TW202131997A - Porous substance regeneration apparatus - Google Patents
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Abstract
Description
本發明關於多孔性物質再生裝置。The present invention relates to a porous material regeneration device.
先前已知一種水處理裝置,其對於含有有機化合物等污染物質之待處理水,藉由多孔性物質等的吸附材料來吸附污染物質,以將待處理水加以清淨化。吸附有作為被吸附物的污染物質等之吸附材料,例如以加熱的方式來使被吸附物解吸出來而再生。已知一種水處理裝置(例如,後述專利文獻1),其交替地實行這種被吸附物的吸附和解吸。A water treatment device is previously known, which uses an adsorbent such as a porous substance to adsorb the pollutants for the water to be treated containing pollutants such as organic compounds, so as to purify the water to be treated. The adsorbent that has adsorbed contaminants such as the adsorbate is desorbed and regenerated by heating, for example. There is known a water treatment device (for example, Patent Document 1 described later) that alternately performs adsorption and desorption of such adsorbed substances.
[先前技術文獻] (專利文獻) 專利文獻1:日本特開2006-055713號公報[Prior Technical Literature] (Patent Document) Patent Document 1: Japanese Patent Application Publication No. 2006-055713
[發明所欲解決的問題] 專利文獻1中,記載:在水處理裝置的解吸步驟中,使用180℃的空氣作為加熱氣體。但是,依據被吸附於多孔性物質等的吸附材料中的被吸附物的種類,會有在上述溫度也不能夠使被吸附物解吸出來的情況。另一方面,使加熱氣體的溫度高溫化,就必須增大加熱裝置的容量,而會有增加裝置成本和裝置空間的問題。[The problem to be solved by the invention] Patent Document 1 describes that in the desorption step of the water treatment device, air at 180°C is used as the heating gas. However, depending on the type of the adsorbate adsorbed in the adsorbent such as a porous substance, it may not be possible to desorb the adsorbate at the above-mentioned temperature. On the other hand, to increase the temperature of the heating gas, the capacity of the heating device must be increased, which may increase the cost and space of the device.
本發明是鑒於上述問題而完成,其目的在於提供一種多孔性物質再生裝置,能夠在適當溫度下實行多孔性物質的再生,且能夠減少設備成本和設置空間。The present invention was completed in view of the above-mentioned problems, and its object is to provide a porous material regeneration device that can regenerate the porous material at an appropriate temperature, and can reduce equipment cost and installation space.
[解決問題的技術手段] (1)本發明關於一種多孔性物質再生裝置,是將已吸附有被吸附物之多孔性物質進行加熱和再生之多孔性物質再生裝置,具有:多孔性物質槽,其填充有前述多孔性物質;加熱裝置,其加熱第一氣體,該第一氣體以接觸前述多孔性物質的方式在前述多孔性物質槽中流通;及,燃燒裝置,其使在前述多孔性物質的再生時解吸出來的前述被吸附物燃燒;其中,前述多孔性物質的再生時的溫度為300℃~800℃的範圍內,並且,使用在前述燃燒裝置中進行前述被吸附物的燃燒時產生的第二氣體來加熱前述多孔性物質。[Technical means to solve the problem] (1) The present invention relates to a porous material regeneration device, which is a porous material regeneration device that heats and regenerates the porous material that has adsorbed the adsorbate. It has: a porous material tank filled with the aforementioned porous material ; A heating device that heats the first gas, and the first gas circulates in the porous substance tank so as to contact the porous substance; and, a combustion device that desorbs the aforementioned porous substance during the regeneration Burning of the adsorbate; wherein the temperature during the regeneration of the porous material is in the range of 300°C to 800°C, and the second gas generated during the combustion of the adsorbate in the combustion device is used to heat the aforementioned Porous material.
(2)如(1)所述之多孔性物質再生裝置,其中,使前述第二氣體在前述多孔性物質槽中流通,以加熱前述多孔性物質。(2) The porous material regeneration device according to (1), wherein the second gas is circulated in the porous material tank to heat the porous material.
(3)如(1)或(2)所述之多孔性物質再生裝置,其中,前述加熱裝置,包含在前述第二氣體與前述第一氣體之間實行熱交換的熱交換裝置。(3) The porous material regeneration device according to (1) or (2), wherein the heating device includes a heat exchange device that performs heat exchange between the second gas and the first gas.
(4)如(1)至(3)的任一者所述之多孔性物質再生裝置,其中,前述第一氣體含有水蒸氣,且具有使前述水蒸氣產生之水蒸氣產生裝置。(4) The porous material regeneration device according to any one of (1) to (3), wherein the first gas contains water vapor, and has a water vapor generator that generates the water vapor.
(5)如(4)所述之多孔性物質再生裝置,其中,前述第二氣體在前述水蒸氣產生裝置中實行熱交換。(5) The porous material regeneration device according to (4), wherein the second gas is heat exchanged in the water vapor generator.
(6)如(1)至(5)的任一者所述之多孔性物質再生裝置,其中,將與前述被吸附物一起燃燒的燃料,供給到前述燃燒裝置中。(6) The porous material regeneration device according to any one of (1) to (5), wherein the fuel combusted together with the adsorbate is supplied to the combustion device.
(7)如(1)至(6)的任一者所述之多孔性物質再生裝置,其中,前述多孔性物質是活性碳。(7) The porous material regeneration device according to any one of (1) to (6), wherein the porous material is activated carbon.
(8)如(1)至(7)的任一者所述之多孔性物質再生裝置,其中,前述多孔性物質的再生時的溫度,是被吸附於前述多孔性物質中的前述被吸附物開始蒸發和分解的至少一種的溫度以上之溫度,且是未滿前述多孔性物質的因為加熱而開始分解的溫度之溫度。(8) The porous material regeneration device according to any one of (1) to (7), wherein the temperature at the time of regeneration of the porous material is the adsorbate adsorbed in the porous material The temperature above the temperature at which at least one of evaporation and decomposition begins, and is a temperature lower than the temperature at which decomposition of the aforementioned porous material begins due to heating.
(9)如(8)所述之多孔性物質再生裝置,其中,被吸附於前述多孔性物質中的前述被吸附物開始蒸發和開始分解的至少一種的溫度、及前述多孔性物質的因為加熱而開始分解的溫度,是藉由將已吸附有前述被吸附物之前述多孔性物質進行熱重量分析,並測定針對已吸附有前述被吸附物之前述多孔性物質開始重量減少的溫度來決定。(9) The porous material regeneration device according to (8), wherein the temperature at which the adsorbate adsorbed in the porous material starts to evaporate and decompose, and the temperature at which the porous material is heated The temperature at which the decomposition begins is determined by thermogravimetric analysis of the porous material that has adsorbed the adsorbate, and measurement of the temperature at which the porous material that has adsorbed the adsorbate begins to lose weight.
(10)一種水處理裝置,是具備(1)至(9)的任一者所述之多孔性物質再生裝置之水處理裝置,其中,將填充有前述多孔性物質之前述多孔性物質槽,作為可供待處理水流通的吸附層來使用,且前述被吸附物已自該多孔性物質解吸出來。(10) A water treatment device comprising the porous material regeneration device described in any one of (1) to (9), wherein the porous material tank filled with the porous material It is used as an adsorption layer through which the water to be treated can circulate, and the aforementioned adsorbed substance has been desorbed from the porous substance.
[發明的效果] 依據本發明,能夠提供一種多孔性物質再生裝置,能夠在適當溫度下實行多孔性物質的再生,且能夠減少設備成本和設置空間。[Effects of the invention] According to the present invention, it is possible to provide a porous material regeneration device, which can regenerate the porous material at an appropriate temperature, and can reduce equipment cost and installation space.
以下,針對本發明的實施形態進行說明。但是,以下所示的實施形態是用以例示本發明,但是本發明不被限定於以下實施形態。Hereinafter, an embodiment of the present invention will be described. However, the embodiments shown below are for illustrating the present invention, but the present invention is not limited to the following embodiments.
[第一實施形態]
關於本發明的實施形態的多孔性物質再生裝置1,如第1圖所示,具有多孔性物質槽10、加熱裝置11和16、燃燒裝置12、水蒸氣產生裝置13、軟水器14、泵裝置15、及可供液體流通的管線L1、L2、L3、L4、L5。多孔性物質再生裝置1能夠作為水處理裝置來使用,其可進行多孔性物質的再生,並且使用再生後的多孔性物質來進行現場(on‐site)的水處理,該多孔性物質可用於待處理物的吸附。[First Embodiment]
Regarding the porous material regeneration device 1 of the embodiment of the present invention, as shown in Figure 1, it has a
多孔性物質槽10,是填充有多孔性物質之槽。被填充在多孔性物質槽10中的多孔性物質,被用於自待處理水中吸附有機化合物等被吸附物來將待處理水加以處理之水處理,而吸附有上述被吸附物。使第一氣體在多孔性物質槽10中流通,藉此實行被吸附物的蒸發和分解之中的至少一種,以使被吸附物自多孔性物質解吸出來,而使多孔性物質能夠再生。另外,本說明書中,「解吸」是表示與「吸附」相反的概念,是指藉由蒸發和分解等現象來使對象自物體表面脫離。待處理水可在多孔性物質槽10中流通,在實行多孔性物質的再生之後,能夠用作在水處理中的吸附槽。The
作為多孔性物質,舉出例如活性碳等碳質材料、沸石、氧化鋁、氧化鈦、氧化鋯、氧化矽等的無機質材料。作為多孔性物質,較佳為使用活性碳。作為活性碳沒有特別限制,可適用源自石碳、源自石油、源自生質等的活性碳。作為形狀沒有特別限制,可使用具有粉狀、粒狀、成形品、纖維等形狀的物質。作為上述多孔性物質,也可以使用混合兩種以上的物質。Examples of the porous substance include carbonaceous materials such as activated carbon, and inorganic materials such as zeolite, alumina, titanium oxide, zirconium oxide, and silica. As the porous substance, activated carbon is preferably used. The activated carbon is not particularly limited, and activated carbon derived from fossil carbon, petroleum, biomass, etc. can be applied. The shape is not particularly limited, and those having shapes such as powder, granules, molded products, fibers, etc. can be used. As the above-mentioned porous material, a mixture of two or more types can also be used.
作為被吸附物,舉出例如碳水化合物、含氧化合物、含氮化合物、含硫化合物、及鹵素化合物等的有機化合物。關於本實施形態的多孔性物質再生裝置1,能夠使被吸附物自多孔性物質解吸出來,該被吸附物具有未滿100℃的沸點。作為上述被吸附物沒有特別限制,舉出例如苯(沸點80℃左右)、三氯乙烯(沸點87℃左右)等。關於本實施形態的多孔性物質再生裝置1,能夠在適當溫度下實行被填充在多孔性物質槽10中的多孔性物質的再生。因此,即便在作為被吸附物包含有例如具有100℃以上或200℃以上的沸點的有機化合物的情況,也能夠實行被吸附物的解吸。作為上述有機化合物沒有特別限制,舉出例如1,4-二噁烷(沸點101℃左右)、三乙二醇(沸點285℃左右)、石碳酸(沸點182℃左右)、對特辛基苯酚(沸點280℃左右)、聚乙二醇、十二烷基苯磺酸鈉等。Examples of the adsorbate include organic compounds such as carbohydrates, oxygen-containing compounds, nitrogen-containing compounds, sulfur-containing compounds, and halogen compounds. Regarding the porous material regeneration device 1 of the present embodiment, the adsorbed material can be desorbed from the porous material, and the adsorbed material has a boiling point of less than 100°C. The adsorbent is not particularly limited, and examples include benzene (boiling point around 80°C), trichloroethylene (boiling point around 87°C), and the like. Regarding the porous material regeneration device 1 of this embodiment, the porous material filled in the
在多孔性物質槽10中,第一氣體以接觸前述多孔性物質的方式流通。
第一氣體,例如是下述之中的至少一種:水蒸氣;氮氣;二氧化碳;氦氣、氬氣等稀有氣體;及,氟氯烷等惰性氣體。也可以是上述2種以上的氣體混合而成。在第一氣體中,較佳是含有水蒸氣。在第一氣體中含有水蒸氣,而藉由後述水蒸氣氣化反應,來促進由被吸附物質的分解所造成的解吸。以下說明中,以在第一氣體中含有水蒸氣來進行說明。較佳為在上述中,再加上第一氣體實質上不含有氧氣。例如,較佳為在第一氣體中含有的氧氣是0.01體積%以下。藉由上述,能夠使用與氧氣反應會劣化之活性碳等碳質材料來作為多孔性物質。In the
第一氣體被加熱並使其接觸多孔性物質,藉此,被吸附物被加熱而自多孔性物質解吸出來。當第一氣體含有水蒸氣時,考慮到水蒸氣與被吸附於多孔性物質中的被吸附物會產生由下述化學式(1)所示的水蒸氣氣化反應、及由化學式(2)所示的轉化反應,以分解被吸附物。 Cn Hm +nH2 O=nCO+(n+m/2)H2 (1) nCO+nH2 O=nCO2 +nH2 (2)The first gas is heated and brought into contact with the porous substance, whereby the adsorbate is heated and desorbed from the porous substance. When the first gas contains water vapor, it is considered that the water vapor and the adsorbate adsorbed in the porous material will produce the water vapor vaporization reaction shown by the following chemical formula (1), and the chemical formula (2) The conversion reaction shown to decompose the adsorbate. C n H m +nH 2 O=nCO+(n+m/2)H 2 (1) nCO+nH 2 O=nCO 2 +nH 2 (2)
多孔性物質的再生時的溫度,在本實施形態中為300℃~800℃。上述再生時的溫度,較佳為例如400℃以上,更佳為500℃以上。又,較佳為700℃以下。多孔性物質的再生時的溫度滿足上述條件,藉此,在再生時能夠使大多的被吸附物解吸出來。又,當多孔性物質是活性碳時,能夠抑制由於活性碳的活化而造成的重量減少。The temperature during the regeneration of the porous material is 300°C to 800°C in this embodiment. The temperature during the regeneration is preferably, for example, 400°C or higher, and more preferably 500°C or higher. Furthermore, it is preferably 700°C or lower. The temperature during the regeneration of the porous material satisfies the above-mentioned conditions, whereby most of the adsorbed substances can be desorbed during the regeneration. In addition, when the porous material is activated carbon, the weight loss due to activation of activated carbon can be suppressed.
被填充在多孔性物質槽10中的多孔性物質的再生時的溫度,較佳為被吸附物開始蒸發和分解之中的至少一種並藉此進行解吸的溫度以上之溫度。使被吸附於多孔性物質中的被吸附物解吸出來的溫度,是被吸附物的沸點以上的溫度。例如,當將對特辛基苯酚(沸點280℃左右)作為被吸附物,使作為已吸附有該被吸附物之多孔性物質的活性碳再生時,即便將活性碳的再生時的溫度設為例如280℃時,也不能夠實行活性碳的再生。這被認為是因為被吸附物藉由分子間力和依據情況而形成化學鍵,並被吸附在活性碳等多孔性物質中的細微孔中。又,多孔性物質的再生時的溫度,較佳為未滿多孔性物質的因為加熱而開始分解的溫度之溫度。當多孔性物質例如是活性碳時,依據被吸附物質的種類會使活性碳開始分解的溫度有所變動。The temperature at the time of regeneration of the porous substance filled in the
上述使被吸附物解吸出來的溫度及使多孔性物質開始分解的溫度,較佳為藉由熱重量分析來決定。熱重量分析,能夠藉由測定例如在規定的溫度範圍,例如自室溫至1000℃之間的已吸附有被吸附物之多孔性物質的重量變化來實行。熱重量分析,能夠使用例如熱重量分析裝置(TGA,Thermogravimetric analysis)和熱重量-熱示差同時測定裝置(TG-DTA,Thermogravimetric-Differential thermal analysis)來實行。另外,熱重量分析,能夠在氮氣、氬氣、空氣、水蒸氣等氣氛下實行。因為要測定多孔性物質的因為加熱而被分解的溫度,所以較佳為在水蒸氣氣氛下實行分析。The temperature at which the adsorbate is desorbed and the temperature at which the porous material starts to decompose are preferably determined by thermogravimetric analysis. Thermogravimetric analysis can be carried out by measuring, for example, the weight change of the porous material that has adsorbed the adsorbate in a predetermined temperature range, for example, from room temperature to 1000°C. Thermogravimetric analysis can be performed using, for example, a thermogravimetric analysis device (TGA, Thermogravimetric analysis) and a thermogravimetric-thermal differential simultaneous measurement device (TG-DTA, Thermogravimetric-Differential thermal analysis). In addition, thermogravimetric analysis can be performed in an atmosphere such as nitrogen, argon, air, and water vapor. Since the temperature at which the porous material is decomposed by heating is to be measured, it is better to perform the analysis in a water vapor atmosphere.
多孔性物質的再生時的溫度,藉由上述熱重量分析裝置來分析,並基於被吸附物開始蒸發和分解之中的至少一種的溫度、及多孔性物質的因為加熱而開始分解的溫度來決定。例如,在多孔性物質槽10中流通的第一氣體的溫度,基於藉由被吸附物開始蒸發和分解之中的至少一種的溫度來決定,該溫度是藉由上述熱重量分析來求得。The temperature at the time of the regeneration of the porous material is analyzed by the above-mentioned thermogravimetric analysis device, and is determined based on the temperature of at least one of the evaporation and decomposition of the adsorbate and the temperature at which the porous material starts to decompose due to heating . For example, the temperature of the first gas circulating in the
加熱裝置11和16,是加熱第一氣體的裝置。加熱裝置11沒有特別限制,例如是可通電並加熱的電氣式加熱器裝置。加熱裝置11,當第一氣體是水蒸氣時,加熱水蒸氣而產生規定溫度的過熱水蒸氣。加熱裝置16是熱交換裝置,且被設置在加熱裝置11的上游側。加熱裝置16,使後述第二氣體與第一氣體進行熱交換,以加熱第一氣體。作為加熱裝置16而使用的熱交換裝置沒有特別限制,舉出二重管式、套管式、殼管式、螺旋式、板式等熱交換裝置。The
燃燒裝置12,使在多孔性物質的再生時解吸出來的被吸附物燃燒。作為燃燒裝置12沒有特別限制,能夠使用例如直接燃燒裝置和觸媒燃燒裝置等。燃燒裝置12,具備燃燒器裝置,將自外部導入的空氣與有機化合物等被吸附物混合並使其燃燒。燃燒裝置12,也可以具備可導入空氣的鼓風機。藉由上述燃燒來將被吸附物分解成CO2
和H2
O,而加以除臭和無害化。自上述燃燒裝置12排出的排出氣體也就是第二氣體是高溫的,會在作為熱交換裝置之加熱裝置16中,與第一氣體進行熱交換。The
水蒸氣產生裝置13,是產生作為第一氣體的水蒸氣之裝置。水蒸氣產生裝置13,例如是鍋爐裝置,可使燃料燃燒以產生熱。水蒸氣產生裝置,具備熱交換裝置,在所產生的熱與水之間實行熱交換,使水氣化而產生水蒸氣。作為水蒸氣產生裝置13之鍋爐裝置,也可以包含燃燒室和送風機等。作為這種鍋爐裝置沒有特別限制,能夠使用習知的裝置。The
軟水器14,可除去原水中的硬度成分並加以軟水化。軟水器14,具備例如離子交換樹脂。離子交換樹脂,可吸附原水中所包含的Ca離子和Mg離子等硬度成分,並放出自身具有的Na離子等來取代,以將原水加以軟水化。藉此,能夠抑制對於管線L1產生水垢(scale)。作為這種軟水器14,能夠使用習知的裝置。The
泵裝置15,可將待處理水往多孔性物質槽10壓送並流通。當藉由泵裝置15使得待處理水在多孔性物質槽10中流通時,多孔性物質槽10可用作水處理中的吸附槽。作為泵裝置15沒有特別限制,只要能夠壓送液體即可,舉出例如渦流式等離心泵、隔膜泵等容積(變化)式泵等。The
(使用多孔性物質再生裝置1之多孔性物質的再生方法)
管線L1,如第1圖所示,是第一氣體流通的路徑。在管線L1中,自上游側依序設置有軟水器14、水蒸氣產生裝置13、加熱裝置16、加熱裝置11。自來水等的水,通過管線L1往軟水器14流通。在管線L1中,也可以設置將水往軟水器14壓送的泵裝置(省略圖示)。通過軟水器14而軟水化後的水,流入水蒸氣產生裝置13中,被氣化成作為第一氣體的水蒸氣。所產生的水蒸氣,藉由加熱裝置16和加熱裝置11而被加熱到沸點以上,成為例如300℃以上的過熱水蒸氣。使上述過熱水蒸氣在多孔性物質槽10中流通,使被吸附於多孔性物質中的被吸附物解吸出來,以使多孔性物質再生。(Method of Regenerating Porous Substance Using Porous Substance Regenerating Device 1)
The line L1, as shown in Fig. 1, is a path through which the first gas flows. In the pipeline L1, a
管線L2,是自多孔性物質槽10排出的氣體流通的路徑。管線L2的上游側與多孔性物質槽10連接。在管線L2上,設置有燃燒裝置12。自多孔性物質槽10排出的氣體中,含有水蒸氣、及自多孔性物質解吸出來的被吸附物。在被吸附物中含有有機化合物等,若未處理而往外部排出則為不佳。因此,自多孔性物質槽10排出的氣體,通過管線L2往燃燒裝置12流入,與空氣混合並燃燒。藉此,將被吸附物加以除臭和無害化。The line L2 is a path through which the gas discharged from the
管線L3,是自燃燒裝置12排出的第二氣體流通的路徑。管線L3的上游側與燃燒裝置12連接。在管線L3中,設置有熱交換裝置也就是加熱裝置16。第二氣體是高溫的氣體,其包含使被吸附物燃燒並分解而產生的氣體、及水蒸氣。在加熱裝置16中,第一氣體與比第一氣體更高溫的第二氣體進行熱交換。亦即,使用第二氣體,間接地對多孔性物質進行加熱。在管線L3中實行熱交換之後的第二氣體,因為還具有熱量,所以也可以與其他系統實行熱調節(heat accommodation),因為已被除臭和無害化,所以也可以往外部排出。The line L3 is a path through which the second gas discharged from the
(排水處理方法)
接著,針對將多孔性物質槽10用作吸附槽並實行排水處理的方法進行說明,填充在該多孔性物質槽10中的多孔性物質已藉由上述再生方法而再生。
管線L4,如第1圖所示,是待處理水流通的路徑。在管線L4中,設置有泵裝置15。例如含有有機化合物之待處理水,藉由泵裝置15被壓送,通過管線L4而流入用作吸附槽之多孔性物質槽10。上述待處理水中所含有的有機化合物等的被吸附物,被吸附在已填充於作為吸附槽的多孔性物質槽10中的多孔性物質中,藉此,實行水處理。在被吸附物被吸附之後的無害化後的經處理水,通過管線L5而被排出到例如外部。(Drainage treatment method)
Next, a method of using the
依據關於上述第一實施形態的多孔性物質再生裝置1,可發揮以下效果。在多孔性物質再生裝置1中,對於已填充有多孔性物質(已吸附有被吸附物)之多孔性物質槽10,使被加熱後的第一氣體流通以使被吸附物解吸出來,以使多孔性物質再生,並且,使用解吸出來的被吸附物燃燒時所產生的第二氣體來加熱多孔性物質。藉由上述,利用第二氣體具有的熱能量來加熱第一氣體,能夠間接地加熱多孔性物質,所以能夠減少多孔性物質的再生所需要的能量消耗。又,能夠抑制加熱裝置11的裝置成本和設置空間,且將多孔性物質的再生時的溫度設為適合被吸附物的解吸之適當溫度。According to the porous material regeneration device 1 of the first embodiment described above, the following effects can be exhibited. In the porous material regeneration device 1, for the
[第二實施形態]
接著,針對關於本發明的第二實施形態的多孔性物質再生裝置1a進行說明。以下說明中,對於與已說明的實施形態同樣的構成,會有省略說明的情況。[Second Embodiment]
Next, a description will be given of the porous
多孔性物質再生裝置1a,如第2圖所示,具有加熱裝置11a和11b。加熱裝置11a和11b,與加熱裝置11同樣,是可通電並加熱的電熱式加熱器裝置。加熱裝置11a,與加熱裝置11同樣,被設置在管線L1上並加熱第一氣體。加熱裝置11b,被設置在多孔性物質槽10的外側並加熱多孔性物質槽10。The porous
依據第二實施形態的多孔性物質再生裝置1a,可發揮以下效果。除了加熱裝置11a,再追加設置可對多孔性物質槽直接加熱的加熱裝置11b,藉此能夠將第一氣體的溫度設為適合被吸附物的解吸之高溫的氣體。又,當對於將多孔性物質槽10作為吸附槽使用之後的殘存有水分的狀態的多孔性物質進行加熱時,為了實行水分的氣化而成為需要大量的熱量。藉由加熱裝置11b,能夠自加熱裝置11b直接地賦予上述的氣化需要的熱,所以能夠減少能量成本。又,使多孔性物質中殘存的水分氣化,藉此促進被吸附物的解吸。According to the porous
[第三實施形態]
關於第三實施形態的多孔性物質再生裝置1b,如第3圖所示,具有燃燒裝置12a、及加熱裝置16a。
如第3圖所示,燃料與空氣一起供給到燃燒裝置12a中。這種燃燒裝置12a,例如是直接燃燒裝置。作為上述燃料沒有特別限制,可使用例如燈油、重油、輕油等液體燃料、或者液化天然氣(LNG,Liquefied Natural Gas)、液化石油氣(LPG,Liquefied Petroleum Gas)等氣體燃料。上述燃料,與當多孔性物質的再生時解吸出來的被吸附物一起燃燒。藉由燃燒裝置12a,能夠將自燃燒裝置12a排出的第二氣體設為更高溫。[Third Embodiment]
The porous material regeneration device 1b of the third embodiment has a
加熱裝置16a是熱交換裝置,可供自燃燒裝置12a排出的第二氣體流通。在加熱裝置16a中流通的第二氣體,是比關於第一實施形態和第二實施形態的第二氣體更高溫。因此,即便在管線L1上不設置其他加熱裝置,也能夠藉由第二氣體與第一氣體的熱交換來充分地加熱第一氣體。The
依據關於上述第三實施形態的多孔性物質再生裝置1b,可發揮以下效果。將多孔性物質再生裝置1b構成為設置有燃燒裝置12a,燃料與空氣一起供給到該燃燒裝置12a中並與被吸附物一起燃燒。藉此,能夠將自燃燒裝置12a產生的第二氣體加以高溫化。因此,能夠僅使用加熱裝置16a來實行第二氣體與第一氣體的熱交換並加熱第一氣體,所以能夠減少多孔性物質再生裝置的設置空間。According to the porous material regeneration device 1b of the third embodiment described above, the following effects can be exhibited. The porous material regeneration device 1b is configured to include a
[第四實施形態]
關於第四實施形態的多孔性物質再生裝置1c,如第4圖所示,具有多孔性物質槽10a。又,具有與第三實施形態同樣的燃燒裝置12a、及加熱裝置16a。[Fourth Embodiment]
As shown in Fig. 4, the porous material regeneration device 1c of the fourth embodiment has a
多孔性物質槽10a,如第4圖所示,可供第一氣體和待處理水流通,並且可供第二氣體流通。第7圖是表示多孔性物質槽10a的構成的縱向剖面圖。如第7圖所示,多孔性物質槽10a,具有填充部101、導熱管102、及套管103。The
填充部101,是填充有作為多孔性物質的例如活性碳的處所。在填充部101中,第一氣體和待處理水可通過入口部101a而流入,並通過出口部101b而流出。作為第一氣體的水蒸氣,以與活性碳直接接觸的方式在填充部101中流通,藉此使被吸附物自活性碳解吸出來。待處理水,以與活性碳直接接觸的方式在填充部101中流通,藉此使含有的被吸附物被吸附於活性碳而被淨化,並作為經處理水而被排出到外部。The filling
導熱管102,是可供自燃燒裝置12a排出的第二氣體流通的管子。如第7圖所示,導熱管102具有在填充部101內流通的複數條折返流路。上述流路,也可以在填充部101的內部具有分歧處。第8圖是第7圖中的A-A’剖線的剖面圖。如第8圖所示,導熱管102遍及整個填充部101而流通。第二氣體可通過導熱管入口102a而流入導熱管102,並通過導熱管出口102b而自導熱管102流出。具有高溫的第二氣體在導熱管102中流通,藉此能夠加熱被填充在填充部101中的多孔性物質。導熱管102的材質沒有特別限制,可使用例如不銹鋼材(SUS)、鈦、銅等。The
套管103,與導熱管102同樣,是可供自燃燒裝置12a排出的第二氣體流通的流路。如第7圖和第8圖所示,套管103以覆蓋填充部101的周圍的方式形成。第二氣體可通過套管入口103a而流入套管103,並通過套管出口103b而自套管103流出。除了導熱管102,再追加套管103來使第二氣體流通,藉此能夠對於被填充在填充部101中的多孔性物質賦予更多的熱量。The
(使用多孔性物質再生裝置1c的多孔性物質的再生方法) 多孔性物質再生裝置1c的管線L1和管線L2,具有與第一實施形態同樣的構成,所以省略說明。管線L31和管線L32,是可供第二氣體流通的路徑。(Method of Regenerating Porous Material Using Porous Material Regenerating Device 1c) The pipeline L1 and the pipeline L2 of the porous substance regenerating device 1c have the same configuration as that of the first embodiment, so the description is omitted. The line L31 and the line L32 are paths through which the second gas can circulate.
管線L31,是連接燃燒裝置12a與多孔性物質槽10a的路徑。管線L31的上游側,與燃燒裝置12a連接。管線L31的下游側,與多孔性物質槽10a的導熱管入口102a和套管入口103a連接。例如,當對於將多孔性物質槽10a作為吸附槽使用之後的殘存有水分的狀態的多孔性物質進行加熱時,需要大量的熱量,所以能夠使第二氣體在導熱管102和套管103中流通並加熱多孔性物質。當沒有殘存的水分之後,也可以使第二氣體在導熱管102和套管103之中的任一方中流通並加熱多孔性物質。The line L31 is a path connecting the
管線L32,是多孔性物質槽10a的下游側的路徑。管線L32的上游側,與多孔性物質槽10a的導熱管出口102b和套管出口103b連接。在管線L32中,設置有加熱裝置16a來作為熱交換裝置。因為自燃燒裝置12a排出的第二氣體仍具有大量的熱量,所以能夠在加熱裝置16a中與第一氣體實行熱交換,藉此加熱第一氣體。The line L32 is a path on the downstream side of the
[第五實施形態]
關於第五實施形態的多孔性物質再生裝置1d,如第5圖所示,具有水蒸氣產生裝置13a。又,具有與第四實施形態同樣的多孔性物質槽10a、燃燒裝置12a、及加熱裝置16a。[Fifth Embodiment]
Regarding the porous
多孔性物質再生裝置1d,在多孔性物質槽10a的下游側的路徑也就是管線L32中,除了加熱裝置16a之外,再追加設置水蒸氣產生裝置13a。
水蒸氣產生裝置13a,可供第二氣體流通,且實行第二氣體與水的熱交換,藉此使水氣化而產生作為第一氣體的水蒸氣。自加熱裝置16a流出的第二氣體,即便在實行與第一氣體的熱交換之後,仍具有充分的熱量。因此,在加熱裝置16a的下游側設置水蒸氣產生裝置13a,藉此能夠自第二氣體進一步實行熱回收。因此,能夠進一步減少多孔性物質的再生所需要的能量成本。In the porous
[第六實施形態]
關於第六實施形態的多孔性物質再生裝置1e,如第6圖所示,具有與第五實施形態同樣的多孔性物質槽10a、燃燒裝置12a、水蒸氣產生裝置13a、及加熱裝置16a。[Sixth Embodiment]
Regarding the porous
多孔性物質再生裝置1e,在多孔性物質槽10a的上游側的路徑也就是管線L31中,設置有熱交換裝置也就是加熱裝置16a。管線L31的上游側,與燃燒裝置12a連接。自燃燒裝置12a排出的第二氣體,會有例如800℃以上的高溫的情況。因此,沒有使第二氣體直接流通到多孔性物質槽10a中,而是在熱交換裝置也就是加熱裝置16a中與第一氣體實行熱交換之後再流通到多孔性物質槽10a中。藉由上述,能夠控制流通到多孔性物質槽10a中的第二氣體的溫度,而能夠將多孔性物質的再生時的溫度設為適當溫度。In the porous
以上,對於本發明的較佳實施形態進行說明。但是,本發明不限定於上述實施形態,在不損害本發明的效果的範圍內可進行適當的變化。Above, the preferred embodiment of the present invention has been described. However, the present invention is not limited to the above-mentioned embodiment, and can be appropriately changed within a range that does not impair the effects of the present invention.
關於上述實施形態的多孔性物質再生裝置,以具有單一的多孔性物質槽10或10a進行說明。但是,不限定於上述。多孔性物質再生裝置,也可以具有複數個多孔性物質槽。例如,能夠設置2個多孔性物質槽。藉由上述,在使用1個多孔性物質槽來實行水處理的期間,使用其他的多孔性物質槽來實行多孔性物質的再生、或維修,而能夠連續地實行水處理。又,當待處理水的負荷暫時地增大時,使待處理水流通到複數個多孔性物質槽中而並行地實行水處理,藉此能夠暫時地提升水處理能力。除了上述之外,也能夠將多孔性物質槽設為3個或其以上的數目。藉此,能夠確保水處理中的儲備能力(reserve capacity),所以即便在待處理水的負荷的變動激烈的情況也能夠實行水處理。The porous material regenerating device of the above-mentioned embodiment will be described with a single
[多孔性物質再生試驗] 對於在關於上述實施形態的多孔性物質再生裝置中使用的多孔性物質,利用以下方法來實行多孔性物質的再生試驗。[Porous material regeneration test] Regarding the porous material used in the porous material regeneration device of the above-mentioned embodiment, the porous material regeneration test was carried out by the following method.
(定溫熱分析試驗) 對於作為多孔性物質的活性碳,使用十二烷基苯磺酸鈉(以下記載為「ABS」)和聚乙二醇(分子量4000,以下記載為「PEG」)作為被吸附物,使用已吸附有規定量的該被吸附物之該活性碳,作為試驗用的樣本。使用20%水蒸氣、80%氮氣的混合氣體(水蒸氣分壓20.2kPa),作為第一氣體。溫度條件,自70~80℃附近的溫度以10℃/分鐘的升溫速度,升溫到在以下表1中各自表示的規定溫度,並以保持在各自的規定溫度下合計2小時的方式實行。(Constant temperature thermal analysis test) For the activated carbon as a porous material, sodium dodecylbenzene sulfonate (hereinafter referred to as "ABS") and polyethylene glycol (molecular weight 4000, hereinafter referred to as "PEG") are used as the adsorbent, and the adsorbed material is used. The activated carbon with a prescribed amount of the adsorbate is used as a sample for the test. A mixed gas of 20% water vapor and 80% nitrogen (water vapor partial pressure 20.2 kPa) is used as the first gas. The temperature conditions were performed from a temperature in the vicinity of 70 to 80°C at a temperature increase rate of 10°C/min to the respective specified temperatures shown in Table 1 below, and maintained at the respective specified temperatures for a total of 2 hours.
在上述定溫熱分析試驗中,以解吸出來的被吸附物的重量除以被吸附物的初期重量,來定義活性碳的再生率R。具體來說,藉由以下算式(3)來求得活性碳的再生率R。另外,假設在已吸附有ABS之活性碳中,會殘留有ABS所含有的硫酸鈉,並求得再生率R。 再生率R=(Wdry -Wt )/(Wdry ×A/100)×100 (3) 此處,算式中的記號如下所示。 R :處理時間t時的再生率(%) Wdry :乾燥試料重量(mg) Wt :處理時間t時的試料重量(mg) A :被吸附物的初期吸附率(wt%)In the above constant temperature thermal analysis test, the weight of the desorbed adsorbate is divided by the initial weight of the adsorbate to define the regeneration rate R of activated carbon. Specifically, the regeneration rate R of activated carbon is obtained by the following formula (3). In addition, suppose that the sodium sulfate contained in ABS remains in the activated carbon that has adsorbed ABS, and the regeneration rate R is obtained. Regeneration rate R=(W dry -W t )/(W dry ×A/100)×100 (3) Here, the symbols in the formula are as follows. R: Regeneration rate (%) at treatment time t W dry : Dry sample weight (mg) W t : Sample weight at treatment time t (mg) A: Initial adsorption rate of adsorbate (wt%)
以下表1和第9圖中,表示被吸附物是ABS之活性碳的再生率R。以下表2和第10圖中,表示被吸附物是PEG之活性碳的再生率R。The following Table 1 and Figure 9 show the regeneration rate R of activated carbon in which the adsorbate is ABS. The following Table 2 and Figure 10 show the regeneration rate R of activated carbon in which the adsorbate is PEG.
[表1] [Table 1]
[表2] [Table 2]
若參照表1和第9圖,則吸附有ABS之活性碳,在450℃的條件實行120分鐘的再生的情況的再生率R是83.5%,在500℃的條件下120分鐘後的再生後的再生率R達到100%。在550℃的條件下30分鐘後的再生後的再生率R達到100%。因此,即便是將活性碳的再生時的溫度設為ABS的沸點(約205℃)以上的情況,也表示不能夠藉由再生溫度在短時間使活性碳完全再生的結果。If referring to Table 1 and Figure 9, the regeneration rate R is 83.5% when the activated carbon with ABS is adsorbed and the regeneration is performed at 450°C for 120 minutes, and the regeneration rate R is 83.5% after the regeneration at 500°C for 120 minutes. The regeneration rate R reaches 100%. The regeneration rate R after regeneration after 30 minutes under the condition of 550°C reached 100%. Therefore, even if the temperature during the regeneration of activated carbon is set to the boiling point of ABS (about 205° C.) or higher, it means that the activated carbon cannot be completely regenerated in a short time at the regeneration temperature.
若參照表2和第10圖,則吸附有PEG之活性碳,在350℃的條件實行30分鐘的再生的情況的再生率R是86.5%,60分鐘的再生後的再生率R是100%。在400℃的條件下5分鐘後的再生率R達到100%。因此,藉由與表1和第9圖得比較,表示依據活性碳的被吸附物的種類會使得較佳的再生溫度不同的結果。Referring to Table 2 and Figure 10, the regeneration rate R of the case where the activated carbon with PEG is adsorbed and the regeneration is performed at 350°C for 30 minutes is 86.5%, and the regeneration rate R after 60 minutes of regeneration is 100%. The regeneration rate R reaches 100% after 5 minutes at 400°C. Therefore, the comparison with Table 1 and Figure 9 shows that the optimal regeneration temperature is different depending on the type of the adsorbed substance of the activated carbon.
(升溫熱分析試驗)
使用活性碳(石碳的碎碳,標準粒度8/32網目,比表面積965m2
/g)作為多孔性物質的活性碳,準備上述活性碳並實行水處理的實地使用而成為已吸附有被吸附物的狀態。使用20%水蒸氣、80%氮氣的混合氣體(水蒸氣分壓20.2kPa),作為第一氣體。升溫條件,自70~80℃附近的溫度以10℃/分鐘的升溫速度,升溫到在1000℃。在第11圖中表示結果。(Temperature temperature analysis test) Use activated carbon (stone carbon broken carbon,
第11圖是表示上述升溫熱分析試驗的結果的圖表。第11圖中,橫軸表示溫度(℃),縱軸表示重量(mg)。第11圖中,以實線來表示樣本的溫度變化。如第11圖所示,首先在自升溫開始後不久的80℃附近至100℃附近的溫度帶,呈現重量減少。考慮到這是因為在活性碳中含有的水分的蒸發所導致。接著,在溫度T1表示重量減少的開始。考慮到這是因為被吸附於活性碳的被吸附物的蒸發和分解之中的至少一者造成的被吸附物的解吸所導致。上述重量減少,持續直到成為溫度T2,其以後的重量變化呈現固定值。考慮到這是因為被吸附於活性碳的被吸附物已全部解吸出來所導致。接著,在溫度T3表示重量減少的開始。考慮到這是活性碳的因為活化造成的分解所導致。Fig. 11 is a graph showing the results of the above-mentioned temperature-rising thermal analysis test. In Figure 11, the horizontal axis represents temperature (°C), and the vertical axis represents weight (mg). In Figure 11, the temperature change of the sample is represented by a solid line. As shown in Fig. 11, first, the weight decreases in the temperature range from around 80°C to around 100°C immediately after the start of the temperature increase. It is considered that this is caused by the evaporation of water contained in the activated carbon. Next, the temperature T1 indicates the start of weight loss. It is considered that this is caused by the desorption of the adsorbate caused by at least one of the evaporation and decomposition of the adsorbate adsorbed on the activated carbon. The above-mentioned weight reduction continues until the temperature T2 is reached, and the weight change thereafter assumes a fixed value. It is considered that this is because the adsorbate adsorbed on the activated carbon has all been desorbed. Next, the temperature T3 indicates the start of weight loss. It is considered that this is caused by the decomposition of activated carbon due to activation.
藉由上述分析結果,將活性碳的再生時的溫度,設為T1以上的溫度和未滿溫度T3的溫度,該T1是被吸附物開始蒸發和分解之中的至少一種的溫度,該T3是活性碳的因為活化而開始分解的溫度,藉此確認到能夠實行被吸附物的解吸,且在活性碳沒有因為活化而分解的情況使活性碳再生。Based on the above analysis results, the temperature during the regeneration of activated carbon is set to a temperature above T1 and a temperature below T3, where T1 is the temperature at which the adsorbate starts to evaporate and decompose, and T3 is The temperature at which the activated carbon starts to decompose due to activation, thereby confirming that the desorption of the adsorbate can be performed, and the activated carbon is regenerated when the activated carbon is not decomposed due to the activation.
1,1a,1b,1c,1d,1e:多孔性物質再生裝置(水處理裝置)
10,10a:多孔性物質槽(吸附槽)
11,11a,11b:加熱裝置(加熱器裝置)
12,12a:燃燒裝置
13,13a:水蒸氣產生裝置(鍋爐)
14:軟水器
15:泵裝置
16,16a:加熱裝置(熱交換裝置)
101:填充部
101a:入口部
101b:出口部
102:導熱管
102a:導熱管入口
102b:導熱管出口
103:套管
103a:套管入口
103b:套管出口
L1,L2,L3,L4,L5,L31,L32:管線1,1a,1b,1c,1d,1e: Porous material regeneration device (water treatment device)
10, 10a: Porous substance tank (adsorption tank)
11, 11a, 11b: heating device (heater device)
12, 12a:
第1圖是表示關於本發明的第一實施形態的多孔性物質再生裝置的構成的圖。 第2圖是表示關於本發明的第二實施形態的多孔性物質再生裝置的構成的圖。 第3圖是表示關於本發明的第三實施形態的多孔性物質再生裝置的構成的圖。 第4圖是表示關於本發明的第四實施形態的多孔性物質再生裝置的構成的圖。 第5圖是表示關於本發明的第五實施形態的多孔性物質再生裝置的構成的圖。 第6圖是表示關於本發明的第六實施形態的多孔性物質再生裝置的構成的圖。 第7圖是表示關於本發明的實施形態的多孔性物質槽的縱向剖面圖。 第8圖是沿著第7圖的多孔性物質槽中的A-A’剖線的剖面圖。 第9圖是表示已吸附有被吸附物之活性碳的定溫熱分析結果的圖表。 第10圖是表示已吸附有被吸附物之活性碳的定溫熱分析結果的圖表。 第11圖是表示已吸附有被吸附物之活性碳的升溫熱分析結果的圖表。Fig. 1 is a diagram showing the configuration of a porous material regeneration device according to a first embodiment of the present invention. Fig. 2 is a diagram showing the configuration of a porous material regeneration device related to a second embodiment of the present invention. Fig. 3 is a diagram showing the configuration of a porous material regeneration device according to a third embodiment of the present invention. Fig. 4 is a diagram showing the configuration of a porous material regenerating device according to a fourth embodiment of the present invention. Fig. 5 is a diagram showing the configuration of a porous material regenerating device according to a fifth embodiment of the present invention. Fig. 6 is a diagram showing the structure of a porous material regenerating device according to a sixth embodiment of the present invention. Fig. 7 is a longitudinal cross-sectional view showing a porous material tank according to an embodiment of the present invention. Fig. 8 is a cross-sectional view taken along the line A-A' in the porous material tank of Fig. 7; Figure 9 is a graph showing the result of constant temperature thermal analysis of activated carbon that has adsorbed substances. Fig. 10 is a graph showing the result of constant temperature thermal analysis of activated carbon on which adsorbate has been adsorbed. Fig. 11 is a graph showing the result of temperature increase thermal analysis of activated carbon on which the adsorbate has been adsorbed.
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1:多孔性物質再生裝置(水處理裝置) 1: Porous material regeneration device (water treatment device)
10:多孔性物質槽(吸附槽) 10: Porous substance tank (adsorption tank)
11:加熱裝置(加熱器裝置) 11: Heating device (heater device)
12:燃燒裝置 12: Combustion device
13:水蒸氣產生裝置(鍋爐) 13: Steam generator (boiler)
14:軟水器 14: Water softener
15:泵裝置 15: Pump device
16:加熱裝置(熱交換裝置) 16: heating device (heat exchange device)
L1,L2,L3,L4,L5:管線 L1, L2, L3, L4, L5: pipeline
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JPS52792A (en) * | 1975-06-24 | 1977-01-06 | Asahi Chem Ind Co Ltd | Process for fluidized regeneration of active carbon |
JPS5983921A (en) * | 1982-11-05 | 1984-05-15 | Kuraray Chem Kk | Apparatus for regeneration of waste activated carbon |
JP2543364B2 (en) * | 1987-05-27 | 1996-10-16 | 治郎 笹岡 | Low temperature regeneration method of activated carbon |
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