TW201806661A - Impurity removal method removing impurities such as dust contained in a gas such as exhaust gas with good efficiency and at low cost - Google Patents
Impurity removal method removing impurities such as dust contained in a gas such as exhaust gas with good efficiency and at low cost Download PDFInfo
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- TW201806661A TW201806661A TW105127698A TW105127698A TW201806661A TW 201806661 A TW201806661 A TW 201806661A TW 105127698 A TW105127698 A TW 105127698A TW 105127698 A TW105127698 A TW 105127698A TW 201806661 A TW201806661 A TW 201806661A
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- 239000012535 impurity Substances 0.000 title claims abstract description 63
- 239000000428 dust Substances 0.000 title claims abstract description 17
- 238000000034 method Methods 0.000 title claims abstract description 13
- 239000007788 liquid Substances 0.000 claims abstract description 100
- 239000006185 dispersion Substances 0.000 claims abstract description 35
- 230000014759 maintenance of location Effects 0.000 claims abstract description 21
- 238000007664 blowing Methods 0.000 claims abstract description 3
- 239000006260 foam Substances 0.000 claims description 66
- 238000010521 absorption reaction Methods 0.000 claims description 17
- 239000002245 particle Substances 0.000 claims description 14
- 239000007789 gas Substances 0.000 abstract description 132
- 238000005192 partition Methods 0.000 description 13
- 230000000630 rising effect Effects 0.000 description 9
- 238000005265 energy consumption Methods 0.000 description 8
- 238000000926 separation method Methods 0.000 description 8
- 239000007787 solid Substances 0.000 description 7
- 239000002250 absorbent Substances 0.000 description 6
- 230000002745 absorbent Effects 0.000 description 6
- 239000000779 smoke Substances 0.000 description 6
- 238000002347 injection Methods 0.000 description 5
- 239000007924 injection Substances 0.000 description 5
- 238000004140 cleaning Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 238000005406 washing Methods 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 239000000470 constituent Substances 0.000 description 3
- 238000006477 desulfuration reaction Methods 0.000 description 3
- 230000023556 desulfurization Effects 0.000 description 3
- 238000000605 extraction Methods 0.000 description 3
- 239000010419 fine particle Substances 0.000 description 3
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 3
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 3
- 230000003647 oxidation Effects 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 239000003440 toxic substance Substances 0.000 description 3
- 229940043430 calcium compound Drugs 0.000 description 2
- 150000001674 calcium compounds Chemical class 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- 231100000167 toxic agent Toxicity 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000010926 purge Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000013535 sea water Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
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- Treating Waste Gases (AREA)
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Abstract
Description
本發明,係有關於去除排氣等氣體中所包含的懸浮微粒等雜質的雜質去除方法。 The present invention relates to an impurity removing method for removing impurities such as suspended particles contained in a gas such as exhaust gas.
以往,為了從含有SO2或懸浮微粒等環境污染物質(雜質)的排氣中去除該等雜質,已公知有一種濕式排氣處理法,其係使排氣接觸吸收液。 Conventionally, in order to remove such impurities from exhaust gas containing environmental pollutants (impurities) such as SO 2 or suspended particles, a wet exhaust gas treatment method has been known in which the exhaust gas is brought into contact with an absorption liquid.
例如,已知一種脫硫方法,其係在內部劃分為兩室或三室的密閉槽內的最下方室收容吸收液,將排氣透過安裝在劃分最下方室與其上方室的隔板之複數個排氣分散管吹入至吸收液中而脫硫,並使受到淨化的排氣從最下方室排出,或是從最下方室引導至最上方室而排出(參照專利文獻1~4)。 For example, a desulfurization method is known, which contains an absorption liquid in the lowermost chamber of an enclosed tank divided into two or three chambers, and passes exhaust gas through a plurality of partition plates installed in the lower chamber and the upper chamber. The exhaust dispersion pipe is blown into the absorption liquid to desulfurize, and the purified exhaust gas is discharged from the lowermost chamber, or is discharged from the lowermost chamber to the uppermost chamber (see Patent Documents 1 to 4).
[專利文獻1]日本專利第3734291號公報 [Patent Document 1] Japanese Patent No. 3732291
[專利文獻2]日本專利第4616142號公報 [Patent Document 2] Japanese Patent No. 4616142
[專利文獻3]日本特公平4-9570號公報 [Patent Document 3] Japanese Patent Publication No. 4-9570
[專利文獻4]日本特公平3-70532號公報 [Patent Document 4] Japanese Patent Publication No. 3-70532
關於如此之脫硫方法,至目前為止針對防止裝置之結垢(scaling)問題的發生、裝置的自動控制化、裝置的耐久性提升等裝置運轉時會遭遇的問題點、或是裝置的大型化時會產生的問題點等進行了眾多研究,並獲得了長足的技術性進展。然而,就裝置成本的縮減或裝置運轉成本的縮減等經濟性的方面而言,或是就裝置運轉的穩定化的方面而言,尚未達到足以滿意的階段。 With regard to such a desulfurization method, there have been problems in operation of the device, such as prevention of scaling problems of the device, automatic control of the device, and improvement of the durability of the device, or upsizing of the device. Numerous studies have been carried out on problems and issues that have occurred at the time, and considerable technical progress has been made. However, it has not yet reached a sufficiently satisfactory stage in terms of economical aspects such as reduction in device cost or reduction in device operation cost, or in terms of stabilization of device operation.
另外,於前述專利文獻1~4,係並未敘明作為氣液接觸區域的氣泡泡沫層(泡沫(froth)層)的詳情,另外,針對包含了以PM2.5為代表的次微米級的細微粒子之粉塵等的去除,亦未獲得充分的性能。 In addition, in the aforementioned Patent Documents 1 to 4, the details of the bubble foam layer (froth layer) as a gas-liquid contact area are not described. In addition, for the submicron-level ones including PM2.5, Removal of fine particles of dust, etc., has not obtained sufficient performance.
本發明,係有鑑於前述情事而完成者,其目的在於提供一種能夠將排氣等氣體中所包含的懸浮微粒等雜質效率良好且低成本地去除的雜質去除方法。 The present invention has been made in view of the foregoing circumstances, and an object thereof is to provide an impurity removal method capable of efficiently and inexpensively removing impurities such as suspended particles contained in a gas such as exhaust gas.
為達成前述目的之本發明的雜質去除方法,係具有:對收容於槽內的吸收液中,透過氣體分散管將包含雜質的氣體吹入,藉此於前述槽內形成泡沫層的步驟; 其特徵為: In order to achieve the aforementioned object, the method for removing impurities according to the present invention includes the steps of blowing a gas containing impurities into a absorbing liquid contained in a tank through a gas dispersion tube, thereby forming a foam layer in the tank; Its characteristics are:
(i)將前述泡沫層的氣體滯留設定為0.4~0.9 (i) Set the gas retention of the foam layer to 0.4 ~ 0.9
(ii)將前述泡沫層的高度設定為0.2~1.8m。進而,較佳為分別將前述氣體滯留設定為0.5~0.8,並將前述泡沫層的高度設定為0.4~1.2m。 (ii) The height of the foam layer is set to 0.2 to 1.8 m. Furthermore, it is preferable to set the gas retention to 0.5 to 0.8, and to set the height of the foam layer to 0.4 to 1.2 m, respectively.
在此,將泡沫層之氣體滯留設定為0.4~0.9,係根據以下理由。 Here, the gas retention of the foam layer is set to 0.4 to 0.9 for the following reasons.
亦即,若氣體滯留未達0.4則無法獲得充分的氣液接觸面積,去除性能(雜質去除率)顯著低落,無法發揮預定的性能。 That is, if the gas retention is less than 0.4, a sufficient gas-liquid contact area cannot be obtained, the removal performance (impurity removal rate) is significantly lowered, and predetermined performance cannot be exhibited.
另外,若氣體滯留超過0.9,則泡沫層內會產生氣體的捷徑,而無法形成穩定的泡沫層,故不佳;另外,會造成氣體大量吹入,使投入至氣體分散管的能量變得過大。 In addition, if the gas retention exceeds 0.9, a shortcut of gas will be generated in the foam layer, and a stable foam layer cannot be formed, which is not good. In addition, a large amount of gas will be blown in, and the energy input into the gas dispersion tube will be excessive .
在此,將泡沫層之高度設定為0.2~1.8m,係根據以下理由。 Here, the height of the foam layer is set to 0.2 to 1.8 m for the following reasons.
亦即,若泡沫層的高度未達0.2m,則無法獲得充分的氣液接觸時間,去除性能(雜質去除率)顯著低落,無法發揮預定的性能。 That is, if the height of the foam layer is less than 0.2 m, sufficient gas-liquid contact time cannot be obtained, the removal performance (impurity removal rate) is significantly lowered, and predetermined performance cannot be exhibited.
另外,若泡沫層的高度超過1.8m,則為了避免在淨化排氣中伴隨著包含固體粒子的煙霧一起排出至系統外,係產生了使從泡沫層上端至氣體出口開口部為止的距離增大的必要性,而使裝置高度提高,並無任何經濟上的效益,且將氣體吹入所需的能量會變得過大,故不佳。 In addition, if the height of the foam layer exceeds 1.8m, in order to prevent the exhaust gas from being discharged out of the system with the smoke containing solid particles in the purified exhaust gas, the distance from the upper end of the foam layer to the opening of the gas outlet is increased. The need to increase the height of the device does not have any economic benefits, and the energy required to blow the gas will be too large, so it is not good.
於本發明中,係藉由將泡沫層的氣體滯留設 定為0.4~0.9,並將泡沫層的高度設定為0.2~1.8m,而能夠將排氣等氣體中所包含的粉塵、或是以SOx或氯化氫所代表之氣體狀有毒物質等的雜質效率良好且低成本地去除。 In the present invention, by setting the gas retention of the foam layer to 0.4 to 0.9 and the height of the foam layer to 0.2 to 1.8 m, dust contained in gas such as exhaust gas, or SO can be used. Impurities such as gaseous toxic substances represented by x or hydrogen chloride are efficiently and inexpensively removed.
特別是,能夠將具有一般的噴霧式之液分散型的去除裝置難以捕集的次微米級的微粒子的粉塵進行捕集而去除。 In particular, it is possible to capture and remove dust having submicron-level fine particles which are difficult to be captured by a general spray type liquid dispersion type removal device.
於本發明之前述構成當中,進而(iii)將前述泡沫層的每單位體積的氣液接觸面積設定為1000~3000m2/m3為佳。 In the aforementioned configuration of the present invention, (iii) the gas-liquid contact area per unit volume of the foam layer is preferably set to 1000 to 3000 m 2 / m 3 .
另外,將泡沫層的每單位體積的氣液接觸面積設定為1500~2500m2/m3更佳。 In addition, the gas-liquid contact area per unit volume of the foam layer is more preferably set to 1500 to 2500 m 2 / m 3 .
將前述泡沫層的每單位體積的氣液接觸面積設定為1000~3000m2/m3為佳,係根據以下理由。 The gas-liquid contact area per unit volume of the foam layer is preferably set to 1000 to 3000 m 2 / m 3 for the following reasons.
亦即,藉由使氣液混合層(泡沫層)的每單位體積的氣液接觸面積為1000m2/m3以上,並進一步確保充分的氣液接觸面積,係能夠穩定地維持去除性能(雜質去除率);另外,若從氣體分散管的排氣噴出孔之氣體噴出速度越大,則氣泡越細,且能夠使氣泡直徑的分佈縮小而提升去除性能(雜質去除率),然而欲使氣體噴出速度增大,則氣體分散管所負荷之能量消耗(伴隨著噴出之壓力損失增大)亦增大,故藉由使氣液接觸面積為3000m2/m3以下,能夠一邊穩定維持去除性能(雜質去除率)一邊抑制過度的能量消耗。 That is, by making the gas-liquid contact area per unit volume of the gas-liquid mixed layer (foam layer) 1000 m 2 / m 3 or more, and further ensuring a sufficient gas-liquid contact area, the removal performance (impurities) can be stably maintained (Removal rate); In addition, if the gas ejection speed from the gas discharge hole of the gas dispersion pipe is greater, the bubbles are finer, and the distribution of the bubble diameter can be reduced to improve the removal performance (impurity removal rate). As the ejection speed increases, the energy consumption of the gas dispersion tube (the pressure loss accompanying the ejection increases) also increases. Therefore, the removal performance can be stably maintained while the gas-liquid contact area is 3000 m 2 / m 3 or less. (Impurity removal rate) Excessive energy consumption is suppressed.
根據如此之構成,能夠獲得充分的氣液接觸面積,故能夠將雜質效率良好且低成本地去除,另外,能夠抑制氣體分散管所負荷的能量消耗。 With such a configuration, a sufficient gas-liquid contact area can be obtained, so that impurities can be removed efficiently and at low cost, and energy consumption by the gas dispersion tube can be suppressed.
於本發明之前述構成中,雜質係亦可包含前述氣體中的粉塵,或是前述氣體中含有粒徑0.1~10μm的雜質。 In the aforementioned configuration of the present invention, the impurities may include dust in the gas, or the gas may contain impurities having a particle diameter of 0.1 to 10 μm.
根據如此之構成,就從氣體中去除特別是粉塵或粒徑為0.1~10μm的雜質的目的而言,與以往技術相比能夠發揮更高的去除效率。 According to such a structure, compared with the conventional technology, the purpose of removing especially dust or the impurity with a particle diameter of 0.1-10 micrometers from a gas can exhibit higher removal efficiency compared with the prior art.
根據本發明,係能夠將排氣等氣體中所包含的粉塵、或是以SOx或氯化氫所代表之氣體狀有毒物質等的雜質效率良好且低成本地連續去除。 According to the present invention, it is possible to continuously and efficiently remove dust contained in a gas such as exhaust gas or impurities such as a gaseous toxic substance represented by SO x or hydrogen chloride at low cost.
1‧‧‧雜質去除裝置 1‧‧‧ impurity removal device
2‧‧‧密閉槽(槽) 2‧‧‧closed tank (slot)
3‧‧‧第一隔板 3‧‧‧ first partition
4‧‧‧第一室 4‧‧‧The first room
5‧‧‧第二室 5‧‧‧Second Room
6‧‧‧排氣導入口 6‧‧‧ exhaust inlet
7‧‧‧排氣分散管 7‧‧‧ exhaust dispersion pipe
8‧‧‧排氣噴出孔 8‧‧‧ exhaust outlet
9‧‧‧排氣排出口 9‧‧‧ exhaust outlet
10‧‧‧攪拌機 10‧‧‧ Mixer
11‧‧‧吸收劑供給管 11‧‧‧ Absorbent supply tube
12‧‧‧氧化用空氣供給管 12‧‧‧ Oxidation air supply pipe
13‧‧‧吸收液抽出管 13‧‧‧ Absorption liquid extraction tube
14‧‧‧第二隔板 14‧‧‧Second partition
15‧‧‧第三室 15‧‧‧ Third Room
16‧‧‧排氣上升筒 16‧‧‧Exhaust riser
17‧‧‧洗淨液供給管 17‧‧‧wash liquid supply pipe
18‧‧‧洗淨液排出口 18‧‧‧washing liquid discharge port
A‧‧‧氣液混合層(泡沫層) A‧‧‧Gas-liquid mixed layer (foam layer)
B‧‧‧固液分離空間 B‧‧‧Solid-liquid separation space
D‧‧‧排氣噴出孔的直徑 D‧‧‧ diameter of exhaust nozzle
L‧‧‧吸收液 L‧‧‧ Absorbent
W‧‧‧吸收液的靜止液面 W‧‧‧ static liquid level of absorption liquid
[第1圖]係表示本發明之實施形態之雜質去除裝置之一例的示意圖。 [Fig. 1] Fig. 1 is a schematic diagram showing an example of an impurity removing apparatus according to an embodiment of the present invention.
[第2圖]係用以說明本發明之實施形態之雜質去除方法,並表示雜質的去除率與氣體滯留的關係的圖表。 [Fig. 2] A graph for explaining an impurity removing method according to an embodiment of the present invention, and showing a relationship between the removal rate of impurities and gas retention.
[第3圖]同上,並表示雜質去除率與泡沫層的高度的關係的圖表。 [Fig. 3] A graph showing the relationship between the impurity removal rate and the height of the foam layer as described above.
[第4圖]同上,並表示雜質去除率與泡沫層每單位體 積的氣液接觸面積的關係的圖表。 [Figure 4] Same as above, and shows the removal rate of impurities and the unit volume of the foam layer Graph showing the relationship between the accumulated gas-liquid contact area.
[第5圖]同上,並表示排氣中的粉塵粒子的各粒徑的捕集效率(雜質去除率)的圖表。 [Fig. 5] A graph showing the collection efficiency (impurity removal rate) of each particle diameter of dust particles in the exhaust gas, as described above.
[第6圖]係表示本發明之實施形態之雜質去除裝置之其他例的示意圖。 [Fig. 6] Fig. 6 is a schematic diagram showing another example of the impurity removing device according to the embodiment of the present invention.
以下,參照所附圖式對本發明的實施形態進行說明。 Hereinafter, embodiments of the present invention will be described with reference to the drawings.
第1圖,係表示本發明之三室構造之雜質去除裝置之一例的示意圖。於該圖中,符號係分別表示:1係脫硫裝置,2係密閉槽,3係第一隔板,4係第一室,5係第二室,6係排氣導入口,7係排氣分散管,8係排氣噴出孔,9係排氣排出口,10係攪拌機,10'係攪拌軸,11係吸收劑供給管,12係氧化用空氣供給管,13係吸收液抽出管,14係第二隔板,15係第三室,16係排氣上升筒,17係洗淨液供給管,18係洗淨液排出管,L係吸收液,W係吸收液的靜止液面,A係氣液混合層(泡沫層),B係固液分離空間。 FIG. 1 is a schematic diagram showing an example of an impurity removing device having a three-chamber structure according to the present invention. In the figure, the symbols refer to: 1 series desulfurization device, 2 series closed tank, 3 series first partition, 4 series first chamber, 5 series second chamber, 6 series exhaust inlet, and 7 series exhaust Gas dispersion tube, 8 series exhaust outlet, 9 series exhaust outlet, 10 series mixer, 10 'series stirring shaft, 11 series absorbent supply tube, 12 series oxidation air supply tube, 13 series absorption liquid extraction tube, 14 series second partition, 15 series third chamber, 16 series exhaust riser, 17 series cleaning liquid supply pipe, 18 series cleaning liquid discharge pipe, L series absorption liquid, W series absorption liquid, A series gas-liquid mixed layer (foam layer), B series solid-liquid separation space.
第1圖所示之雜質去除裝置,係將密閉槽2的內部藉由第一隔板3及第二隔板14進行劃分,而形成第一室4、第二室5、以及第三室15的三室構造。第一隔板3及第二隔板14,係水平板、階梯狀板、傾斜板等之任一者皆可,然而特別是使用傾斜板為佳。另外,第一室 4係收容通過排氣分散管7被吹入含有雜質的氣體之吸收液的腔室,並設置於密閉槽2的下部。 The impurity removing device shown in FIG. 1 divides the inside of the closed tank 2 by the first partition plate 3 and the second partition plate 14 to form a first chamber 4, a second chamber 5, and a third chamber 15. Three-room construction. The first partition plate 3 and the second partition plate 14 may be any of a horizontal plate, a stepped plate, and an inclined plate. However, it is particularly preferable to use an inclined plate. In addition, the first room The 4th type is a chamber which accommodates the absorption liquid blown into the gas containing an impurity through the exhaust dispersion pipe 7, and is provided in the lower part of the closed tank 2.
於第二室5係配置有排氣導入口6,自該排氣導入口6導入的排氣,係通過排氣分散管7從排氣噴出孔8吹入至比吸收液L的靜止液面W更下方的部分。於比排氣噴出孔8更上方處,係形成有氣液混合層(泡沫層)A,排氣中的粉塵或亞硫酸氣體係在此受到吸收。作為吸收液L,係使用含有鈣化合物或鈣化合物含有物,例如石灰石及/或熟石灰作為吸收劑的石膏漿液。 An exhaust gas inlet 6 is arranged in the second chamber 5. The exhaust gas introduced from the exhaust gas inlet 6 is blown into the stationary liquid surface of the specific absorption liquid L through an exhaust gas dispersion pipe 7 from an exhaust gas discharge hole 8. W the lower part. A gas-liquid mixed layer (foam layer) A is formed above the exhaust gas ejection hole 8, and the dust or sulfurous acid gas system in the exhaust gas is absorbed therein. As the absorption liquid L, a gypsum slurry containing a calcium compound or a calcium compound-containing substance such as limestone and / or slaked lime is used as an absorbent.
被排放至第一室4內的氣液混合層(泡沫層)A的上方之淨化排氣,係一邊上升至第一室4的上部空間B(固液分離空間)一邊往水平方向移動。於淨化排氣如此流動期間,排氣中的煙霧以及無法以氣液混合層(泡沫層)A去除的粒徑相對較大的固體粒子,係於固液分離空間B中藉由重力沉降以及與排氣分散管7的碰撞而將其大部分從淨化排氣中分離。受到固液分離之淨化排氣,係於排氣上升筒16上升,並被導入至第三室15。於第三室15中,淨化排氣係自上升流轉換方向為大致水平流,且伴隨著淨化排氣的煙霧及固體粒子的受到分離後後,該淨化排氣自排氣排出口9被排出。 The purified exhaust gas discharged above the gas-liquid mixed layer (foam layer) A in the first chamber 4 moves horizontally while rising to the upper space B (solid-liquid separation space) of the first chamber 4. During the flow of the purified exhaust gas, the smoke in the exhaust gas and the relatively large solid particles that cannot be removed by the gas-liquid mixed layer (foam layer) A are deposited in the solid-liquid separation space B by gravity settlement and The collision of the exhaust dispersion pipe 7 separates most of it from the purified exhaust gas. Purified exhaust gas subjected to solid-liquid separation is lifted by the exhaust riser 16 and is introduced into the third chamber 15. In the third chamber 15, the purified exhaust gas is switched from an upward flow direction to a substantially horizontal flow, and after the smoke and solid particles are separated from the purified exhaust gas, the purified exhaust gas is discharged from the exhaust discharge port 9. .
沉積於第三室15的底面(第二隔板14)上的固體粒子,係例如藉由間歇地或連續地從洗淨液供給管17供給洗淨液,例如含石膏漿液、分離了石膏的吸收液、水、海水等液體,而自第二隔板14的表面剝離,並連同 洗淨液一起從一個部位以上的洗淨液排出口18排出。 The solid particles deposited on the bottom surface (second partition plate 14) of the third chamber 15 are, for example, intermittent or continuous supply of a cleaning liquid from a cleaning liquid supply pipe 17, such as a gypsum-containing slurry, a Absorbs liquid, water, seawater, etc., and peels off from the surface of the second partition plate 14 together with The washing liquid is discharged together from the washing liquid discharge port 18 at one or more locations.
本發明者,係發現:對如上述般收容於密閉槽1的第一室4的吸收液中,通過排氣分散管7將排氣吹入,藉此,在第一室4形成氣液混合層(泡沫層)A之際,將氣液混合層(泡沫層)A的氣液構成要件設定為以下之(i)及(ii),能夠藉此將排氣中所含有的粉塵等雜質效率良好且低成本地連續去除。 The inventors have found that the absorption liquid contained in the first chamber 4 of the closed tank 1 as described above is blown in by the exhaust gas dispersion pipe 7 to form a gas-liquid mixture in the first chamber 4 In the case of layer A (foam layer) A, the gas-liquid components of gas-liquid mixed layer (foam layer) A are set to the following (i) and (ii), thereby enabling the efficiency of impurities such as dust contained in the exhaust gas to be effectively reduced. Good and low cost continuous removal.
(i)將前述泡沫層之氣體滯留設定為0.4~0.9。 (i) The gas retention of the foam layer is set to 0.4 to 0.9.
(ii)將前述泡沫層之高度設定為0.2~1.8m。 (ii) The height of the foam layer is set to 0.2 to 1.8 m.
所謂氣體滯留,係指氣液混合層(泡沫層)A之氣體所佔的比例,該氣體滯留Φ、氣液混合層(泡沫層)A的高度H、以及氣體吹入深度L的關係,係能夠由以下式子表示。又,氣液混合層(泡沫層)A的高度H,係指從排氣噴出孔8的中心至氣液混合層(泡沫層)A的上端為止之垂直方向的長度;氣體吹入深度L,係指將氣體吹入前之從排氣噴出孔8的中心至吸收液L的靜止液面W為止之垂直方向的長度。 The so-called gas retention refers to the proportion of gas in the gas-liquid mixed layer (foam layer) A. The relationship between the gas retention Φ, the height H of the gas-liquid mixed layer (foam layer) A, and the gas injection depth L, is It can be expressed by the following formula. The height H of the gas-liquid mixed layer (foam layer) A refers to the length in the vertical direction from the center of the exhaust gas discharge hole 8 to the upper end of the gas-liquid mixed layer (foam layer) A; the gas injection depth L, The length in the vertical direction from the center of the exhaust gas ejection hole 8 to the stationary liquid level W of the absorption liquid L before the gas is blown in.
H=L×1/(1-Φ) H = L × 1 / (1-Φ)
在此,將氣液混合層(泡沫層)A的氣液構成要件設定為以下之(i)及(ii)之理由,係如以下所述。 Here, the reason for setting the gas-liquid constituents of the gas-liquid mixed layer (foam layer) A to (i) and (ii) below is as follows.
亦即,若氣體滯留未達0.4,則無法獲得充分的氣液接觸面積,去除性能(雜質去除率)顯著低落,無法發揮預定的性能。另一方面,若氣體滯留超過0.9,則氣液混合層(泡沫層)A內會產生氣體的捷徑,而無法形成穩定的氣 液混合層(泡沫層)A,故不佳;另外,會造成氣體大量吹入,使投入至排氣分散管7的能量變得過大。因此,將前述氣體滯留設定為0.4~0.9。 That is, if the gas retention is less than 0.4, a sufficient gas-liquid contact area cannot be obtained, the removal performance (impurity removal rate) is significantly lowered, and predetermined performance cannot be exhibited. On the other hand, if the gas retention exceeds 0.9, a gas shortcut is generated in the gas-liquid mixed layer (foam layer) A, and a stable gas cannot be formed. The liquid mixing layer (foam layer) A is not good. In addition, a large amount of gas is blown in, and the energy input to the exhaust dispersion pipe 7 becomes excessive. Therefore, the gas retention is set to 0.4 to 0.9.
另外,如第2圖所示,當氣體滯留超過0.5左右時,去除性能(雜質去除率)的上升率便開始下降,當超過0.8左右時,去除性能(雜質去除率)便到達上限。 In addition, as shown in FIG. 2, when the gas retention exceeds about 0.5, the increase rate of the removal performance (impurity removal rate) starts to decrease, and when it exceeds about 0.8, the removal performance (impurity removal rate) reaches the upper limit.
因此,從第2圖及能量消耗的觀點來看,氣體滯留係設定為0.5~0.8更佳。 Therefore, from the viewpoint of Fig. 2 and energy consumption, the gas retention system is more preferably set to 0.5 to 0.8.
另外,若氣液混合層(泡沫層)A的高度未達0.2m,則無法獲得充分的氣液接觸時間,去除性能(雜質去除率)顯著低落,無法發揮預定的性能。另一方面,若氣液混合層(泡沫層)A的高度超過1.8m,則為了避免包含固體粒子的煙霧伴隨著淨化排氣一起排出至雜質去除裝置1之外,係產生了使從泡沫層上端至氣體出口開口部(排氣排出口9)為止的距離增大的必要性,而使裝置高度提高,並無任何經濟上的效益,且將氣體吹入所需的能量會變得過大,故不佳。因此,將前述泡沫層之高度設定為0.2~1.8m。 In addition, if the height of the gas-liquid mixed layer (foam layer) A is less than 0.2 m, sufficient gas-liquid contact time cannot be obtained, the removal performance (impurity removal rate) is significantly lowered, and predetermined performance cannot be exhibited. On the other hand, if the height of the gas-liquid mixed layer (foam layer) A exceeds 1.8 m, in order to prevent the smoke containing solid particles from being discharged out of the impurity removal device 1 along with the purified exhaust gas, the foam layer is generated. It is necessary to increase the distance from the upper end to the gas outlet opening (exhaust exhaust port 9), so that the height of the device is increased without any economic benefits, and the energy required to blow the gas becomes too large, So bad. Therefore, the height of the foam layer is set to 0.2 to 1.8 m.
另外,如第3圖所示,當泡沫層的高度超過0.4m左右時,去除性能(雜質去除率)的上升率便開始下降,當超過1.2m左右時,去除性能(雜質去除率)便到達上限。 In addition, as shown in FIG. 3, when the height of the foam layer exceeds about 0.4 m, the increase rate of removal performance (impurity removal rate) starts to decrease, and when it exceeds about 1.2 m, the removal performance (impurity removal rate) reaches Ceiling.
因此,從第3圖及能量消耗的觀點來看,氣液混合層(泡沫層)A的高度,係設定為0.4~1.2m更佳。 Therefore, from the viewpoint of FIG. 3 and energy consumption, the height of the gas-liquid mixed layer (foam layer) A is preferably set to 0.4 to 1.2 m.
另外,本發明者,係發現:(iii)藉由將前述泡 沫層的每單位體積的氣液接觸面積設定為1000~3000m2/m3,亦能夠將排氣中所包含的粉塵等之雜質效率良好且低成本地連續去除。 In addition, the present inventors have discovered that (iii) by setting the gas-liquid contact area per unit volume of the foam layer to 1000 to 3000 m 2 / m 3 , it is also possible to include impurities such as dust contained in the exhaust gas Continuous removal with good efficiency and low cost.
如此限定泡沫層的每單位體積的氣液接觸面積,係因為:藉由使氣液混合層(泡沫層)A的每單位體積的氣液接觸面積為1000m2/m3以上,並進一步確保充分的氣液接觸面積,係能夠穩定地維持去除性能(雜質去除率);另外,若從排氣分散管7的排氣噴出孔8之氣體噴出速度越大,則氣泡越細,且能夠使氣泡直徑的分佈縮小而提升去除性能(雜質去除率),然而欲使氣體噴出速度增大,則排氣分散管7所負荷之能量消耗(伴隨著噴出之壓力損失增大)亦增大,故藉由使氣液接觸面積為3000m2/m3以下,能夠一邊穩定維持去除性能(雜質去除率)一邊抑制過度的能量消耗。 The reason why the gas-liquid contact area per unit volume of the foam layer is so limited is because the gas-liquid contact area per unit volume of the gas-liquid mixed layer (foam layer) A is 1000 m 2 / m 3 or more, and further ensure sufficient The gas-liquid contact area can stably maintain the removal performance (impurity removal rate). In addition, the larger the gas ejection speed from the exhaust gas discharge holes 8 of the exhaust dispersion pipe 7, the finer the bubbles and the larger the bubbles The diameter distribution is reduced to improve the removal performance (impurity removal rate). However, if the gas ejection speed is to be increased, the energy consumption (increased by the ejection pressure loss) carried by the exhaust dispersion pipe 7 is also increased. When the gas-liquid contact area is 3000 m 2 / m 3 or less, it is possible to suppress excessive energy consumption while stably maintaining removal performance (impurity removal rate).
另外,如第4圖所示,當泡沫層每單位體積的氣液接觸面積超過1500m2/m3左右時,去除性能(雜質去除率)的上升率便開始下降,當超過2500m2/m3左右時,去除性能(雜質去除率)便到達上限。 In addition, as shown in Figure 4, when the gas-liquid contact area per unit volume of the foam layer exceeds about 1500 m 2 / m 3 , the rate of increase in removal performance (impurity removal rate) starts to decrease, and when it exceeds 2500 m 2 / m 3 At the left and right, the removal performance (impurity removal rate) reaches the upper limit.
因此,從第4圖及能量消耗的觀點來看,泡沫層的每單位體積的氣液接觸面積,係設定為1500~2500m2/m3更佳。 Therefore, from the viewpoint of FIG. 4 and energy consumption, the gas-liquid contact area per unit volume of the foam layer is more preferably set to 1500 to 2500 m 2 / m 3 .
泡沫層的每單位體積的氣液接觸面積SA,係如以下般計算。 The gas-liquid contact area SA per unit volume of the foam layer is calculated as follows.
SA=Sb.N/Vf SA = Sb. N / Vf
Sb:形成泡沫層之平均的單一氣泡的表面積 Sb: average surface area of a single bubble forming a foam layer
Sb=π.db2 Sb = π. db 2
db:氣泡直徑 db: bubble diameter
N:泡沫層內的氣泡數 N: Number of bubbles in the foam layer
Vf:泡沫層體積 Vf: volume of foam layer
Vf=L.1/(1-Φ).S Vf = L. 1 / (1-Φ). S
N=Vf.Φ/Vb N = Vf. Φ / Vb
Vb=1/6.π.db3(單一氣泡的體積) Vb = 1/6. π. db 3 (volume of a single bubble)
L:氣體吹入深度(將氣體吹入前之從氣體分散管的氣體噴出孔中心至靜止液面為止的深度) L: gas injection depth (depth from the center of the gas injection hole of the gas dispersion tube to the stationary liquid surface before the gas is injected)
Φ:氣體滯留 Φ: gas retention
S:泡沫層剖面積(從氣液混合層(泡沫層)A的水平剖面積減去排氣分散管7的水平剖面積等之淨化排氣無法通過的構造物之水平剖面積的合計之水平剖面積) S: The cross-sectional area of the foam layer (from the horizontal cross-sectional area of the gas-liquid mixed layer (foam layer) A minus the horizontal cross-sectional area of the exhaust dispersion pipe 7 and the horizontal cross-sectional area of the structure such that the purified exhaust cannot pass through. (Cross-sectional area)
又,欲將氣液混合層(泡沫層)A的氣液構成要件設定為如上述之(i)~(iii)般,係例如將排氣分散管7的等效內直徑、排氣噴出孔8的等效直徑、從排氣噴出孔8的噴出速度、從複數個排氣噴出孔8的中心點的平均位置至該排氣分散管7的開口下端為止的距離、第一室4之淨化排氣的平均上升速度、第一室4之淨化排氣的平均水平速度、於排氣上升筒16上升之淨化排氣的速度等適當設定而進行。 In addition, the gas-liquid components of the gas-liquid mixed layer (foam layer) A are to be set as described in (i) to (iii) above. 8 equivalent diameter, the ejection speed from the exhaust ejection hole 8, the distance from the average position of the center points of the exhaust ejection holes 8 to the lower end of the exhaust dispersion pipe 7, and the purification of the first chamber 4 The average rising speed of the exhaust gas, the average horizontal speed of the purified exhaust gas in the first chamber 4, the speed of the purified exhaust gas rising from the exhaust rising cylinder 16, and the like are set as appropriate.
排氣分散管之等效內直徑及排氣噴出孔的等效直徑係 以次式表示。 The equivalent internal diameter of the exhaust dispersion pipe and the equivalent diameter of the exhaust nozzle Represented by the equation.
排氣分散管之等效內直徑=(4×A)/B Equivalent inner diameter of exhaust dispersion pipe = (4 × A) / B
A:排氣分散管的排氣噴出孔的配設位置之內部空間的水平剖面積 A: Horizontal cross-sectional area of the internal space of the arrangement position of the exhaust gas discharge holes of the exhaust dispersion pipe
B:包圍排氣分散管的排氣噴出孔的配設位置之內部空間的水平剖面的周邊的長度 B: Length of the periphery of the horizontal cross section of the internal space surrounding the arrangement position of the exhaust gas discharge holes of the exhaust dispersion pipe
排氣噴出孔之等效直徑=(4×C)/D Equivalent diameter of exhaust nozzle = (4 × C) / D
C:排氣噴出孔之面積 C: The area of the exhaust nozzle
D:排氣噴出孔的周邊的長度 D: Length of the periphery of the exhaust gas ejection hole
另外,所謂第一室4之淨化排氣的平均上升速度,係指基於從比氣液混合層(泡沫層)A更上方的空間B之水平剖面積減去排氣分散管7之水平剖面積等淨化排氣無法通過的構造物之水平剖面積的合計之水平剖面積的速度。 The average rising speed of the purified exhaust gas in the first chamber 4 is based on the horizontal cross-sectional area of the space B above the gas-liquid mixed layer (foam layer) A minus the horizontal cross-sectional area of the exhaust dispersion pipe 7. The speed of the horizontal cross-sectional area of the total of the horizontal cross-sectional area of the structure through which the purge exhaust cannot pass.
所謂第一室4之淨化排氣的平均水平速度,係指基於從比氣液混合層A更上方的空間B之排氣上升筒16的下端部開口周邊的垂直剖面積的速度。 The average horizontal velocity of the purified exhaust gas in the first chamber 4 is a velocity based on the vertical cross-sectional area around the opening of the lower end portion of the exhaust gas riser 16 from the space B above the gas-liquid mixed layer A.
排氣分散管7,係能夠為圓形、三角形、四角形、六角形等多角形,或是為溝槽(trough)等任意的剖面形狀。另外,於排氣分散管7的側壁,係在離水平面幾乎為一定高度的位置開有複數個排氣噴出孔8,該排氣噴出孔的形狀可為圓形、三角、四角、六角、星型等任意形狀,亦能夠為狹縫狀。該排氣噴出孔,係對於排氣分散管以一定的高度配置為一列亦可,以不同的高度配置為兩列 或三列以上亦可。 The exhaust dispersion pipe 7 can have a polygonal shape such as a circle, a triangle, a quadrangle, or a hexagon, or an arbitrary cross-sectional shape such as a trough. In addition, a plurality of exhaust gas ejection holes 8 are formed on the side wall of the exhaust gas dispersion pipe 7 at a certain height from the horizontal plane. The shape of the exhaust gas ejection holes can be circular, triangular, quadrangular, hexagonal, or star. Any shape, such as a pattern, can also be a slit shape. The exhaust gas ejection holes may be arranged in a row at a certain height for the exhaust dispersion pipe, and arranged in two rows at different heights. Or three or more columns are also acceptable.
排氣分散管7的下端開口部的形狀,係單純具有水平端面者、具有任意的傾斜端面者、具有鋸子之刃狀或是切出複數個缺口的形狀者之任意者皆可。 The shape of the opening at the lower end of the exhaust dispersion pipe 7 may be any of a simple one having a horizontal end surface, an arbitrary inclined end surface, a blade shape of a saw, or a shape having a plurality of cutouts.
另外,排氣上升筒16的橫剖面形狀,係可為圓形、正方形、長方形等各種形狀。 The cross-sectional shape of the exhaust rising cylinder 16 may be various shapes such as a circle, a square, and a rectangle.
接著,對實驗例進行說明。 Next, experimental examples will be described.
將泡沫層A的氣液構成要件設定為如前述(i)~(ii)。 The gas-liquid constituents of the foam layer A are set as described in (i) to (ii) above.
此時之排氣分散管(噴布器,sparger)的尺寸、排氣噴出孔的直徑(孔徑)等其他條件係如以下之表1所述。 Other conditions such as the size of the exhaust gas dispersion pipe (sparger) and the diameter (hole diameter) of the exhaust gas discharge hole are as described in Table 1 below.
又,表1中所謂之入口係在本實驗中將排氣導入至實驗裝置的導入口,所謂出口係將去除了雜質等的排氣從實驗裝置排出的排出口。 In addition, the so-called inlet in Table 1 is an introduction port for introducing exhaust gas to the experimental device in this experiment, and the so-called outlet is a discharge port for exhaust gas from which the impurities and the like are removed from the experimental device.
孔徑係排氣噴出孔的等效直徑,孔數係每一根排氣分散管的排氣噴出孔的數目,孔噴出速度係從排氣噴出孔被噴出的排氣的流速。 The hole diameter is the equivalent diameter of the exhaust gas ejection hole, the number of holes is the number of exhaust gas ejection holes of each exhaust dispersion pipe, and the ejection velocity of the hole is the flow velocity of the exhaust gas ejected from the exhaust gas ejection hole.
浸液深度係氣體吹入深度,且係將氣體吹入前之從排氣噴出孔的中心至吸收液的靜止液面為止之垂直方向的長度。泡沫層高度係從排氣噴出孔的中心至泡沫層的上端為止之垂直方向的長度。 The depth of the immersion liquid refers to the depth of the gas injection, and the length in the vertical direction from the center of the exhaust gas ejection hole to the stationary liquid surface of the absorption liquid before the gas is injected. The height of the foam layer is the length in the vertical direction from the center of the exhaust gas discharge hole to the upper end of the foam layer.
泡沫層氣體空塔速度(superficial tower velocity)係第1圖所示的第一室4之淨化排氣的平均上升速度。 The superficial tower velocity of the foam layer gas is the average rising speed of the purified exhaust gas in the first chamber 4 shown in FIG. 1.
將其結果示於第5圖。 The results are shown in FIG. 5.
如第5圖所示,藉由本實驗,可知能夠將具有一般的液分散型的去除裝置難以捕集的次微米級的微粒子的粉塵進行捕集而去除。 As shown in FIG. 5, from this experiment, it can be seen that dust having submicron-level fine particles that are difficult to be captured by a general liquid dispersion type removal device can be captured and removed.
如以上般,根據本實施形態,係將氣液混合層(泡沫層)A的氣體滯留設定為0.4~0.9,並將氣液混合層(泡沫層)A的高度設定為0.2~1.8m,故能夠將排氣等氣體中所包含的粉塵、或是以SOx或氯化氫所代表之氣體狀有毒物質等的雜質效率良好且低成本地連續去除。 As described above, according to this embodiment, the gas retention of the gas-liquid mixed layer (foam layer) A is set to 0.4 to 0.9, and the height of the gas-liquid mixed layer (foam layer) A is set to 0.2 to 1.8 m. It is possible to continuously and efficiently remove dust contained in a gas such as exhaust gas or impurities such as a gaseous toxic substance represented by SO x or hydrogen chloride at low cost.
第6圖,係表示本發明之兩室構造之雜質去除裝置之一例的示意圖。於該圖中,與第1圖所示之符號為相同的符號係具有相同的意義。 Fig. 6 is a schematic diagram showing an example of an impurity removing device having a two-chamber structure according to the present invention. In this figure, the same symbols as those shown in Figure 1 have the same meaning.
於第6圖所示之雜質去除裝置中,與第一室4內的吸收液接觸而受到淨化的排氣,係保持在平均上升速度0.5~5m/s,較佳為0.7~4m/s,平均水平速度為8m/s以下,較佳為6m/s以下,一邊於第一室4的上部空間B上升一邊往水平方向移動。於淨化排氣如此流動期間,排氣中的煙霧以及固體粒子,係於固液分離空間B中藉由重力沉降以及與排氣分散管7的碰撞分離而從排氣中受到分離,分離了煙霧及固體的淨化排氣係從排氣排出口9受到排出。 In the impurity removal device shown in Fig. 6, the exhaust gas purified by contact with the absorption liquid in the first chamber 4 is maintained at an average rising speed of 0.5 to 5 m / s, preferably 0.7 to 4 m / s. The average horizontal velocity is 8 m / s or less, preferably 6 m / s or less, and moves in the horizontal direction while rising in the upper space B of the first chamber 4. During the flow of the purified exhaust gas, the smoke and solid particles in the exhaust gas are separated from the exhaust gas in the solid-liquid separation space B by gravity settlement and collision separation with the exhaust dispersion pipe 7, and the smoke is separated. The purified exhaust gas and solids are discharged from the exhaust discharge port 9.
於如此之雜質去除裝置中,係與上述情形相同,藉由將氣液混合層(泡沫層)A的氣液構成要件設定為如前述(i)~(iii)般,能夠將排氣中所包含的粉塵、或SOx等之雜質效率良好且低成本地連續去除。 In such an impurity removal device, as in the above-mentioned case, by setting the gas-liquid constituent elements of the gas-liquid mixed layer (foam layer) A as described in (i) to (iii), the exhaust gas can be removed. The contained dust or impurities such as SO x are efficiently and continuously removed at low cost.
1‧‧‧雜質去除裝置 1‧‧‧ impurity removal device
2‧‧‧密閉槽(槽) 2‧‧‧closed tank (slot)
3‧‧‧第一隔板 3‧‧‧ first partition
4‧‧‧第一室 4‧‧‧The first room
5‧‧‧第二室 5‧‧‧Second Room
6‧‧‧排氣導入口 6‧‧‧ exhaust inlet
7‧‧‧排氣分散管 7‧‧‧ exhaust dispersion pipe
8‧‧‧排氣噴出孔 8‧‧‧ exhaust outlet
9‧‧‧排氣排出口 9‧‧‧ exhaust outlet
10‧‧‧攪拌機 10‧‧‧ Mixer
10’‧‧‧攪拌軸 10’‧‧‧ mixing shaft
11‧‧‧吸收劑供給管 11‧‧‧ Absorbent supply tube
12‧‧‧氧化用空氣供給管 12‧‧‧ Oxidation air supply pipe
13‧‧‧吸收液抽出管 13‧‧‧ Absorption liquid extraction tube
14‧‧‧第二隔板 14‧‧‧Second partition
15‧‧‧第三室 15‧‧‧ Third Room
16‧‧‧排氣上升筒 16‧‧‧Exhaust riser
17‧‧‧洗淨液供給管 17‧‧‧wash liquid supply pipe
18‧‧‧洗淨液排出口 18‧‧‧washing liquid discharge port
A‧‧‧氣液混合層(泡沫層) A‧‧‧Gas-liquid mixed layer (foam layer)
B‧‧‧固液分離空間 B‧‧‧Solid-liquid separation space
L‧‧‧吸收液 L‧‧‧ Absorbent
Claims (3)
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| TW105127698A TW201806661A (en) | 2016-08-29 | 2016-08-29 | Impurity removal method removing impurities such as dust contained in a gas such as exhaust gas with good efficiency and at low cost |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| TW105127698A TW201806661A (en) | 2016-08-29 | 2016-08-29 | Impurity removal method removing impurities such as dust contained in a gas such as exhaust gas with good efficiency and at low cost |
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| Publication Number | Publication Date |
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| TW201806661A true TW201806661A (en) | 2018-03-01 |
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