TW202222691A - Continuous fluidized bed hydrothermal reaction device and method for continuous hydrothermal synthesis of porous materials which comprises a reaction tank, a feeding port, a discharging port, a heating element, a solid-liquid separation unit, a circulating pipeline, and a two-way circulating pump - Google Patents
Continuous fluidized bed hydrothermal reaction device and method for continuous hydrothermal synthesis of porous materials which comprises a reaction tank, a feeding port, a discharging port, a heating element, a solid-liquid separation unit, a circulating pipeline, and a two-way circulating pump Download PDFInfo
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本發明係關於一種連續式流體化床水熱反應裝置,以及使用該連續式流體化床水熱反應裝置之連續式水熱合成多孔性材料的方法。The present invention relates to a continuous fluidized bed hydrothermal reaction device and a method for continuous hydrothermal synthesis of porous materials using the continuous fluidized bed hydrothermal reaction device.
按,根據環保署統計資料顯示,我國每年產生之含矽無機廢棄物量高達千萬公噸,包含焚化底渣與飛灰、廢玻璃、面板玻璃、集塵灰、鍋爐灰、煉鋼爐碴、爐石、磚瓦陶瓷、無機性污泥、石材廢料等等,且作為前述含矽無機廢棄物之處理方式,一般係將其固化/穩定化處理後堆置/掩埋於掩埋場。然而,因國內掩埋場容量不足,無法成為長久可行的處理方式。According to statistics from the Environmental Protection Agency, the amount of silicon-containing inorganic waste produced in my country is as high as 10 million metric tons each year, including incineration bottom slag and fly ash, waste glass, panel glass, dust collection ash, boiler ash, steelmaking ballast, furnace Stone, brick ceramics, inorganic sludge, stone waste, etc., and as the treatment method for the aforementioned silicon-containing inorganic waste, it is generally solidified/stabilized and then stacked/buried in a landfill. However, due to insufficient capacity of domestic landfills, it cannot be a long-term feasible treatment method.
又,由於許多含矽無機廢棄物中富含矽、鋁、鈣等金屬氧化物,具備合成沸石等多孔性材料之潛力,故作為前述堆置/掩埋處理的替代,有人提出使含矽無機廢棄物進行水熱反應來合成沸石。In addition, since many silicon-containing inorganic wastes are rich in metal oxides such as silicon, aluminum, and calcium, and have the potential to synthesize porous materials such as zeolite, as an alternative to the aforementioned stacking/burying treatment, some people propose to make silicon-containing inorganic wastes waste. The zeolite is synthesized by hydrothermal reaction.
而就將含矽無機廢棄物進行水熱反應來合成沸石的反應設備而言,一般係使用小型之加蓋密封水熱反應器。As for the reaction equipment for synthesizing zeolite by hydrothermally reacting silicon-containing inorganic waste, a small-sized hydrothermal reactor with a lid is generally used.
然而,因前述加蓋密封的水熱反應器係屬於批次型態的反應設備,且通常為容量有限之小型反應裝置,故放大量產與應用發展空間受限。又,因為批次型態的反應設備僅能夠進行批次生產,並無法連續式地生產,故無法達到工業化的需求。However, because the above-mentioned hydrothermal reactors with caps and seals are batch-type reaction equipment and are usually small-scale reaction devices with limited capacity, the space for large-scale production and application development is limited. In addition, because the batch-type reaction equipment can only perform batch production and cannot be continuously produced, it cannot meet the needs of industrialization.
另外,在習知的前述使含矽無機廢棄物進行水熱反應來合成沸石之方法中,通常僅使用攪拌器進行攪拌,並未在反應器內產生流體化現象,故水熱反應中反應物的混合效果仍有進一步提升的空間。In addition, in the conventional method for synthesizing zeolite by hydrothermally reacting silicon-containing inorganic waste, usually only a stirrer is used for stirring, and no fluidization phenomenon occurs in the reactor, so the reactants in the hydrothermal reaction are There is still room for further improvement in the mixing effect.
此外,在批次生產的過程中,當完成一個批次的生產後,通常必須除去反應器內殘存的物質,始能進行下一批次的生產。然而,若將反應器內殘存的物質除去,則未能夠有效再利用該等殘存的物質。In addition, in the process of batch production, after the production of one batch is completed, it is usually necessary to remove the remaining substances in the reactor before the production of the next batch can be carried out. However, if the substances remaining in the reactor are removed, the remaining substances cannot be reused effectively.
為了解決上述問題,本發明一態樣的連續式流體化床水熱反應裝置,其係包含: 反應槽,其係包括:直立圓柱形的槽體;以及倒圓錐形的底部; 投料口,其係用於投入水解反應原料或水熱反應原料,且其係設置於該反應槽的上方並與該反應槽的頂部連通; 出料口,其係用於排出水解反應產物或水熱反應產物,且其係與該反應槽的底部連通; 加熱元件,其係用於加熱該反應槽; 固液分離單元,其係用於將該水解反應產物或水熱反應產物固液分離,且其係設置於該出料口的下方並與該出料口連通; 循環管線,其係與該反應槽的頂部、該固液分離單元之一側的底部以及該出料口連通; 雙向循環泵,其係設置於該循環管線上,且其係用於執行下述至少之一者:使自該反應槽的頂部而被導引之水解反應原料或水熱反應原料經由該循環管線而被注入該反應槽的底部;或者使藉由該固液分離單元而被分離出之水解反應產物的液體或水熱反應產物的液體,經由該循環管線而被注入該反應槽的頂部。 In order to solve the above problems, a continuous fluidized bed hydrothermal reaction device of one aspect of the present invention comprises: A reaction tank, which includes: an upright cylindrical tank body; and an inverted conical bottom; a feeding port, which is used to input hydrolysis reaction raw materials or hydrothermal reaction raw materials, and is arranged above the reaction tank and communicated with the top of the reaction tank; A discharge port, which is used to discharge the hydrolysis reaction product or the hydrothermal reaction product, and is communicated with the bottom of the reaction tank; a heating element for heating the reaction tank; a solid-liquid separation unit, which is used for solid-liquid separation of the hydrolysis reaction product or the hydrothermal reaction product, and is arranged below the discharge port and communicated with the discharge port; a circulation line, which is communicated with the top of the reaction tank, the bottom of one side of the solid-liquid separation unit, and the outlet; A bidirectional circulating pump, which is arranged on the circulating line, and which is used to perform at least one of the following: the hydrolysis reaction raw material or the hydrothermal reaction raw material guided from the top of the reaction tank passes through the circulating line and injected into the bottom of the reaction tank; or the liquid of the hydrolysis reaction product or the liquid of the hydrothermal reaction product separated by the solid-liquid separation unit is injected into the top of the reaction tank through the circulation line.
在一實施例中,該循環管線係包括:第一循環管線,其係設置於該反應槽之一側並與該反應槽的頂部及出料口連通;第二循環管線,其係與該固液分離單元之一側的底部及該第一循環管線連通。In one embodiment, the circulation line system includes: a first circulation line, which is arranged on one side of the reaction tank and communicates with the top of the reaction tank and the discharge port; a second circulation line, which is connected with the solids. The bottom of one side of the liquid separation unit communicates with the first circulation line.
在一實施例中,該固液分離單元係包括:濾網孔徑為100µm的粗過濾板;及濾網孔徑為20µm的細過濾板。In one embodiment, the solid-liquid separation unit includes: a coarse filter plate with a filter mesh aperture of 100 μm; and a fine filter plate with a filter mesh aperture of 20 μm.
在一實施例中,該連續式流體化床水熱反應裝置還包含:分散板,其係設置於該反應槽的底部。In one embodiment, the continuous fluidized bed hydrothermal reaction device further comprises: a dispersing plate, which is arranged at the bottom of the reaction tank.
在一實施例中,該連續式流體化床水熱反應裝置還包含:攪拌器,其係設置於該槽體內。In one embodiment, the continuous fluidized bed hydrothermal reaction device further includes: a stirrer disposed in the tank.
在一實施例中,該連續式流體化床水熱反應裝置還包含:熱電偶、壓力錶及液位計所組成之群組中至少任一者,且前述熱電偶、壓力錶及液位計係設置於該反應槽並分別用於檢測該反應槽內的溫度、壓力及液位。In one embodiment, the continuous fluidized bed hydrothermal reaction device further comprises: at least any one of the group consisting of a thermocouple, a pressure gauge and a liquid level gauge, and the aforementioned thermocouple, pressure gauge and liquid level gauge It is arranged in the reaction tank and is used to detect the temperature, pressure and liquid level in the reaction tank respectively.
在一實施例中,該連續式流體化床水熱反應裝置還包含:自動控制盤,其係與前述熱電偶、壓力錶及液位計電性連接,並藉由前述熱電偶、壓力錶及液位計,來監測及自動控制該反應槽內的溫度、壓力及液位。In one embodiment, the continuous fluidized bed hydrothermal reaction device further comprises: an automatic control panel, which is electrically connected with the aforementioned thermocouple, pressure gauge and liquid level gauge, and through which the aforementioned thermocouple, pressure gauge and A liquid level gauge is used to monitor and automatically control the temperature, pressure and liquid level in the reaction tank.
為了解決上述問題,本發明一態樣的連續式水熱合成多孔性材料的方法,其係包含:(a)提供一含矽無機廢棄物;(b)調整前述含矽無機廢棄物的矽鋁比,以獲得鹼熔反應原料;(c)於前述鹼熔反應原料加入鹼劑,並進行鹼熔反應,以獲得水解反應原料;(d)於前述水解反應原料加入適當比例之純水(最佳液固比)並進行水解反應,且將水解反應產物的至少一部分作為水熱反應原料;(e)於前述水熱反應原料加入模板劑並調整pH值,以進行水熱反應,並獲得一水熱反應產物;(f)將前述水熱反應產物進行固液分離,以獲得前述水熱反應產物的液體及多孔性材料前驅物固體,並將前述水熱反應產物的液體循環使用作為水解反應原料;(g)將前述多孔性材料前驅物固體進行烘乾與鍛燒,以獲得多孔性材料;其中,前述(d)~(f)步驟係在本發明的連續式流體化床水熱反應裝置內進行。In order to solve the above problems, a method for continuous hydrothermal synthesis of porous materials according to an aspect of the present invention comprises: (a) providing a silicon-containing inorganic waste; (b) adjusting the silicon-alumina of the silicon-containing inorganic waste (c) adding alkali agent to the aforementioned raw materials for alkaline melting reaction, and performing alkaline melting reaction to obtain raw materials for hydrolysis reaction; (d) adding an appropriate proportion of pure water (most (e) adding a templating agent to the aforementioned hydrothermal reaction raw material and adjusting the pH value to carry out a hydrothermal reaction, and obtain a Hydrothermal reaction product; (f) carrying out solid-liquid separation of the aforementioned hydrothermal reaction product to obtain the liquid of the aforementioned hydrothermal reaction product and the solid of the porous material precursor, and recycling the aforementioned liquid of the aforementioned hydrothermal reaction product as a hydrolysis reaction raw materials; (g) drying and calcining the aforementioned porous material precursor solid to obtain a porous material; wherein, the aforementioned steps (d) to (f) are performed in the continuous fluidized bed hydrothermal reaction of the present invention carried out in the device.
在一實施例中,在(b)步驟中,將前述含矽無機廢棄物的矽鋁比(矽/鋁的莫耳比)調整為10~40。In one embodiment, in step (b), the silicon-aluminum ratio (molar ratio of silicon/aluminum) of the aforementioned silicon-containing inorganic waste is adjusted to 10˜40.
又,在一實施例中,在(c)步驟中,鹼劑/鹼熔反應原料的重量比(鹼劑量比)為1.0~1.5。Also, in one embodiment, in the step (c), the weight ratio (alkali dosage ratio) of the alkali agent/alkali melting reaction raw material is 1.0 to 1.5.
又,在一實施例中,在(d)步驟中,將純水/水解反應原料的重量比(液固比)調整為50~200,並前述水解反應產物進行固液分離,且使前述水解反應產物的液體作為水熱反應原料。Also, in one embodiment, in step (d), the weight ratio (liquid-solid ratio) of pure water/hydrolysis reaction raw materials is adjusted to 50 to 200, and the aforementioned hydrolysis reaction product is subjected to solid-liquid separation, and the aforementioned hydrolysis is performed. The liquid of the reaction product is used as the raw material for the hydrothermal reaction.
又,在一實施例中,在(e)步驟中,前述模板劑為溴化十六烷基三甲銨(CTAB),且前述模板劑的使用量為前述水熱反應原料的0.5~1.5重量%,且水熱反應前驅液的pH值為8~12,水熱反應溫度為105~150℃,水熱反應時間為8~16小時。Also, in one embodiment, in the step (e), the aforementioned templating agent is cetyltrimethylammonium bromide (CTAB), and the usage amount of the aforementioned templating agent is 0.5 to 1.5% by weight of the aforementioned hydrothermal reaction raw materials , and the pH value of the hydrothermal reaction precursor liquid is 8~12, the hydrothermal reaction temperature is 105~150 °C, and the hydrothermal reaction time is 8~16 hours.
又,在一實施例中,在(a)步驟中,前述含矽無機廢棄物係選自:由焚化底渣、飛灰、廢玻璃、面板玻璃、集塵灰、鍋爐灰、煉鋼爐碴、爐石、磚瓦陶瓷、無機性污泥及石材廢料所組成之群組中的至少任一者。Also, in one embodiment, in the step (a), the silicon-containing inorganic waste is selected from the group consisting of incineration bottom slag, fly ash, waste glass, panel glass, dust collection ash, boiler ash, and steelmaking furnace slag , at least one of the group consisting of hearthstone, brick ceramics, inorganic sludge and stone waste.
本發明一態樣是鑒於上述習知的問題點所完成者,其目的是,提供一種用於連續式流體化床水熱反應裝置,其係藉由反應槽的設計以達流體化床的效果,並藉由雙向循環泵及循環管線而能夠充分利用水熱合成過程中的各項資源(例如水解反應後溶液、水熱反應後溶液、模板劑、含矽無機廢棄物(矽源)等),以節省能源與資源之消耗,降低操作成本,並能夠達成連續式生產及放大生產規模之效果。One aspect of the present invention is made in view of the above-mentioned conventional problems, and an object of the present invention is to provide a continuous fluidized bed hydrothermal reaction device, which achieves the effect of a fluidized bed through the design of the reaction tank , and can make full use of various resources in the hydrothermal synthesis process (such as solution after hydrolysis reaction, solution after hydrothermal reaction, template agent, silicon-containing inorganic waste (silicon source), etc.) , in order to save energy and resource consumption, reduce operating costs, and can achieve the effect of continuous production and scale-up of production.
本發明的一態樣係提供一種連續式水熱合成多孔性材料的方法,其係藉由在本發明的連續式流體化床水熱反應裝置中進行水解反應及水熱反應,而能夠達成連續式生產及放大生產規模之效果。One aspect of the present invention provides a method for continuous hydrothermal synthesis of porous materials, which can achieve continuous hydrolysis and hydrothermal reactions in the continuous fluidized bed hydrothermal reaction device of the present invention. The effect of type production and scale-up of production.
<連續式流體化床水熱反應裝置>
首先,請參照圖1,圖1係為本發明一實施例之連續式流體化床水熱反應裝置的示意圖。如圖1所示,本發明提供一種連續式流體化床水熱反應裝置100,其係包含:反應槽1、投料口2、出料口3、加熱元件4、固液分離單元5、雙向循環泵6、循環管線(於本實施例中,其為第一循環管線L1及第二循環管線L2)。
<Continuous Fluidized Bed Hydrothermal Reactor>
First, please refer to FIG. 1 , which is a schematic diagram of a continuous fluidized bed hydrothermal reaction apparatus according to an embodiment of the present invention. As shown in FIG. 1, the present invention provides a continuous fluidized bed
其中,該反應槽1係包括:直立圓柱形的槽體11;以及倒圓錐形的底部12。藉由使反應槽1成為上述形狀,則能夠有利於產生流體化床作用。又,反應槽1的體積可依工業上量產的實際需求量設計,例如可為50公升、100公升、150公升及200公升等,並不限於此。Wherein, the
又,該投料口2係用於投入水解反應原料或水熱反應原料,且其係設置於該反應槽1的上方並與該反應槽1的頂部連通。該投料口2係可為管狀,以利投入原料。就該水解反應原料而言,可例如為經過後述(a)~(c)步驟之原料,更具體而言,該水解反應原料係可為,使調整矽鋁比後的含矽無機廢棄物進行鹼熔反應後所獲得者。又,就該水熱反應原料而言,可例如為水解反應產物的至少一部分(例如較佳係水解反應產物的液體)作為反應原料,亦可將水解反應產物直接作為反應原料。In addition, the
又,應注意的是,雖然本發明較佳係藉由前述之雙向循環泵6、循環管線(例如第一循環管線L1及第二循環管線L2)來將水解反應產物的一部分(例如水解產物的液體)作為水熱反應原料,並使該水熱反應原料經由該第二循環管線L2及該第一循環管線L1而被注入該反應槽1的頂部的入口(詳述於後),但亦可將該水解反應產物的一部分導引至投料口2來投入水解反應原料。且在投入水熱反應原料的情況下,與投入水解反應原料時相同地,亦能夠選擇自該反應槽1的頂部的入口(圖1的開關閥a1處)投入或自投料口2投入。又,本發明的循環管線,只要與反應槽1的頂部、固液分離單元5之一側的底部以及出料口3連通即可,並未限定為第一循環管線L1及第二循環管線L2之組合。Also, it should be noted that although the present invention preferably uses the aforementioned bidirectional circulating
接著,該出料口3係用於排出在該反應槽1內進行完水解反應或水熱反應後之水解反應產物或水熱反應產物,且該出料口3係與該反應槽1的倒圓錐形底部12連通。能夠於出料口3與圓錐形底部12之間設置開關閥a7,且其係用以控制該反應槽1內的水解反應產物或水熱反應產物導引至出料口3的流量、流速等。Next, the
接著,該加熱元件4係用於加熱該反應槽1,使該反應槽1成為適合進行水解反應或水熱反應的溫度。又,該加熱元件4係設置於在該反應槽1的周圍,且為了達到均勻加熱的效果,可設置在該反應槽1的周圍設置複數個加熱元件4。又,就該加熱元件4的較佳態樣而言,如後述圖2所示,其可為包覆槽體11四周的加熱線圈以及保溫隔熱材料,藉此能夠具有良好的蓄熱保溫效果,減少熱損失。Next, the
接著,如圖1所示,固液分離單元5係設置於該出料口3的下方並與該出料口3連通。該固液分離單元5係用於將前述水解反應產物或水熱反應產物固液分離。又,能夠於出料口3與固液分離單元5之間設置開關閥a8,且其係用以控制經過該出料口3內的水解反應產物或水熱反應產物導引至固液分離單元5的流量、流速等。又,就該固液分離單元5的較佳態樣而言,如後述圖2所示,其可包括:濾網孔徑為100µm的粗過濾板51;及濾網孔徑為20µm的細過濾板52。Next, as shown in FIG. 1 , the solid-
接著,如圖1所示,第一循環管線L1係設置於該反應槽1之一側並與該反應槽1的頂部及出料口3連通。能夠在該第一循環管線L1與該反應槽1的頂部的連通處設置開關閥a1以進行流量、流速等控制。又,該第一循環管線L1係用於使涉及水解反應/水熱反應的物質在其管線內流動,並能夠基於該雙向循環泵6的控制,來改變涉及水解反應/水熱反應的物質在該第一循環管線L1內的流向。能夠在該第一循環管線L1與出料口3之間設置開關閥a6,以控制涉及水解反應/水熱反應的物質(例如水解反應產物)從出料口3朝第一循環管線L1內的流量、流速等。Next, as shown in FIG. 1 , the first circulation line L1 is arranged on one side of the
又,如圖1所示,第二循環管線L2係與該固液分離單元5之一側的底部並與該第一循環管線L1連通。該第一循環管線L2係用於使經過固液分離後之水解反應產物或水熱反應產物在其管線內流動,並將前述水解反應產物或水熱反應產物導入至該第一循環管線L1內,之後再經由第一循環管線L1導入至該反應槽1的頂部(開關閥a1處)。能夠在該固液分離單元5與第二循環管線L2之間設置開關閥a5進行控制,亦能夠在第二循環管線L2與第一循環管線L1之間設置開關閥a4進行控制。Furthermore, as shown in FIG. 1 , the second circulation line L2 communicates with the bottom of one side of the solid-
另外,如圖1所示,本發明的連續式流體化床水熱反應裝置還包含:雙向循環泵6,其係設置於循環管線上,且其係用於執行下述至少之一者:使自該反應槽1的頂部而被導引之水解反應原料或水熱反應原料經由該第一循環管線L1而被注入該反應槽1的底部12;或者使藉由該固液分離單元5而被分離出之水解反應產物的液體或水熱反應產物的液體,經由該第二循環管線L2及該第一循環管線L1而被注入該反應槽1的頂部(開關閥a1處)。又,能夠在雙向循環泵6的上游及下游分別設置開關閥a2、a3以進行控制。藉此,藉由從反應槽1的頂部將反應槽1內的液體連續導引(抽引)並由反應槽1的底部12注入,而使反應槽1內的流體與水解反應原料或水熱反應原料產生流體化現象,達到均勻混合之目的,可促進水解反應與水熱反應之效果,並能夠連續地流動循環,而達成連續式流體化床水熱反應裝置的功能。In addition, as shown in FIG. 1 , the continuous fluidized bed hydrothermal reaction device of the present invention further comprises: a bidirectional circulating
接著,請參照圖2,圖2係為本發明另一實施例之連續式流體化床水熱反應裝置的示意圖。如圖2所示,與圖1相同地,本發明另一實施例之連續式流體化床水熱反應裝置100’亦包含:反應槽1、投料口2、出料口3、加熱元件4、固液分離單元5、雙向循環泵6、第一循環管線L1、第二循環管線L2以及開關閥a1~a8等各個元件。因此,於圖2中,將此等與圖1相同的元件賦予相同的符號,並省略其說明。Next, please refer to FIG. 2 , which is a schematic diagram of a continuous fluidized bed hydrothermal reaction apparatus according to another embodiment of the present invention. As shown in FIG. 2, similar to FIG. 1, the continuous fluidized bed hydrothermal reaction device 100' according to another embodiment of the present invention also includes: a
其中,如前述般,圖2係顯示了加熱元件4及固液分離單元5的較佳態樣。舉例來說,加熱元件4可為包覆直立圓柱形的槽體11四周的加熱線圈以及保溫隔熱材料,藉此能夠具有良好的蓄熱保溫效果,減少熱損失。此外,為了減少在出料口3、第一循環管線L1及第二循環管線L2等處的熱損失,亦可使用加熱元件4針對出料口3、第一循環管線L1及第二循環管線L2等處進行加熱,且較佳地,加熱元件4可為包覆出料口3、第一循環管線L1及第二循環管線L2四周的加熱線圈以及保溫隔熱材料。又,該固液分離單元5較佳係可為不鏽鋼過濾網所構成,且濾網孔徑分別為100µm(上層的粗過濾板51)與20µm(下層的細過濾板52)。藉此,經由粗/細過濾板的組合,能夠達到更好的篩分效果,以利將自水熱反應產物所分離出之固體成分進行後述的鍛燒步驟等。此外,上述濾網孔徑僅係本發明的較佳態樣,能夠視需求而調整變化適當分離篩網,且藉由設計成可調式的多層分離裝置,更具操作彈性。Among them, as mentioned above, FIG. 2 shows a preferred aspect of the
又,在圖2中,還可於該槽體11內設置攪拌器8,以增加各種反應原料的混合效果。該攪拌器8可視需要進行攪拌,且能夠將其轉速設計為0~100 rpm之間。又,在圖2中,還能夠於該反應槽1的底部12設置有分散板(未圖示)。該分散板可依需求設置,且藉由該分散板,能夠產生向上的流體作用力,而使槽體11內流體與各種反應原料產生流體化現象,達到混合均勻並持續攪動之目的。In addition, in FIG. 2 , a
此外,在圖2中,還可依需求於反應槽1(例如於反應槽1的頂部)設置壓力錶7、熱電偶溫度計9、洩壓閥10及液位計(未圖示)等。藉由設置上述壓力錶7、熱電偶(熱電偶溫度計)9及液位計等,能夠監測反應過程中的壓力、溫度、液位等。且藉由洩壓閥10,能夠在確保在反應過程中不會因為壓力過大而產生危險。另外,還能夠設置自動控制盤20,該自動控制盤20係與前述熱電偶9、壓力錶7及液位計電性連接,並藉由前述熱電偶9、壓力錶7及液位計,來監測及自動控制該反應槽內的溫度、壓力及液位,以確保系統操作與控制操作皆能達到準確、穩定、安全之要求。In addition, in FIG. 2 , a
又,能夠在投料口2設置開關閥a9,以控制各種原料的投入時的流速、流量等。In addition, an on-off valve a9 can be provided in the charging
以上已針對本發明連續式流體化床水熱反應裝置的各實例及變化態樣進行說明,且上述各實例及變化態樣僅係例示性的說明,並非用於限制本發明的範圍,與上述各實例及變化態樣等效之其他態樣亦被包含在本發明的範圍內。以下針對本發明之連續式水熱合成多孔性材料的方法進行說明。The examples and variations of the continuous fluidized bed hydrothermal reaction device of the present invention have been described above, and the above examples and variations are only illustrative, and are not intended to limit the scope of the present invention. Other equivalents of the examples and variations are also included within the scope of the invention. The method for continuous hydrothermal synthesis of a porous material of the present invention will be described below.
<連續式水熱合成多孔性材料的方法> 本發明之連續式水熱合成多孔性材料方法的基本原理係利用鹼熔步驟將含矽無機廢棄物中的矽氧化物與鋁氧化物解離溶出後,再利用水解及水熱反應將矽氧化物與鋁氧化物於適當控制條件下重新排列組合並凝核、縮聚、結晶成類似合成沸石等無機多孔性材料,使其具有良好的比表面積與孔洞分布特性;又,藉由於上述本發明之連續式流體化床水熱反應裝置中進行水解及水熱反應,而能夠連續式地合成多孔性材料,進而完成本發明之連續式水熱合成多孔性材料的方法。 <Method for continuous hydrothermal synthesis of porous material> The basic principle of the continuous hydrothermal method for synthesizing porous materials of the present invention is to dissociate and dissolve the silicon oxides and aluminum oxides in the silicon-containing inorganic waste by the alkali melting step, and then use hydrolysis and hydrothermal reaction to dissociate the silicon oxides. Rearranged and combined with aluminum oxide under appropriate control conditions, nucleated, polycondensed, and crystallized into inorganic porous materials similar to synthetic zeolite, so that it has good specific surface area and pore distribution characteristics; The hydrolysis and hydrothermal reaction are carried out in the fluidized bed hydrothermal reaction device, so that the porous material can be continuously synthesized, thereby completing the continuous hydrothermal synthesis method of the porous material of the present invention.
首先,請參照圖3,圖3係為本發明一實施例之連續式水熱合成多孔性材料的方法的流程圖。如圖3所示,本發明一實施例的連續式水熱合成多孔性材料的方法係包含(a)~(g)步驟。以下分別針對各個步驟進行說明。First, please refer to FIG. 3 , which is a flowchart of a method for continuous hydrothermal synthesis of porous materials according to an embodiment of the present invention. As shown in FIG. 3 , the method for continuous hydrothermal synthesis of porous materials according to an embodiment of the present invention includes steps (a) to (g). Each step is described below.
-(a)步驟- (a)步驟係提供一含矽無機廢棄物。在(a)步驟中,前述含矽無機廢棄物係可選自:由焚化底渣、飛灰、廢玻璃、面板玻璃、集塵灰、鍋爐灰、煉鋼爐碴、爐石、磚瓦陶瓷、無機性污泥及石材廢料所組成之群組中的至少任一者。又,在(a)步驟中,亦可針對前述含矽無機廢棄物進行習知的粉碎與篩分處理,以獲得形態均勻的前述含矽無機廢棄物。 -(a) Step- The step (a) is to provide a silicon-containing inorganic waste. In step (a), the aforementioned silicon-containing inorganic waste can be selected from: bottom slag from incineration, fly ash, waste glass, panel glass, dust collection ash, boiler ash, steelmaking slag, furnace stone, brick and tile ceramics , at least one of the group consisting of inorganic sludge and stone waste. In addition, in the step (a), conventional pulverization and sieving can also be performed on the aforementioned silicon-containing inorganic waste, so as to obtain the aforementioned silicon-containing inorganic waste with a uniform shape.
-(b)步驟- (b)步驟係調整前述含矽無機廢棄物的矽鋁比,以獲得用於鹼熔反應的原料(鹼熔反應原料)。能夠根據所欲獲得的多孔性材料來調整含矽無機廢棄物的矽鋁比(矽/鋁的莫耳比)。在一實施例中,較佳係將前述含矽無機廢棄物之矽鋁比調整為10~40,更佳係將矽鋁比調整為20。因為前述含矽無機廢棄物亦通常包含鋁等其他金屬,故能夠藉由回收前述含矽無機廢棄物中的矽化合物與鋁化合物,來調整成適當的矽鋁比。 -(b) Step- The step (b) is to adjust the silicon-aluminum ratio of the aforementioned silicon-containing inorganic waste to obtain a raw material for alkali fusion reaction (a raw material for alkali fusion reaction). The silicon-aluminum ratio (molar ratio of silicon/aluminum) of the silicon-containing inorganic waste can be adjusted according to the desired porous material. In one embodiment, the silicon-aluminum ratio of the aforementioned silicon-containing inorganic waste is preferably adjusted to 10-40, and more preferably, the silicon-aluminum ratio is adjusted to 20. Because the above-mentioned silicon-containing inorganic waste also usually contains other metals such as aluminum, it can be adjusted to an appropriate silicon-aluminum ratio by recovering the silicon compound and the aluminum compound in the above-mentioned silicon-containing inorganic waste.
-(c)步驟- (c)步驟係於前述鹼熔反應原料中加入鹼劑,並進行鹼熔反應,以獲得水解反應原料。就(c)步驟中所使用的鹼劑而言,能夠使用例如氫氧化鈉(NaOH)、氫氧化鉀(KOH)、碳酸鈉(Na 2CO 3)或其組合,並不限於此。就鹼劑量比(鹼劑/鹼熔反應原料的重量比)而言,較佳係1.0~1.5%,更佳係1.2%。又,就(c)步驟所使用的反應裝置而言,能夠使用習知的高溫爐,並在200~800℃之間進行反應20~80分鐘,且較佳係在400~600℃之間進行反應40~60分鐘,更佳係在400℃進行反應60分鐘。最後,將經過鹼熔反應後的產物作為水解反應原料。 -(c) step- (c) step is to add an alkali agent to the above-mentioned alkali-melting reaction raw materials, and carry out alkali-melting reaction to obtain hydrolysis reaction raw materials. As the alkaline agent used in the (c) step, for example, sodium hydroxide (NaOH), potassium hydroxide (KOH), sodium carbonate (Na 2 CO 3 ), or a combination thereof can be used, but not limited thereto. In terms of alkali dosage ratio (weight ratio of alkali agent/alkali melting reaction raw material), it is preferably 1.0 to 1.5%, more preferably 1.2%. In addition, as for the reaction apparatus used in the step (c), a conventional high-temperature furnace can be used, and the reaction can be carried out at 200 to 800° C. for 20 to 80 minutes, and preferably at 400 to 600° C. The reaction is carried out for 40 to 60 minutes, preferably at 400° C. for 60 minutes. Finally, the product after alkali fusion reaction is used as the raw material for the hydrolysis reaction.
-(d)步驟-
(d)步驟係於前述水解反應原料加入純水並進行水解反應,且將水解反應產物的至少一部分作為水熱反應原料。(d)步驟係在本發明之連續式流體化床水熱反應裝置中進行,即可例如將水解反應原料與純水從前述投料口2投入反應器1內來進行。就(d)步驟中,純水與水解反應原料之重量比(液固比)而言,較佳係為50~200。水解反應係可例如為在105℃下反應40分鐘來進行,反應結束後冷卻降溫。
-(d) Step-
The step (d) is to add pure water to the above-mentioned hydrolysis reaction raw materials and carry out the hydrolysis reaction, and use at least a part of the hydrolysis reaction product as the hydrothermal reaction raw material. The step (d) is carried out in the continuous fluidized bed hydrothermal reaction device of the present invention, for example, the hydrolysis reaction raw materials and pure water can be put into the
又,能夠將經過(d)步驟(水解反應)後的水解反應產物的全部直接作為水熱反應原料,亦可僅將經過水解反應後的水解反應產物中的一部分(例如水解反應產物的液體部分)來作為水熱反應原料(例如,水熱反應用的液體)。具體而言,能夠在水解反應後,打開開關閥a7、a8,使水解反應產物進入固液分離單元5,並藉由上述之固液分離單元5針對水解反應產物進行固液分離。之後,藉由雙向循環泵6控制流向,並打開開關閥a1~a5,以將固液分離後之水解反應產物的液體從固液分離單元5的底部經由第二循環管線L2及第一循環管線L1而被注入該反應槽1的頂部。相較於直接使用水解反應產物來作為水熱反應原料的情況,在使用固液分離後之水解反應產物的液體來作為水熱反應原料的情況下,因為藉由固液分離去除了非所欲的固體雜質,故能夠提升最終合成之多孔性材料的比表面積。Also, the whole of the hydrolysis reaction product after the step (d) (hydrolysis reaction) can be directly used as the hydrothermal reaction raw material, or only a part of the hydrolysis reaction product after the hydrolysis reaction (for example, the liquid part of the hydrolysis reaction product can be used. ) as a raw material for hydrothermal reaction (eg, liquid for hydrothermal reaction). Specifically, after the hydrolysis reaction, the on-off valves a7 and a8 can be opened, so that the hydrolysis reaction product enters the solid-
-(e)步驟-
(e)步驟係於前述水熱反應原料加入模板劑並調整pH值,以進行水熱反應,並獲得一水熱反應產物。(e)步驟係在本發明之連續式流體化床水熱反應裝置中進行,即可例如將模板劑從前述投料口2投入反應器1內,並與前述水熱反應原料(例如經回流之水解反應產物的液體或水解反應產物本身)進行反應。就(e)步驟中所加入的模板劑而言,可例如為溴化十六烷基三甲銨(CTAB)。就模板劑的添加量而言,較佳係前述水熱反應原料的0.5~1.5重量%,更佳係1.2重量%。又,於(e)步驟中,較佳係將添加有模板劑的水熱反應原料的pH值調整為8~12,更佳係調整為10。就調整pH值的方法而言,可例如為添加酸或鹼等。在一具體例中,添加1M的硫酸溶液來將添加有模板劑的水熱反應原料調整pH值為10左右,以完成水熱反應前驅液。
-(e) Step-
The step (e) is to add a template agent to the above-mentioned hydrothermal reaction raw materials and adjust the pH value to conduct a hydrothermal reaction and obtain a hydrothermal reaction product. Step (e) is carried out in the continuous fluidized bed hydrothermal reaction device of the present invention, for example, the template agent is put into the
又,在(e)步驟中,針對前述水熱反應前驅液,較佳係以80~200℃的溫度進行水熱合成反應8~24小時,更佳係105~150℃的溫度水熱反應8~16小時。經(e)步驟的水熱反應後,獲得水熱反應產物。In addition, in the step (e), for the aforementioned hydrothermal reaction precursor solution, it is preferable to carry out the hydrothermal synthesis reaction at a temperature of 80 to 200° C. for 8 to 24 hours, and it is more preferable to perform a hydrothermal reaction at a temperature of 105 to 150° C. 8 ~16 hours. After the hydrothermal reaction in step (e), a hydrothermal reaction product is obtained.
-(f)步驟-
(f)步驟係將前述水熱反應產物進行固液分離,以獲得前述水熱反應產物的液體及多孔性材料前驅物固體,並將前述水熱反應產物的液體作為水解反應原料(例如水解反應用的液體)。(f)步驟係在本發明之連續式流體化床水熱反應裝置中進行,即可例如將經過固液分離單元5固液分離後之水熱反應產物的液體,從固液分離單元5的底部經由第二循環管線L2及第一循環管線L1而被注入該反應槽1的頂部。又,針對在(f)步驟所獲得的多孔性材料前驅物固體進行後述(g)步驟。
-(f) Step-
(f) step is to carry out solid-liquid separation of the aforementioned hydrothermal reaction product to obtain the liquid of the aforementioned hydrothermal reaction product and the solid of the porous material precursor, and to use the aforementioned liquid of the aforementioned hydrothermal reaction product as a hydrolysis reaction raw material (for example, a hydrolysis reaction liquid used). The step (f) is carried out in the continuous fluidized bed hydrothermal reaction device of the present invention, that is, for example, the liquid of the hydrothermal reaction product after the solid-liquid separation of the solid-
-(g)步驟- (g)步驟係將前述多孔性材料前驅物固體進行烘乾與鍛燒,以獲得多孔性材料。又,較佳係將該多孔性材料前驅物固體清洗後再進行烘乾與煅燒。在(g)步驟中,烘乾的反應條件可例如為在100~120℃下進行3~6小時,煅燒可在450~650(較佳係550℃)下進行3~6小時。 -(g) Step- The step (g) is drying and calcining the porous material precursor solid to obtain the porous material. Furthermore, it is preferable to dry and calcine the porous material precursor after solid cleaning. In step (g), the reaction conditions for drying can be, for example, 100-120° C. for 3-6 hours, and calcination can be performed at 450-650° C. (preferably 550° C.) for 3-6 hours.
又,就該多孔性材料而言,可例如為合成沸石。該多孔性材料亦可進一步加工製成吸附劑、濾材、觸媒載體等產品,應用於環保、化工、材料、光電、焚化、建築等相關產業。Moreover, as this porous material, synthetic zeolite can be used, for example. The porous material can also be further processed into adsorbents, filter materials, catalyst carriers and other products, which are used in environmental protection, chemical industry, materials, optoelectronics, incineration, construction and other related industries.
[實施例] 以下說明本發明的各實施例及比較例。本發明並不受該等實施例及比較例所限制。 [Example] Examples and comparative examples of the present invention will be described below. The present invention is not limited by these Examples and Comparative Examples.
<試驗例1~16:實驗室等級之多孔性材料的製備>
使用實驗室等級用的10升(10L)的水熱反應器(加蓋密封的熱水反應器)來進行(d)~(f)步驟。又,除了不進行(f)步驟中「將前述水熱反應產物的液體作為水解反應原料」且將水解時間調整2~24小時之外,依據上述(a)步驟~(g)步驟,在實驗室等級下合成多孔性材料。(a)步驟~(g)步驟的具體細節係如下所述。又,將實驗結果顯示於下述表1。
(a)步驟:分別使用台灣中部某垃圾焚化廠的焚化混合灰(鍋爐灰及飛灰等的混合物)(試驗例1~16)作為含矽無機廢棄物。將前述含矽無機廢棄物進行粉碎及篩分處理。
(b)步驟:將前述含矽無機廢棄物的矽鋁比調整為下述表1。
(c)步驟:使用1.2重量%的氫氧化鈉(NaOH)作為鹼劑。在高溫爐進行進行鹼熔反應1小時。鹼劑量比及鹼熔溫度顯示於表1。
(d)步驟:水解反應溫度為105℃,水解反應時間固定為24小時。在水解反應後有進行固液分離,並取液體部分進行(e)步驟。將液固比顯示於表1。
(e)步驟:添加1.2重量%的溴化十六烷基三甲銨(CTAB)作為模板劑,且水熱反應溫度為105℃。使用硫酸溶液將添加有模板劑的水熱反應原料調整pH值為10。將水熱反應時間顯示於表1。
(f)步驟:使用雙層篩網(上層孔徑為100µm;下層孔徑為20µm)針對水熱反應產物進行固液分離。
(g)步驟:清洗(f)步驟中所分離出之固體,並在110℃的條件下烘乾4小時,在550℃的條件煅燒3小時,獲得實驗等級的多孔性材料。
<Test Examples 1 to 16: Preparation of Laboratory Grade Porous Materials>
Steps (d)-(f) were performed using a
[表1]
從表1的結果來看,吾人認為當鹼熔溫度(℃)、液固比及水熱時間在表1的範圍內時,此等參數皆為可接受的程度,並非影響沸石比表面積的關鍵因素。又,從表1的結果能夠得知,試驗例1~4使用矽鋁比為5的含矽無機廢棄物,皆無法獲得比表面積大於600 m 2/g的沸石,故不佳。又,在試驗例5~8中,雖然矽鋁比皆為10,但僅有鹼劑量比為1~1.5的條件下能夠獲得比表面積大於600 m 2/g的沸石,故吾人認為鹼劑量比較佳係為1~1.5,且矽鋁比需為10以上。 From the results in Table 1, we believe that when the alkali melting temperature (°C), the liquid-solid ratio and the hydrothermal time are within the range of Table 1, these parameters are all acceptable levels, not the key to affecting the specific surface area of zeolite factor. In addition, as can be seen from the results in Table 1, Test Examples 1 to 4 were unsatisfactory because they could not obtain zeolite with a specific surface area larger than 600 m 2 /g using silicon-containing inorganic wastes with a Si/Al ratio of 5. In addition, in Test Examples 5 to 8, although the ratio of silicon to aluminum is 10, only under the condition that the alkali dose ratio is 1 to 1.5, zeolite with a specific surface area greater than 600 m 2 /g can be obtained, so we think that the alkali dose is relatively The optimal system is 1~1.5, and the silicon-aluminum ratio needs to be more than 10.
接著,試驗例9~16使用矽鋁比為20及40的含矽無機廢棄物,其所合成之沸石的比表面積皆大於600 m 2/g,故可得知矽鋁比較佳在10~40之間。又,因為在試驗例10中能夠獲得比表面積為962.08 m 2/g的沸石,故可得知在使用焚化混合灰的情況下,矽鋁比為20、鹼劑量比為1.5係為最佳的參數選擇。且經由表1能夠得知,矽鋁比及鹼劑量比係為影響沸石比表面積的關鍵因素。 Next, in Test Examples 9-16, silicon-containing inorganic wastes with a Si-Al ratio of 20 and 40 were used, and the specific surface areas of the synthesized zeolites were all greater than 600 m 2 /g, so it can be known that the Si-Al ratio is preferably 10-40 between. In addition, since the zeolite with a specific surface area of 962.08 m 2 /g was obtained in Test Example 10, it can be seen that in the case of using the incineration mixed ash, the silicon-alumina ratio of 20 and the alkali dose ratio of 1.5 are optimal. Preferences. And it can be known from Table 1 that the silicon-aluminum ratio and the alkali dosage ratio are the key factors affecting the specific surface area of zeolite.
<試驗例17~32:實驗室等級之多孔性材料的製備> 除了使用廢玻璃作為焚化混合灰的替代以外,以與上述試驗例1~16相同的方式進行多孔性材料的製備。將實驗參數及結果顯示於表2。 <Test Examples 17 to 32: Preparation of laboratory-grade porous materials> Preparation of porous materials was carried out in the same manner as in the above-mentioned Test Examples 1 to 16, except that waste glass was used as a substitute for the incineration mixed ash. The experimental parameters and results are shown in Table 2.
[表2]
與表1的結果相似地,從表2的結果來看,吾人認為當鹼熔溫度(℃)、液固比及水熱時間在表2的範圍內時,此等參數皆為可接受的程度,並非影響沸石比表面積及產率的關鍵因素。又,當矽鋁比為1及5時(試驗例17~24),皆無法合成比表面積大於600 m 2/g的沸石,故不佳。因此,在以廢玻璃作為含矽無機廢棄物的情況下,較佳的矽鋁比係為10~20。 Similar to the results in Table 1, from the results in Table 2, we believe that when the alkali melting temperature (°C), liquid-solid ratio and hydrothermal time are within the ranges of Table 2, these parameters are all acceptable. , is not a key factor affecting the specific surface area and yield of zeolite. In addition, when the silicon-alumina ratio was 1 and 5 (Test Examples 17 to 24), it was not possible to synthesize a zeolite with a specific surface area larger than 600 m 2 /g, which was not good. Therefore, in the case of using waste glass as the inorganic waste containing silicon, the preferred ratio of silicon to aluminum is 10-20.
接著,雖然試驗例25(矽鋁比10、鹼劑量比0.6)及試驗例29(矽鋁比20、鹼劑量比0.6)皆能夠獲得比表面積大於1000 m
2/g的沸石,但試驗例25及試驗例29的產率皆為20%以下,故不佳。相對於此,在試驗例30(矽鋁比20、鹼劑量比1.2)及試驗例31(矽鋁比20、鹼劑量比1.8)中,能夠獲得沸石比表面積及產率較理想的實驗結果。以下,使用試驗例30中的矽鋁比20與鹼劑量比1.2之條件嘗試擴大生產,並藉由本發明的連續式流體化床水熱反應裝置,連續地合成多孔性材料。
Next, although both Test Example 25 (silicon-
<實施例1:量產等級之多孔性材料的製備> 進行本發明連續地合成多孔性材料的方法之(a)~(g)步驟。在(d)~(f)步驟中使用本發明的連續式流體化床水熱反應裝置(體積為100L)。且如前述般,藉由從反應槽的頂部將反應槽內的液體連續導引(抽引)並由反應槽的底部注入,而使反應槽內的流體與水解反應原料或水熱反應原料產生流體化現象,而達到均勻混合之目的,以促進水解反應與水熱反應之效果。 <Example 1: Preparation of mass production grade porous material> Steps (a) to (g) of the method for continuously synthesizing a porous material of the present invention are carried out. In the steps (d) to (f), the continuous fluidized bed hydrothermal reaction device of the present invention (with a volume of 100 L) is used. And as described above, by continuously guiding (pumping) the liquid in the reaction tank from the top of the reaction tank and injecting it from the bottom of the reaction tank, the fluid in the reaction tank and the hydrolysis reaction raw material or the hydrothermal reaction raw material are generated. Fluidization phenomenon, and achieve the purpose of uniform mixing, in order to promote the effect of hydrolysis reaction and hydrothermal reaction.
接著,針對實施例1的反應條件說明如下:在(a)步驟中使用廢玻璃作為含矽無機廢棄物。在(b)步驟中將矽鋁比設為20。在(c)步驟中將鹼劑量比設為1.2、鹼熔溫度設為400℃、鹼熔反應時間為1小時。在(d)步驟中將液固比設為100、水解反應溫度設為105℃、水解反應時間設為40分鐘;又,在(d)步驟後針對水解反應產物進行固液分離,並將水解反應產物的液體部分作為水熱反應原料,而從固液分離單元5回流至反應槽1。在(e)步驟中使用1.2%之CTAB模板劑,加入6M硫酸將pH值調整至10;且水熱反應的溫度為105℃、水熱反應的時間為12小時。在(f)步驟中使用的固液分離單元係包括:濾網孔徑為100µm的粗過濾板;及濾網孔徑為20µm的細過濾板;又,將水熱反應產物固液分離後的液體回流至反應槽1的頂部。在(g)步驟中,清洗(f)步驟中所分離出之固體,並在110℃的條件下烘乾4小時,在550℃的條件煅燒3小時,獲得量產等級的多孔性材料。Next, the reaction conditions for Example 1 are explained as follows: In the step (a), waste glass is used as the silicon-containing inorganic waste. The Si/Al ratio was set to 20 in step (b). In the step (c), the alkali dose ratio was set to 1.2, the alkali melting temperature was set to 400° C., and the alkali melting reaction time was set to 1 hour. In the (d) step, the liquid-solid ratio is set to 100, the hydrolysis reaction temperature is set to 105° C., and the hydrolysis reaction time is set to 40 minutes; and, after the (d) step, the hydrolysis reaction product is subjected to solid-liquid separation, and the hydrolysis reaction product is separated. The liquid part of the reaction product is returned to the
<比較例1>
各步驟的反應條件與實施例1相同。但是並未使用本發明的連續式流體化床水熱反應裝置,而是使用實驗室等級用的10升(10L)的水熱反應器(加蓋密封的熱水反應器)。又,在比較例1中不進行(d)步驟及(f)步驟的回流。
<Comparative Example 1>
The reaction conditions of each step are the same as in Example 1. However, instead of using the continuous fluidized bed hydrothermal reactor of the present invention, a
<比較例2> 除了不進行(d)步驟(水解反應)後的固液分離以外,其他條件與比較例1相同。將實施例1及比較例1~2的實驗結果顯示於下述表3。 <Comparative Example 2> The other conditions were the same as those in Comparative Example 1, except that the solid-liquid separation after the step (d) (hydrolysis reaction) was not performed. The experimental results of Example 1 and Comparative Examples 1 to 2 are shown in Table 3 below.
[表3]
從表3能夠得知,在使用廢玻璃作為含矽無機廢棄物的情況下,雖然實驗室等級(前述試驗例17~32及比較例1)能夠獲得比表面積較高的沸石,但產率皆未超過60%,且無法實現連續式生產。因此,雖然實施例1的沸石比表面積(300 m 2/g)相較於比較例1(972.24 m 2/g)仍有提升的空間,但實施例1已能實現連續式生產。此外,因為實施例1充分利用水熱合成過程中的各項資源(例如水解反應後溶液、水熱反應後溶液等),故能夠將沸石的產率提升至90.00%。 As can be seen from Table 3, in the case of using waste glass as silicon-containing inorganic waste, although laboratory grades (the aforementioned Test Examples 17 to 32 and Comparative Example 1) can obtain zeolites with higher specific surface areas, the yields are all Less than 60%, and continuous production cannot be achieved. Therefore, although the zeolite specific surface area (300 m 2 /g) of Example 1 still has room for improvement compared to Comparative Example 1 (972.24 m 2 /g), Example 1 has been able to achieve continuous production. In addition, because Example 1 makes full use of various resources in the hydrothermal synthesis process (such as solution after hydrolysis reaction, solution after hydrothermal reaction, etc.), the yield of zeolite can be increased to 90.00%.
又,從實驗室等級的比較例1及比較例2能夠看出,若在水解反應後未進行固液分離,雖然能夠略為提升產率(產率從56.81%提升至68.46%),但有沸石比表面積大幅下降(比表面積從972.24 m 2/g下降為288.12 m 2/g)的情形。因此,吾人預期在量產等級的情況下,若在水解反應後未進行固液分離也會呈現「雖然能夠略為提升產率但沸石比表面積大幅下降」的情形。因此,藉由在水解反應後進行固液分離而去除非所欲的固體雜質,能夠提升最終合成之多孔性材料的比表面積。 In addition, as can be seen from the comparative examples 1 and 2 of the laboratory grade, if the solid-liquid separation is not carried out after the hydrolysis reaction, although the yield can be slightly improved (the yield is increased from 56.81% to 68.46%), there are zeolites. The case where the specific surface area decreased significantly (the specific surface area decreased from 972.24 m 2 /g to 288.12 m 2 /g). Therefore, we expect that in the case of mass production, if the solid-liquid separation is not carried out after the hydrolysis reaction, there will be a situation of "although the yield can be slightly improved, but the specific surface area of zeolite is greatly reduced". Therefore, by performing solid-liquid separation after the hydrolysis reaction to remove undesired solid impurities, the specific surface area of the final synthesized porous material can be increased.
本發明並不限定於上述各實施形態,可在請求項所示之範圍內做各種的變更,且將不同的實施形態中所揭示之技術手段適宜地組合而得之實施形態亦包含在本發明的技術範圍內。The present invention is not limited to the above-described embodiments, and various modifications can be made within the scope of the claims, and embodiments obtained by appropriately combining technical means disclosed in different embodiments are also included in the present invention. within the technical scope.
1:反應槽
11:(直立圓柱形的)槽體
12:(倒圓錐形的)底部
2:投料口
3:出料口
4:加熱元件
5:固液分離單元
51:粗過濾板
52:細過濾板
6:雙向循環泵
7:壓力錶
8:攪拌器
9:熱電偶(熱電偶溫度計)
10:洩壓閥
20:自動控制盤
100, 100’:連續式流體化床水熱反應裝置
a1~a9:開關閥
L1:第一循環管線
L2:第二循環管線
(a)~(g):步驟
1: Reaction tank
11: (upright cylindrical) tank body
12: (inverted conical) bottom
2: Feeding port
3: discharge port
4: Heating element
5: Solid-liquid separation unit
51: Coarse filter plate
52: Fine filter plate
6: Bidirectional circulating pump
7: Pressure gauge
8: Blender
9: Thermocouple (thermocouple thermometer)
10: Pressure relief valve
20:
[圖1]係為本發明一實施例之連續式流體化床水熱反應裝置的示意圖。 [圖2]係為本發明另一實施例之連續式流體化床水熱反應裝置的示意圖。 [圖3]係為本發明一實施例之連續式水熱合成多孔性材料的方法的流程圖。 Fig. 1 is a schematic diagram of a continuous fluidized bed hydrothermal reaction device according to an embodiment of the present invention. [Fig. 2] is a schematic diagram of a continuous fluidized bed hydrothermal reaction device according to another embodiment of the present invention. 3 is a flow chart of a method for continuous hydrothermal synthesis of porous materials according to an embodiment of the present invention.
1:反應槽 1: Reaction tank
11:(直立圓柱形的)槽體 11: (upright cylindrical) tank body
12:(倒圓錐形的)底部 12: (inverted conical) bottom
2:投料口 2: Feeding port
3:出料口 3: discharge port
4:加熱元件 4: Heating element
5:固液分離單元 5: Solid-liquid separation unit
6:雙向循環泵 6: Bidirectional circulating pump
100:連續式流體化床水熱反應裝置 100: Continuous Fluidized Bed Hydrothermal Reactor
a1~a8:開關閥 a1~a8: On-off valve
L1:第一循環管線 L1: The first circulation line
L2:第二循環管線 L2: Second circulation line
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TWI723352B (en) * | 2019-03-13 | 2021-04-01 | 逢甲大學 | Method of incineration ash reused for synthesis of porous materials |
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2020
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