TWI772846B - Biochar production method - Google Patents
Biochar production method Download PDFInfo
- Publication number
- TWI772846B TWI772846B TW109124789A TW109124789A TWI772846B TW I772846 B TWI772846 B TW I772846B TW 109124789 A TW109124789 A TW 109124789A TW 109124789 A TW109124789 A TW 109124789A TW I772846 B TWI772846 B TW I772846B
- Authority
- TW
- Taiwan
- Prior art keywords
- biochar
- present
- calcination temperature
- heating chamber
- bamboo shoot
- Prior art date
Links
Images
Landscapes
- Carbon And Carbon Compounds (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
Abstract
一種生物炭(Biochar)製造方法,包括:將一植物原料置入一加熱爐的一加熱腔室中。該植物原料包括一茭白筍殼。注入一氮氣至該加熱腔室中。該加熱爐以一鍛燒溫度對該加熱腔室中的該植物原料進行加熱一裂解時間。經加熱後的該植物原料形成一生物炭。該鍛燒溫度在490°C至710°C之間,該裂解時間在1.8小時至2.2小時之間。A biochar (Biochar) manufacturing method comprises: placing a plant raw material into a heating chamber of a heating furnace. The plant material includes a bamboo shoot shell of water bamboo. A nitrogen gas was injected into the heating chamber. The heating furnace heats the plant material in the heating chamber at a calcination temperature for a cracking time. The heated plant material forms a biochar. The calcination temperature is between 490°C and 710°C, and the cracking time is between 1.8 hours and 2.2 hours.
Description
本發明是有關於一種生物炭製造方法,且特別關於一種利用茭白筍殼製造生物炭的方法。The present invention relates to a method for producing biochar, and particularly relates to a method for producing biochar using bamboo shoot shells of water bamboo.
近年來,生物炭(Biochar)作為一種新型環境功能材料已引起廣泛關注。生物炭在土壤改良、溫室氣體減量及受污染環境復育等方面,均展現出應用潛力。In recent years, Biochar has attracted extensive attention as a new type of environmental functional material. Biochar has shown potential applications in soil improvement, greenhouse gas reduction, and restoration of polluted environments.
然而,習知的生物炭往往會有炭化不均勻的問題,習知生物炭的表面積也很難提高。致使生物炭的吸附能力不佳。因此,如何提高生物炭的效能,實為本領域相關人員所關注的焦點。However, the conventional biochar often has the problem of uneven carbonization, and it is difficult to increase the surface area of the conventional biochar. As a result, the adsorption capacity of biochar is poor. Therefore, how to improve the efficiency of biochar is the focus of attention of those in the field.
“先前技術”段落只是用來幫助了解本發明內容,因此在“先前技術”段落所揭露的內容可能包含一些沒有構成所屬技術領域中具有通常知識者所知道的習知技術。在“先前技術”段落所揭露的內容,不代表該內容或者本發明一個或多個實施例所要解決的問題,在本發明申請前已被所屬技術領域中具有通常知識者所知曉或認知。The "prior art" paragraph is only used to help understand the present disclosure, so the content disclosed in the "prior art" paragraph may contain some that do not constitute the prior art known to those with ordinary skill in the art. The content disclosed in the "prior art" paragraph does not represent the content or the problem to be solved by one or more embodiments of the present invention, and has been known or recognized by those with ordinary knowledge in the technical field before the application of the present invention.
本發明提供一種生物炭製造方法,可以大幅提高生物炭的效能。The present invention provides a method for producing biochar, which can greatly improve the efficiency of the biochar.
本發明的其他目的和優點可以從本發明所揭露的技術特徵中得到進一步的了解。Other objects and advantages of the present invention can be further understood from the technical features disclosed in the present invention.
本發明的生物炭(Biochar)製造方法包括:將一植物原料置入一加熱爐的一加熱腔室中。該植物原料包括一茭白筍殼。注入一氮氣至該加熱腔室中。該加熱爐以一鍛燒溫度對該加熱腔室中的該植物原料進行加熱一裂解時間。經加熱後的該植物原料形成一生物炭。該鍛燒溫度在490°C至710°C之間,該裂解時間在1.8小時至2.2小時之間。The biochar manufacturing method of the present invention comprises: placing a plant raw material into a heating chamber of a heating furnace. The plant material includes a bamboo shoot shell of water bamboo. A nitrogen gas was injected into the heating chamber. The heating furnace heats the plant material in the heating chamber at a calcination temperature for a cracking time. The heated plant material forms a biochar. The calcination temperature is between 490°C and 710°C, and the cracking time is between 1.8 hours and 2.2 hours.
在本發明的一實施例中,上述之該加熱腔室內的該氮氣的體積百分比大於99%。In an embodiment of the present invention, the volume percentage of the nitrogen gas in the heating chamber is greater than 99%.
在本發明的一實施例中,上述之該加熱腔室內的一氧氣的體積百分比小於1%。In an embodiment of the present invention, the volume percentage of an oxygen gas in the heating chamber is less than 1%.
在本發明的一實施例中,上述之該鍛燒溫度在490°C至510°C之間,或該鍛燒溫度在590°C至610°C之間,或該鍛燒溫度在690°C至710°C之間。In an embodiment of the present invention, the above-mentioned calcination temperature is between 490°C to 510°C, or the calcination temperature is between 590°C to 610°C, or the calcination temperature is 690°C Between C and 710°C.
在本發明的一實施例中,上述之該茭白筍殼在置入該加熱爐之前,該茭白筍殼先進行一清洗製程、一風乾製程及/或一切碎製程。In an embodiment of the present invention, before the above-mentioned bamboo shoot shells are placed in the heating furnace, the bamboo shoot shells are subjected to a cleaning process, an air drying process and/or a shredding process.
在本發明的一實施例中,上述之該茭白筍殼在進行該清洗製程、該風乾製程及/或該切碎製程之後,該茭白筍殼還進行一烘乾脫水製程。In an embodiment of the present invention, after the above-mentioned water bamboo shoot shells are subjected to the cleaning process, the air-drying process and/or the chopping process, the water bamboo shoot shells are also subjected to a drying and dehydration process.
在本發明的一實施例中,上述之該茭白筍殼在經該烘乾脫水製程後,該茭白筍殼以一篩網過篩,經該篩網篩選後的該茭白筍殼置入該加熱爐中,其中該篩網的一目數(mesh)是8、9、10或12。In an embodiment of the present invention, after the drying and dehydration process of the bamboo shoots, the bamboo shoots are sieved with a screen, and the bamboo shoots screened by the screen are placed in the heating furnace, wherein a mesh of the screen is 8, 9, 10 or 12.
在本發明的一實施例中,上述之該生物炭經一活化(Activation)製程後形成一活性炭。In an embodiment of the present invention, the above-mentioned biochar is subjected to an activation process to form an activated carbon.
基於上述,本發明提供的生物炭製造方法透過在氮氣環境下加熱包括茭白筍殼的植物原料,能有效解決炭化不均勻的問題,可以製成具有高吸附表面積的生物炭,大幅提高生物炭的效能。Based on the above, the biochar production method provided by the present invention can effectively solve the problem of uneven carbonization by heating the plant raw materials including the bamboo shoot shells in a nitrogen environment, and can produce biochar with high adsorption surface area, greatly improving the biochar efficacy.
為讓本發明的上述特徵和優點能更明顯易懂,下文特舉實施例,並配合所附圖式作詳細說明如下。In order to make the above-mentioned features and advantages of the present invention more obvious and easy to understand, the following embodiments are given and described in detail with the accompanying drawings as follows.
有關本發明之前述及其他技術內容、特點與功效,在以下配合參考圖式之一較佳實施例的詳細說明中,將可清楚的呈現。以下實施例中所提到的方向用語,例如:上、下、左、右、前或後等,僅是參考附加圖式的方向。因此,使用的方向用語是用來說明並非用來限制本發明。The foregoing and other technical contents, features and effects of the present invention will be clearly presented in the following detailed description of a preferred embodiment with reference to the drawings. The directional terms mentioned in the following embodiments, such as: up, down, left, right, front or rear, etc., are only for referring to the directions of the attached drawings. Accordingly, the directional terms used are illustrative and not limiting of the present invention.
請參照圖1,圖1是本發明一實施例的生物炭(Biochar)的製造裝置1的示意圖。該製造裝置1包括一加熱爐13。該加熱爐13包括一加熱腔室131。Please refer to FIG. 1 , which is a schematic diagram of a biochar (Biochar)
請同時參照圖2,圖2是本發明一實施例的生物炭製造方法100的流程圖。本實施例的生物炭製造方法100包括下列步驟:在步驟S101中,將一植物原料11置入該加熱爐13的該加熱腔室131中。在本實施例中,該植物原料11包括一茭白筍殼WS。接著,步驟S103,注入一氮氣151至該加熱腔室131中。在步驟S105中,該加熱爐13以一鍛燒溫度T對該加熱腔室131中的該植物原料11進行加熱一裂解時間(未圖示)。Please also refer to FIG. 2 , which is a flowchart of a
在本實施例中,該鍛燒溫度T在490°C至710°C之間。該裂解時間在1.8小時至2.2小時之間。經加熱後的該植物原料11形成一生物炭C。In this embodiment, the calcination temperature T is between 490°C and 710°C. The lysis time was between 1.8 hours and 2.2 hours. The heated
本實施例包括該茭白筍殼WS的該植物原料11,在該氮氣151的環境下,經490°C至710°C之間的該鍛燒溫度T加熱1.8小時至2.2小時之間的該裂解時間,能解決炭化不均勻的問題,可以製成具有高吸附表面積(未圖示)的該生物炭C,大幅提高該生物炭C的效能。本實施例生物炭製造方法100製造的該生物炭C的炭孔隙結構發達、吸附能力強、環境穩定性高。本實施例的該生物炭C可以作為一種新型的環境功能材料,在例如土壤改良、溫室氣體減量及受污染環境復育等方面均有極佳的應用。The present embodiment includes the plant
此外,生產茭白筍產生的農業剩餘資材(即本實施例的該茭白筍殼WS)的再利用一直都是受矚目的議題。茭白筍是重要的經濟作物,但廢棄的該茭白筍殼WS對於景觀、衛生、環境品質及居民健康影響相甚鉅。透過本實施例的生物炭製造方法100,能有效將該茭白筍殼WS轉化成有用且更高價的該生物炭C。該生物炭C例如可以應用於水質淨化與土壤改良,進而達成高循環經濟效益。本實施例的生物炭製造方法不但可解決茭白筍農業剩餘資材造成的問題,更可以製成具有高經濟效益的該生物炭C。In addition, the reuse of agricultural surplus materials produced by the production of water bamboo shoots (that is, the water bamboo shoot shells WS in this embodiment) has always been a topic of attention. Water bamboo shoots are important economic crops, but the discarded water bamboo shoot shells WS have a great impact on landscape, sanitation, environmental quality and residents' health. Through the
如圖1所示,該加熱爐13例如可以包括一加熱器133,該加熱器133用於對該加熱腔室131進行加熱。該加熱爐13例如可以包括一進氣口135,該進氣口135用於向該加熱腔室131注入該氮氣151。該製造裝置1例如可以包括一氮氣源15,該氮氣源15用於提供該氮氣151。圖1所示該加熱器133、該進氣口135及該氮氣源15的結構與形式僅為一舉例說明,並非用以限制本發明。
在本發明一實施例中,該加熱腔室131內的該氮氣151的體積百分比大於99%。包括該茭白筍殼WS的該植物原料11在體積百分比大於99%的該氮氣151環境下加熱,可以解決炭化不均勻的問題,以製成具有高吸附表面積的該生物炭C。在本發明一實施例中,該加熱腔室131內的該氮氣151的體積百分比大於99.95%。As shown in FIG. 1 , the
在本發明一實施例中,該加熱腔室131內的一氧氣(未圖示)的體積百分比小於1%。包括該茭白筍殼WS的該植物原料11在氧氣的體積百分比小於1%的該氮氣151環境下加熱,可以解決炭化不均勻的問題,以製成具有高吸附表面積的該生物炭C。在本發明一實施例中,該加熱腔室131內的氧氣的體積百分比小於0.05%。In an embodiment of the present invention, the volume percentage of an oxygen gas (not shown) in the
在本發明一實施例中,該鍛燒溫度T在490°C至510°C之間。在本發明一實施例中,該鍛燒溫度T在590°C至610°C之間。在本發明一實施例中,該鍛燒溫度T在690°C至710°C之間。在本發明一實施例中,該裂解時間是2小時左右。In an embodiment of the present invention, the calcination temperature T is between 490°C and 510°C. In an embodiment of the present invention, the calcination temperature T is between 590°C and 610°C. In an embodiment of the present invention, the calcination temperature T is between 690°C and 710°C. In an embodiment of the present invention, the cracking time is about 2 hours.
經實驗分析,以比表面積與孔隙度分析儀(Specific Surface Area and Porosimetry Analyzer)量測該生物炭製造方法100製成的該生物炭C的BET比表面積。包括該茭白筍殼WS的該植物原料11分別以500°C、600°C及700°C的該鍛燒溫度T,加熱2小時的裂解時間所生成的生物炭,經實驗量測的結果如表1所示。
由表1可知,本發明以包括該茭白筍殼WS的該植物原料11製造的生物炭皆具有很高的BET比表面積,可以對有機物有很好的去除效果,並例如可以用於水質淨化等。As can be seen from Table 1, the biochar produced by the
請同時參照圖3,圖3是本發明一實施例的生物炭製造方法的前置作業200的流程圖。本實施例的生物炭製造方法在圖2所示的步驟S101之前,還可以進行該前置作業200。在步驟S101,在該茭白筍殼WS置入該加熱爐13之前,該茭白筍殼WS可以先進行一清洗製程S11、一風乾製程S13及/或一切碎製程S15。該清洗製程S11可以將該茭白筍殼WS上的各種髒汙除去。該風乾製程S13可以除去該茭白筍殼WS上大部分的水分。該切碎製程S15可以將該茭白筍殼WS切成碎片/微粒,以利後續的生物炭製造。該切碎製程S15可以任何可能的切割機器來實現。Please refer to FIG. 3 at the same time. FIG. 3 is a flow chart of the pre-operation 200 of the biochar manufacturing method according to an embodiment of the present invention. Before step S101 shown in FIG. 2 , in the biochar manufacturing method of the present embodiment, the pre-operation 200 may also be performed. In step S101 , before the bamboo shoots WS are placed in the
此外,在該茭白筍殼WS在進行該清洗製程S11、該風乾製程S13及/或該切碎製程S15之後,該茭白筍殼WS例如還可以進行一烘乾脫水製程S17,以進一步除去該茭白筍殼WS的水分,以利後續的生物炭製造。該烘乾脫水製程S17可以一獨立於該加熱爐13外的烘箱或烤箱來實現,或該烘乾脫水製程S17可以直接以該加熱爐13來實現。在本發明一實施例中,該烘乾脫水製程S17以100°C至110°C之間的溫度進行烘乾脫水。在本發明一實施例中,該烘乾脫水製程S17以105°C的溫度進行烘乾脫水。In addition, after the water bamboo shoot shell WS is subjected to the cleaning process S11, the air-drying process S13 and/or the chopping process S15, the water bamboo shoot shell WS may, for example, undergo a drying and dehydration process S17 to further remove the water bamboo shoots. The moisture of bamboo shoot shell WS is convenient for subsequent biochar production. The drying and dehydration process S17 may be implemented by an oven or oven independent of the
另外,在該茭白筍殼WS經該烘乾脫水製程S17後,該茭白筍殼WS可以一篩網(未圖示)過篩。該篩網可以篩選除去體積較大的該茭白筍殼WS,以利後續的生物炭製造。經該篩網篩選後的該茭白筍殼WS置入該加熱爐13中,以進行後續的生物炭製造(即步驟S101)。在本實施例中,該篩網的一目數(mesh)是8、9、10或12,而目數8、9、10、12對應篩選的粒徑是2.36 mm、2.00 mm、1.70 mm、1.40 mm。在本發明一實施例中,該篩網的該目數是10,以利後續的生物炭製造。In addition, after the water bamboo shoot shell WS is subjected to the drying and dehydration process S17, the water bamboo shoot shell WS can be sieved through a screen (not shown). The screen can screen and remove the bamboo shoot shell WS with a larger volume, so as to facilitate the subsequent production of biochar. The bamboo shoot shells WS screened by the screen are placed in the
透過該前置作業200對包括該茭白筍殼WS的該植物原料11進行處理,再進行生物炭製造,能解決炭化不均勻的問題,可以製成具有高吸附表面積的該生物炭C。Through the pre-operation 200, the
請同時參照圖4,圖4是本發明一實施例的生物炭製造方法的活性炭製程300的流程圖。本實施例的生物炭製造方法在圖2所示的步驟S105之後,還可以進行該活性炭製程300。在步驟S105形成該生物炭C後,該生物炭C還可以經一活化(Activation)製程以形成一活性炭AC。該活化製程例如可以一活性炭活化物理法或一活性炭活化化學法來實現,但本發明並不以此為限制。Please refer to FIG. 4 at the same time. FIG. 4 is a flowchart of an activated
本實施例包括該茭白筍殼WS的該植物原料11製成的該生物炭C具有很高的BET比表面積,因此由該生物炭C製成的該活性炭AC具有極高的效能。本實施例的生物炭製造方法不但能解決茭白筍農業剩餘資材造成的問題,更可以製成具有高經濟效益的該活性炭AC。The biochar C made from the
綜上所述,本發明實施例的生物炭製造方法透過在氮氣環境下加熱包括茭白筍殼的植物原料,能有效解決炭化不均勻的問題,可以製成具有高吸附表面積的生物炭,大幅提高生物炭的效能。To sum up, the biochar production method of the embodiment of the present invention can effectively solve the problem of uneven carbonization by heating the plant material including the bamboo shoot shells in a nitrogen environment, and can produce biochar with a high adsorption surface area, which greatly improves the performance of the biochar. The efficacy of biochar.
1:製造裝置 100:生物炭製造方法 11:植物原料 13:加熱爐 131:加熱腔室 133:加熱器 135:進氣口 15:氮氣源 151:氮氣 200:前置作業 300:活性炭製程 AC:活性炭 C:生物炭 S101、S103、S105、S107:步驟 S11、S13、S15、S17、S19:步驟 T:鍛燒溫度 WS:茭白筍殼1: Manufacturing device 100: Biochar manufacturing method 11: Plant Raw Materials 13: Heating furnace 131: Heating chamber 133: Heater 135: Air intake 15: Nitrogen source 151: Nitrogen 200: Preliminary work 300: Activated carbon process AC: activated carbon C: Biochar S101, S103, S105, S107: steps S11, S13, S15, S17, S19: Steps T: calcination temperature WS: Water bamboo shoot shell
圖1是本發明一實施例的生物炭的製造裝置的示意圖。 圖2是本發明一實施例的生物炭製造方法的流程圖。 圖3是本發明一實施例的生物炭製造方法的前置作業的流程圖。 圖4是本發明一實施例的生物炭製造方法的活性炭製程的流程圖。FIG. 1 is a schematic diagram of an apparatus for producing biochar according to an embodiment of the present invention. FIG. 2 is a flow chart of a method for producing biochar according to an embodiment of the present invention. 3 is a flow chart of the pre-operation of the biochar production method according to an embodiment of the present invention. FIG. 4 is a flow chart of the activated carbon manufacturing process of the biochar manufacturing method according to an embodiment of the present invention.
S101、S103、S105:步驟S101, S103, S105: Steps
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW109124789A TWI772846B (en) | 2020-07-22 | 2020-07-22 | Biochar production method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW109124789A TWI772846B (en) | 2020-07-22 | 2020-07-22 | Biochar production method |
Publications (2)
Publication Number | Publication Date |
---|---|
TW202204250A TW202204250A (en) | 2022-02-01 |
TWI772846B true TWI772846B (en) | 2022-08-01 |
Family
ID=81323645
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
TW109124789A TWI772846B (en) | 2020-07-22 | 2020-07-22 | Biochar production method |
Country Status (1)
Country | Link |
---|---|
TW (1) | TWI772846B (en) |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109575967A (en) * | 2018-12-17 | 2019-04-05 | 轻工业环境保护研究所 | The method for preparing charcoal and activated carbon from activated sludge using agriculture and forestry organic waste material |
-
2020
- 2020-07-22 TW TW109124789A patent/TWI772846B/en active
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109575967A (en) * | 2018-12-17 | 2019-04-05 | 轻工业环境保护研究所 | The method for preparing charcoal and activated carbon from activated sludge using agriculture and forestry organic waste material |
Also Published As
Publication number | Publication date |
---|---|
TW202204250A (en) | 2022-02-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100389063C (en) | Method for carbonizing active giantreed carbon and pore-forming | |
CN107803395A (en) | A kind of organic abraum salt low-temperature carbonization handling process | |
CN104087326B (en) | A kind of method preparing charcoal for raw material wet method thermal cracking with agricultural organic solid waste | |
CN103865552A (en) | Method of preparing charcoal based on agricultural and forestry wastes and charcoal | |
CN109759011A (en) | The preparation method of straw base magnetic bio charcoal | |
WO2020077673A1 (en) | Easy-control technology for preparing biomass skeletal charcoal having micropore-mesopore structure and high specific surface area | |
CN103145126B (en) | A kind of take waste leather as the method for raw material microwave legal system for gac | |
CN109734089A (en) | A kind of high-specific surface area vinasse method for preparation of active carbon | |
CN107758660A (en) | A kind of method that bagasse matrix activated carbon is prepared using zinc chloride as activator | |
CN104609420A (en) | Preparation method of rice hull-based active carbon | |
CN103272562B (en) | Preparation method of filter material base activated carbon fiber | |
CN104326471A (en) | Method for preparing active carbon from licorice waste residue | |
CN108579673B (en) | Silkworm excrement biochar and preparation method and application thereof | |
CN108706585A (en) | A kind of preparation method of big kenaf stalk activated charcoal | |
KR20130083164A (en) | A method for preparing hemp active carbon and the preparation apparatus therefor | |
CN102838112B (en) | Preparation method of activated carbon | |
TWI772846B (en) | Biochar production method | |
CN104891488A (en) | High-temperature carbonization preparation method of bamboo activated carbon with high yield | |
CN104477907A (en) | High-temperature carbonization preparation method of activated bamboo carbon with high absorption rate | |
CN108529624A (en) | Multi-well high-throughput activated carbon and its technology of preparing | |
CN106744949A (en) | A kind of method for preparing activated carbon as raw material with sesame stalk | |
CN112279244B (en) | Preparation method and application of activated carbon | |
CN110142022A (en) | Preparation method of graphene aerogel for air purification | |
CN105439619B (en) | A kind of method of utilization waste and old wood grain production light ceramic ball | |
CN103657605A (en) | Peanut shell modification method |