TW200537056A - Method and apparatus for producing ceramics - Google Patents

Method and apparatus for producing ceramics Download PDF

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TW200537056A
TW200537056A TW93113502A TW93113502A TW200537056A TW 200537056 A TW200537056 A TW 200537056A TW 93113502 A TW93113502 A TW 93113502A TW 93113502 A TW93113502 A TW 93113502A TW 200537056 A TW200537056 A TW 200537056A
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aforementioned
ceramic
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patent application
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TW93113502A
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Yoshiyuki Tokuda
Hideo Itoh
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Yoshiyuki Tokuda
Hideo Itoh
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Priority to TW93113502A priority Critical patent/TW200537056A/en
Publication of TW200537056A publication Critical patent/TW200537056A/en

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Abstract

The present invention relates to a method and an apparatus for producing ceramics by utilizing a pyrolyzer of organic materials. A method of the present invention includes a step for pyrolyzing organic materials having a small quantity of inorganic components and a step for treating gases generated in said pyrolzing step, wherein said pyrolyzing step includes a step for decomposing said organic materials into gas components and carbides including said inorganic components, a step for keeping a reaction chamber in reductive condition by providing a large amount of electrons to said decomposed carbides and for gasifying said carbides to separate said inorganic materials from said carbides, a steps for reacting said separated inorganic components with oxygen components which have been sent along with said electrons to generate oxides.

Description

200537056 玫、發明說明: 【發明所屬之技術領域】 成方法及裝置,特別是有 驟中生成陶瓷之再生型陶 本發明係有關於一種陶曼生 關於一種在有機廢棄物熱分解步 瓷生成方法及裝置。 【先前技術】 一般而言,陶瓷之製造須锢耐*200537056 Description of the invention: [Technical field to which the invention belongs] Method and device for forming ceramics, in particular regenerating ceramics that produce ceramics in a step The present invention relates to a method and device for producing ceramics by thermal decomposition of organic wastes . [Prior art] Generally speaking, ceramics must be resistant to manufacture *

月配當作原料之無機物和IMonthly distribution as raw materials of inorganic substances and I

量成分,對其燒結而成。因而 %知陶瓷製造方法一定須^ 焙燒步驟,該焙燒步驟須要大Ingredients are made by sintering. Therefore, it is known that the ceramic manufacturing method must require a baking step, which requires a large baking step.

八重的能源。又,目前陶瓷J 商必須特意地購入無機無作為用M A Α 巧原枓來製造陶瓷。 又’生成具有優良惡臭物皙Λ 、切買吸附、分解效果、殺菌5 果等之高品質陶产,在還原環境中培燒原料後,必須… 在氧氣環境中再度焙燒的步驟,須要費許多功夫。而且 因此必須有氧化爐及還原爐装置才可,在設備投資上亦寶 要很多成本。Yae Energy. In addition, at present, ceramics manufacturers must purchase inorganic inorganic inertia to make ceramics using M A Α Kouhara. It also produces high-quality ceramic products with excellent malodor, absorbing and decomposing, decomposing effects, and sterilization. After roasting raw materials in a reducing environment, you must ... the step of firing again in an oxygen environment requires a lot of effort. Moreover, it is necessary to have an oxidation furnace and a reduction furnace device, which also requires a lot of cost in equipment investment.

另一方面’垃圾等所謂產業廢棄物之處理方法,一般 疋在焚燒爐燃燒處理掉。該燃燒處理雖然可以將廢棄物之 體積減少率減少體積約為零左右,但是燃燒時需要大量外 部能源之同時,有燒燃時產生戴奥辛(dioxin)、二氧化碳等 環境破壞性之問題。為了解決該問題,最近開始有利用碳 化爐、熱分解反應等進行產業廢棄物處理,藉由在還原環 境下熱分解都市垃圾,使廢棄物完全燃燒可以抑制戴奥 辛、二氧化碳氣體等產生之都市垃圾處理裝置,進而再利 3 200537056 用該熱分解步驟所發生的熱、水等資源,有許多系統正在 開發中。 [專利文獻] 曰本特開平1 1 -230522號公報 【發明内容】 如前述,習知之陶究製造步冑,在利用電或火力之焙 燒步驟須要大量的能源,又,該燃燒步驟,因為產生戴奥 辛或是二氧化碳氣體而有地球逐漸溫暖化之問題發生。而 且,因為購買作為陶究原料之無機物亦需要成本,亦有陶 瓷製造成本提高之問題存在。 本發明之目的係提供一種生成陶瓷的方法及裝置,係 使用有機㈣別是在都市垃圾等產f廢棄物中所含有的。 2木、乙稀類(以氣乙稀、聚乙婦、聚苯乙稀等作為材料) 艮°口殘渣等作為原/钭,利用熱分解該等有機廢棄物之步驟 來生成陶瓷。 依照本發明,因為可以使用前述之類的產業廢棄物作 為原料來生產陶瓷,在能夠謀求降低原料成本之同時,因 為該產業妄AL· —r ^ ,、匆可W利用係一般處理步驟之熱分解處理, 斤、#乎不須使用外部能源亦能夠生產陶冑,結合原料成 本之減少可以大幅度地降低陶瓷之製造成本。 "藉由配置施设電加熱器或是熱交換管,不必培 只須加敎J5施70 ·、 ’、槽内的有機廢棄物使其熱分解亦可。燃燒方 200537056 法之設備會被視為燃燒爐必須取得設置許可之手續才可 以’但若是採用燃燒以外的方法強制提高裝置内溫度之構 成時則不需要該手續,設置地點亦沒有限制。On the other hand, the so-called industrial waste treatment methods such as rubbish are generally treated by burning in an incinerator. Although the combustion treatment can reduce the volume reduction rate of the waste by about zero, a large amount of external energy is required during combustion, and there is a problem of environmental damage such as dioxin and carbon dioxide during combustion. In order to solve this problem, industrial waste treatment has recently started using carbonization furnaces and thermal decomposition reactions. The municipal waste treatment by dioxin, carbon dioxide gas, etc. can be suppressed by thermally decomposing municipal waste in a reducing environment and completely burning the waste. Device, and furthermore 3 200537056 Many resources are being developed using the heat, water and other resources generated in this thermal decomposition step. [Patent Document] Japanese Patent Application Laid-Open No. 1 1-230522 [Summary of the Invention] As mentioned above, the conventional manufacturing method requires a large amount of energy in the firing step using electricity or firepower. In addition, the burning step is because Dioxin or carbon dioxide gas has caused the problem of gradual warming of the earth. In addition, the purchase of inorganic materials used as raw materials for ceramics also requires costs, and there are also problems in increasing the cost of manufacturing ceramics. It is an object of the present invention to provide a method and an apparatus for producing ceramics, which are used in organic wastes and are contained in wastes such as municipal waste. 2 Wood and ethene (using gas ethene, polyethene, polystyrene, etc.) as raw materials and residues, and the use of thermal decomposition of organic waste to generate ceramics. According to the present invention, since industrial wastes such as those described above can be used as raw materials for the production of ceramics, while the cost of raw materials can be reduced, the industry can make use of the heat of ordinary processing steps because of the AL · · r ^. Decomposition processing, Jin, # almost without the use of external energy can also be produced pottery, combined with the reduction of raw material costs can greatly reduce the manufacturing cost of ceramics. " Equipped with electric heaters or heat exchange tubes, there is no need to purge, just add J5, Shi 70 ·, ', organic waste in the tank to thermally decompose. The burner's method of 200537056 will be regarded as a procedure in which the burner must obtain a permit before it can be installed. 'However, if the method of forcibly increasing the temperature in the device by a method other than combustion is not required, there is no restriction on the location of the installation.

依"、、本發明,為了得到良好品質之陶瓷可以施行 必要的還原及氧化步驟各一:欠,可以使用更簡便的裝置來 得到良好品質之陶κ吏用本發明之方法所生成的陶究, 對惡臭物質的吸附、分解或是對大腸菌、沙門氏桿菌、 MRSA等細菌之殺菌效果非常優良。巾且,該陶竟生成過 程所發生的副產物木醋酸亦可以有效地使用在防蟲劑、土 壤改良材等各式各樣領域。According to the invention, in order to obtain good quality ceramics, one of the necessary reduction and oxidation steps can be performed: less, a simpler device can be used to obtain good quality ceramics. The ceramics produced by the method of the present invention The reason is that the adsorption and decomposition of malodorous substances or the bactericidal effect on bacteria such as coliform, salmonella, and MRSA are very good. In addition, wood acetic acid, a by-product of the pottery production process, can also be effectively used in various fields such as insect repellents and soil improvement materials.

又,如上所述,為了抑制戴奥辛、二氧化碳等之發生 最近產業廢棄物之熱分解處理被廣泛地利用,但是習知之 熱分解處理只進行至將廢棄物碳化處理而已,因為熱分解 終了時爐内還殘留在大量的有機物,廢棄物之體積減少率 為約只有減少至1/10〜1/20程度。又,習知之熱分解裝置 因為在燃燒室中燃燒因熱分解所發生的氣體,在排氣處理 有發生戴奥辛、二氧化碳的問題。本發明因為從熱分解處 理開始至排氣處理為止,完全沒有燃燒步驟,可以提供非 常向的安全性。 為解決前述課題,本發明之陶瓷生成方法,其特徵為, 具備有使含有微量無機成分之原料有機物熱分解之步驟、 和處理在該熱分解步驟所發生氣體之氣體處理步驟,該熱 分解步驟具備有在反應槽内將前述原料有機物分解成為含 5 200537056 有前述無機成分之碳化物、和氣體成分之分解步驟;和將 大量的電子送入前述反應槽中使前述反應槽内保持還原環 境之同時,將前述碳化物氣化使前述無機成分從前述碳化 物中分離之步驟;和使前述分離之無機成分與氧成分反應 形成氧化物之步驟。 本發明之陶瓷生成方法,藉由對在有機物之熱分解步 驟所發生之碳化物送入大量的電子,碳化物進而分解、氣 化而使無機成分從碳化物分離,而且有機物資源所含有之 氧氣與從碳化物所分離之無機成分結合成為無機氧化物, 亦即生成陶瓷。 因為利用有機物熱分解步驟,所以陶瓷之生成不需要 習知所必需要的焙燒步驟,可以大幅地降低製造成本。又, 在本發明所生成的陶瓷,因為係經過還原步驟和氧化步驟 所生成,顯示具有非常高惡臭成分吸附、分解、殺菌等效 果。 本發明方法,若含有微量之無機成分,全部有機物都 可以使用作為原料,特別是可以使用產業廢棄物所含有的 紙、木材、乙烯類(氣乙烯、聚乙烯、聚丙烯、聚苯乙烯等), 或是食品殘渣等作為適合的原料。目前熱分解處理產業廢 棄物被廣泛地進行,因此,不必特意地購買陶瓷原料(無機 物)亦可以生成陶瓷,可以降低製造成本。 本發明方法’其特徵為,前述熱分解步驟具備升高前 述反應槽内溫度之加熱步驟。 200537056 原料有機物之熱分解步驟可以使用通常之廢棄物處理 方式進行燃燒,但若是採用燃燒以外的方法例如電加熱 器、使暖風循環之熱交換管等強制提高裝置内溫度之構成 時,則不需要燃燒就可以達成原料有機物之熱分解。藉此, 本發明之方法,從熱分解處理開始至排氣處理為止,完全 不需要燃燒步驟,在不需要取得燃燒爐設置許可之同時, 可以提供非常高的安全性。 又’在反應槽内燃燒原料有機物時,前述原料有機物 以含有3000卡路里/g以上熱量為佳。藉由原料含有該程 度之卡路里,熱分解可以活潑地進行,可以有效率地生成 陶瓷。 而且,本發明之陶瓷生成方法,其特徵為,前述氣體 處理步驟具備有冷卻 '液化前述熱分解步驟所發生之氣體 及收集該液體之步驟。 如此’在熱分解步驟所發生之氣體,因為係碳化物之 氣化物而含有碳成分,將其液化會成為木醋酸。本發明裝 置所收集之木醋酸,經由中和處理等進行二次加工,可以 有效地利用作為防蟲劑、土壤改良劑等。 又’本發明之陶瓷生成方法’其特徵為,前述氣體處 理步驟具備有對從前述反應槽排出之氣體送入電子之還原 步驟。在則述熱分解步驟所排出的氣體雖然幾乎未含有戴 奥辛及碳酸氣,但是因為殘留有此等雖然是微量之物質, 因為期望達到完全而對此供給電子(負離子)使其無害化。 而且,在此處亦可以具有使大部份有電子送入之氣體 200537056 重返前述反應槽 如上述,排 成分重新被導入 化。 而且,本發 處理步驟,具有 之處理水中,使 驟。如上述,排 使殘留有害的氫 變為安全的水與 本發明有關 解反應槽其具備 熱分解反應槽内 前述在熱分解反 如此,本發 化物送入多量的 同時,碳化物進 材料有機物中含 分(礦物質)反應 棄物之熱分解反 瓷’並非大規模 氧化和環原兩步 物質吸附、分解 由從生成物取出 热之步驟。 明之陶瓷生成方法,其特徵為,前述氣體 將前述氣體或是其液㈣投人含有活性氧 其與處理水中的活性氧反應之氧化分解步 氣之大部分液化或是藉由電子分解,最後 和氧化碳與活性氧進行接觸,將此等轉 二氧化碳而無害化。 之陶瓷生成裝置,其特徵為,具備有熱分 有材料投入口和陶竟取出口、和對前述在 所發生之碳化物送入電子之手段、和收集 應槽内所產生排氣之排氣收集手段。 明之裝置,因為對熱分解反應所產生之碳 電子,反應槽上部在經常保持還原環境之 而分解而氣體化。又,反應槽的下部,在 有之氧成分與從碳化物分離之微量無機成 生成陶瓷。本發明之裝置,因為在利用廢 應槽之同時,該同一反應槽亦可以生成陶 的設備亦可以生成陶瓷。又,因為係經由 驟所生成之陶瓷,可以提供具有優良惡臭 效果、殺菌效果等之高品質陶瓷。而且藉 口依順序將陶瓷取出,原材料可以連續投As described above, in order to suppress the occurrence of dioxin, carbon dioxide, and the like, thermal decomposition treatment of industrial waste has been widely used recently, but conventional thermal decomposition treatment is only performed until the carbonization of the waste is performed because the thermal decomposition is completed in the furnace. A large amount of organic matter remains, and the volume reduction rate of the waste is only reduced to about 1/10 to 1/20. Further, the conventional thermal decomposition device has a problem that dioxin and carbon dioxide are generated in the exhaust gas treatment because the gas generated by thermal decomposition is burned in the combustion chamber. In the present invention, since there is no combustion step at all from the start of the thermal decomposition treatment to the exhaust treatment, it can provide extraordinary safety. In order to solve the aforementioned problems, the ceramic production method of the present invention is characterized by including a step of thermally decomposing a raw material organic substance containing a trace amount of an inorganic component, and a gas treatment step for treating a gas generated in the thermal decomposition step, and the thermal decomposition step It is provided with a decomposition step of decomposing the raw material organic matter into 5 200537056 containing the inorganic component and the gas component in the reaction tank; and sending a large amount of electrons into the reaction tank to maintain a reducing environment in the reaction tank. At the same time, the step of gasifying the carbide and separating the inorganic component from the carbide; and the step of reacting the separated inorganic component with an oxygen component to form an oxide. The ceramic production method of the present invention sends a large amount of electrons to the carbides generated in the thermal decomposition step of the organic matter, and the carbides are further decomposed and gasified to separate the inorganic components from the carbides, and the oxygen contained in the organic resources Combined with the inorganic components separated from carbides to form inorganic oxides, that is, ceramics are formed. Because the organic matter is thermally decomposed, the production of ceramics does not require a conventional firing step, which can significantly reduce manufacturing costs. In addition, the ceramics produced in the present invention are produced through a reduction step and an oxidation step, and have the equivalent effect of adsorbing, decomposing, and sterilizing very high malodorous components. In the method of the present invention, if a trace amount of an inorganic component is contained, all organic substances can be used as raw materials, and in particular, paper, wood, and ethylene (gas ethylene, polyethylene, polypropylene, polystyrene, etc.) contained in industrial waste can be used. , Or food residues, etc. as suitable raw materials. At present, industrial waste from thermal decomposition treatment is widely used. Therefore, it is not necessary to purchase ceramic raw materials (inorganic materials) to produce ceramics, which can reduce manufacturing costs. The method of the present invention is characterized in that the thermal decomposition step includes a heating step for raising the temperature in the reaction tank. 200537056 The thermal decomposition step of the raw material organic matter can be burned using the usual waste treatment methods, but it is not necessary to use a method other than combustion such as an electric heater or a heat exchange tube that circulates warm air to force the temperature inside the device to be increased. Thermal decomposition of raw material organic matter can be achieved by combustion. Thereby, the method of the present invention does not need a combustion step at all from the start of the thermal decomposition treatment to the exhaust treatment, and it does not need to obtain a combustion furnace installation permit, and can provide very high safety. When the raw material organic matter is burned in the reaction tank, the raw material organic matter preferably contains 3,000 calories / g or more. Since the raw material contains such a degree of calories, thermal decomposition can be actively performed, and ceramics can be efficiently produced. The ceramic production method of the present invention is characterized in that the gas treatment step includes a step of cooling the liquefied gas generated in the thermal decomposition step and collecting the liquid. In this way, the gas generated in the thermal decomposition step contains a carbon component because it is a gaseous carbide, and liquefied, it becomes lignoacetic acid. The wood acetic acid collected by the device of the present invention can be effectively used as an insect repellent, a soil improver, etc., through secondary processing through a neutralization treatment or the like. Furthermore, the "ceramic production method of the present invention" is characterized in that the gas processing step includes a reduction step of feeding electrons to the gas discharged from the reaction tank. Although the gas exhausted in the thermal decomposition step contains almost no dioxin and carbon dioxide gas, since these are trace amounts of substances, the electrons (negative ions) are supplied to make them harmless because they are expected to be complete. In addition, it is also possible to have a gas to return most of the electrons here. 200537056 Return to the aforementioned reaction tank. As mentioned above, the discharged components are reintroduced. Moreover, the present treatment step has a step of treating water. As mentioned above, it is related to the present invention to dissolve the remaining harmful hydrogen into safe water. It is equipped with a thermal decomposition reaction tank. The foregoing is the case with thermal decomposition. As the present compound is sent in a large amount, the carbide is entered into the material organic matter. Thermal decomposition anti-porcelain containing mineral (mineral) reaction waste is not a step of large-scale oxidation and primordial two-step adsorption and decomposition of materials by removing heat from the product. The method for producing ceramics of the Ming Dynasty is characterized in that the aforementioned gas or the liquid gas is thrown into a large part of the oxidative decomposition step containing active oxygen which reacts with the active oxygen in the treated water to be liquefied or decomposed by electrons, and finally Carbon oxide is contacted with active oxygen, and this is converted to carbon dioxide without harm. The ceramic generating device is characterized in that it has a heat input and material input port and a ceramic outlet, a means for feeding electrons to the aforementioned carbides, and an exhaust gas for collecting exhaust gas generated in the tank. Means of collection. The device of the Ming Dynasty decomposes and gasifies the carbon and electrons generated by the thermal decomposition reaction while maintaining the reducing environment. In the lower part of the reaction tank, ceramics are formed by an oxygen component and a small amount of inorganic components separated from carbides. In the device of the present invention, while using the waste reaction tank, the same reaction tank can also produce ceramic equipment and ceramics. In addition, since the ceramics produced by this step can provide high-quality ceramics having excellent malodorous effects, sterilizing effects, and the like. Moreover, the ceramics can be taken out in sequence under the pretext that raw materials can be continuously cast.

200537056 入’可以提高裝置之動用效率。 又,例如若設置有電加熱器或是暖風供給器等強制提 高裝置内溫度之加熱手段時,可以使反應槽内的材料不發 生燃燒而進行熱分解,可以完全不需要燃燒步驟。 又’本發明之陶瓷生成裝置,亦可以具備有在對熱分 解反應槽内生成碳化物送入前述大量電子之同時,亦送入 微量氧成分之氧供給手段。#用在反應槽内使有機物燃燒 之構成時,藉由送入氧成分可以促進燃燒而有利於陶瓷化。 又,本發明陶瓷生成裝置,前述排氣收集手段係採用 將前述排氣冷卻、液化之構成,乃是有效的。又,亦可以 具備有對使用前述排氣收集手段所收集之排氣送入電子之 第2電子供給手段。此時,採用前述電子供給手段之構成, 可以使大部份有電子送入之氣體被重新送入前述反應槽, 乃是有效的。而且,本發明之陶瓷生成裝置,在前述排氣 收集手段,具備有將收集到排氣送入處理槽(裝有含活性氧 之水)之手段,乃是有效的。 如此,排氣之大部分排氣液化或是藉由電子分解,最 後使殘留有害的氫和一氧化碳與活性氧進行接觸,將此等 轉變為安全的水與二氧化碳而無害化。使用習知熱分解係 發生之全部氣體燃燒處理,使用上述步驟完全不需要燃燒 步驟即可以達成排氣處理。 採用使排氣與活性氧反應之構成時,陶瓷生成裝置I 備有活性氧製造手段、和將使用該手段所製成活性氧送入 前述處理槽内水中之手段,乃是有效的。此處,前述活性 9 200537056 氧製造手段最好是具備有使前述處理槽中之水成為還原狀 態之手段、和臭氧發生裝置為佳。使該處理槽中之水成為 還原狀態之手段,最好是具備有電子(e·)發生裝置及/或將 還原劑投入前述處理槽中之手段。 如此,本發明可以使處理槽中水含有活性氧(Q-)來進 行排氣的氧化分解。使水中含有該活性氧時,藉由使處理 槽中的水成為還原狀態’可以使不易溶解在水中的臭氣變 為容易溶解。臭氧在水中分裂成為02和〇-,該活性氧0-與殘留之有害氩(HO及一氧化碳(C〇)反應(氧化分解)成為 無害的水(H2〇)和二氧化碳(C〇2) ^又,使水成為還原狀態 時,對處理槽中的水打進電子、在處理水中添加還原劑等, 可以更有效率地加速氧化分解。 【實施方式】 以下,參照圖示說明本發明有關之陶瓷生成ί裝置。 第1圖係用以說明本發明之陶瓷生成裝置整體構成之 圖。 本發明裝置,具備有熱分解反應槽1、和為了對該反 Φ 應槽内供給電子/氧之電子發生裝置2、和收集熱分解反應 槽1内所發生反應氣體之反應氣收集槽3、和處理該處所 收集到排氣之排氣處理裝置4。 熱分解反應槽1在上部具備有原料投入口 11,在下部 具備有陶瓷取出口 1 2,更具備有反應氣體收集用開口 1 3。 又’其構成為將原料投入口 i 1和陶瓷取出口 1 2關閉時可 · 10 200537056 以保持反應槽1内部為氣密狀態。反應氣體收集用開口 i 3 係通過導管13a與反應氣收集槽3連通。又,槽3更通過 導管13b與排氣處理裝置4連通。導管13b設置有風扇或 是幫浦等氣體吸收裝置14,可使將反應氣體導入收集槽3 容易進行。 本發明裝置,更具備有電子發生裝置2,其構成係為 了將電子送入反應槽1。電子發生裝置2可以使用任何構 成之裝置,藉由發生高電壓從單極之輸出電極發生電子之 形式、或是使空氣通過強磁場激發空氣中電子來發生電子 之形式、以及利用可以連續放出電子的礦物之裝置等為特 別適合加以利用。又,將電子送入之位置,可以在反應槽 1内之後述碳化層產生位置送入。 在排氣槽3下部,具備有接收槽内壁凝結液狀成分(木 醋酸)之接收部(圖中未顯示)、以及該液狀成分之取出口 13c 〇 以下’說明本裝置之陶瓷生成步驟。 首先’說明運轉初期步驟。從原料投入口 11投入作為 原料之有機廢棄物,從設置於反應槽下方之陶磁取出口 1 2,使用燃燒器等點火手段對原料直接點火。此處,原料 投入口係打開著使氧進入反應槽1内,原料一旦燃燒,其 後將原料投入口 11及陶磁取出口 1 2關閉。 由於關閉原料投入口 11及陶磁取出口 1 2,原料燃燒 停止’火亦熄滅,但是熱分解反應槽1内的溫度,因為先 前之燃燒而上升至300〜500度程度,反應槽1内之原料開 200537056 始產生熱分解。原料係使用具有至少含有3〇〇〇卡路里 程度熱量之有機物,可以用自已所具有的熱量進熱分解。 如此之有機物,可以使用例如都市垃圾中之紙、木材 乙 烯類(氣乙烯、聚乙烯、聚丙烯、聚苯乙烯等),或是食品 殘渣等作為適合的原料。 上述之初期燃燒及熱分解所發生的氣體呈煙狀,通過 導管1 3流至排氣槽3那一側。 如上所述,本裝置具備有電子發生裝置2,其構成係 用以從該裝置2經由設置於反應槽1側壁之電子供給口對 反應槽1供給電子。該電子供給口設置有吸入外部空氣之 吸氣口(圖未顯示),因熱分解而在反應槽1内所產生氣體 會流出至排放槽1 3,而和其流出至排氣槽j 3之相同量的 空氣與電子會一起流入反應槽1内。反應槽1内與電子一 起流入之空氣所含之氧亦當然會被送入,但是因為送入之 電子其能量比這更大,所以反應槽丨内之還原環境可以保 持’槽内的溫度即使上升亦原料不會有起火情形。 亦即’熱分解槽丨内係利用作為原料投入之有機物自 身所具有之卡路里來進行熱分解。熱分解進行時,原料有 機物變成為碳化物而在熱分解反應槽i的下部產生碳化層 5。又,電子發生裝置2之電子供給口,因為係設置在上述 碳化層產生之位置’在碳化層5產生之後,可以向著該碳 化層供給電子或是空氣(氧成分)。 如上述’投入有機物原料、點火、使原料進行某程度 之燃燒RI斷空氣而媳火時,藉由該燃燒所發生的熱,有 12 200537056 機物開始熱分解及氣化。亦即,原料中所含之碳成分及微 1之無機礦物質成分以外之成分化為氣體而蒸發。殘留之 碳成分則留存於反應槽1下部之碳化槽中。藉由對碳化層 内送入來自電子發生器之大量電子,碳化層中的熱分解繼 續進行,該碳成分亦化為氣體而蒸發,最後,只剩下原料 中所含有之無機礦物質殘留。該無機礦物質和從電子發生 褒置2進來之空氣中所含有微量氧結合成為無機氧化物, 亦即陶瓴6而殘留在反應槽1之底部。從設置於反應槽1 下部或底部之陶瓷取出口 i 2取出該陶瓷6而加以利用。 依照本發明方法所生成的陶瓷,因為在原料中所含有 的微量無機物轉變成氧化物而殘留,其重量為最初投入有 機物原料之數百分之一程度。相對於原料雖然生成物之回 收率低’但是可以有效地利用產業廢棄物。該產業廢棄物 最近採用熱分解處理之處理方法正廣泛地進行,只需要對 該廢棄物之熱分解装置稍加改良,即可以作為廢棄物處理 之一環用來生成陶瓷。 又’藉由該方法所生成的陶瓷,因為係經由還原步驟 所生成,具有優良的脫臭性 '抗菌性,可以在多方面有效 性地利用。 又若技入之有機物較少時,反應槽1内的卡路里減 夕熱刀解減弱’反應槽1内的溫度降低。$了防止因該溫 度降低使熱分解循環停止,最好經常繼續地投入原料。亦 即’ 一旦開始運轉,本裝置因為只要繼續地投入材料即可 200537056 以連續地運轉’裝置可以效率良好地進行運轉。 該反應槽1之另外實施形態,亦可以設置加熱反應槽 1内部之加熱裝置。亦即,對陶瓷生成裝置之反應槽内進 行強制性加熱之電氣加熱器、或是例如使熱交換管環繞反 應槽使1000度之暖風循環等,可以不使用燃燒將内部溫度 上升至300〜5 00度使在反應槽内原料有機物進行熱分解。 採用如此之構成時,因為不管原料有機物具有的熱量如何 都可以將溫度提高,可以適合使用於卡路里較少之資源進 行陶瓷化。又,因為即使對反應槽1投入較少之有機物時 亦能夠保持在所希望的溫度,可以使熱分解進行到最後為 止’因為可以防止熱分解循環停止,可以不必經常投入原 料。又,採用該構成時,因為可以達成從熱分解至後述之 排氣處理為止所有之步驟都不需要燃燒,在提高安全性之 同時,本發明裝置不須被視為燃燒爐因而不必申請設置許 cfj" 〇 又’上述實施例之構成,雖然送入多量電子之同時送 入氧,但是該氧供給手段並非必須之構成。亦即,因為即 使在熱分解中未對反應槽送入氧,只靠在原料有機物所含 有的氧亦可以進行陶瓷化,為了謀求削減成本省去另外設 置氧供給手段亦可。 上述熱分解過程所發生之氣體,係因為原料中含有大 量的油脂成分、氫、碳等,為可燃性氣體。通常產業廢棄 物之熱分解裝置,另設燃燒室來燃燒該氣體。但是燃燒該 14 200537056 氣體時’因為有發生戴奥辛公害、發生二氧化碳氣體導致 地球溫暖化等問題,然而本發明裝置,不必依靠燃燒即可 進行獨自的氣體處理。以下說明該氣體處理。200537056 入 ’can improve the utilization efficiency of the device. Further, for example, if heating means for forcibly increasing the temperature in the apparatus such as an electric heater or a heater is provided, the materials in the reaction tank can be thermally decomposed without burning, and a combustion step can be completely eliminated. Further, the ceramic generating device of the present invention may be provided with an oxygen supply means for feeding carbides generated in the pyrolysis reaction tank and feeding a large amount of electrons as well as a small amount of oxygen components. #When used in the structure that burns organic matter in the reaction tank, the oxygen component can be used to promote combustion and facilitate ceramization. Further, in the ceramic generating apparatus of the present invention, the exhaust gas collection means is effective in that the exhaust gas is cooled and liquefied. Furthermore, a second electron supply means for feeding electrons to the exhaust gas collected by the exhaust gas collection means may be provided. At this time, it is effective to use the structure of the aforementioned electron supply means to allow most of the gas with electrons to be sent to the aforementioned reaction tank again. Furthermore, the ceramic generating device of the present invention is effective in that the exhaust gas collecting means includes a means for sending the collected exhaust gas into a processing tank (containing active oxygen-containing water). In this way, most of the exhaust gas is liquefied or decomposed by electrons, and finally harmful hydrogen and carbon monoxide are brought into contact with active oxygen, which is converted into safe water and carbon dioxide without harm. Using the conventional thermal decomposition system for all gas combustion treatments, the above steps can be used to achieve exhaust treatment without the need for a combustion step. In the case where the exhaust gas is reacted with active oxygen, the ceramic generating device I is provided with active oxygen production means and means for feeding active oxygen produced by the means into the water in the aforementioned treatment tank. Here, it is preferable that the above-mentioned activity 9 200537056 means for producing oxygen is provided with a means for reducing water in the treatment tank and an ozone generating device. The means for bringing the water in the processing tank into a reduced state is preferably provided with an electron (e ·) generating device and / or a means for putting a reducing agent into the processing tank. As described above, the present invention can oxidize and decompose exhaust gas by containing active oxygen (Q-) in the water in the treatment tank. When the active oxygen is contained in water, the water in the treatment tank is brought into a reduced state ', thereby making it possible to easily dissolve an odor which is not easily dissolved in water. Ozone is split into 02 and 0- in water, and the active oxygen 0- reacts (oxidatively decomposes) with residual harmful argon (HO and carbon monoxide (CO)) into harmless water (H20) and carbon dioxide (CO2). When the water is brought into a reduced state, electrons can be injected into the water in the processing tank, and a reducing agent can be added to the processed water to more efficiently accelerate the oxidative decomposition. [Embodiment] Hereinafter, the ceramics according to the present invention will be described with reference to the drawings. Device for generating ί. Figure 1 is a diagram for explaining the overall structure of the ceramic generating device of the present invention. The device of the present invention includes a thermal decomposition reaction tank 1 and electron generation for supplying electrons / oxygen to the reaction tank. Device 2, a reaction gas collection tank 3 that collects the reaction gas generated in the thermal decomposition reaction tank 1, and an exhaust gas treatment device 4 that processes the exhaust gas collected there. The thermal decomposition reaction tank 1 is provided with a raw material input port 11 at the top. The lower part is provided with a ceramic take-out port 1 2 and a reaction gas collection opening 13. It is also configured so that when the raw material input port i 1 and the ceramic take-out port 1 2 are closed, it can be guaranteed. The inside of the reaction tank 1 is airtight. The reaction gas collection opening i 3 is connected to the reaction gas collection tank 3 through a conduit 13a. The tank 3 is further connected to the exhaust treatment device 4 through a conduit 13b. The conduit 13b is provided with a fan or It is a gas absorption device 14 such as a pump, which can easily introduce the reaction gas into the collection tank 3. The device of the present invention further includes an electron generating device 2 which is configured to send electrons into the reaction tank 1. The electron generating device 2 can Using any device, a form that generates electrons from a unipolar output electrode by generating a high voltage, or a form that generates electrons by exciting air in the air with a strong magnetic field, and a device that uses minerals that can continuously emit electrons. It is particularly suitable for use. In addition, the position where electrons are sent in can be sent in the position where the carbonized layer is generated later in the reaction tank 1. The lower part of the exhaust tank 3 is provided with a condensed liquid component (wood acetic acid) on the inner wall of the receiving tank. The receiving section (not shown in the figure) and the liquid component extraction outlet 13c are described below for the ceramic production steps of this device. The initial steps of the operation are explained. Organic waste is used as the raw material from the raw material input port 11. Take the outlet 12 from the ceramic magnet installed below the reaction tank, and use the burner and other ignition means to directly ignite the raw material. Here, the raw material input port is open. As the oxygen enters the reaction tank 1, once the raw material is burned, the raw material input port 11 and the ceramic magnetic take-out outlet 12 are closed. Since the raw material input port 11 and the ceramic magnetic take-out outlet 12 are closed, the raw material combustion is stopped. The temperature in the thermal decomposition reaction tank 1 rises to about 300 to 500 degrees due to the previous combustion. The raw materials in the reaction tank 1 start to be thermally decomposed since 200537056. The raw materials are organic substances that contain at least 3,000 calories. You can use the heat you have for thermal decomposition. As such organic materials, for example, paper, wood vinyls (gas ethylene, polyethylene, polypropylene, polystyrene, etc.) in urban waste, or food residues can be used as suitable raw materials. The gas generated during the initial combustion and thermal decomposition described above is in the form of a smoke, and flows to the side of the exhaust groove 3 through the duct 13. As described above, this device is provided with the electron generating device 2 which is configured to supply electrons from the device 2 to the reaction tank 1 through the electron supply port provided on the side wall of the reaction tank 1. The electronic supply port is provided with an air intake port (not shown) for drawing in external air, and the gas generated in the reaction tank 1 due to thermal decomposition flows out to the exhaust tank 13 and flows out to the exhaust tank j 3 The same amount of air and electrons will flow into the reaction tank 1 together. Of course, the oxygen contained in the air flowing with the electrons in the reaction tank 1 will also be sent in, but because the electrons sent in have greater energy than this, the reducing environment in the reaction tank 丨 can maintain the temperature in the tank even if There will be no fire in the raw materials. That is, the inside of the 'thermal decomposition tank' uses the calories of the organic substance input as a raw material to perform thermal decomposition. When the thermal decomposition proceeds, the organic material of the raw material becomes a carbide, and a carbonized layer 5 is generated in the lower part of the thermal decomposition reaction tank i. The electron supply port of the electron generating device 2 is provided at the position where the carbonized layer is generated. After the carbonized layer 5 is generated, electrons or air (oxygen component) can be supplied to the carbonized layer. As mentioned above, when the organic material is put in, ignited, and the raw material is burned to a certain degree, the air is cut off, and the flame is caused by the heat generated by the combustion. That is, components other than the carbon component contained in the raw material and the micromineral inorganic component are converted into a gas and evaporated. The remaining carbon components remain in the carbonization tank at the lower part of the reaction tank 1. By feeding a large amount of electrons from the electron generator into the carbonized layer, the thermal decomposition in the carbonized layer continues, and the carbon component is also converted into a gas and evaporated. Finally, only the inorganic minerals contained in the raw material remain. This inorganic mineral is combined with a trace amount of oxygen contained in the air coming in from the electron generating unit 2 to form an inorganic oxide, that is, pottery tin 6 and remains at the bottom of the reaction tank 1. The ceramic 6 is taken out from a ceramic take-out port i 2 provided at the bottom or bottom of the reaction tank 1 and used. The ceramics produced according to the method of the present invention remain in a trace amount because the trace inorganic substances contained in the raw materials are converted into oxides, and their weight is about one hundredth of the amount of the organic material raw materials initially charged. Although the yield of the product relative to the raw material is low ', industrial waste can be effectively used. The industrial waste has recently been extensively treated by thermal decomposition. Only a slight improvement of the thermal decomposition device of the waste can be used as a part of waste treatment to produce ceramics. Furthermore, since the ceramics produced by this method are produced through a reduction step, they have excellent deodorizing properties, and have antibacterial properties, and can be effectively used in many ways. If there is less organic matter to be injected, the calories in the reaction tank 1 are reduced and the thermal knife solution is reduced. The temperature in the reaction tank 1 is reduced. In order to prevent the thermal decomposition cycle from being stopped due to the temperature decrease, it is best to continue to feed the raw materials. That is, once the operation starts, the device can be operated continuously as long as materials are continuously put into operation. 200537056 The device can be operated continuously. The device can operate efficiently. In another embodiment of the reaction tank 1, a heating device for heating the inside of the reaction tank 1 may be provided. That is, an electric heater forcibly heating the reaction tank of the ceramic production device, or for example, a heat exchange tube surrounding the reaction tank to circulate 1,000 degrees of warm air, etc., the internal temperature can be raised to 300 ~ without using combustion. 5,000 degrees of thermal decomposition of raw material organic matter in the reaction tank. With this structure, the temperature can be increased regardless of the amount of heat of the raw organic matter, which makes it suitable for use in ceramics with fewer calories. In addition, because the organic matter can be kept at a desired temperature even when a small amount of organic matter is charged into the reaction tank 1, the thermal decomposition can be carried out to the end 'because the thermal decomposition cycle can be prevented from being stopped, and it is not necessary to frequently charge the raw materials. In addition, when this structure is adopted, all steps from thermal decomposition to exhaust gas treatment to be described later can be achieved without combustion. While improving the safety, the device of the present invention does not need to be regarded as a combustion furnace, so it is not necessary to apply for a license. cfj "The structure of the above-mentioned embodiment, although a large amount of electrons are fed together with oxygen, but this oxygen supply means is not an essential configuration. That is, even if oxygen is not fed to the reaction tank during thermal decomposition, it is possible to ceramize only the oxygen contained in the raw material organic matter. In order to reduce costs, an additional oxygen supply means may be omitted. The gas generated in the above thermal decomposition process is a flammable gas because the raw material contains a large amount of oil and fat components, hydrogen, carbon and the like. Usually, the thermal decomposition device of industrial wastes has a separate combustion chamber to burn the gas. However, when the 14 200537056 gas is burned, there are problems such as the occurrence of dioxin pollution and global warming caused by the generation of carbon dioxide gas. However, the device of the present invention can perform independent gas treatment without relying on combustion. The gas treatment will be described below.

首先是氣體從進入排氣槽3,因為此槽與外氣連接而 自然地被冷卻,於是進入之氣體被冷卻而在槽内面凝結, 能夠以液體形式回收。該回收液體之主要成分為碳,係木 醋酸(CHsCOOH)狀態,可以經由中和處理等二次處理而利 用作為防蟲劑、土壤改良材等。又,依投入原料而定,亦 可能含有油脂成分、氣等,可以適當地進行去除此等成分。The first is that the gas enters the exhaust tank 3 because it is naturally cooled because it is connected to the outside air, so the incoming gas is cooled and condenses on the inside of the tank, and can be recovered as a liquid. The main component of the recovered liquid is carbon, which is in the state of acetic acid (CHsCOOH). It can be used as an insect repellent or soil improvement material through secondary treatment such as neutralization. In addition, depending on the input materials, it may contain a fat component, gas, etc., and these components can be removed appropriately.

無法藉由排氣槽凝結現象來回收之氣體,因為係極度 酸性之氣體,在排氣處理裝置4使用氫氧化鈉等鹼水進行 中和處理。又,在排氣處理裝置設置有對排氣送入電子之 第2電子發裝置(圖中未顯示)。排氣處理裝置4有配管7 連接用以將氣體再度送回反應槽1中,該構成係為了使處 理槽4内之大部份氣體再次被送回反應槽1。而且,該處 未能送回反應槽1之部分,如第2圖所示送至第2處理裝 置9。 該最後所殘留之氣體含有雖然微量但有害之氫及一 氧化碳。因為本發明希望達到完全,將該處理水所殘留之 氣體導入含有活性氧之水中,使氫及一氧化碳產生氧化分 解。亦即,例如在水中溶入臭氧(03),使其分裂成為〇2和 cr,藉由該〇-(活性氧)來氧化分解殘留氣體。但是,因為 臭氧具有不容易溶於水中之性質,採用以下的手法有效率 15 200537056 地將臭氧溶入水中。 如第2圖所示,第2處理裝置9具備有處理槽1、臭 氧發生裝置92、和磁場發生裝置93等。在處理槽^中加 入水,使用磁場發生裴置93來發生磁場,使處理場中的水 成為磁場水’將臭氧發生裝置92所發生之臭氧送入該處。 因為磁場水中產生電子(e·),臭氧可以容易地溶入水中而 分裂成〇2和CT。該活性氧(〇-)和氫(H)及一氧化碳(c〇)結 合’生成無害的水(H2O)和二氧化碳(C〇2)。 又’用以替代磁場發生裝置93,亦可以進而設置電 子發生器’將該處所產生之電子(e·)打入處理槽9 1中,使 處理水全體成為還原水之構成亦可。亦即,亦可以使處理 槽1中的水呈現缺氧狀態後,從該處臭氧發生裝置92送入 臭氧來製造活性氧,用以氧化分解排氣。 又’若設置有用來攪拌還原狀態之水和臭氧之攪拌裝 置時’可以使臭氧溶入水中更為容易。又,若在臭氧發生 裝置92設置有氧透過過濾器94,使從外部進來的空氣通 過透過過濾器94而送入臭氧發生裝置時,可以更有效率地 產生兩濃度的臭氧。又,藉由氧透過過濾器94,因為可以 会除空氣中所含的其他成分,可以抑制NOx、SOx等之發 生。 又’亦可以不使用臭氧發生裝置92,改使用在處理 水中投入過氧化氫等氧化劑之手段,來得到含有活性氧的 處理水。又,替代臭氧發生裝置92 ,亦可以設置電分解裝 16 200537056 置(圖中未顯示),電分解水來製造活性氧並打入水中。 本發明者等,為確認使用上述裝置進行熱分解所生成 陶瓷之特性,進行以下之消臭試驗和抗菌試驗。 (1) 消臭試驗 準備彿石5g(試樣1)、本發明裝置所生成之陶究粉末 5g為試樣,使用圖3所示之試驗裝置進行消臭試驗。 準備試驗裝置20、尺寸300 x3 00 X 3 00mm容量約27 公升之壓克力容器21。因為容器21設置有注入裝置22, 可以在容器21注入試驗氣體。在容器21内放入上側具有 複數孔穴之試樣容器23,上面放置可以攪拌容器内空氣之 反應風扇24(1 ·2πι3/分鐘)。容器21更具備有氣體測定口 25 ’係使用幫浦能夠由該處吸引内部氣體、藉由檢測器27 可以測定其濃度之構成。又,符號28係試樣插入口。 試驗氣體,準備初期濃度150ppm之氨(試驗氣體〇 和初期濃度32ppm曱醛(試驗氣體2)。 將上述試驗氣體導入試驗裝置20,測定各試樣1小 時後、2小時後、4小時後、6小時後、24小時後殘留氣體 濃度’算出殘留率。又,初期濃度係氣體注入試驗容器後 2分鐘後所測定之數值。 試驗氣體1之殘留濃度之變化及殘留率如第4圖所 示’試驗氣體2之殘留濃度之變化及殘留率如第5圖所示。 由此等試驗結果可以清楚知道,本製品陶瓷和一般使 用作為消臭劑之沸石比較,氣體之殘留濃度有意義地較 17 200537056 低,因此可以知道具有較高之除臭效果。 (2) 抗菌試驗 準備使用滅菌生理食鹽水稀釋本發明裝置所生成之 陶瓷粉末而成之 〇·〇1°/。、0.05%、0.1%、0.5%、1.0%、10.0% 之試樣,及對照用試樣。 供試菌The gas that cannot be recovered by the condensation phenomenon of the exhaust gas tank is an extremely acidic gas, and the exhaust gas treatment device 4 is neutralized with alkaline water such as sodium hydroxide. A second electron generator (not shown) for sending electrons to the exhaust gas is provided in the exhaust gas treatment device. The exhaust gas treatment device 4 has a pipe 7 connected to return the gas to the reaction tank 1 again. This structure is to return a large part of the gas in the processing tank 4 to the reaction tank 1 again. The part that could not be returned here to the reaction tank 1 was sent to the second processing device 9 as shown in Fig. 2. The last remaining gas contains trace amounts of harmful hydrogen and carbon monoxide. Because the present invention is intended to be complete, the gas remaining in the treated water is introduced into the water containing active oxygen to cause oxidative decomposition of hydrogen and carbon monoxide. That is, for example, ozone (03) is dissolved in water, and it is split into 0 2 and cr, and the residual gas is oxidized and decomposed by the 0- (active oxygen). However, because ozone is not easily soluble in water, the following method is used to efficiently dissolve ozone in water. As shown in Fig. 2, the second processing device 9 includes a processing tank 1, an ozone generating device 92, a magnetic field generating device 93, and the like. Water is added to the treatment tank ^, and a magnetic field is generated using the magnetic field generator Pei 93, so that the water in the treatment field becomes magnetic water. The ozone generated by the ozone generator 92 is sent there. Because electrons (e ·) are generated in magnetic water, ozone can be easily dissolved in water and split into O2 and CT. This active oxygen (0-) is combined with hydrogen (H) and carbon monoxide (c0) 'to produce harmless water (H2O) and carbon dioxide (C02). It is also possible to use an "electron generator" instead of the magnetic field generating device 93 to drive the generated electrons (e ·) into the processing tank 91 so that the whole treated water becomes reduced water. That is, after the water in the treatment tank 1 is brought into an anoxic state, ozone may be sent from the ozone generating device 92 there to produce active oxygen for oxidatively decomposing the exhaust gas. In addition, when a stirring device for stirring water in a reduced state and ozone is provided, ozone can be dissolved in water more easily. Further, if the ozone generating device 92 is provided with an oxygen permeation filter 94, the air coming in from the outside is transmitted through the filter 94 to the ozone generating device, so that ozone at two concentrations can be generated more efficiently. In addition, since the oxygen permeation filter 94 can remove other components contained in the air, the occurrence of NOx, SOx, and the like can be suppressed. Alternatively, instead of using the ozone generating device 92, a method of adding an oxidant such as hydrogen peroxide to the treated water may be used to obtain treated water containing active oxygen. In addition, instead of the ozone generating device 92, an electrolysis device (200537056) (not shown in the figure) may be provided to electrolyze water to produce active oxygen and inject it into the water. The present inventors conducted the following deodorization test and antibacterial test in order to confirm the characteristics of ceramics produced by thermal decomposition using the above-mentioned apparatus. (1) Deodorization test 5 g of Buddha stone (Sample 1) and 5 g of ceramic powder produced by the apparatus of the present invention were prepared as samples, and the deodorization test was performed using the test apparatus shown in FIG. 3. A test device 20 and an acrylic container 21 with a size of 300 x 300 x 300 mm and a capacity of about 27 liters were prepared. Because the container 21 is provided with an injection device 22, the test gas can be injected into the container 21. In the container 21, a sample container 23 having a plurality of holes on the upper side was placed, and a reaction fan 24 (1.2 m3 / min) capable of agitating the air in the container was placed thereon. The container 21 is further provided with a gas measurement port 25 ', which is a structure in which the internal gas can be sucked in using the pump and the concentration can be measured by the detector 27. Reference numeral 28 denotes a sample insertion port. The test gas was prepared with an initial concentration of 150 ppm of ammonia (test gas 0 and an initial concentration of 32 ppm of formaldehyde (test gas 2). The test gas was introduced into a test device 20, and each sample was measured after 1 hour, 2 hours, 4 hours, After 6 hours and 24 hours, the residual gas concentration was calculated. The initial concentration is the value measured 2 minutes after the gas was injected into the test container. The change in the residual concentration of the test gas 1 and the residual ratio are shown in Figure 4. 'The change in the residual concentration of the test gas 2 and the residual rate are shown in Figure 5. From the results of these tests, it is clear that the residual concentration of the gas in this product is significantly higher than that of zeolite, which is generally used as a deodorant. 200537056 is low, so it can be known to have a high deodorizing effect. (2) Antibacterial test prepared by diluting ceramic powder produced by the device of the present invention with sterilized physiological saline, 0.05%, 0.1% , 0.5%, 1.0%, 10.0% samples, and control samples.

準備以下菌種,使用SA培養基、37°C、24小時前培 養此等菌種供試驗用。 1) Eschericia coli 大腸菌 KEC-B-001 2) Staphylococcus auresus 黃色葡萄球菌 KEC-B-002 3) Pseudomonas aeruginosa 綠濃菌 KIEC-B-003 4) Bacillus sobtillus 枯草菌 KEC-B-007 5) Salmonera typhimurium 沙氏門菌 KEC-B-009 第6圖係顯示本抗菌試驗之試驗順序之圖。 使用滅菌生理食鹽水將前培養之供試菌調整成為The following strains were prepared and cultured in SA medium at 37 ° C for 24 hours before testing. 1) Eschericia coli KEC-B-001 2) Staphylococcus auresus KEC-B-002 3) Pseudomonas aeruginosa KIEC-B-003 4) Bacillus sobtillus KEC-B-007 5) Salmonera typhimurium Klebsiella KEC-B-009 Fig. 6 is a diagram showing the test sequence of this antibacterial test. Use sterilized physiological saline to adjust the previously cultured test bacteria to

ΙΟ7 X CFU/ml。將該細胞液0.1ml接種於各檢測試樣,在 室溫下使用振盪機1 85/rpm進行振盪,經過規定時間(24 小時、48小時)後,取出被檢測試樣,使用滅菌生理食鹽 水製成10倍稀釋階段系列。接著,將其塗抹接種於pDA 培養基上進行培養,細菌為37t、2曰,酵母為25^、2 曰,黴菌為28艺、7曰,測定培養基上所形成之群體。 第7圖至第1 2圖係顯示上述抗菌試驗社要 、口不的表。如 各表所示’可看出使用本發明所生成之陶瓷具右 — 、巧翔著的抗 18 200537056 菌效果。 本發明陶瓷生成方法^ ^ 古因為未經培燒步驟即可以生成 陶究,可以謀求削減能源〇 ^ ^ ^ ^ 又,沒有因產生而引起戴奥辛 的公害問題、因產生二 一虱化衩而導致地球溫暖化問題等而 可以生成陶瓷。 依照本方法,因為初期 ^ ^ . h 1例瑚階段一旦開始,藉由有機物之 …、刀解可以使裝置内的溫度維持在3〇〇〜5〇〇度,原料自已1007 X CFU / ml. 0.1 ml of this cell liquid was inoculated into each test sample, and shaken using a shaker at 1 85 / rpm at room temperature. After a predetermined time (24 hours, 48 hours), the test sample was taken out, and sterile physiological saline was used. Made into a 10-fold dilution stage series. Next, it was smeared and inoculated on pDA medium for culture. The bacteria were 37t, 2nd, yeast 25, 2nd, and mold 28, 7th. The population formed on the medium was measured. Figures 7 to 12 are tables showing the main points of the above-mentioned antibacterial test agency. As shown in the tables, it can be seen that the ceramics produced by using the present invention have the right antibacterial effect of 18 200537056. The method for generating ceramics of the present invention ^ ^ Because ancient ceramics can be generated without firing steps, and energy can be reduced ^ ^ ^ ^ In addition, there is no pollution problem caused by dioxin due to generation, and diploid pupation caused by generation Ceramics can be produced by issues such as global warming. According to this method, once the initial stage of ^^^ h is started, the temperature in the device can be maintained at 3000 ~ 500 degrees by the organic matter ...

靶製坆出熱分解所需要的溫度,冑置運轉自身亦可以在低 成本、低公害之下進行。 又’因為原材料可以利用有機系廢棄物,可以有效地 進行廢棄物之再生。 而且,本發明方法所生成的陶瓷,因為經過還原步 驟,脫臭性、抗菌性優良,可以應用在各式各樣領域。又, 使排氟液化所得到的木醋酸’藉由施加二次加工亦可以有 效地利用。 【囷式簡單說明】The target system produces the temperature required for thermal decomposition, and the installation operation itself can be performed at low cost and low pollution. Also, because raw materials can use organic waste, waste can be effectively recycled. In addition, the ceramics produced by the method of the present invention can be used in various fields because they have excellent deodorizing properties and antibacterial properties after the reduction step. In addition, lignoacetic acid 'obtained by liquefying the exhausted fluorine can be effectively used by subjecting it to secondary processing. [Simplified description of 囷 style]

第1圖係顯示本發明陶瓷製造裝置之構成圖。 第2圖係顯示第2處理裝置9之構成圖。 第3圖係顯示本發明裝置所成生陶瓷之消臭試驗所使用試 驗裝置之構成圖。 第4圖係顯示本發明裝置所成生陶竟之消臭試驗結果之圖 表。 第5圖係顯示本發明裝置所成生陶瓷之消臭試驗結果之圖 19 200537056 表。 第6圖係顯示關於進行本發明裝置所成生陶瓷之抗菌試驗 之順序圖。 第7圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之圖 表。 第8圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之圖 表。 第9圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之圖Fig. 1 is a structural diagram showing a ceramic manufacturing apparatus of the present invention. FIG. 2 is a configuration diagram showing a second processing device 9. Fig. 3 is a structural diagram showing a test device used in a deodorization test of a raw ceramic produced by the device of the present invention. Fig. 4 is a graph showing the deodorization test results of raw ceramics produced by the device of the present invention. Fig. 5 is a table showing the results of the deodorization test of raw ceramics produced by the device of the present invention. Fig. 6 is a sequence diagram showing an antibacterial test performed on a ceramic produced by the apparatus of the present invention. Fig. 7 is a graph showing the antibacterial test results of the raw ceramics produced by the device of the present invention. Fig. 8 is a graph showing the results of an antibacterial test on the ceramic produced by the device of the present invention. FIG. 9 is a graph showing the antibacterial test results of the ceramic produced by the device of the present invention

第1 〇圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之 圖表。 第11圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之 圖表。 第12圖係顯示本發明裝置所成生陶瓷之抗菌試驗結果之 圖表。 【元件代表符號簡單說明】 1 熱分解反應槽 2 電子發生裝置 3 排氣槽 4 排氣處理裝置 9 第2處理裝置 11 原料投入口 12 生成物取出口 20 200537056 13a 導管 13b 導管 13c 液體成分收集口 14 吸引裝置Figure 10 is a graph showing the antibacterial test results of the ceramic produced by the device of the present invention. Fig. 11 is a graph showing the antibacterial test results of the green ceramics produced by the device of the present invention. Fig. 12 is a graph showing the results of an antibacterial test on the ceramic produced by the device of the present invention. [Simple description of component representative symbols] 1 Thermal decomposition reaction tank 2 Electron generation device 3 Exhaust tank 4 Exhaust treatment device 9 Second treatment device 11 Raw material input port 12 Product extraction port 20 200537056 13a Duct 13b Duct 13c Liquid component collection port 14 Suction device

21twenty one

Claims (1)

200537056 拾、申讀專利範圍: 1· 一種陶瓷生成方法,其特徼盘 做马,其至少含·且 分解含有微量無機成分之原料有撫% 4 饰’… 负機物之步驟,和處理該埶分 解步驟所發生氣體之處理步驟,該叙八> •“ 通熟分解步驟具 原料有機物分解成為含有前述無機 ν ν ^ Μ ”、風y刀之碳化物和氣體成 分之分解步驟,·和 對前述分離之碳化物送入多量之φ 电予,在保持前述反應 槽内為還原環境之同時,將前述碳化仏#200537056 The scope of the patent application: 1. A ceramic production method, which uses a special plate to make horses, which contains at least and decomposes raw materials containing trace inorganic components. 4% Decorations ... Steps for processing negative materials, and processing the处理 The treatment step of the gas generated in the decomposition step, the eighth step> "The familiar decomposition step has the decomposition of raw material organic matter into the decomposition step containing the aforementioned inorganic ν ν ^ Μ", the carbide and gas components of the wind y knife, and A large amount of φ electricity is sent to the aforementioned separated carbides, and the aforementioned carbides are maintained while maintaining a reducing environment in the aforementioned reaction tank. I啜化物氣體化並將前述無機 物從前述碳化物分離之夕驟;和 將前述分離之無機成分與氧成分 人刀反應形成氧化物之步 驟0 2. 如申請專利範㈣1項所述之陶究生成方法,其中 前述之原料有機物係產業廢棄物。 3. 如申請專利範圍$ i項或第2項所述之陶究生成方 法,#中前述之熱分解步驟具備有對前述反應槽内加熱之 加熱步驟。The step of gasifying and separating the aforementioned inorganic material from the aforementioned carbide; and the step of reacting the separated inorganic component with the oxygen component by a knife to form an oxide The production method, wherein the aforementioned raw material organic matter is an industrial waste. 3. As described in the patent application scope of item i or item 2 of the method for generating ceramics, the aforementioned thermal decomposition step in # has a heating step of heating the aforementioned reaction tank. 4. 如申請專利範圍第i項或第2項所述之陶究生成方 法’其中前述之原料有機物係至少含有3〇〇〇卡路里化之 熱量。 5. 如申請專利範圍第1項所述之陶瓷生成方法,其中 前述之氣體處理步驟係具備有將從前述反應槽所排出氣體 冷卻、液化及收集該液化物之步驟。 6. 如申請專利耗圍第1項或第5項所述之陶究生成方 法’其甲前述之氣體處理步驟係具備有對從前述反應槽所 22 200537056 排出氣體送入電子之還原步驟。 7·如申請專利範圍第6所述之 述之氣體處理步驟更具備 ’’,其中刖 乂哪更具·備有將大部份有 返前述反應槽進行加熱之步驟。 《之乳體重 8.如申請專利範圍第1 赤 法,其中/第5項所述之陶瓷生成方 浐入入古革“各 具備將刖述氣體或其液化物 技入3有活性氧處理水來進行氧化分解之步驟。 9· 一種陶瓷生成裝置,其 ^ # a ^ ^ 、特徵為,具備有熱分解反應 槽’其具備有材料投入口和陶瓷 不W免取出口;和對前述在熱分 解反應槽内所發生之碳化物送 ^ ^ v 疋八電子之構件;和收集前述 在熱为解反應槽内所產生排氣之排氣收集構件。 ίο.如申請專利範圍第9項所述之陶究生成裝置 具備有提熱分反應槽内溫度之加熱構件。 Π.如申請專利範圍第9項所述之陶究生成裝置 前述加熱構件係電加熱器或是使熱風循環之熱交換管 12·如申請專利範圍第9項所述之陶瓷生成裝置 具備有在對熱分解反應槽内生成碳化物送入前述大量電 之同時,亦送入微量氧成分之氧供給構件。 13·如申請專利範圍第9項至第12項中任一項所述 陶瓷生成裝置,其中前述排氣收集構件具備有冷卻、液化 述氣體之構成。4. The method of researching and producing as described in item i or item 2 of the scope of patent application, wherein the aforementioned raw material organic substance contains at least 3,000 calories. 5. The ceramic production method according to item 1 of the scope of patent application, wherein the aforementioned gas processing step is provided with steps for cooling, liquefying, and collecting the liquefied gas discharged from the reaction tank. 6. According to the patent application method described in item 1 or item 5, the aforementioned gas treatment step is provided with a reduction step of feeding electrons discharged from the reaction tank 22 200537056 into the electron. 7. The gas treatment step described in the scope of the patent application No. 6 is more equipped with '', of which 刖 which is more. · There is a step of returning most of it to the aforementioned reaction tank for heating. "Milk weight 8. As described in the scope of patent application No. 1 red method, in which the ceramic producer described in / item 5 into the ancient leather" "Each of them has the technology of introducing the gas or its liquefaction into 3 active oxygen treated water To carry out the step of oxidative decomposition. 9. A ceramic generating device, which is characterized in that it is provided with a thermal decomposition reaction tank, which is provided with a material input port and ceramics without an outlet; and Carbide delivery in the decomposition reaction tank ^ ^ v 疋 eight electrons; and the exhaust gas collection member that collects the aforementioned exhaust gas generated in the pyrolysis reaction tank. Ο. As described in item 9 of the scope of patent application The ceramic research generating device is provided with a heating member for increasing the temperature in the reaction tank. Π. The ceramic heating generating device described in item 9 of the patent application scope, the heating member is an electric heater or a heat exchange tube that circulates hot air. 12. The ceramic generating device according to item 9 of the scope of the patent application is provided with an oxygen supply member that supplies the aforementioned large amount of electricity to the carbides generated in the thermal decomposition reaction tank and also a trace amount of oxygen components. Patent Scope 9 Constituting gases to item 12 in any one of the ceramic generating means, wherein the exhaust gas collector is provided with a cooling member, said liquefaction. 其 其 其Its its its 14·如申請專利範圍第9項所述之陶瓷生成裝置,其中 具備有對使用前述排氣收集構件所收集之排氣送入電子之 第2電子供給構件。 23 200537056 1 5 ·如申請專利範圍第14項所述之陶瓷生成裝置,其 · 中具備有可將大部分前述有電子送入之排氣,再送回前述熱 分解反應槽中之構成。 16·如申請專利範圍第9項所述之陶瓷生成裝置,其中 具備有將使用前述排氣收集手段所收集到的排氣,送入處理 槽(裝有含活性氧之水)之構件。 17·如申請專利範圍第16項所述之陶瓷生成裝置,其 中具備具備有活性氧製造構件、和將使用該構件所製成活 性氧送入前述處理槽内水中之構件。 φ 18·如申請專利範圍第17項所述之陶瓷生成裝置,其 中前述活性氧製造構件,係臭氧發生裝置或是水之電分解 裝置。 1 9·如中請專利範圍第16項所述之陶堯生成裝置,其中 具備有使前述處理槽中的水成為還原狀態之構件。、 二·如申請專利範圍第19項所述之陶究生成裝置,其 中使前述處理槽中的水成為還原狀態之構件,係具備有電子 (e )發生裝置或是在前述處理槽中投入還原劑之構件。 21· -種陶瓷,其特徵為,採用前述申請專利範圍第丨 · 項所述之陶瓷生成方法所生成。 種木醋S夂,其特徵為,採用前述申請專利圍第 5項所述之陶瓷生成方法所生成。 2414. The ceramic generating device according to item 9 of the patent application scope, further comprising a second electron supply means for feeding electrons to the exhaust gas collected by the exhaust gas collection means. 23 200537056 1 5 · The ceramic generating device described in item 14 of the scope of patent application, which includes a structure in which most of the aforementioned electrons can be sent into the exhaust gas and then returned to the aforementioned thermal decomposition reaction tank. 16. The ceramic generating device according to item 9 of the scope of the patent application, which includes a member for sending the exhaust gas collected by the aforementioned exhaust gas collection means to a processing tank (containing active oxygen-containing water). 17. The ceramic generating device according to item 16 of the scope of application for a patent, which includes a member provided with an active oxygen production member and a member that feeds active oxygen produced using the member into the water in the treatment tank. φ18. The ceramic generating device according to item 17 of the scope of patent application, wherein the aforementioned active oxygen production member is an ozone generating device or an electrolysis device for water. 19. The Tao Yao generating device according to item 16 of the patent scope, which includes a means for making the water in the treatment tank into a reduced state. 2. The ceramic generating device according to item 19 of the scope of the patent application, wherein the component for making the water in the processing tank into a reduced state is provided with an electron (e) generating device or is put into the processing tank for reduction剂 的 组合。 The components of the agent. 21 · -ceramics, which are produced by using the ceramic generation method described in item 丨 · of the aforementioned patent application scope. A kind of wood vinegar S 夂 is characterized in that it is produced by the ceramic production method described in item 5 of the aforementioned patent application. twenty four
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI447093B (en) * 2008-11-17 2014-08-01 N M G Environmental Dev Co Ltd Livestock and poultry processing methods and methods of livestock manure, organic matter treatment methods and methods of using organic matter, as well as building materials and the use of the building materials built from the building

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI447093B (en) * 2008-11-17 2014-08-01 N M G Environmental Dev Co Ltd Livestock and poultry processing methods and methods of livestock manure, organic matter treatment methods and methods of using organic matter, as well as building materials and the use of the building materials built from the building

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