TWI417376B - Method of converting bio-waste into solid fuel by micro-baking reaction - Google Patents

Method of converting bio-waste into solid fuel by micro-baking reaction Download PDF

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TWI417376B
TWI417376B TW99141839A TW99141839A TWI417376B TW I417376 B TWI417376 B TW I417376B TW 99141839 A TW99141839 A TW 99141839A TW 99141839 A TW99141839 A TW 99141839A TW I417376 B TWI417376 B TW I417376B
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microwave
waste
solid fuel
reaction
biomass
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TW201224134A (en
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Shang Lien Lo
Pei Te Chueh
Mei Ju Wang
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Univ Nat Taiwan
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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
    • 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
    • Y02E50/10Biofuels, e.g. bio-diesel
    • 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

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利用微波誘發焙燒反應將生質廢棄物轉化為固態燃料之方法Method for converting biomass waste into solid fuel by microwave induced roasting reaction

本發明係關於一種將生質廢棄物轉化為固態燃料之方法,詳言之,係有關於一種將生質廢棄物焙燒形成固態燃料之方法。The present invention relates to a method of converting biomass waste into a solid fuel, and more particularly to a method of calcining biomass waste to form a solid fuel.

生質物(biomass)為泛指在地球上的生物或其所產生的有機物質,透過物理、化學或生物等方法可將該生質物轉化成固相、液態及氣態之生質能源。Biomass refers to the biomass on the earth or the organic matter produced by it. It can be converted into solid, liquid and gaseous biomass energy through physical, chemical or biological methods.

目前將生質物轉化成生質能源的熱處理技術主要有燃燒技術(combustion)、氣化技術(gasification)及熱裂解技術(pyrolysis)。例如,第I281496號中華民國專利揭示一種將生質有機資源材料轉化成工業原料之方法,該方法之熱能源係飽和蒸汽及/或過熱蒸汽、電熱能或其他熱媒流體、介質熱能其中之一者或混合應用;第2005/0022553號號美國專利揭示一種利用生質燃料系統將生質物轉化成能量及有用的產物之方法,該方法係利用供應氧氣以使生質物於燃燒室燃燒之燃燒技術;第4497637號美國專利揭示一種將生質物轉化成合成氣之方法,該方法係使用裂解技術裂解生質物以形成包括一氧化碳及氫之合成氣。At present, heat treatment technologies for converting biomass into biomass energy mainly include combustion, gasification and pyrolysis. For example, the Republic of China Patent No. I281496 discloses a method for converting raw organic resource materials into industrial raw materials, the thermal energy of which is one of saturated steam and/or superheated steam, electrothermal energy or other heat medium fluid, and medium heat energy. Or a hybrid application; US Patent No. 2005/0022553 discloses a method for converting biomass into energy and useful products using a biomass fuel system, which utilizes combustion technology that supplies oxygen to burn biomass in a combustion chamber. U.S. Patent 4,497,637 discloses a method of converting biomass into syngas by cracking the biomass using a cracking technique to form a syngas comprising carbon monoxide and hydrogen.

生質物的焙燒反應需要在無氧的環境下進行,在焙燒的過程中會移除生質物中的水分、低分子量有機揮發物及打斷長鏈多醣,生產出能量密度高且研磨性好之疏水性固態產物,又稱為焙燒炭或生質炭。以往,生質物的焙燒反應都是利用傳統的加熱方式進行,熱能主要藉由傳導方式由外傳遞至生質物內部,故升溫速度慢,所需的反應時間長,且會耗費較多能量。The calcination reaction of the biomass needs to be carried out in an oxygen-free environment. During the calcination process, the moisture in the biomass, the low molecular weight organic volatiles and the long-chain polysaccharide are removed, and the energy density is high and the abrasiveness is good. Hydrophobic solid product, also known as calcined charcoal or green charcoal. In the past, the calcination reaction of the biomass was carried out by a conventional heating method. The heat was mainly transferred from the outside to the inside of the biomass by conduction, so the heating rate was slow, the required reaction time was long, and more energy was consumed.

因此,仍需要一種可大幅縮短反應時間,獲得具有高熱值焙燒炭之方法。Therefore, there is still a need for a method which can greatly shorten the reaction time and obtain a calcined carbon having a high calorific value.

為達成上揭及其他目的,本發明係提供一種利用微波誘發焙燒反應,將生質廢棄物轉化為固態燃料之方法,包括將生質廢棄物原料置於微波反應器中;以及在無氧狀況下,利用微波加熱進行焙燒反應,使生質廢棄物轉化為固態燃料。本發明之方法是利用微波加熱的方式進行焙燒處理,不但可以有效提高固態燃料的熱值密度、降低固相產物之氧/碳比值(O/C ratio),亦兼具有縮短焙燒處理時間,減少能量消耗之優點。To achieve the above and other objects, the present invention provides a method for converting a biomass waste into a solid fuel by using a microwave-induced calcination reaction, comprising placing a raw material of the raw waste in a microwave reactor; and in an anaerobic condition. Next, the calcination reaction is carried out by microwave heating to convert the raw waste into a solid fuel. The method of the invention is to perform the calcination treatment by means of microwave heating, which can not only effectively increase the calorific value density of the solid fuel, reduce the oxygen/carbon ratio (O/C ratio) of the solid phase product, but also shorten the roasting treatment time. Reduce the benefits of energy consumption.

以下係藉由特定的具體實施例說明本發明之實施方式,熟習此技藝之人士可由本說明書所揭示之內容輕易地瞭解本發明之優點及功效。本發明亦可藉由其它不同之實施方式加以施行或應用,本說明書中的各項細節亦可基於不同觀點與應用,在不悖離本發明所揭示之精神下賦予不同之修飾與變更。The embodiments of the present invention are described by way of specific examples, and those skilled in the art can readily understand the advantages and functions of the present invention from the disclosure. The present invention may be embodied or applied by other different embodiments, and the various details of the present invention may be variously modified and changed without departing from the spirit and scope of the invention.

本發明方法係利用微波加熱的方式進行生質廢棄物之焙燒處理,將該生質廢棄物轉化為具有高熱值密度之固態燃料。本發明方法係使用農林廢棄物作為進行微波誘發焙燒處理之生質廢棄物,該農林廢棄物之實例包括稻穀、甘蔗渣等。使用稻穀或甘蔗渣作為生質廢棄為進行微波誘發焙燒處理前,可先利用高速粉碎機進行破碎,並於105℃烘箱進行乾燥,再以篩網進行過篩,形成經乾燥與破碎之生質廢棄物原料。The method of the present invention performs the calcination treatment of the biomass waste by means of microwave heating, and converts the biomass waste into a solid fuel having a high calorific value density. The method of the present invention uses agricultural and forestry waste as a biomass waste for performing microwave-induced calcination treatment, and examples of the agricultural forestry waste include rice, bagasse, and the like. Before using rice or sugar cane bagasse as raw biomass for microwave-induced calcination, it can be crushed by high-speed pulverizer, dried in an oven at 105 °C, and sieved through a sieve to form dried and broken biomass. Waste materials.

一般而言,使用粒徑過大之生質廢棄物原料行微波誘發焙燒處理,容易因殘留過多空氣,導致反應物燃燒反應,造成焙燒不均勻。生質廢棄物原料之粒徑越小,則具有較大的容積密度及顆粒間接觸面積,有助於提升生質廢棄物原料內部之熱傳導效果,大幅增加整體反應溫度;另一方面,若生質廢棄物原料粒徑太小,反應效果可能超過預期,由於反應溫度提高,導致固相產物中具高熱值的固定碳成份開始發生裂解,所形成的固態燃料的熱值亦較低。因此,本發明方法所使用之生質廢棄物原料並不需要耗費過多能量進行研磨,原料粒徑通常係介於50網目(Mesh)和100綱目(Mesh)之間為最佳。In general, the microwave-induced calcination treatment of the raw material waste material having an excessively large particle size is likely to cause excessive combustion of the air, resulting in a combustion reaction of the reactant, resulting in uneven baking. The smaller the particle size of the raw waste raw material, the larger the bulk density and the contact area between the particles, which helps to improve the heat conduction effect inside the raw material of the raw waste, and greatly increases the overall reaction temperature; on the other hand, if the raw material is produced The particle size of the waste material is too small, and the reaction effect may exceed expectations. As the reaction temperature increases, the fixed carbon component with high calorific value in the solid phase product begins to crack, and the solid fuel formed has a lower calorific value. Therefore, the raw waste raw material used in the method of the present invention does not require excessive energy for grinding, and the raw material particle size is usually preferably between 50 mesh and 100 mesh.

利用焙燒處理使生質廢棄物轉化為固態燃料,必需在無氧狀態下進行,以避免發生燃燒反應。於一具體實例中,該生質廢棄物原料置於微波反應器後,先通入非氧氣,例如氮氣、氦氣、氬氣或二氧化碳,置換微波反應器內的空氣體;或先抽出反應器內之空氣,再通入非氧氣體,待反應腔體中皆為載流氣體充滿後,再啟動微波進行焙燒反應,使該生質廢棄物原料在無氧狀況下,進行微波誘發焙燒處理,形成固態燃料。The conversion of biomass waste into a solid fuel by roasting treatment must be carried out in an anaerobic state to avoid a combustion reaction. In a specific example, after the raw material of the raw waste is placed in the microwave reactor, the non-oxygen gas, such as nitrogen, helium, argon or carbon dioxide, is first introduced to replace the air body in the microwave reactor; or the reactor is first withdrawn. The air inside is re-introduced into the non-oxygen gas. After the carrier gas is filled in the reaction chamber, the microwave is started to be calcined, so that the raw material of the raw waste is subjected to microwave-induced roasting under anaerobic conditions. Forming a solid fuel.

本發明之方法中,微波加熱之功率過低,反應溫度不夠,生質廢棄物無法完全進行焙燒反應。另一方面,高微波功率雖然可以增加升溫速率,提高反應溫度,提升固相產物之熱值,但整體反應較不穩定,容易發生反應不完全的狀況。因此,本發明方法之微波加熱通常係於150至400W之微波功率條件下進行,較佳係於250至350W之微波功率條件下進行,且依不同大小之微波功率調整不同微波照射時間使反應溫度介於200至400℃之溫度條件下進行焙燒反應。In the method of the present invention, the power of microwave heating is too low, the reaction temperature is insufficient, and the raw waste cannot be completely calcined. On the other hand, although the high microwave power can increase the heating rate, increase the reaction temperature, and increase the calorific value of the solid phase product, the overall reaction is less stable and the reaction is less likely to occur. Therefore, the microwave heating of the method of the present invention is generally carried out under microwave power conditions of 150 to 400 W, preferably under microwave power conditions of 250 to 350 W, and different microwave irradiation times are adjusted according to different microwave powers to make the reaction temperature. The calcination reaction is carried out at a temperature of from 200 to 400 °C.

微波照射的時間會隨著功率增加而縮短。根據分析結果顯示,固相產物中的氧元素含量會隨反應時間增加而逐漸下降,氫元素含量則無明顯變化。另一方面,若微波照射時間過長,固相產物中的碳元素則會被反應分解,反而不利於增加固相產物之熱值密度。因此,本發明方法中,微波照射之時間係介於5至30分鐘,升溫速率則以不超過65℃/分鐘較佳。The time of microwave irradiation is shortened as power is increased. According to the analysis results, the content of oxygen in the solid phase product gradually decreases with the increase of reaction time, and the content of hydrogen does not change significantly. On the other hand, if the microwave irradiation time is too long, the carbon element in the solid phase product will be decomposed by the reaction, which is not advantageous for increasing the heat value density of the solid phase product. Therefore, in the method of the present invention, the microwave irradiation time is from 5 to 30 minutes, and the temperature increase rate is preferably not more than 65 ° C / minute.

本發明之方法係利用微波加熱進行生質廢棄物之焙燒處理,相較於傳統加熱方法之生質廢棄物焙燒處理,本發明方法所形成之固相產物中,O/C比例與H/C比例下降幅度較大,反應時間更短;其中,在本發明中,稻殼(O元素:43.94%,O/C ratio:0.99)之焙燒炭,其O元素可降至30.53%,O/C比例可由0.99降低至0.50,H/C比例可由0.15降低至0.04;甘蔗渣(O元素:40.45%,O/C ratio:0.82)焙燒炭,O元素降至27.95%,O/C比例可由0.82降低至0.46,H/C比例可由0.14降低至0.09,更適合作為優質固態燃料。The method of the invention utilizes microwave heating to carry out the calcination treatment of the raw waste, and the O/C ratio and the H/C ratio of the solid phase product formed by the method of the invention are compared with the calcination treatment of the raw waste by the conventional heating method. The ratio of the decrease is larger and the reaction time is shorter. Among them, in the present invention, the calcined carbon of the rice husk (O element: 43.94%, O/C ratio: 0.99) can be reduced to 30.53%, O/C. The ratio can be reduced from 0.99 to 0.50, the H/C ratio can be reduced from 0.15 to 0.04; the bagasse (O element: 40.45%, O/C ratio: 0.82) is used to roast the carbon, the O element is reduced to 27.95%, and the O/C ratio can be lowered by 0.82. To 0.46, the H/C ratio can be reduced from 0.14 to 0.09, which is more suitable as a high quality solid fuel.

以下係藉由特定之具體實施例進一步說明本發明之特點與功效,但非用於限制本發明之範疇。The features and effects of the present invention are further illustrated by the following specific examples, but are not intended to limit the scope of the invention.

實施例Example 實施例1Example 1

使用乾燥稻穀作為生質廢棄物,利用高速粉碎機加以破碎後,以50/100網目(mesh)之篩網進行過篩,獲得生質廢棄物原料,並將其置入微波反應爐內。接著,以每分鐘50毫升之流量連續通入氮氣,待爐內原有之空氣被通入之氮氣取代後,將微波功率調整為250W,分別照射8、10、12、20、30分鐘,進行微波誘發焙燒反應。反應完畢後,分析微波反應爐內之固相產物的熱值密度,結果如第1圖所示。固相產物之C、H、O元素含量,如第2圖所示。Dry rice was used as raw waste, which was crushed by a high-speed pulverizer, sieved with a 50/100 mesh screen to obtain raw waste materials, and placed in a microwave reactor. Next, nitrogen gas is continuously supplied at a flow rate of 50 ml per minute. After the original air in the furnace is replaced by nitrogen gas, the microwave power is adjusted to 250 W, and irradiation is performed for 8, 10, 12, 20, and 30 minutes, respectively. The microwave induced roasting reaction. After the completion of the reaction, the heat value density of the solid phase product in the microwave reactor was analyzed, and the results are shown in Fig. 1. The content of C, H, and O elements of the solid phase product is shown in Figure 2.

分析結果顯示,當微波照射時間增加時,固相產物之熱值密度也隨之升高,微波照射20分鐘後,熱值密度提高26%,微波照射30分鐘後,熱值密度開始下降。固相產物的C元素含量在反應20分鐘時達到最高,超過20分鐘後開始下降,顯示反應時間過長,會使固相產物中的C元素被反應分解掉,此結果亦可說明第1圖之熱值密度變化。The analysis results show that when the microwave irradiation time increases, the heat value density of the solid phase product also increases. After microwave irradiation for 20 minutes, the heat value density increases by 26%. After microwave irradiation for 30 minutes, the heat value density begins to decrease. The content of C element in the solid phase product reached the highest at 20 minutes after the reaction, and began to decrease after more than 20 minutes, indicating that the reaction time was too long, and the C element in the solid phase product was decomposed by the reaction. The result can also be illustrated. The heat value density changes.

利用元素分析儀分析固相產物的元素含量變化。O元素含量隨反應時間增加逐漸下降,H元素含量則無太大變化。根據第2圖結果顯示,在微波功率250W之條件下,照射20分鐘後,可去除O元素,去除率為31%,且計算O/C比例可由原先0.99降至0.50,H/C比例可由降至0.15降至0.04。The elemental analyzer was used to analyze the change in the elemental content of the solid phase product. The content of O element decreased gradually with the increase of reaction time, and the content of H element did not change much. According to the results of Figure 2, under the condition of microwave power of 250W, after 20 minutes of irradiation, the O element can be removed, the removal rate is 31%, and the calculated O/C ratio can be reduced from 0.99 to 0.50, and the H/C ratio can be lowered. It drops to 0.04 to 0.15.

實施例2Example 2

使用甘蔗渣作為生質廢棄物,利用高速粉碎機加以破碎後,以50/100網目(mesh)之篩網進行過篩,獲得生質廢棄物原料,並將其置入微波反應爐內。接著,以每分鐘50毫升之流量連續通入氮氣,待爐內原有之空氣被通入之氮氣取代後,將微波功率調整為250W,分別照射4、5、6、15、20、30分鐘,進行微波誘發焙燒反應。反應完畢後,分析微波反應爐內之固相產物的熱值密度,結果如第3圖所示。The bagasse was used as a raw waste, which was crushed by a high-speed pulverizer, sieved with a 50/100 mesh screen to obtain a raw waste material, and placed in a microwave reactor. Next, nitrogen gas was continuously supplied at a flow rate of 50 ml per minute. After the original air in the furnace was replaced by nitrogen gas, the microwave power was adjusted to 250 W for 4, 5, 6, 15, 20, 30 minutes respectively. , microwave induced roasting reaction. After the completion of the reaction, the caloric value density of the solid phase product in the microwave reactor was analyzed, and the results are shown in Fig. 3.

分析結果顯示,當微波照射時間增加時,固相產物之熱值密度也隨之升高,微波照射15分鐘後,熱值密度提高57%,微波照射20分鐘後,熱值密度開始下降。The analysis results show that when the microwave irradiation time increases, the heat value density of the solid phase product also increases. After 15 minutes of microwave irradiation, the heat value density increases by 57%. After microwave irradiation for 20 minutes, the heat value density begins to decrease.

利用元素分析儀分析固相產物的元素含量變化。O元素含量隨反應時間增加逐漸下降,H元素含量則無太大變化。根據第4圖結果顯示,在微波功率250W之條件下,照射15分鐘後,可去除O元素,去除率為70%,且計算O/C比例可由原先0.90降至0.16,H/C比例由降至0.13降至0.04。The elemental analyzer was used to analyze the change in the elemental content of the solid phase product. The content of O element decreased gradually with the increase of reaction time, and the content of H element did not change much. According to the results of Fig. 4, under the condition of microwave power of 250W, the O element can be removed after irradiation for 15 minutes, the removal rate is 70%, and the calculated O/C ratio can be reduced from 0.90 to 0.16, and the H/C ratio is lowered. It drops to 0.04 to 0.13.

實施例3Example 3

使用乾燥稻穀作為生質廢棄物,利用高速粉碎機加以破碎後,以50/100網目(mesh)之篩網進行過篩,獲得生質廢棄物原料,並將其置入微波反應爐內。接著,以每分鐘50毫升之流量連續通入氮氣,待爐內原有之空氣被通入之氮氣取代後,將微波功率調整為350W,分別照射4、6、8、10、30分鐘,進行微波誘發焙燒反應。反應完畢後,分析微波反應爐內之固相產物的熱值密度,結果如第5圖所示。Dry rice was used as raw waste, which was crushed by a high-speed pulverizer, sieved with a 50/100 mesh screen to obtain raw waste materials, and placed in a microwave reactor. Next, nitrogen gas is continuously supplied at a flow rate of 50 ml per minute. After the original air in the furnace is replaced by nitrogen gas, the microwave power is adjusted to 350 W, and irradiation is performed for 4, 6, 8, 10, and 30 minutes, respectively. The microwave induced roasting reaction. After the completion of the reaction, the heat value density of the solid phase product in the microwave reactor was analyzed, and the results are shown in Fig. 5.

分析結果顯示,當微波照射時間增加時,固相產物之熱值密度也隨之升高,微波照射10分鐘後,熱值密度提高26%。亦顯示出利用較高的微波功率更可縮短微波照射時間,而達到相同之焙燒效果。The analysis results show that when the microwave irradiation time increases, the heat value density of the solid phase product also increases, and the heat value density increases by 26% after microwave irradiation for 10 minutes. It has also been shown that the use of higher microwave power can shorten the microwave irradiation time and achieve the same baking effect.

第1圖係本發明方法實施例1之固相產物熱值密度變化圖;Figure 1 is a graph showing the change in the heat value density of the solid phase product of Example 1 of the method of the present invention;

第2圖係本發明方法實施例1之固相產物元素含量變化圖;Figure 2 is a graph showing changes in elemental content of solid phase products in Example 1 of the method of the present invention;

第3圖係本發明方法實施例2之固相產物熱值密度變化圖;Figure 3 is a graph showing the change in the heat value density of the solid phase product of Example 2 of the method of the present invention;

第4圖示本發明方法實施例2之固相產物元素含量變化圖:以及Figure 4 is a graph showing the change in the content of the solid phase product element in Example 2 of the method of the present invention:

第5圖係本發明方法實施例3之固相產物熱值密度變化圖。Figure 5 is a graph showing the change in the heat value density of the solid phase product of Example 3 of the method of the present invention.

Claims (10)

一種利用微波誘發焙燒反應將生質廢棄物轉化為固態燃料之方法,包括下列步驟:將生質廢棄物原料置於微波反應器中;以及利用微波加熱的方式進行熱處理,形成固態燃料。A method for converting a biomass waste into a solid fuel by using a microwave-induced calcination reaction, comprising the steps of: placing a raw material of the raw waste in a microwave reactor; and performing heat treatment by means of microwave heating to form a solid fuel. 如申請專利範圍第1項所述之方法,係以通入非氧氣體之方式使該生質廢棄物原料在無氧狀況下進行熱處理。The method of claim 1, wherein the raw waste material is heat-treated under an anaerobic condition by introducing a non-oxygen gas. 如申請專利範圍第1項所述之方法,其中,該生質廢棄物為稻殼或甘蔗渣。The method of claim 1, wherein the raw waste is rice husk or bagasse. 如申請專利範圍第3項所述之方法,其中,該稻殼或甘蔗渣進行微波加熱前,係經破碎、乾燥、及篩選,形成粒徑介於50/100網目之生質廢棄物原料。The method according to claim 3, wherein the rice husk or the bagasse is crushed, dried, and screened before being heated by microwaves to form a raw material of biomass waste having a particle size of 50/100 mesh. 如申請專利範圍第2項所述之方法,其中,該非氧氣體為氮氣、氦氣、氬氣或二氧化碳。The method of claim 2, wherein the non-oxygen gas is nitrogen, helium, argon or carbon dioxide. 如申請專利範圍第1項所述之方法,其中,該微波加熱係於150至400 W之微波功率條件下進行。The method of claim 1, wherein the microwave heating is performed under microwave power of 150 to 400 W. 如申請專利範圍第1項所述之方法,其中,該微波加熱係於200至400℃之溫度條件下進行。The method of claim 1, wherein the microwave heating is performed at a temperature of from 200 to 400 °C. 如申請專利範圍第1項所述之方法,其中,該微波照射之時間係介於5至30分鐘。The method of claim 1, wherein the microwave irradiation time is between 5 and 30 minutes. 如申請專利範圍第1項所述之方法,其中,該微波加熱之升溫速率係小於65℃/分鐘。The method of claim 1, wherein the heating rate of the microwave heating is less than 65 ° C / min. 如申請專利範圍第1項所述之方法,其中,該固態燃料的O/C比率係小於0.50,且H/C比例係小於0.04。The method of claim 1, wherein the solid fuel has an O/C ratio of less than 0.50 and an H/C ratio of less than 0.04.
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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US139289A (en) * 1873-05-27 Improvement in dust-conveying attachments for thrashing-machines
JPH099625A (en) * 1995-06-15 1997-01-10 Matsushita Electric Works Ltd Power supply apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US139289A (en) * 1873-05-27 Improvement in dust-conveying attachments for thrashing-machines
JPH099625A (en) * 1995-06-15 1997-01-10 Matsushita Electric Works Ltd Power supply apparatus

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