sublimated, ceramics, and other inorganic materials. However, metals are separated and reused, and other inorganic materials (such as sand, stones, and other ceramics) are dissolved. After that, it is granulated (for example, 1 mm to 5 mm) by water granulation or air crushing, and used as a material for aggregates such as building materials or blocks.

この発明のシステムの実施例を図2、3に基づいて説明すると、処理炉1へ、ゼットガスバーナー2、2と、汚泥水給送パイプ3及び吸引器4を連結する。前記吸引器4の吐出側を、集塵機5の入力側に接続し、集塵機5の吐出側を、膜分離器6の入力側に接続する。この膜分離器6は、分離膜7により水素のみを分離するのである。前記分離器6の排気をガス処理筒8で処理し、煙突9から矢示16のように外界へ放出する。   An embodiment of the system of the present invention will be described with reference to FIGS. 2 and 3, wherein the gas furnaces 2 and 2, the sludge water feed pipe 3 and the suction device 4 are connected to the processing furnace 1. The discharge side of the suction device 4 is connected to the input side of the dust collector 5, and the discharge side of the dust collector 5 is connected to the input side of the membrane separator 6. This membrane separator 6 separates only hydrogen by the separation membrane 7. The exhaust gas from the separator 6 is processed by the gas processing cylinder 8 and discharged from the chimney 9 to the outside as indicated by an arrow 16.

またゼットガスは、ゼットガス発生器10へ送電及び給水し、水を電気分解してゼットガスを発生させる。図中11は分配器であって、ゼットガスを矢示17のように必要な場所へ送る。   Moreover, zet gas transmits and supplies water to the zet gas generator 10, and electrolyzes water to generate zet gas. In the figure, reference numeral 11 denotes a distributor, which sends zet gas to a necessary place as indicated by an arrow 17.

次に図3の実施例は、処理炉1の他の構造を示すものである。   Next, the embodiment of FIG. 3 shows another structure of the processing furnace 1.

図3の処理炉1aの中央部に、セラミック製のロストル12を設置し、ロストル12の下部にゼットガスバーナー2、2を設置して、ロストル12を加熱する。   A ceramic rooster 12 is installed at the center of the processing furnace 1a in FIG. 3, and a zet gas burner 2, 2 is installed at the lower portion of the rooster 12 to heat the rooster 12.

前記ロストル12の上方の側壁へ、汚泥水の送水筒13端を固定してある。   The end of the sludge water pipe 13 is fixed to the upper side wall of the rooster 12.

前記において、送水筒13から矢示14のように汚泥水を処理炉1a内のロストル上へ送水すると共に、ゼットガスバーナー2、2を点火して、ロストル12の下面を加熱すると、ロストル12の下面は、例えば2000℃に加熱される。   In the above, when the sludge water is fed from the water feeding tube 13 onto the rooster in the processing furnace 1a as indicated by the arrow 14 and the lower surface of the rooster 12 is heated by igniting the jet gas burners 2 and 2, The lower surface is heated to 2000 ° C., for example.

そこで、水及び低融点物は、昇華して、矢示15のように上昇し、図2のように吸引器4に吸引される。一方昇華しない固形物18(例えば金属など)となってロストル12の下に溜まる。   Therefore, the water and the low-melting point substance sublimate and rise as indicated by arrow 15 and are sucked into the suction device 4 as shown in FIG. On the other hand, it becomes a solid 18 (for example, metal) that does not sublime and accumulates under the rooster 12.

前記において、セラミック製のロストル12は、触媒作用があって、汚水の分解時に水素ガスと酸素ガスを生成するので、排気処理で水素ガスを分離することができる。   In the above, the ceramic rooster 12 has a catalytic action and generates hydrogen gas and oxygen gas when the sewage is decomposed, so that the hydrogen gas can be separated by the exhaust treatment.

この発明で用いるゼットガス生成の為の水の電気分解を図4について説明すると、電解槽20内に、多数の電極板21、21を縦に並列設置して、各電極板21、21は導板22、22aにより夫々プラス極、マイナス極を形成している。前記電解槽20の下部には、送水パイプ23の一端が連結され、送水パイプ23の他端は、電解水槽24に連結してある。   The electrolysis of water used to generate the jet gas used in the present invention will be described with reference to FIG. 4. A large number of electrode plates 21 and 21 are installed in parallel in the electrolytic cell 20, and each electrode plate 21 and 21 is a conductive plate. 22 and 22a form a positive pole and a negative pole, respectively. One end of a water supply pipe 23 is connected to the lower part of the electrolytic tank 20, and the other end of the water supply pipe 23 is connected to an electrolytic water tank 24.

また電解槽20の上部は、排水パイプ25の基端が連結され、排水パイプ25の他端は、前記電解水槽24の上部の分離匣26に連結されている。前記電解水槽24の上部は、混合ガスの排出パイプ27に連結されている。そこで各電極板21、21に通電すると共に、送水パイプ23のポンプ28を始動すると、電気分解されて生成した水素ガスと酸素ガスと水を、排水パイプ25から矢示29のように取り出し、分離匣26で分離して、排出パイプ27から分配器11に送り(図2)、分配器11から必要個所に分配する。前記ゼットガスの発生器10は一例であって、他の構造を採用することもできる。要は、水素ガスと酸素ガスを混合したゼットガスを生成すれば利用することができる。図中30は電解水槽24への送水パイプ、31は水位計測室、32は水位計、33は電磁バルブ、34は給排気パイプ、35は連通孔、36は電磁石、37はスペーサー、41はスペーサー37の取付ピンである。   Further, the upper end of the electrolytic cell 20 is connected to the base end of the drainage pipe 25, and the other end of the drainage pipe 25 is connected to the separation rod 26 at the upper part of the electrolytic water tank 24. The upper part of the electrolyzed water tank 24 is connected to a mixed gas discharge pipe 27. Accordingly, when the electrode plates 21 and 21 are energized and the pump 28 of the water supply pipe 23 is started, the hydrogen gas, oxygen gas and water generated by electrolysis are taken out from the drain pipe 25 as shown by arrow 29 and separated. It isolate | separates with the eaves 26, and it sends to the distributor 11 from the discharge pipe 27 (FIG. 2), and distributes from the distributor 11 to a required location. The jet gas generator 10 is an example, and other structures may be adopted. In short, it can be utilized by generating a jet gas in which hydrogen gas and oxygen gas are mixed. In the figure, 30 is a water supply pipe to the electrolytic water tank 24, 31 is a water level measurement chamber, 32 is a water level gauge, 33 is an electromagnetic valve, 34 is a supply / exhaust pipe, 35 is a communication hole, 36 is an electromagnet, 37 is a spacer, 41 is a spacer 37 mounting pins.

前記実施例において、各電極21、21及び電磁石36に通電すると共に、ポンプ28を始動すると、電解水は、矢示38、39、40のように、電解水槽24から電解槽20に流入かつ上昇流動しつつ、電気分解され、多数の水素ガス及び酸素ガスを含んだ混合水として、排水パイプ25から矢示29のように流動して分離匣26に入り、気液分離される。   In the above embodiment, when the electrodes 21 and 21 and the electromagnet 36 are energized and the pump 28 is started, the electrolyzed water flows into the electrolyzer 20 from the electrolyzed water tank 24 and rises as indicated by arrows 38, 39 and 40. While flowing, it is electrolyzed and mixed water containing a large number of hydrogen gas and oxygen gas flows from the drain pipe 25 as indicated by arrow 29 and enters the separation tank 26 for gas-liquid separation.

前記において、水素ガスと酸素ガスは分解されるとすぐに流動水と共に上昇するので、電極面は常時清掃された状態となっており、分解効率が良好である。   In the above, since the hydrogen gas and the oxygen gas rise together with the flowing water as soon as they are decomposed, the electrode surface is always cleaned and the decomposition efficiency is good.

また前記電磁石に通電すると、通過する水は磁化水となり、一層分離を良好にすることができる。更に電解槽内へ超音波発振器(洗浄用と同程度)を設置すれば、振動により分解効率を良好にすると共に、電極面の気泡を除去することができる。   Further, when the electromagnet is energized, the passing water becomes magnetized water, which can further improve the separation. Furthermore, if an ultrasonic oscillator (similar to that for cleaning) is installed in the electrolytic cell, the decomposition efficiency can be improved by vibration and bubbles on the electrode surface can be removed.

この発明の実施例のブロック図。The block diagram of the Example of this invention. 同じく模式図。Similarly schematic diagram. 同じく処理炉の一例を示す拡大断面図。The expanded sectional view which similarly shows an example of a processing furnace. (a)同じくゼットガス発生器の実施例の概略図、(b)同じく電極の一例を示す拡大斜視図。(A) The schematic diagram of the Example of a zet gas generator similarly, (b) The expansion perspective view which similarly shows an example of an electrode.

符号の説明Explanation of symbols

1 処理炉
2 ゼットガスバーナー
3 汚泥水給送パイプ
4 吸引器
5 集塵機
6 膜分離器
7 分離膜
8 処理筒
9 煙突
10 ゼットガス発生器
DESCRIPTION OF SYMBOLS 1 Processing furnace 2 Zet gas burner 3 Sludge water feed pipe 4 Suction device 5 Dust collector 6 Membrane separator 7 Separation membrane 8 Processing cylinder 9 Chimney 10 Zet gas generator

Claims (9)

処理炉中の汚泥水にゼットガスバーナーからゼットガス炎を吹きつけて、瞬時に超高温加熱し、水分及び低融点物質を気化させ、前記蒸発気体は、集塵機で気体と固体を分離し、分離気体は、分離膜を介して水素ガスと、未透過ガスとに分離し、未透過ガスを処理してクリーン気体を外界へ放出し、前記集塵機で分離した固体を集め、前記処理炉に残った未昇華金属その他の固形物を回収することを特徴とした汚泥処理方法。   Blowing a jet gas flame from the jet gas burner to the sludge water in the treatment furnace, instantaneously heating it to ultra high temperature to vaporize moisture and low melting point material, the vaporized gas separates the gas and solid with a dust collector, separated gas Is separated into hydrogen gas and non-permeated gas through a separation membrane, the non-permeated gas is processed to release clean gas to the outside, the solid separated by the dust collector is collected, and the unremained untreated gas remains in the processing furnace. A sludge treatment method characterized by recovering sublimation metal and other solid matter. ゼットガスは、水を電気分解して生成した水素ガスと酸素ガスをそのまま混合して混合ガスとすることを特徴とした請求項1記載の汚泥処理方法。   2. The sludge treatment method according to claim 1, wherein the jet gas is a mixed gas obtained by directly mixing hydrogen gas and oxygen gas generated by electrolyzing water. 分離膜は水素ガス透過膜であって、分離器内を二分するように張設してあり、透過膜の一側に排気を導き、他側に水素ガスの出口を設けたことを特徴とする請求項1記載の汚泥処理方法。   The separation membrane is a hydrogen gas permeable membrane, and is stretched so as to bisect the inside of the separator, characterized in that exhaust gas is guided to one side of the permeable membrane and a hydrogen gas outlet is provided to the other side. The sludge treatment method according to claim 1. 汚泥水にゼットガス炎を吹きつけて焼却処理する処理手段と、処理手段により生じた排気の集塵手段と、その気体の処理をする分離手段と、ガス処理器及び固形物処理手段とを組み合せたことを特徴とする汚泥処理システム。   Combining processing means for incinerating sludge water with a jet gas flame, dust collection means for exhaust gas generated by the processing means, separation means for processing the gas, gas treatment device and solid matter treatment means A sludge treatment system characterized by that. 処理手段は、処理炉にゼットガスバーナーと、汚泥給送手段と、排気手段とを組み合せたことを特徴とする請求項4記載の汚泥処理システム。   5. The sludge treatment system according to claim 4, wherein the treatment means is a combination of a jet gas burner, sludge feed means, and exhaust means in the treatment furnace. 分離手段は、槽内に分離膜を張設し、分離膜の一側に排気を供給し、他側に水素ガスの出口を設けたことを特徴とする請求項4記載の汚泥処理システム。   The sludge treatment system according to claim 4, wherein the separation means includes a separation membrane stretched in the tank, exhaust gas is supplied to one side of the separation membrane, and an outlet for hydrogen gas is provided on the other side. 集塵手段は、サイクロンとしたことを特徴とした請求項4記載の汚泥処理システム。   The sludge treatment system according to claim 4, wherein the dust collecting means is a cyclone. 処理手段は、処理炉の下部に耐熱性触媒ロストルを設置し、該耐熱触媒ロストルの下面部へゼットガスバーナーからゼットガス炎を吹きつけ、前記処理炉の上部から前記ロストルの上面に向けて、加圧汚泥の噴射手段を設けたことを特徴とした請求項4記載の汚泥処理システム。   The processing means is provided with a heat-resistant catalyst rooster at the lower part of the processing furnace, a jet gas flame is blown from the lower face of the heat-resistant catalyst rooster to the upper surface of the rooster from the upper part of the processing furnace. The sludge treatment system according to claim 4, further comprising pressure sludge injection means. 加圧汚泥の噴射手段は、ポンプ移送としたことを特徴とする請求項8記載の汚泥処理システム。   The sludge treatment system according to claim 8, wherein the pressurized sludge injection means is pump transfer.
JP2004364937A 2004-12-16 2004-12-16 Sludge treatment method and treatment system Expired - Fee Related JP4526373B2 (en)

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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10176172A (en) * 1996-12-19 1998-06-30 Hitachi Ltd Process and apparatus for recovering solid with jet burner
JPH11246984A (en) * 1998-03-05 1999-09-14 Zipangu Energy:Kk Electrolyte apparatus for water and water stove as well as production of electrode
JP2000039123A (en) * 1998-07-24 2000-02-08 Ekoo Kk Method and device for incinerating waste using blown gas
JP2002105466A (en) * 2000-09-29 2002-04-10 Osaka Gas Co Ltd Manufacturing method of fuel gas
JP2002147734A (en) * 2000-11-15 2002-05-22 Yoshinobu Kobayashi Treatment apparatus and method for pcb waste oil

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10176172A (en) * 1996-12-19 1998-06-30 Hitachi Ltd Process and apparatus for recovering solid with jet burner
JPH11246984A (en) * 1998-03-05 1999-09-14 Zipangu Energy:Kk Electrolyte apparatus for water and water stove as well as production of electrode
JP2000039123A (en) * 1998-07-24 2000-02-08 Ekoo Kk Method and device for incinerating waste using blown gas
JP2002105466A (en) * 2000-09-29 2002-04-10 Osaka Gas Co Ltd Manufacturing method of fuel gas
JP2002147734A (en) * 2000-11-15 2002-05-22 Yoshinobu Kobayashi Treatment apparatus and method for pcb waste oil

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