TWI722956B - Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques - Google Patents
Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques Download PDFInfo
- Publication number
- TWI722956B TWI722956B TW109127981A TW109127981A TWI722956B TW I722956 B TWI722956 B TW I722956B TW 109127981 A TW109127981 A TW 109127981A TW 109127981 A TW109127981 A TW 109127981A TW I722956 B TWI722956 B TW I722956B
- Authority
- TW
- Taiwan
- Prior art keywords
- particle
- cavity
- impact
- water
- flow
- Prior art date
Links
Images
Abstract
Description
本發明是關於一種微粒收集設備。The present invention relates to a particle collection device.
在半導體產業中,由處理室或高溫洗滌器產生的次微米和微小顆粒的排放經常無法得到妥善的處理,從而成為白煙排放的來源。現有的微粒控制裝置包括靜電集塵器、集塵室及文式洗滌器,這些微粒控制裝置分別因為不能用於去除爆炸物、有著火危險並佔用大量空間、以及具有大的壓損而不能令人滿意。因此,如何提供一種能避免前述缺失的簡易微粒控制裝置實是本領域技術人員所思量的。In the semiconductor industry, the emission of submicron and fine particles generated by processing chambers or high-temperature scrubbers often cannot be properly treated, thus becoming a source of white smoke emissions. Existing particulate control devices include electrostatic precipitators, dust collection chambers, and vent scrubbers. These particulate control devices cannot be used to remove explosives, have a fire hazard, take up a lot of space, and have a large pressure loss. People are satisfied. Therefore, how to provide a simple particle control device that can avoid the aforementioned deficiencies is really contemplated by those skilled in the art.
本發明之主要目的在於提供一種簡易的微粒控制裝置。The main purpose of the present invention is to provide a simple particle control device.
為了達成上述及其他目的,本發明提供一種結合微粒凝結成長及慣性衝擊技術的PM2.5控制設備,其包括一微粒凝結成長器及一濕式多噴嘴慣性衝擊器;微粒凝結成長器包括一氣膠流入口、一蒸汽流入口、一混合腔、一成長腔及一混合氣膠流出口,該氣膠流入口連通於該混合腔並位於該混合腔的上游,該蒸汽流入口位於該混合腔內,該成長腔位於該混合腔的下游,該混合氣膠流出口連通於該成長腔並位於該成長腔的下游;濕式多噴嘴慣性衝擊器包括一混合氣膠流入口、一預備腔、一噴嘴板、一注水式衝擊板、一介於噴嘴板與注水式衝擊板之間的間隙、一尾流腔及一尾流出口,該混合氣膠流入口連通於該混合氣膠流出口及該預備腔並位於該預備腔的上游,該噴嘴板設於該注水式衝擊板並位於該預備腔與該注水式衝擊板之間,且該噴嘴板具有多個連通於該預備腔與該衝擊腔之間的噴孔,該注水式衝擊板具有一微粒衝擊面、至少一形成於該微粒衝擊面的注水口、一注水流道、一局部環繞該微粒衝擊面的集水井、一局部環繞該集水井的氣流通道及一汲水流道,該注水流道連通於該注水流道,該汲水流道連通於該集水井,該氣流通道連通於該間隙及該尾流腔之間、該尾流出口連通於該尾流腔;其中,該氣膠流入口是供導入一含有多個微粒的氣膠流,該蒸汽流入口是供導入一水蒸汽流,該混合腔是供所述氣膠流及所述水蒸汽流混合成一混合氣膠流,該成長腔是供過飽和的水蒸汽凝結於所述微粒表面而增加所述微粒的粒徑,該噴嘴板是供增加混合氣膠流噴向該間隙的流速,該微粒衝擊面是供收集因慣性衝擊該微粒衝擊面的所述微粒,該注水口是供注水於該微粒衝擊面而收集該微粒衝擊面上的所述微粒,並加以洗除,該集水井是供收集該注水口向該微粒衝擊面注出的水,該氣流通道是供微粒分離後的混合氣膠流的尾流流向該尾流腔。In order to achieve the above and other objectives, the present invention provides a PM2.5 control device that combines particle coagulation growth and inertial impact technology, which includes a particle coagulation growth device and a wet multi-nozzle inertial impactor; the particle coagulation growth device includes an aerosol Inlet, a steam inflow, a mixing chamber, a growth chamber and a mixed aerosol outflow, the aerosol inflow is connected to the mixing chamber and located upstream of the mixing chamber, and the steam inflow is in the mixing chamber The growth chamber is located downstream of the mixing chamber, and the mixed aerosol flow outlet is connected to the growth chamber and located downstream of the growth chamber; the wet multi-nozzle inertial impactor includes a mixed aerosol flow inlet, a preparation chamber, and a Nozzle plate, a water injection impingement plate, a gap between the nozzle plate and the water injection impingement plate, a wake cavity and a wake outlet, the mixed gas glue flow inlet is connected to the mixed gas glue flow outlet and the preparation The cavity is located upstream of the preparation cavity, the nozzle plate is arranged on the water injection impingement plate and between the preparation cavity and the water injection impingement plate, and the nozzle plate has a plurality of communication between the preparation cavity and the impingement cavity. The water injection impact plate has a particle impact surface, at least one water injection port formed on the particle impact surface, a water injection channel, a water collection well partially surrounding the particle impact surface, and a water collection well partially surrounding the water collection well The airflow channel and a water pumping channel connected to the water injection channel, the water pumping channel connected to the water collection well, the air channel connected between the gap and the wake cavity, and the wake outlet connected In the wake chamber; wherein, the aerosol flow inlet is for introducing an aerosol flow containing a plurality of particles, the steam inlet is for introducing a water vapor flow, and the mixing chamber is for the aerosol flow and all The water vapor stream is mixed into a mixed aerosol flow, the growth chamber is for supersaturated water vapor to condense on the surface of the particles to increase the particle size of the particles, and the nozzle plate is used to increase the mixed aerosol flow to the gap The particle impact surface is used to collect the particles impacting the particle impact surface due to inertia, and the water injection port is for injecting water on the particle impact surface to collect and wash the particles on the particle impact surface. The water collection well is used to collect the water injected from the water injection port to the particle impact surface, and the air flow channel is for the wake of the mixed gas glue stream after the particles are separated to flow to the wake cavity.
通過上述設計,氣膠流中的微粒會在微粒凝結成長器中凝結成長為較大的粒徑,而後在濕式多噴嘴慣性衝擊器中被注水式衝擊板收集,從而實現了低壓損、低處理成本及高收集效率等效果。Through the above design, the particles in the aerogel flow will condense and grow into a larger particle size in the particle coagulation growth device, and then be collected by the water injection impact plate in the wet multi-nozzle inertial impactor, thereby achieving low pressure loss and low pressure loss. Effects of processing cost and high collection efficiency.
請參考第1至3圖,所繪示者為本發明微粒凝結成長結合慣性衝擊設計的PM2.5控制設備(以下簡稱微粒控制設備)的其中一實施例,其包括一微粒凝結成長器1及一濕式多噴嘴慣性衝擊器2。該微粒控制設備可用於去除氣體中的微粒,例如可用於處理半導體製程中所產生的廢氣,其中可能含有但不限於二氧化矽等微粒,這些微粒的粒徑可能介於0.1-1 µm,為白煙排放的主要來源。Please refer to Figures 1 to 3, which shows one of the embodiments of the PM2.5 control device (hereinafter referred to as the particle control device) designed for particle coagulation growth combined with inertial impact of the present invention, which includes a particle
微粒凝結成長器1包括一氣膠流入口11、一蒸汽流入口12、一混合腔13、一成長腔14及一混合氣膠流出口15。氣膠流入口11連通於混合腔13並位於混合腔13的上游,供導入一含有微粒的氣膠流(Aerosol stream)。蒸汽流入口12是形成於蒸汽流導管121的末端,蒸汽流導管121的入口端具有較大的內徑,例如5 mm,末端則具有較小的內徑,例如1 mm,從而使得所導入的水蒸汽流可以較高的流速被噴入混合腔13並形成紊流(turbulent flow),呈紊流的水蒸汽流可與氣膠流以更好的混合效率在混合腔13內混合成一混合氣膠流;被導入混合腔13的氣膠流在混合腔13的流向與水蒸汽流被噴入的方向相同,但也可設計成相反方向以增加氣膠流與水蒸汽流的混合效果;其中,所導入的氣膠流例如為常溫,水蒸汽流的溫度例如為100℃,兩者相混後,混合氣膠流的溫度將會下降,從而使得混合氣膠流處於過飽和的狀態。The particle
成長腔14位於混合腔13的下游,混合氣膠流中過飽和的水蒸汽可在成長腔14內凝結於微粒表面而增加微粒的粒徑,混合氣膠流在成長腔14中實質上在一軸向L上流動;設置時,本實施例的微粒控制設備可被傾斜設置,例如與水平面之間具有25∘的夾角,並且成長腔14的下游側高於其上游測,如此一來,凝結於成長腔14腔壁141上的水不會流向下游的濕式多噴嘴衝擊器2,且至少部分凝結於成長腔14腔壁141上的水可從腔壁141上的凝結水排出口142排出,其中,該腔壁141界定了成長腔14,凝結水排出口142則位於腔壁141中重力位能最低的一側,例如位於微粒控制設備傾斜後靠近地面的一側的底部。混合氣膠流出口15連通於成長腔14並位於成長腔14的下游。The
濕式多噴嘴慣性衝擊器2包括一混合氣膠流入口21、一預備腔22、一噴嘴板23、一注水式衝擊板25、噴嘴板與注水式衝擊板之間的一間隙(gap)24、一尾流腔26及一尾流出口27。混合氣膠流入口21連通於混合氣膠流出口15及預備腔22並位於預備腔22的上游,混合氣膠流入口21與混合氣膠流出口15之間可設有轉接環/轉接管而將兩者加以連接。噴嘴板23設於注水式衝擊板25並位於預備腔22與間隙24之間,間隙24的高度為噴嘴板23與注水式衝擊板25之間的距離(或稱噴流至衝擊板的距離,jet-to-plate distance),通常很小只為噴嘴直徑的一半到數倍(例如2倍)之間,且噴嘴板23具有多個噴孔231,噴孔231的孔徑越小,混合氣膠流經由噴嘴噴向間隙24的氣膠流速將被加速得越快,可以增加微粒的慣性使注水式衝擊板25可收集到較小的微粒(或截取氣動直徑較小),但易導致氣流的壓損提高;相反地,噴孔231的孔徑越大,混合氣膠流24經由噴嘴噴向間隙24的流速越小,微粒慣性較小,注水式衝擊板25只能收集到較大的微粒,但壓損較低。The wet multi-nozzle
注水式衝擊板25具有一微粒衝擊面251、一形成於微粒衝擊面251的注水口252、一注水流道253、一局部環繞微粒衝擊面251的集水井254、一局部環繞集水井254的氣流通道255及一汲水流道256。微粒衝擊面251是供收集因慣性衝擊微粒衝擊面251的微粒,微粒衝擊面251上可放置材質可為但不限於玻璃纖維的濾紙。注水流道253連通於注水口252,讓注水口252可供注水於微粒衝擊面251而收集微粒衝擊面251的微粒,並加以洗除,在可能的實施方式中,微粒衝擊面251上可設置濾紙(未繪示),濾紙的設置可以使注水不易被高速氣流吹飛,增加微粒收集的效率。集水井254是供收集微粒衝擊面251上的注水,所收集的注水可自汲水流道256排出;其中,注水式衝擊板25更具有一界定集水井254外輪廓的井壁257,井壁257具有一與微粒衝擊面251等高的頂面2571,藉此避免或至少大幅減少混合氣膠流中的水蒸汽凝結於井壁257內緣的情形。氣流通道255連通於衝擊腔24及尾流腔26之間,可供微粒分離後的混合氣膠流的尾流流向尾流腔26,尾流出口27則連通於尾流腔26,讓所述尾流能夠離開濕式多噴嘴慣性衝擊器2。The water
為了便於調整濕式多噴嘴慣性衝擊器2的截取氣動直徑,濕式多噴嘴慣性衝擊器2更可包括至少一高度調整墊片28設於噴嘴板23與注水式衝擊板25之間,用以調整噴孔231至微粒衝擊面251的間隙24的高度(或稱噴流至衝擊板的距離,jet-to-plate distance),所述高度調整墊片28例如可為厚度介於0.25-0.8 mm的聚四氟乙烯墊片及/或厚度約0.1 mm的金屬片,當所述間隙24的高度藉由設置高度調整墊片而調整時,濕式多噴嘴慣性衝擊器2的截取氣動直徑即可被調整,通常此高度越小,截取氣動直徑越小,但間隙24的高度應維持在噴嘴的直徑的一半以上,否則會顯著提高氣流壓損。In order to facilitate the adjustment of the intercepted aerodynamic diameter of the wet multi-nozzle
在一項微粒收集效率測試中,含有粒徑介於20-980 nm(眾數直徑mode diameter為126.3 nm)的氯化鈉微粒的常溫氣膠流被導入前述實施例的氣膠流入口,另有100 ℃的蒸汽流被導入蒸汽流入口與常溫氣膠流混合,在蒸汽流和氣膠流的質量流率混合比為0.1及0.12(蒸汽流:氣膠流)時分別進行二種情況的測試,濕式多噴嘴慣性衝擊器的氣動截取直徑(D pa50)設定為1 µm,其中噴孔的直徑為0.72 mm,噴孔至微粒衝擊面的距離為0.72 mm(jet-to-plate distance, 此時S/W=1),測試後的結果如下表一、表二所示。 In a particle collection efficiency test, a room-temperature aerosol stream containing sodium chloride particles with a particle size of 20-980 nm (mode diameter of 126.3 nm) was introduced into the aerosol inlet of the previous embodiment. A steam stream of 100 ℃ is introduced into the steam inlet to mix with the normal temperature aerosol stream. When the mass flow rate mixing ratio of the steam stream and the aerosol stream is 0.1 and 0.12 (steam stream: aerosol stream), the two conditions are tested respectively. , The aerodynamic intercept diameter (D pa50 ) of the wet multi-nozzle inertial impactor is set to 1 µm, the diameter of the nozzle hole is 0.72 mm, and the distance from the nozzle hole to the particle impact surface is 0.72 mm (jet-to-plate distance, this When S/W=1), the results after the test are shown in Table 1 and Table 2.
表一
表二
從表一的測試結果可見,當蒸汽流與氣膠流的質量混合比介於0.1-0.12時,可預期微粒收集的效率可達97%以上(數量濃度收集效率)及將近100%(重量濃度收集效率)。此外,進一步分析不同微粒粒徑的數量濃度收集效率,也可以發現氣膠流中的次微米(小於1微米或1000 nm)微粒的效率均高於96.9%以上,當微粒小至47 nm時仍有超過97%的收集效率,由此可證,本發明所提供的微粒控制設備中,即便濕式多噴嘴慣性衝擊器的氣動截取直徑高達1 µm,但與微粒凝結成長器合併使用後,對於次微米的小微粒(粒徑在47 nm以上)的收集效率很高,微粒的控制性能十分優異。除此之外,由於濕式多噴嘴慣性衝擊器氣動截取直徑為微米級,噴孔孔徑大,因此當混合比例為0.1時,微粒控制設備可以收集到次微米的微粒,且工作壓損僅為2840 Pa,為相當低的工作壓損,並有效的減少抽氣幫浦的耗電量,而這進一步衍生了另一項優點在於:本發明的微粒處理成本極低,費用分析如下表三所示。It can be seen from the test results in Table 1 that when the mass mixing ratio of the steam flow and the aerogel flow is between 0.1-0.12, the particle collection efficiency can be expected to reach over 97% (quantity concentration collection efficiency) and nearly 100% (weight concentration) Collection efficiency). In addition, further analysis of the collection efficiency of the number and concentration of different particle sizes, it can also be found that the efficiency of sub-micron (less than 1 micron or 1000 nm) particles in the aerosol flow is higher than 96.9%, and the particles are still as small as 47 nm. With a collection efficiency of over 97%, it can be proved that in the particle control equipment provided by the present invention, even if the aerodynamic intercepting diameter of the wet multi-nozzle inertial impactor is as high as 1 µm, it is The collection efficiency of sub-micron small particles (diameter above 47 nm) is very high, and the control performance of the particles is very excellent. In addition, because the wet multi-nozzle inertial impactor has a pneumatic interception diameter of micrometers and a large nozzle hole diameter, when the mixing ratio is 0.1, the particle control equipment can collect sub-micron particles, and the working pressure loss is only 2840 Pa, which is quite low working pressure loss, and effectively reduces the power consumption of the pumping pump, and this further derives another advantage: the particle processing cost of the present invention is extremely low, and the cost analysis is shown in Table 3 below Show.
表三
從表三的費用試算可見,由於本發明不需要通過高壓損、以較低的混合比例即可取得優異的微粒去除效率,並且用水量少,幫浦電費及水費極低,處理費用的大宗來源為產生水蒸汽所需的加熱器電費,但即便如此,每公升廢氣的處理費仍僅為新台幣0.00036元,為相當便宜的處理成本。如果能利用廠內的多餘蒸汽,或通過回收製程廢熱或利用再生能源降低加熱器的電費,則處理成本還可進一步降低。It can be seen from the cost calculations in Table 3 that, because the present invention does not require high pressure loss, can achieve excellent particle removal efficiency with a low mixing ratio, and uses less water, the pump electricity and water costs are extremely low, and the processing costs are large. The source is the heater electricity fee required to generate water vapor, but even so, the treatment fee per liter of exhaust gas is still only NT$0.00036, which is a fairly cheap treatment cost. If the excess steam in the plant can be utilized, or the electricity bill of the heater can be reduced by recycling process waste heat or using renewable energy, the processing cost can be further reduced.
在另一項利用第1至3圖所示實施例進行的負載測試中,四個測試組被依下表四所示的條件進行測試,氣膠流中含有多徑(polydisperse)二氧化鈦微粒,其中二氧化鈦微粒被導入微粒控制設備的流量為1.22 mg/min,測試組一、二分別進行25分鐘的負載測試,測試組三、四分別進行45分鐘的負載測試,各測試組其餘測試條件彼此相同。經過測試後,比較測試前後的微粒控制設備壓損,結果顯示於表五,測試組三、四的微粒收集效率則另顯示於表六。In another load test using the embodiment shown in Figures 1 to 3, four test groups were tested under the conditions shown in Table 4 below. The aerogel stream contained polydisperse titanium dioxide particles, where The flow rate of titanium dioxide particles introduced into the particle control device was 1.22 mg/min. Test groups one and two were subjected to a 25-minute load test, and test groups three and four were subjected to a 45-minute load test. The remaining test conditions of each test group were the same. After the test, the pressure loss of the particle control equipment before and after the test is compared, and the results are shown in Table 5. The particle collection efficiency of test groups 3 and 4 are also shown in Table 6.
表四
表五
表六
根據測試結果,發現測試組一的負載測試表現不佳,測試後在微粒衝擊面正對噴孔處觀察到多個峰狀微粒堆積,並且,在噴孔周圍觀察到線狀微粒堆積。從表五的測試結果可見,只要微粒控制設備內有被導入水蒸汽流,無論注水口是否注水,測試前後的壓損提升率都能被大幅降低;例如,測試組二即便注水口沒有被注水,但經過25分鐘負載測試後,壓損就提升了17%;相對地,測試組三經過45分鐘負載測試後,壓損卻只提升了7.5%,發明人發現這是因為水蒸汽會凝結於微粒表面,衝擊微粒衝擊面之後,所凝結的水就能起到將微粒帶離微粒衝擊面的效果,使得注水口沒有注水的情況下,微粒在微粒衝擊面累積的情況並不明顯,從而不會使壓損顯著提高,並且能維持與測試組四相近的微粒去除效率。另一方面,與測試組三相較,測試組四表現了更好的長效性,其經過45分鐘負載測試後,壓損僅僅提升了2.9%,壓損隨時間提高的情形並不明顯,幾可忽略,並且,測試後完全沒有在微粒衝擊面及噴孔周圍觀察到微粒積累,而這顯然克服了本技術領域的技術偏見在於,過往認為微粒凝結成長技術不適合與慣性衝擊技術併用,因為微粒凝結成長後,將更容易地造成噴孔堵塞的問題。然而,通過實驗證明,將微粒凝結成長技術與慣性衝擊技術併用後,只要能有效地將微粒衝擊面上的水及微粒移除,就不會產生微粒積累、噴孔堵塞等現象。According to the test results, the load test performance of
請參考第4圖,所繪示者為本發明微粒控制設備的其中一實施例,其與前述實施例的差異主要在於,微粒衝擊面251表面形成有更多的注水口252,從而使注水、沖洗的效果更為均勻,適用於工作流量大的使用場合。Please refer to FIG. 4, which is one of the embodiments of the particle control device of the present invention. The main difference from the previous embodiments is that more
綜合上述,氣膠流中的微粒會在微粒凝結成長器中凝結成長為較大的粒徑,而後在具有較大截取氣動直徑的濕式多噴嘴慣性衝擊器中被注水式衝擊板收集並加以洗除,從而實現了低壓損、低處理成本及高收集效率等效果,為相當優異的微粒控制設備。In summary, the particles in the aerosol flow will condense and grow into a larger particle size in the particle coagulation growth device, and then be collected by the water injection impact plate in the wet multi-nozzle inertial impactor with a larger intercepted aerodynamic diameter. Washing off, thus achieving the effects of low pressure loss, low processing cost and high collection efficiency, it is a very excellent particle control equipment.
1:微粒凝結成長器 11:氣膠流入口 12:蒸汽流入口 121:蒸汽流導管 13:混合腔 14:成長腔 141:腔壁 142:凝結水排出口 15:混合氣膠流出口 2:濕式多噴嘴慣性衝擊器 21:混合氣膠流入口 22:預備腔 23:噴嘴板 231:噴孔 24:間隙 25:注水式衝擊板 251:微粒衝擊面 252:注水口 253:注水流道 254:集水井 255:氣流通道 256:汲水流道 257:井壁 2571:頂面 26:尾流腔 27:尾流出口 28:高度調整墊片 L:軸向1: Particle Condensation Growth Device 11: Aerosol inlet 12: Steam inlet 121: Steam flow duct 13: Mixing cavity 14: Growing cavity 141: Cavity Wall 142: Condensate Outlet 15: Mixed aerosol outlet 2: Wet multi-nozzle inertial impactor 21: Mixed aerosol inlet 22: Preparation cavity 23: Nozzle plate 231: nozzle 24: gap 25: Water injection impact plate 251: Particle Impact Surface 252: Water Filling Port 253: Water Injection Channel 254: Catch Well 255: Airflow channel 256: Water Flow Path 257: Well Wall 2571: top surface 26: Wake cavity 27: Wake exit 28: height adjustment gasket L: axial
第1圖為本發明其中一實施例的縱剖面示意圖。Figure 1 is a schematic longitudinal cross-sectional view of one of the embodiments of the present invention.
第2圖為本發明其中一實施例的濕式多噴嘴慣性衝擊器分解圖。Figure 2 is an exploded view of a wet multi-nozzle inertial impactor according to one embodiment of the present invention.
第3圖為本發明其中一實施例的濕式多噴嘴慣性衝擊器的注水式衝擊板的俯視示意圖。FIG. 3 is a schematic top view of the water injection type impact plate of the wet multi-nozzle inertial impactor according to one embodiment of the present invention.
第4圖為本發明另一實施例的濕式多噴嘴慣性衝擊器的注水式衝擊板的俯視示意圖。Fig. 4 is a schematic top view of a water-injection impact plate of a wet multi-nozzle inertial impactor according to another embodiment of the present invention.
1:微粒凝結成長器 1: Particle Condensation Growth Device
11:氣膠流入口 11: Aerosol inlet
12:蒸汽流入口 12: Steam inlet
121:蒸汽流導管 121: Steam flow duct
13:混合腔 13: Mixing cavity
14:成長腔 14: Growing cavity
141:腔壁 141: Cavity Wall
142:凝結水排出口 142: Condensate Outlet
15:混合氣膠流出口 15: Mixed aerosol outlet
2:濕式多噴嘴慣性衝擊器 2: Wet multi-nozzle inertial impactor
21:混合氣膠流入口 21: Mixed aerosol inlet
22:預備腔 22: Preparation cavity
23:噴嘴板 23: Nozzle plate
231:噴孔 231: nozzle
24:間隙 24: gap
25:注水式衝擊板 25: Water injection impact plate
251:微粒衝擊面 251: Particle Impact Surface
252:注水口 252: Water Filling Port
253:注水流道 253: Water Injection Channel
254:集水井 254: Catch Well
255:氣流通道 255: Airflow channel
256:汲水流道 256: Water Flow Path
257:井壁 257: Well Wall
2571:頂面 2571: top surface
26:尾流腔 26: Wake cavity
27:尾流出口 27: Wake exit
28:高度調整墊片 28: height adjustment gasket
L:軸向 L: axial
Claims (6)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW109127981A TWI722956B (en) | 2020-08-17 | 2020-08-17 | Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW109127981A TWI722956B (en) | 2020-08-17 | 2020-08-17 | Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques |
Publications (2)
Publication Number | Publication Date |
---|---|
TWI722956B true TWI722956B (en) | 2021-03-21 |
TW202208044A TW202208044A (en) | 2022-03-01 |
Family
ID=76035759
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
TW109127981A TWI722956B (en) | 2020-08-17 | 2020-08-17 | Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques |
Country Status (1)
Country | Link |
---|---|
TW (1) | TWI722956B (en) |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100519413C (en) * | 2002-02-19 | 2009-07-29 | 普莱克斯技术有限公司 | Method for removing contaminants from gases |
TWI435755B (en) * | 2011-12-07 | 2014-05-01 | Ind Tech Res Inst | A transonic recovery system for elements |
US20140284203A1 (en) * | 2013-03-08 | 2014-09-25 | Xyleco, Inc. | Controlling process gases |
TWI516754B (en) * | 2014-06-11 | 2016-01-11 | 黃振榮 | Gas and aerosol compositions monitor and aerosol sampler |
CN105536423A (en) * | 2016-01-31 | 2016-05-04 | 河北工业大学 | Smoke gas PM2.5 (particulate matter 2.5) removing device and process of coal burning boiler |
-
2020
- 2020-08-17 TW TW109127981A patent/TWI722956B/en active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100519413C (en) * | 2002-02-19 | 2009-07-29 | 普莱克斯技术有限公司 | Method for removing contaminants from gases |
TWI435755B (en) * | 2011-12-07 | 2014-05-01 | Ind Tech Res Inst | A transonic recovery system for elements |
US20140284203A1 (en) * | 2013-03-08 | 2014-09-25 | Xyleco, Inc. | Controlling process gases |
TWI516754B (en) * | 2014-06-11 | 2016-01-11 | 黃振榮 | Gas and aerosol compositions monitor and aerosol sampler |
CN105536423A (en) * | 2016-01-31 | 2016-05-04 | 河北工业大学 | Smoke gas PM2.5 (particulate matter 2.5) removing device and process of coal burning boiler |
Also Published As
Publication number | Publication date |
---|---|
TW202208044A (en) | 2022-03-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN206701014U (en) | A kind of high Combined dust-cleaning apparatus of efficiency of dust collection | |
KR101919149B1 (en) | Air purification system usin condentional growth | |
CN201818322U (en) | Gas-compressing, deslagging, drilling and dust remover for coal mine downhole | |
CN100462636C (en) | Hydrokinetic type supersonic wave air-conditioning spray chamber | |
CN104906896A (en) | Cloud type dust removal system | |
TWI722956B (en) | Pm2.5 control device designed by combining particle condensation growth and inertial impaction techniques | |
CN103705955B (en) | A kind of circulating fluidised bed apparatus and for the method for pollen pini sterilizing removal of impurities | |
KR101025881B1 (en) | Liquid Collector | |
CN106958454B (en) | Wet-type coal mine dust collector | |
CN108636044A (en) | Cleaner and dust pelletizing system | |
KR100321375B1 (en) | Venturi scrubber dust collection system using steam injection and condensing effect | |
CN212508593U (en) | Air filter with injection dust collecting device | |
CN107983059A (en) | Press mist theisen disintegrator | |
CN205308070U (en) | Dust removal drainage device | |
CN216062585U (en) | Counter-flow wet dust-removing tower | |
CN208066058U (en) | A kind of diesel-driven generator emission-control equipment | |
RU2366493C1 (en) | Air cleaner | |
EP0079081B1 (en) | Atomizing nozzles, so2 reactors and flue gas cleaning plants | |
CN214693343U (en) | Solid sodium chloride aerosol generating device with adjustable counting median diameter distribution | |
KR100435568B1 (en) | Scrubber dust collecting elevation apparatus of rotary kiln | |
CN220835724U (en) | Stone crushing equipment | |
CN211008784U (en) | Pressure surface purging and dewatering structure for hollow stationary blade of steam turbine | |
TWI805400B (en) | Novel inertia impactor for nanoparticle classification | |
CN103924538A (en) | Exhaust gas dust collector of self-energized sweeping machine based on self-circulation of waste water | |
CN218154269U (en) | Dust suction device for slag cooler of boiler |