TWI694226B - Direct combustion return high-efficiency organic waste gas treatment system and method - Google Patents
Direct combustion return high-efficiency organic waste gas treatment system and method Download PDFInfo
- Publication number
- TWI694226B TWI694226B TW108102219A TW108102219A TWI694226B TW I694226 B TWI694226 B TW I694226B TW 108102219 A TW108102219 A TW 108102219A TW 108102219 A TW108102219 A TW 108102219A TW I694226 B TWI694226 B TW I694226B
- Authority
- TW
- Taiwan
- Prior art keywords
- pipeline
- gas
- hot
- heat exchanger
- pipe
- Prior art date
Links
Images
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/06—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with moving adsorbents, e.g. rotating beds
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/40—Further details for adsorption processes and devices
- B01D2259/40083—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption
- B01D2259/40088—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating
- B01D2259/4009—Regeneration of adsorbents in processes other than pressure or temperature swing adsorption by heating using hot gas
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treating Waste Gases (AREA)
Abstract
本發明為一種直燃回流高效率有機廢氣處理系統及其方法,主要係將直燃式焚燒爐的排氣能經由至少三個以上的熱交換器來進行熱回收,並將該直燃式焚燒爐的排氣再經由一個熱交換器和吸附區出口的淨氣排放管路的排出氣體(吸附處理氣體)進行熱交換,而得以冷卻再輸送到該除塵設備中,以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備所輸出的氣體輸送到該廢氣進氣管路,使燃燒後的氣體能進入該吸附轉輪之吸附區循環利用,而不經過該煙囪來進行排放,讓該煙囪的排放量能降低,並使有機廢氣的處理效率能提升。 The invention is a direct-fired reflux high-efficiency organic waste gas treatment system and method, which mainly consists of recovering heat from the exhaust gas of a direct-fired incinerator through at least three or more heat exchangers, and burned the direct-fired incinerator The exhaust gas of the furnace is then heat-exchanged through a heat exchanger and the exhaust gas (adsorption processing gas) of the clean gas discharge pipe at the outlet of the adsorption zone, and then cooled and then sent to the dust removal equipment for dust or silica (SiO 2 ) and other oxides are separated, and finally the gas output from the dust removal device is sent to the exhaust gas inlet line, so that the burned gas can enter the adsorption area of the adsorption wheel for recycling without passing through the The chimney is used to discharge, so that the discharge amount of the chimney can be reduced, and the treatment efficiency of organic waste gas can be improved.
Description
本發明係有關於一種直燃回流高效率有機廢氣處理系統及其方法,尤指一種用來將燃燒後的氣體能進入該吸附轉輪之吸附區循環利用,且不用經過該煙囪來進行排放,使有機廢氣的處理效率能提升,而適用於半導體產業、光電產業或化學相關產業的有機廢氣處理系統或類似設備。 The present invention relates to a direct combustion recirculation high-efficiency organic waste gas treatment system and method, in particular to a system for recycling the burned gas into the adsorption zone of the adsorption runner without recycling through the chimney. The organic waste gas treatment efficiency can be improved, and it is suitable for the organic waste gas treatment system or similar equipment in the semiconductor industry, photoelectric industry or chemical related industries.
按,目前在半導體產業或光電產業的製造生產過程中都會產生具有揮發性有機氣體(VOC),因此,在各廠區都會安裝處理揮發性有機氣體(VOC)的處理設備,以避免揮發性有機氣體(VOC)直接排入空氣中而造成空氣污染。而目前經由該處理設備所脫附的濃縮氣體大都是輸送到該焚燒爐來進行燃燒,再將燃燒後的氣體來輸送到煙囪來進行排放。 According to the current, volatile organic gas (VOC) will be generated in the manufacturing process of the semiconductor industry or optoelectronic industry. Therefore, processing equipment for processing volatile organic gas (VOC) will be installed in each plant to avoid volatile organic gas (VOC) is directly discharged into the air and causes air pollution. At present, most of the concentrated gas desorbed by the processing equipment is sent to the incinerator for combustion, and then the burned gas is sent to the chimney for discharge.
但是近年來,不管是中央政府或是各地方政府都對空氣汙染非常重視,也因此在煙囪的排放標準上訂定了有關懸浮微粒(PM10)及細懸浮微粒(PM2.5)空氣品質標準,並依據其國內健康影響研究結果,以健康影響為優先考量,將「細懸浮微粒(PM2.5)」24小時值訂為35μg/m3、年平均值訂為15μg/m3。且環保署初步訂於民國109(2020)年達成全國細懸浮微粒濃度年平均值15μg/m3的目標,同時將依國際管制趨勢發展,逐期檢討其細懸浮微粒(PM2.5)空氣品質標準,並朝達成WHO提出之空氣品質準則 值(24小時值訂為25μg/m3、年平均值訂為10μg/m3)為空氣品質改善目標。 However, in recent years, both the central government and local governments have attached great importance to air pollution. Therefore, the air quality standards for suspended particulates (PM 10 ) and fine suspended particulates (PM 2.5 ) have been set in the chimney emission standards. And based on the results of its domestic health impact studies, taking health effects as a priority, the 24-hour value of "fine suspended particles (PM 2.5 )" was set at 35 μg/m 3 and the annual average value was set at 15 μg/m 3 . In addition, the EPA is initially scheduled to reach the national average annual fine particle concentration of 15μg/m 3 in 109 (2020) in the Republic of China. At the same time, it will review its air quality standards for fine particulate matter (PM 2.5 ) phase by phase according to the development of international control trends. In order to achieve the air quality improvement goal set by the WHO (the 24-hour value is set at 25 μg/m 3 and the annual average value is set at 10 μg/m 3 ).
因此,本發明人有鑑於上述缺失,期能提出一種具有提升有機廢氣處理效率的直燃回流高效率有機廢氣處理系統及其方法,令使用者可輕易操作組裝,乃潛心研思、設計組製,以提供使用者便利性,為本發明人所欲研發之發明動機者。 Therefore, in view of the above deficiencies, the present inventors hope to propose a direct combustion recirculation high-efficiency organic exhaust gas treatment system and method with improved organic exhaust gas treatment efficiency, so that the user can easily operate the assembly, but devotes himself to the design In order to provide user convenience, it is the motive of the invention that the inventor wants to develop.
本發明之主要目的,在於提供一種直燃回流高效率有機廢氣處理系統及其方法,主要係將直燃式焚燒爐的排氣能經由至少三個以上的熱交換器來進行熱回收,並將該直燃式焚燒爐的排氣再經由一個熱交換器和吸附區出口的淨氣排放管路的排出氣體(吸附處理氣體)進行熱交換,而得以冷卻再輸送到該除塵設備中,以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備所輸出的氣體輸送到該廢氣進氣管路,使燃燒後的氣體能進入該吸附轉輪之吸附區循環利用,而不經過該煙囪來進行排放,讓該煙囪的排放量能降低,並使有機廢氣的處理效率能提升,進而增加整體之實用性。 The main object of the present invention is to provide a direct combustion recirculation high-efficiency organic waste gas treatment system and method thereof, which mainly recover heat from the exhaust gas of a direct combustion incinerator through at least three heat exchangers, and The exhaust gas of the direct-fired incinerator is then subjected to heat exchange through a heat exchanger and the exhaust gas (adsorption treatment gas) of the clean gas discharge pipe at the outlet of the adsorption zone, which is cooled and then transported to the dust removal equipment for Separation of oxides such as dust or silicon dioxide (SiO 2 ), and finally the gas output from the dust removal equipment is sent to the exhaust gas intake line, so that the burned gas can enter the adsorption area of the adsorption rotor for recycling Instead of passing through the chimney for discharge, the discharge of the chimney can be reduced, and the treatment efficiency of organic waste gas can be improved, thereby increasing the overall practicality.
本發明之另一目的,在於提供一種直燃回流高效率有機廢氣處理系統及其方法,透過該冷卻氣輸送管路與該熱氣輸送管路之間設有一連通管路,且該連通管路係設有一連通控制閥門,而該熱氣輸送管路係設有一熱氣控制閥門,並透過該連通控制閥門及該熱氣控制閥門來形成比例風門,藉此,透過該連通控制閥門及該熱氣控制閥門之設計來形成具有比例風門之效能,以能調整控制風力之大小,讓該熱氣輸送管路內的溫度能保持一定高溫來提供給該吸附轉輪之脫附區使用,並具有節省能源之效 能,進而增加整體之使用性。 Another object of the present invention is to provide a direct combustion recirculation high-efficiency organic waste gas treatment system and method thereof, a communication line is provided between the cooling gas transmission line and the hot gas transmission line, and the communication line A communication control valve is provided, and the hot gas delivery pipeline is provided with a hot gas control valve, and a proportional damper is formed through the communication control valve and the hot gas control valve, thereby, through the communication control valve and the hot gas control valve It is designed to form the effect of proportional damper, which can adjust and control the size of wind force, so that the temperature in the hot gas delivery pipeline can maintain a certain high temperature to provide for the desorption area of the adsorption runner, and has the effect of saving energy Can further increase the overall usability.
本發明之在一目的,在於提供一種直燃回流高效率有機廢氣處理系統及其方法,透過該冷卻氣輸送管路與該熱氣輸送管路之間設有一連通管路,且該連通管路係設有一連通控制閥門,而該冷卻氣輸送管路係設有一冷卻氣控制閥門,並透過該連通控制閥門及該冷卻氣控制閥門來形成比例風門,藉此,透過該連通控制閥門及該冷卻氣控制閥門之設計來形成具有比例風門之效能,以能調整控制風力之大小,讓該熱氣輸送管路內的溫度能保持一定高溫來提供給該吸附轉輪之脫附區使用,並具有節省能源之效能,進而增加整體之操作性。 An object of the present invention is to provide a direct combustion recirculation high-efficiency organic waste gas treatment system and method thereof, a communication line is provided between the cooling gas transmission line and the hot gas transmission line, and the communication line A communication control valve is provided, and the cooling gas delivery line is provided with a cooling gas control valve, and a proportional damper is formed through the communication control valve and the cooling gas control valve, thereby, through the communication control valve and the The cooling gas control valve is designed to form the effect of a proportional damper, which can adjust and control the size of the wind force, so that the temperature in the hot gas delivery pipeline can maintain a certain high temperature to provide the desorption area of the adsorption runner, and has Energy-saving efficiency, thereby increasing the overall operability.
為了能夠更進一步瞭解本發明之特徵、特點和技術內容,請參閱以下有關本發明之詳細說明與附圖,惟所附圖式僅提供參考與說明用,非用以限制本發明。 In order to further understand the features, characteristics and technical contents of the present invention, please refer to the following detailed description and drawings of the present invention, but the drawings are provided for reference and explanation only, and are not intended to limit the present invention.
10‧‧‧直燃式焚燒爐 10‧‧‧Direct-fired incinerator
11‧‧‧進氣口 11‧‧‧Air inlet
12‧‧‧出氣口 12‧‧‧ Outlet
20‧‧‧吸附轉輪 20‧‧‧Adsorption rotor
201‧‧‧吸附區 201‧‧‧Adsorption zone
202‧‧‧冷卻區 202‧‧‧ Cooling area
203‧‧‧脫附區 203‧‧‧Desorption zone
21‧‧‧廢氣進氣管路 21‧‧‧Exhaust gas inlet line
22‧‧‧淨氣排放管路 22‧‧‧Clean gas discharge pipeline
221‧‧‧風車 221‧‧‧Windmill
23‧‧‧冷卻氣進氣管路 23‧‧‧cooling air intake line
231‧‧‧氣體旁通管路 231‧‧‧gas bypass line
24‧‧‧冷卻氣輸送管路 24‧‧‧cooling gas delivery pipeline
241‧‧‧冷卻氣控制閥門 241‧‧‧Cooling gas control valve
25‧‧‧熱氣輸送管路 25‧‧‧ hot gas delivery pipeline
251‧‧‧熱氣控制閥門 251‧‧‧Hot gas control valve
26‧‧‧脫附濃縮廢氣管路 26‧‧‧Desorption concentrated waste gas pipeline
27‧‧‧連通管路 27‧‧‧Communication pipeline
271‧‧‧連通控制閥門 271‧‧‧Communication control valve
30‧‧‧第一熱交換器 30‧‧‧The first heat exchanger
301‧‧‧第一冷側管路 301‧‧‧The first cold side pipeline
302‧‧‧第一熱側管路 302‧‧‧The first hot side pipeline
31‧‧‧第一熱氣回收管路 31‧‧‧The first hot gas recovery pipeline
32‧‧‧第一焚燒熱氣回收管路 32‧‧‧The first incineration hot gas recovery pipeline
33‧‧‧第一脫附濃縮氣體輸送管路 33‧‧‧The first desorption concentrated gas delivery pipeline
40‧‧‧第二熱交換器 40‧‧‧Second heat exchanger
401‧‧‧第二冷側管路 401‧‧‧Second cold side pipeline
402‧‧‧第二熱側管路 402‧‧‧Second hot side pipeline
50‧‧‧第三熱交換器 50‧‧‧The third heat exchanger
501‧‧‧第三冷側管路 501‧‧‧The third cold side pipeline
502‧‧‧第三熱側管路 502‧‧‧The third hot side pipeline
51‧‧‧第三脫附濃縮氣體輸送管路 51‧‧‧The third desorption concentrated gas pipeline
52‧‧‧第三熱氣回收管路 52‧‧‧The third hot gas recovery pipeline
60‧‧‧第四熱交換器 60‧‧‧ Fourth heat exchanger
601‧‧‧第四冷側管路 601‧‧‧The fourth cold side pipeline
602‧‧‧第四熱側管路 602‧‧‧The fourth hot side pipeline
61‧‧‧第四脫附濃縮氣體輸送管路 61‧‧‧The fourth desorption concentrated gas delivery pipeline
62‧‧‧第四熱氣回收管路 62‧‧‧The fourth hot gas recovery pipeline
70‧‧‧第五熱交換器 70‧‧‧Fifth heat exchanger
701‧‧‧第五冷側管路 701‧‧‧The fifth cold side pipeline
702‧‧‧第五熱側管路 702‧‧‧The fifth hot side pipeline
71‧‧‧第五熱氣回收管路 71‧‧‧The fifth hot gas recovery pipeline
80‧‧‧除塵設備 80‧‧‧Dust removal equipment
81‧‧‧除塵進氣管路 81‧‧‧ Dust intake pipe
82‧‧‧除塵出氣管路 82‧‧‧Dust-removing air outlet pipe
821‧‧‧風車 821‧‧‧Windmill
90‧‧‧煙囪 90‧‧‧Chimney
91‧‧‧煙囪排放管路 91‧‧‧Chimney discharge pipe
S100‧‧‧吸附區吸附 S100‧‧‧adsorption zone adsorption
S110‧‧‧冷卻區冷卻 S110‧‧‧cooling in cooling zone
S120‧‧‧脫附區脫附 S120‧‧‧Desorption zone desorption
S130‧‧‧脫附濃縮氣體輸送 S130‧‧‧Desorption concentrated gas delivery
S140‧‧‧焚燒氣體回收輸送 S140‧‧‧Incineration gas recovery and transportation
S150‧‧‧焚燒氣體再輸送 S150‧‧‧Incineration gas retransmission
S160‧‧‧經過除塵設備回收 S160‧‧‧Recycled through dust removal equipment
S200‧‧‧吸附區吸附 S200‧‧‧Adsorption zone adsorption
S210‧‧‧冷卻區冷卻 S210‧‧‧cooling zone cooling
S220‧‧‧脫附區脫附 S220‧‧‧Desorption zone desorption
S230‧‧‧脫附濃縮氣體輸送 S230‧‧‧Desorption concentrated gas delivery
S240‧‧‧焚燒氣體回收輸送 S240‧‧‧Incineration gas recycling
S250‧‧‧焚燒氣體再輸送 S250‧‧‧Incineration gas retransmission
S260‧‧‧經過除塵設備回收 S260‧‧‧Recycled through dust removal equipment
第1圖係為本發明之第一種實施方式的主要步驟流程圖。 Figure 1 is a flowchart of the main steps of the first embodiment of the present invention.
第2圖係為本發明之第一種實施方式的主要架構示意圖。 Figure 2 is a schematic diagram of the main structure of the first embodiment of the present invention.
第3圖係為本發明之第一種實施方式的第一種比例風門的架構示意圖。 FIG. 3 is a schematic structural diagram of a first proportional damper according to the first embodiment of the present invention.
第4圖係為本發明之第一種實施方式的第二種比例風門的架構示意圖。 FIG. 4 is a schematic structural diagram of a second proportional damper according to the first embodiment of the present invention.
第5圖係為本發明之第二種實施方式的主要步驟流程圖。 Figure 5 is a flowchart of the main steps of the second embodiment of the present invention.
第6圖係為本發明之第二種實施方式的主要架構示意圖。 Figure 6 is a schematic diagram of the main structure of the second embodiment of the present invention.
第7圖係為本發明之第二種實施方式的第一種比例風門的架構示意圖。 FIG. 7 is a schematic structural diagram of a first proportional damper in a second embodiment of the present invention.
第8圖係為本發明之第二種實施方式的第二種比例風門的架構示意圖。 FIG. 8 is a schematic structural diagram of a second proportional damper according to the second embodiment of the present invention.
請參閱第1~8圖,係為本發明實施例之示意圖,而本發明之直燃回流高效率有機廢氣處理系統及其方法的最佳實施方式係運用於半導體產業、光電產業或化學相關產業的揮發有機廢氣處理系統或類似設備,主要是將燃燒後的氣體能進入該吸附轉輪之吸附區循環利用,且不經過該煙囪來進行排放,使有機廢氣的處理效率能提升。 Please refer to Figures 1~8, which are schematic diagrams of embodiments of the present invention, and the best embodiment of the direct combustion recirculation high-efficiency organic waste gas treatment system and method of the present invention is applied to the semiconductor industry, optoelectronic industry or chemical related industries The volatile organic waste gas treatment system or similar equipment is mainly used to recycle the burned gas into the adsorption area of the adsorption wheel and discharge it without passing through the chimney, so that the treatment efficiency of organic waste gas can be improved.
而本發明第一種實施方式的直燃回流高效率有機廢氣處理系統,主要係設有一直燃式焚燒爐10、一吸附轉輪20、一第一熱交換器30、一第二熱交換器40、一第三熱交換器50、一第五熱交換器70及一除塵設備80(如第2圖至第4圖所示),其中該第一熱交換器30係設有第一冷側管路301及第一熱側管路302,該第二熱交換器40係設有第二冷側管路401及第二熱側管路402,該第三熱交換器50係設有第三冷側管路501及第三熱側管路502,該第五熱交換器70係設有第五冷側管路701及第五熱側管路702,而該除塵設備80係為袋式除塵器、電袋式複合除塵器、慣性除塵器、靜電除塵器、離心式除塵器、濾筒式脈衝除塵器、脈衝袋式除塵器、脈衝濾芯除塵器、脈衝噴吹袋式除塵器、濕式除塵器、濕式電除塵器、濕式靜電除塵器、水膜除塵器、文丘里管除塵器、旋風分離器、煙道除塵器、多層除塵器、負壓反吹濾袋
除塵器、低壓長袋脈衝除塵器、臥式靜電除塵器、無動力除塵器、荷電水霧除塵器、多管旋風除塵器、防爆除塵器之其中任一,另該直燃式焚燒爐(TO)10係設有一進氣口11及一出氣口12,且該直燃式焚燒爐(TO)10內係設有爐頭及爐膛,使該有機廢氣能由該進氣口11來進入該爐頭進行燃燒,再讓經過燃燒後之氣體能穿過該爐膛並由該出氣口12來排出。
The direct combustion reflux high-efficiency organic waste gas treatment system of the first embodiment of the present invention is mainly provided with a direct-fired
而該吸附轉輪20係為沸石濃縮轉輪或是其他材質之濃縮轉輪,且該吸附轉輪20內係設有吸附區201、冷卻區202及脫附區203,該吸附轉輪20係設有一廢氣進氣管路21、一淨氣排放管路22、一冷卻氣進氣管路23、一冷卻氣輸送管路24、一熱氣輸送管路25及一脫附濃縮廢氣管路26(如第2圖至第4圖所示),而該廢氣進氣管路21的另一端係連接至該吸附轉輪20之吸附區201的一側,以使該吸附轉輪20之吸附區201能吸附該廢氣進氣管路21內的廢氣,且該淨氣排放管路22之一端係與該吸附轉輪20之吸附區201的另一側連接,讓該廢氣經該吸附轉輪20之吸附區201淨化後再由該淨氣排放管路22來輸送。
The
另該冷卻氣進氣管路23的一端係與該吸附轉輪20之冷卻區202的一側連接,而該冷卻氣進氣管路23係有兩種實施態樣,其中第一種實施態樣為該冷卻氣進氣管路23乃是供外氣進入(如第2圖及第3圖所示),而該外氣係為新鮮空氣,以將該外氣用來輸送到該吸附轉輪20之冷卻區202內提供降溫使用,另第二種實施態樣係該冷卻氣進氣管路23係設有一氣體旁通管路231(如第4圖所示),該氣體旁通管路231之一端係與該冷卻氣進氣管路23連接,而該氣體旁通管路231
之另一端係與該廢氣進氣管路21連接,透過該氣體旁通管路231來將部份的廢氣輸送到該吸附轉輪20之冷卻區203內提供降溫使用。
In addition, one end of the cooling
另該冷卻氣輸送管路24的一端係與該吸附轉輪20之冷卻區203的另一側連接,而該冷卻氣輸送管路24的另一端係與該第二熱交換器40之第二冷側管路401的一端連接,以能將該冷卻氣輸送管路24內的冷卻氣輸送到該第二熱交換器40內進行熱交換(如第2圖至第4圖所示),另該第二熱交換器40之第二冷側管路401的另一端係與該熱氣輸送管路25的另一端連接,而該熱氣輸送管路25的一端係與該吸附轉輪20之脫附區203的另一側連接,且該吸附轉輪20之脫附區203的一側係與該脫附濃縮氣體管路26的一端連接,使將經由該第二熱交換器50所提升之熱氣能透過該熱氣輸送管路25來傳輸到該吸附轉輪20之脫附區203來進行脫附使用,並將經過高溫所脫附下來的脫附濃縮氣體能透過該脫附濃縮氣體管路26來傳輸運送。
In addition, one end of the cooling
另本發明第一種實施方式中的該冷卻氣輸送管路24與該熱氣輸送管路25之間係設有比例風門,而該比例風門係設有兩種實施設計,其中第一種實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該熱氣輸送管路25係設有一熱氣控制閥門251(如第3圖所示),並透過該連通控制閥門271及該熱氣控制閥門25來形成比例風門,另第二實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該冷卻氣輸送管路24係設有一冷卻氣控制閥門241(如第4圖 所示),並透過該連通控制閥門271及該冷卻氣控制閥門241來形成比例風門,藉此,不管是透過該連通控制閥門271及該熱氣控制閥門251之設計的比例風門或是透過該該連通控制閥門271及該冷卻氣控制閥門241之設計的比例風門,皆能調整控制風力之大小,讓該熱氣輸送管路25內的溫度能保持一定高溫來提供給該吸附轉輪20之脫附區203使用。 In addition, in the first embodiment of the present invention, a proportional damper is provided between the cooling gas delivery pipe 24 and the hot gas delivery pipe 25, and the proportional damper is provided with two implementation designs, of which the first implementation design It is because a communication line 27 is provided between the cooling gas conveying line 24 and the hot gas conveying line 25, and the communicating line 27 is provided with a communication control valve 271, and the hot gas conveying line 25 is provided There is a hot gas control valve 251 (as shown in Figure 3), and a proportional damper is formed through the communication control valve 271 and the hot gas control valve 25, and the second implementation design is for the cooling gas delivery pipe 24 and the hot gas delivery A communication pipeline 27 is provided between the pipelines 25, and the communication pipeline 27 is provided with a communication control valve 271, and the cooling gas delivery pipeline 24 is provided with a cooling gas control valve 241 (as shown in FIG. 4) (Shown), and a proportional damper is formed through the communication control valve 271 and the cooling gas control valve 241, whereby, whether through the proportional damper of the communication control valve 271 and the design of the hot gas control valve 251 or through the The proportional damper designed to communicate with the control valve 271 and the cooling gas control valve 241 can adjust the size of the control wind so that the temperature in the hot gas delivery pipeline 25 can maintain a certain high temperature to provide desorption of the adsorption runner 20 Area 203 is used.
再者,該第三熱交換器50係連接有一第三脫附濃縮氣體輸送管路51及一第三熱氣回收管路52,該第三熱交換器50之第三冷側管路51的一端係與該脫附濃縮氣體管路26的另一端連接(如第2圖至第4圖所示),該第三脫附濃縮氣體輸送管路51的一端係與該第三熱交換器50之第三冷側管路501的另一端連接,該第三脫附濃縮氣體輸送管路51的另一端係與該第一熱交換器30之第一冷側管路301的一端連接,該第三熱氣回收管路52的一端係與該第三熱交換器50之第三熱側管路502的一端連接,該第三熱氣回收管路52的另一端係與該第二熱交換器40之第二熱側管路402的另一端連接。藉此,讓該吸附轉輪20之脫附區203所脫附下來的脫附濃縮氣體能透過該脫附濃縮氣體管路26來傳輸到該第三熱交換器50之第三冷側管路502來進行熱交換,並再透過該第三脫附濃縮氣體輸送管路51來傳輸到該第一熱交換器30之第一冷側管路301來進行熱交換。
Furthermore, the
另該第一熱交換器30係連接有一第一熱氣回收管路31、一第一焚燒熱氣回收管路32及一第一脫附濃縮氣體輸送管路33,其中該第一焚燒熱氣回收管路32的一端係與該第一熱交換器30之第一
熱側管路302的一端連接,該第一焚燒熱氣回收管路32的另一端係與該直燃式焚燒爐10之出氣口12連接(如第2圖至第4圖所示),該第一熱氣回收管路31的一端係與該第一熱交換器30之第一熱側管路302的另一端連接,該第一熱氣回收管路31的另一端係與該第二熱交換器40之第二熱側管路402的一端連接,該第一脫附濃縮氣體輸送管路33的一端係與該第一熱交換器30之第一冷側管路301的另一端連接,該第一脫附濃縮氣體輸送管路33的另一端係與該直燃式焚燒爐10之進氣口11連接。藉此,讓經由該第一熱交換器30之第一冷側管路301所輸送的脫附濃縮氣體能透過該第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10的進氣口11,再將經過該直燃式焚燒爐10所燃燒後之氣體能由該出氣口12來透過該第一焚燒熱氣回收管路32來輸送到該第一熱交換器30之第一熱側管路302內進行熱回收,並經由該第一熱氣回收管路31來輸送到該第二熱交換器40之第二熱側管路402內進行熱回收,且再經由該第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502內進行熱回收。
In addition, the
另該第五熱交換器70係連接有一第五熱氣回收管路71,該第五熱交換器70之第五冷側管路701的一端係與該淨氣排放管路22的另一端連接,該第五熱氣回收管路71的一端係與該第五熱交換器70之第五熱側管路702的一端連接,該第五熱氣回收管路71的另一端係與該第三熱交換器50之第三熱側管路502的另一端連接(如第2圖至第4圖所示)。而該除塵設備80係連接有一除塵進氣管路81及一除塵出氣管路82,該除塵進氣管路81的一端係與該除塵設備連80
接,該除塵進氣管路80的另一端係與該第五熱交換器70之第五熱側管路702的另一端連接,該除塵出氣管路82的一端係與該除塵設備80連接,該除塵出氣管路82的另一端係與該廢氣進氣管路21連接。另該除塵出氣管路82係設有一風車821,以能將該除塵出氣管路82內的氣體推向該廢氣進氣管路21內。藉此,將經過該直燃式焚燒爐10所燃燒後之氣體能由該第三熱交換器50之第三熱側管路502來透過該第五熱氣回收管路71輸送到該第五熱交換器70之第五熱側管路702進行熱回收,再透過該除塵進氣管路81來輸送到該除塵設備80內以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備80所輸出的氣體輸送到該廢氣進氣管路21,使燃燒後的氣體能進入該吸附轉輪20之吸附區201循環利用,而不經過該煙囪90來進行排放,讓該煙囪90的排放量能降低,並使有機廢氣的處理效率能提升。
In addition, the
最後,該第五熱交換器70係連接一煙囪90,該煙囪90係設有一煙囪排放管路91,該煙囪排放管路91的一端係與該煙囪90連接(如第2圖至第4圖所示),該煙囪排放管路91的另一端係與該第五熱交換器70之第五冷側管路701的另一端連接。讓經由該淨氣排放管路22所排出淨化後氣體能進入該第五熱交換器70之第五冷側管路701內進行熱交換,再經由該煙囪排放管路91來輸送到煙囪90來進行排放。另該淨氣排放管路22係設有一風車221,以能將該淨氣排放管路22內的氣體推向該第五熱交換器70之第五冷側管路701內。
Finally, the
而本發明第一種實施方式的直燃回流高效率有機廢氣處理方法,其主要係用於有機廢氣處理系統,且包括有一直燃式焚燒爐10, 一吸附轉輪20、一第一熱交換器30、一第二熱交換器40、一第三熱交換器50、一第五熱交換器70及一除塵設備80(如第2圖至第4圖所示),該吸附轉輪20係設有吸附區201、脫附區202及冷卻區203,該吸附轉輪20係連接有一廢氣進氣管路21、一淨氣排放管路22、一冷卻氣進氣管路23、一冷卻氣輸送管路24、一熱氣輸送管路25及一脫附濃縮氣體管路26,該第一熱交換器30係設有第一冷側管路301及第一熱側管路302,該第二熱交換器40係設有第二冷側管路401及第二熱側管路402,該第三熱交換器50係設有第三冷側管路501及第三熱側管路502,該第五熱交換器70係設有第五冷側管路701及第五熱側管路702。 The direct combustion recirculation high-efficiency organic waste gas treatment method of the first embodiment of the present invention is mainly used in an organic waste gas treatment system, and includes a direct-fired incinerator 10, An adsorption runner 20, a first heat exchanger 30, a second heat exchanger 40, a third heat exchanger 50, a fifth heat exchanger 70 and a dust removal device 80 (as shown in Figures 2 to 4) (Shown), the adsorption runner 20 is provided with an adsorption zone 201, a desorption zone 202 and a cooling zone 203, the adsorption runner 20 is connected to an exhaust gas intake line 21, a clean air discharge line 22, a Cooling gas inlet pipe 23, a cooling gas delivery pipe 24, a hot gas delivery pipe 25 and a desorbed concentrated gas pipe 26, the first heat exchanger 30 is provided with a first cold side pipe 301 and The first hot-side pipe 302, the second heat exchanger 40 is provided with a second cold-side pipe 401 and the second hot-side pipe 402, and the third heat exchanger 50 is provided with a third cold-side pipe 501 and a third hot-side pipeline 502, the fifth heat exchanger 70 is provided with a fifth cold-side pipeline 701 and a fifth hot-side pipeline 702.
而該除塵設備80係為袋式除塵器、電袋式複合除塵器、慣性除塵器、靜電除塵器、離心式除塵器、濾筒式脈衝除塵器、脈衝袋式除塵器、脈衝濾芯除塵器、脈衝噴吹袋式除塵器、濕式除塵器、濕式電除塵器、濕式靜電除塵器、水膜除塵器、文丘里管除塵器、旋風分離器、煙道除塵器、多層除塵器、負壓反吹濾袋除塵器、低壓長袋脈衝除塵器、臥式靜電除塵器、無動力除塵器、荷電水霧除塵器、多管旋風除塵器、防爆除塵器之其中任一,另該直燃式焚燒爐(TO)10係設有一進氣口11及一出氣口12,且該直燃式焚燒爐(TO)10內係設有爐頭及爐膛,使該有機廢氣能由該進氣口11來進入該爐頭進行燃燒,再讓經過燃燒後之氣體能穿過該爐膛並由該出氣口12來排出。而該處理方法的主要步驟(如第1圖所示)係包括:步驟S100吸附區吸附:將廢氣透過該廢氣進氣管路21的另一端來送入該吸附轉輪20之吸附區201的一側進行吸附,再將
吸附後之氣體透過該淨氣排放管路22的另一端來輸送到該第五熱交換器70之第五冷側管路701的一端。而完成上述步驟S100後即進行下一步驟S110。
The
其中上述之步驟S100中該第五熱交換器70係連接一煙囪90,該煙囪90係設有一煙囪排放管路91,該煙囪排放管路91的一端係與該煙囪90連接,該煙囪排放管路91的另一端係與該第五熱交換器70之第五冷側管路701的另一端連接(如第2圖至第4圖所示)。讓經由該淨氣排放管路22所排出淨化後氣體能進入該第五熱交換器70之第五冷側管路701內進行熱交換,再經由該煙囪排放管路91來輸送到煙囪90來進行排放。另該淨氣排放管路22係設有一風車221,以能將該淨氣排放管路22內的氣體推向該第五熱交換器70之第五冷側管路701內。
In the above step S100, the
另,下一步進行的步驟S110冷卻區冷卻:透過該冷卻氣進氣管路23的另一端來輸送冷卻氣至該吸附轉輪20之冷卻區202進行冷卻,再透過該冷卻氣輸送管路24的另一端來將經過冷卻區之冷卻氣輸送到該第二熱交換器40之第二冷側管路401的一端。而完成上述步驟S110後即進行下一步驟S120。
In addition, the next step S110 cooling zone cooling: cooling gas is sent to the
其中上述之步驟S110中該冷卻氣進氣管路23的一端係與該吸附轉輪20之冷卻區202的一側連接,而該冷卻氣進氣管路23係有兩種實施態樣,其中第一種實施態樣為該冷卻氣進氣管路23乃是供外氣進入(如第2圖及第3圖所示),而該外氣係為新鮮空氣,以將該外氣用來輸送到該吸附轉輪20之冷卻區202內提供降溫使用,另第二種
實施態樣係該冷卻氣進氣管路23係設有一氣體旁通管路231(如第4圖所示),該氣體旁通管路231之一端係與該冷卻氣進氣管路23連接,而該氣體旁通管路231之另一端係與該廢氣進氣管路21連接,透過該氣體旁通管路231來將部份的廢氣輸送到該吸附轉輪20之冷卻區202內提供降溫使用。
Wherein in the above step S110, one end of the cooling
另,下一步進行的步驟S120脫附區脫附:透過與第二熱交換器40之第二冷側管路401的另一端所連接的熱氣輸送管路25來將熱氣體輸送到該吸附轉輪20之脫附區203進行脫附,再透過該脫附濃縮氣體管路26的另一端來將脫附濃縮氣體輸送到第三熱交換器50之第三冷側管路501的一端。而完成上述步驟S120後即進行下一步驟S130。
In addition, in the next step S120, the desorption zone desorption: the hot gas is transferred to the adsorption rotor through the hot
其中該上述之步驟S120中該冷卻氣輸送管路24與該熱氣輸送管路25之間係設有比例風門,而該比例風門係設有兩種實施設計,其中第一種實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該熱氣輸送管路25係設有一熱氣控制閥門251(如第3圖所示),並透過該連通控制閥門271及該熱氣控制閥門251來形成比例風門,另第二實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該冷卻氣輸送管路24係設有一冷卻氣控制閥門241(如第4圖所示),並透過該連通控制閥門271及該冷卻氣控制閥門241來形成比例風門,藉此,不管是透過該連通控制閥門271及該熱氣控制閥門25
1之設計的比例風門或是透過該連通控制閥門271及該冷卻氣控制閥門241之設計的比例風門,皆能調整控制風力之大小,讓該熱氣輸送管路25內的溫度能保持一定高溫來提供給該吸附轉輪20之脫附區203使用。
In the above step S120, a proportional damper is provided between the cooling gas delivery pipe 24 and the hot gas delivery pipe 25, and the proportional damper is provided with two implementation designs, of which the first implementation design is A communication line 27 is provided between the cooling gas delivery pipe 24 and the hot gas delivery pipe 25, and the communication pipe 27 is provided with a communication control valve 271, and the hot gas delivery pipe 25 is provided with a hot gas control Valve 251 (as shown in Figure 3), and a proportional damper is formed through the communication control valve 271 and the hot gas control valve 251, and the second implementation design is for the cooling gas delivery pipe 24 and the hot gas delivery pipe 25 There is a communication line 27 between them, and the communication line 27 is provided with a communication control valve 271, and the cooling gas delivery line 24 is provided with a cooling gas control valve 241 (as shown in FIG. 4), And through the communication control valve 271 and the cooling gas control valve 241 to form a proportional damper, thereby, whether through the communication control valve 271 and the hot gas control valve 25
The proportional damper designed in 1 or the proportional damper designed through the communication control valve 271 and the cooling gas control valve 241 can adjust the size of the control wind so that the temperature in the hot gas delivery pipeline 25 can maintain a certain high temperature. The
另,下一步進行的步驟S130脫附濃縮氣體輸送:該脫附濃縮氣體再透過該第三熱交換器50之第三冷側管路501的另一端所連接的第三脫附濃縮氣體輸送管路51來輸送到該第一熱交換器30之第一冷側管路301的一端,並再透過該第一熱交換器30之第一冷側管路301的另一端所連接的第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10之進氣口11。而完成上述步驟S130後即進行下一步驟S140。
In addition, in the next step S130, the desorbed concentrated gas is conveyed: the desorbed concentrated gas is then passed through the third desorbed concentrated gas conveying pipe connected to the other end of the third
另,下一步進行的步驟S140焚燒氣體回收輸送:將經過焚燒後之氣體透過與該直燃式焚燒爐10之出氣口12所連接的第一焚燒熱氣回收管路32輸送到該第一熱交換器30之第一熱側管路302的一端,再由該第一熱交換器30之第一熱側管路302的另一端所連接的第一熱氣回收管路31輸送到該第二熱交換器40之第二熱側管路402的一端。而完成上述步驟S140後即進行下一步驟S150。
In addition, the next step S140 incineration gas recovery and transportation: the incinerated gas is transported to the first heat exchange through the first incineration hot
另,下一步進行的步驟S150焚燒氣體再輸送:將輸送到該第二熱交器40之第二熱側管路402的焚燒後之氣體,再經由與該第二熱交換器40之第二熱側管路402的另一端所連接的第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502的一端,並再透過與該第三熱交換器50之第三熱側管路502的另一端所連接的第五
熱氣回收管路71來輸送到該第五熱交換器70之第五熱側管路702的一端。而完成上述步驟S150後即進行下一步驟S160。
In addition, in the next step S150, the incineration gas is delivered again: the incinerated gas delivered to the second hot-
另,下一步進行的步驟S160經過除塵設備回收:將輸送到該第五熱交器70之第五熱側管路702的焚燒後之氣體,再經由與第五熱交換器70之第五熱側管路702的另一端所連接的除塵進氣管路81來輸送到該除塵設備80,並再透過該除塵設備80所連接的除塵出氣管路82來輸送到該廢氣進氣管路21的一端。其中該除塵出氣管路82係設有一風車821,以能將該除塵出氣管路82內的氣體推向該廢氣進氣管路21內。
In addition, the next step S160 is recovered through the dust removal equipment: the incinerated gas delivered to the fifth hot-
藉此,讓該吸附轉輪20之脫附區203所脫附下來的脫附濃縮氣體能透過該脫附濃縮氣體管路26來傳輸到該第三熱交換器50之第三冷側管路501來進行熱交換,並再透過該第三脫附濃縮氣體輸送管路51來傳輸到該第一熱交換器30之第一冷側管路301來進行熱交換(如第2圖至第4圖所示)。再讓經由該第一熱交換器30之第一冷側管路301所輸送的脫附濃縮氣體能透過該第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10的進氣口11,再將經過該直燃式焚燒爐10所燃燒後之氣體能由該出氣口12來透過該第一焚燒熱氣回收管路32來輸送到該第一熱交換器30之第一熱側管路302內進行熱回收,並經由該第一熱氣回收管路31來輸送到該第二熱交換器40之第二熱側管路402內進行熱回收,且再經由該第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502內進行熱回收。另由該第三熱交換器50之第三熱側管路502來透過該第五熱氣回收管路71輸送到該第五熱
交換器70之第五熱側管路702進行熱回收,再透過該除塵進氣管路81來輸送到該除塵設備80內以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備80所輸出的氣體輸送到該廢氣進氣管路21,使燃燒後的氣體能進入該吸附轉輪20之吸附區201循環利用,而不經過該煙囪90來進行排放,讓該煙囪90的排放量能降低,並使有機廢氣的處理效率能提升。
Thereby, the desorbed concentrated gas desorbed by the
而本發明第二種實施方式的直燃回流高效率有機廢氣處理系統,主要係設有一直燃式焚燒爐10、一吸附轉輪20、一第一熱交換器30、一第二熱交換器40、一第三熱交換器50、第四熱交換器60、一第五熱交換器70及一除塵設備80(如第6圖至第8圖所示),其中該第一熱交換器30係設有第一冷側管路301及第一熱側管路302,該第二熱交換器40係設有第二冷側管路401及第二熱側管路402,該第三熱交換器50係設有第三冷側管501路及第三熱側管路502,該第四熱交換器60係設有第四冷側管路601及第四熱側管路602,該第五熱交換器70係設有第五冷側管路701及第五熱側管路702,而該除塵設備80係為袋式除塵器、電袋式複合除塵器、慣性除塵器、靜電除塵器、離心式除塵器、濾筒式脈衝除塵器、脈衝袋式除塵器、脈衝濾芯除塵器、脈衝噴吹袋式除塵器、濕式除塵器、濕式電除塵器、濕式靜電除塵器、水膜除塵器、文丘里管除塵器、旋風分離器、煙道除塵器、多層除塵器、負壓反吹濾袋除塵器、低壓長袋脈衝除塵器、臥式靜電除塵器、無動力除塵器、荷電水霧除塵器、多管旋風除塵器、防爆除塵器之其中任一,另該直燃式焚燒爐(TO)10係設有一進氣口11及一出氣口12,且該直
燃式焚燒爐(TO)10內係設有爐頭及爐膛,使該有機廢氣能由該進氣口11來進入該爐頭進行燃燒,再讓經過燃燒後之氣體能穿過該爐膛並由該出氣口12來排出。
The direct combustion recirculation high-efficiency organic waste gas treatment system of the second embodiment of the present invention is mainly provided with a direct-fired
而該吸附轉輪20係為沸石濃縮轉輪或是其他材質之濃縮轉輪,且該吸附轉輪20內係設有吸附區201、冷卻區202及脫附區203,該吸附轉輪20係設有一廢氣進氣管路21、一淨氣排放管路22、一冷卻氣進氣管路23、一冷卻氣輸送管路24、一熱氣輸送管路25及一脫附濃縮廢氣管路26(如第6圖至第8圖所示),而該廢氣進氣管路21的另一端係連接至該吸附轉輪20之吸附區201的一側,以使該吸附轉輪20之吸附區201能吸附該廢氣進氣管路21內的廢氣,且該淨氣排放管路22之一端係與該吸附轉輪20之吸附區201的另一側連接,讓該廢氣經該吸附轉輪20之吸附區201淨化後再由該淨氣排放管路22來輸送。
The
另該冷卻氣進氣管路23的一端係與該吸附轉輪20之冷卻區202的一側連接,而該冷卻氣進氣管路23係有兩種實施態樣,其中第一種實施態樣為該冷卻氣進氣管路23乃是供外氣進入(如第6圖及第7圖所示),而該外氣係為新鮮空氣,以將該外氣用來輸送到該吸附轉輪20之冷卻區202內提供降溫使用,另第二種實施態樣係該冷卻氣進氣管路23係設有一氣體旁通管路231(如第8圖所示),該氣體旁通管路231之一端係與該冷卻氣進氣管路23連接,而該氣體旁通管路231之另一端係與該廢氣進氣管路21連接,透過該氣體旁通管路21來將部份的廢氣輸送到該吸附轉輪20之冷卻區202內提供降溫使用。
In addition, one end of the cooling
另該冷卻氣輸送管路24的一端係與該吸附轉輪20之冷卻區202的另一側連接,而該冷卻氣輸送管路24的另一端係與該第二熱交換器40之第二冷側管路401的一端連接,以能將該冷卻氣輸送管路24內的冷卻氣輸送到該第二熱交換器40內進行熱交換(如第6圖至第8圖所示),另該第二熱交換器40之第二冷側管路401的另一端係與該熱氣輸送管路25的另一端連接,而該熱氣輸送管路25的一端係與該吸附轉輪20之脫附區203的另一側連接,且該吸附轉輪20之脫附區203的一側係與該脫附濃縮氣體管路26的一端連接,使將經由該第二熱交換器40所提升之熱氣能透過該熱氣輸送管路25來傳輸到該吸附轉輪20之脫附區203來進行脫附使用,並將經過高溫所脫附下來的脫附濃縮氣體能透過該脫附濃縮氣體管路26來傳輸運送。
In addition, one end of the cooling
另本發明第一種實施方式中的該冷卻氣輸送管路24與該熱氣輸送管路25之間係設有比例風門,而該比例風門係設有兩種實施設計,其中第一種實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該熱氣輸送管路25係設有一熱氣控制閥門251(如第7圖所示),並透過該連通控制閥門271及該熱氣控制閥門251來形成比例風門,另第二實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該冷卻氣輸送管路24係設有一冷卻氣控制閥門241(如第8圖所示),並透過該連通控制閥門271及該冷卻氣控制閥門241來形成比例風門,藉此,不管是透過該連通控制閥門271及該熱氣控制閥門25
1之設計的比例風門或是透過該連通控制閥門271及該冷卻氣控制閥門241之設計的比例風門,皆能調整控制風力之大小,讓該熱氣輸送管路25內的溫度能保持一定高溫來提供給該吸附轉輪20之脫附區203使用。
In addition, in the first embodiment of the present invention, a proportional damper is provided between the cooling gas delivery pipe 24 and the hot gas delivery pipe 25, and the proportional damper is provided with two implementation designs, of which the first implementation design It is because a communication line 27 is provided between the cooling gas conveying line 24 and the hot gas conveying line 25, and the communicating line 27 is provided with a communication control valve 271, and the hot gas conveying line 25 is provided There is a hot gas control valve 251 (as shown in Figure 7), and a proportional damper is formed through the communication control valve 271 and the hot gas control valve 251, and the second implementation design is that the cooling gas delivery pipe 24 and the hot gas delivery A communication pipeline 27 is provided between the pipelines 25, and the communication pipeline 27 is provided with a communication control valve 271, and the cooling gas delivery pipeline 24 is provided with a cooling gas control valve 241 (as shown in FIG. 8) Display), and a proportional damper is formed through the communication control valve 271 and the cooling gas control valve 241, thereby, whether through the communication control valve 271 and the hot gas control valve 25
The proportional damper designed in 1 or the proportional damper designed through the communication control valve 271 and the cooling gas control valve 241 can adjust the size of the control wind so that the temperature in the hot gas delivery pipeline 25 can maintain a certain high temperature. The
再者,該第四熱交換器60連接有一第四脫附濃縮氣體輸送管路61及一第四熱氣回收管路62,該第四冷側管路601的一端係與該脫附濃縮氣體管路26的另一端連接,該第四脫附濃縮氣體輸送管路61的一端係與該第四冷側管路601的另一端連接(如第6圖至第8圖所示),該第四脫附濃縮氣體輸送管路61的另一端係與該第三熱交換器50之第三冷側管路501的一端連接,該第四熱氣回收管路62的一端係與該第四熱交換器60之第四熱側管路602的一端連接,該第四熱氣回收管路62的另一端係與該第三熱交換器50之第三熱側管路502的另一端連接。藉此,讓該吸附轉輪20之脫附區203所脫附下來的脫附濃縮氣體能透過該脫附濃縮氣體管路26來傳輸到該第四熱交換器60之第四冷側管路601來進行熱交換,並再透過該第四脫附濃縮氣體輸送管路61來傳輸到該第三熱交換器50之第三冷側管路501來進行熱交換。
Furthermore, the
另該第三熱交換器50係連接有一第三脫附濃縮氣體輸送管路51及一第三熱氣回收管路52,該第三脫附濃縮氣體輸送管路51的一端係與該第三熱交換器50之第三冷側管路501的另一端連接(如第6圖至第8圖所示),該第三脫附濃縮氣體輸送管路51的另一端係與該第一熱交換器30之第一冷側管路301的一端連接,該第三熱氣回收管路52的一端係與該第三熱交換器50之第三熱側管路502的一端連
接,該第三熱氣回收管路52的另一端係與該第二熱交換器40之第二熱側管路402的另一端連接。藉此,將該脫附濃縮氣體再透過該第三脫附濃縮氣體輸送管路51來傳輸到該第一熱交換器30之第一冷側管路301來進行熱交換。
In addition, the
另該第一熱交換器30係連接有一第一熱氣回收管路31、一第一焚燒熱氣回收管路32及一第一脫附濃縮氣體輸送管路33,其中該第一焚燒熱氣回收管路32的一端係與該第一熱交換器30之第一熱側管路302的一端連接,該第一焚燒熱氣回收管路32的另一端係與該直燃式焚燒爐10之出氣口11連接(如第6圖至第8圖所示),該第一熱氣回收管路31的一端係與該第一熱交換器30之第一熱側管路302的另一端連接,該第一熱氣回收管路31的另一端係與該第二熱交換器40之第二熱側管路402的一端連接,該第一脫附濃縮氣體輸送管路33的一端係與該第一熱交換器30之第一冷側管路301的另一端連接,該第一脫附濃縮氣體輸送管路33的另一端係與該直燃式焚燒爐10之進氣口12連接。藉此,讓經由該第一熱交換器30之第一冷側管路301所輸送的脫附濃縮氣體能透過該第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10的進氣口11,再將經過該直燃式焚燒爐10所燃燒後之氣體能由該出氣口12來透過該第一焚燒熱氣回收管路32來輸送到該第一熱交換器30之第一熱側管路302內進行熱回收,並經由該第一熱氣回收管路31來輸送到該第二熱交換器40之第二熱側管路402內進行熱回收,且再經由該第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502內進行熱回收,再經由該第四熱氣回收管路6
2來輸送到該第四熱交換器60之第四熱側管路602內進行熱回收。
In addition, the
另該第五熱交換器70係連接有一第五熱氣回收管路71,該第五熱交換器70之第五冷側管路701的一端係與該淨氣排放管路22的另一端連接,該第五熱氣回收管路71的一端係與該第五熱交換器70之第五熱側管路702的一端連接(如第6圖至第8圖所示),該第五熱氣回收管路71的另一端係與該第四熱交換器60之第四熱側管路602的另一端連接。而該除塵設備80係連接有一除塵進氣管路81及一除塵出氣管路82,該除塵進氣管路81的一端係與該除塵設備80連接,該除塵進氣管路81的另一端係與該第五熱交換器70之第五熱側管路702的另一端連接,該除塵出氣管路82的一端係與該除塵設備80連接,該除塵出氣管路82的另一端係與該廢氣進氣管路21連接。另該除塵出氣管路82係設有一風車821,以能將該除塵出氣管路82內的氣體推向該廢氣進氣管路21內。藉此,將經過該直燃式焚燒爐10所燃燒後之氣體能由該第四熱交換器60之第四熱側管路602來透過該第五熱氣回收管路71輸送到該第五熱交換器70之第五熱側管路702進行熱回收,再透過該除塵進氣管路81來輸送到該除塵設備80內以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備80所輸出的氣體輸送到該廢氣進氣管路21,使燃燒後的氣體能進入該吸附轉輪20之吸附區201循環利用,而不經過該煙囪90來進行排放,讓該煙囪90的排放量能降低,並使有機廢氣的處理效率能提升。
In addition, the
最後,該第五熱交換器70係連接一煙囪90,該煙囪90係設有一煙囪排放管路91,該煙囪排放管路91的一端係與該煙囪90
連接,該煙囪排放管路91的另一端係與該第五熱交換器70之第五冷側管路701的另一端連接(如第6圖至第8圖所示)。讓經由該淨氣排放管路22所排出淨化後氣體能進入該第五熱交換器70之第五冷側管路701內進行熱交換,再經由該煙囪排放管路91來輸送到煙囪90來進行排放。另該淨氣排放管路22係設有一風車221,以能將該淨氣排放管路22內的氣體推向該第五熱交換器70之第五冷側管路701內。
Finally, the
而本發明第二種實施方式的直燃回流高效率有機廢氣處理方法,其主要係用於有機廢氣處理系統,且包括有一直燃式焚燒爐10,一吸附轉輪20、一第一熱交換器30、一第二熱交換器40、一第三熱交換器50、第四熱交換器60、一第五熱交換器70及一除塵設備80(如第6圖至第8圖所示),該吸附轉輪20係設有吸附區201、脫附區202及冷卻區203,該吸附轉輪20係連接有一廢氣進氣管路21、一淨氣排放管路22、一冷卻氣進氣管路23、一冷卻氣輸送管路24、一熱氣輸送管路25及一脫附濃縮氣體管路26,該第一熱交換器30係設有第一冷側管路301及第一熱側管路302,該第二熱交換器40係設有第二冷側管路401及第二熱側管路402,該第三熱交換器50係設有第三冷側管路501及第三熱側管路502,該第四熱交換器60係設有第四冷側管路601及第四熱側管路602,該第五熱交換器70係設有第五冷側管路701及第五熱側管路702。
The direct combustion recirculation high-efficiency organic waste gas treatment method of the second embodiment of the present invention is mainly used in an organic waste gas treatment system, and includes a
而該除塵設備80係為袋式除塵器、電袋式複合除塵器、慣性除塵器、靜電除塵器、離心式除塵器、濾筒式脈衝除塵器、脈衝袋式除塵器、脈衝濾芯除塵器、脈衝噴吹袋式除塵器、濕式除塵器、濕式電除塵
器、濕式靜電除塵器、水膜除塵器、文丘里管除塵器、旋風分離器、煙道除塵器、多層除塵器、負壓反吹濾袋除塵器、低壓長袋脈衝除塵器、臥式靜電除塵器、無動力除塵器、荷電水霧除塵器、多管旋風除塵器、防爆除塵器之其中任一,另該直燃式焚燒爐(TO)10係設有一進氣口11及一出氣口12,且該直燃式焚燒爐(TO)10內係設有爐頭及爐膛,使該有機廢氣能由該進氣口11來進入該爐頭進行燃燒,再讓經過燃燒後之氣體能穿過該爐膛並由該出氣口12來排出。而該處理方法的主要步驟(如第5圖所示)係包括:步驟S200吸附區吸附:將廢氣透過該廢氣進氣管路21的另一端來送入該吸附轉輪20之吸附區201的一側進行吸附,再將吸附後之氣體透過該淨氣排放管路22的另一端來輸送到該第五熱交換器70之第五冷側管路701的一端。而完成上述步驟S100後即進行下一步驟S210。
The
其中上述之步驟S200中該第五熱交換器70係連接一煙囪90,該煙囪90係設有一煙囪排放管路91,該煙囪排放管路91的一端係與該煙囪90連接,該煙囪排放管路91的另一端係與該第五熱交換器70之第五冷側管路701的另一端連接。讓經由該淨氣排放管路22所排出淨化後氣體能進入該第五熱交換器70之第五冷側管路701內進行熱交換,再經由該煙囪排放管路91來輸送到煙囪90來進行排放。另該淨氣排放管路係22設有一風車221,以能將該淨氣排放管路22內的氣體推向該第五熱交換器70之第五冷側管路701內。
In the above step S200, the
另,下一步進行的步驟S210冷卻區冷卻:透過該冷卻氣進氣管路23的另一端來輸送冷卻氣至該吸附轉輪20之冷卻區202進
行冷卻,再透過該冷卻氣輸送管路24的另一端來將經過冷卻區202之冷卻氣輸送到該第二熱交換器40之第二冷側管路401的一端。而完成上述步驟S110後即進行下一步驟S220。
In addition, in the next step S210 cooling of the cooling zone: the cooling gas is sent to the
其中上述之步驟S210中該冷卻氣進氣管路23的一端係與該吸附轉輪20之冷卻區202的一側連接,而該冷卻氣進氣管路23係有兩種實施態樣,其中第一種實施態樣為該冷卻氣進氣管路23乃是供外氣進入(如第6圖及第7圖所示),而該外氣係為新鮮空氣,以將該外氣用來輸送到該吸附轉輪20之冷卻區202內提供降溫使用,另第二種實施態樣係該冷卻氣進氣管路23係設有一氣體旁通管路231,該氣體旁通管路231之一端係與該冷卻氣進氣管路23連接,而該氣體旁通管路231之另一端係與該廢氣進氣管路21連接,透過該氣體旁通管路231來將部份的廢氣輸送到該吸附轉輪20之冷卻區202內提供降溫使用。
In the above step S210, one end of the cooling
另,下一步進行的步驟S220脫附區脫附:透過與第二熱交換器40之第二冷側管路401的另一端所連接的熱氣輸送管路25來將熱氣體輸送到該吸附轉輪20之脫附區203進行脫附,再透過該脫附濃縮氣體管路26的另一端來將脫附濃縮氣體輸送到第四熱交換器60之第四冷側管路601的一端。而完成上述步驟S220後即進行下一步驟S230。
In addition, the next step S220 is the desorption zone desorption: the hot gas is transferred to the adsorption rotor through the hot
其中該上述之步驟S220中該冷卻氣輸送管路24與該熱氣輸送管路25之間係設有比例風門,而該比例風門係設有兩種實施設計,其中第一種實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路2
5之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該熱氣輸送管路25係設有一熱氣控制閥門251(如第7圖所示),並透過該連通控制閥門271及該熱氣控制閥門251來形成比例風門,另第二實施設計乃為該冷卻氣輸送管路24與該熱氣輸送管路25之間設有一連通管路27,且該連通管路27係設有一連通控制閥門271,而該冷卻氣輸送管路24係設有一冷卻氣控制閥門241(如第8圖所示),並透過該連通控制閥門271及該冷卻氣控制閥門241來形成比例風門,藉此,不管是透過該連通控制閥門271及該熱氣控制閥門251之設計的比例風門或是透過該連通控制閥門271及該冷卻氣控制閥門241之設計的比例風門,皆能調整控制風力之大小,讓該熱氣輸送管路25內的溫度能保持一定高溫來提供給該吸附轉輪20之脫附區203使用。
In the above step S220, a proportional damper is provided between the cooling
另,下一步進行的步驟S230脫附濃縮氣體輸送:該脫附濃縮氣體再透過該第四熱交換器60之第四冷側管路601的另一端所連接的第四脫附濃縮氣體輸送管路61來輸送到該第三熱交換器50之第三冷側管路501的一端,並再透過該第三熱交換器50之第三冷側管路501的另一端所連接的第三脫附濃縮氣體輸送管路51來輸送到該第一熱交換器30之第一冷側管路301的一端,且再透過該第一熱交換器30之第一冷側管路301的另一端所連接的第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10之進氣口11。而完成上述步驟S230後即進行下一步驟S240。
In addition, in the next step S230, the desorbed concentrated gas is conveyed: the desorbed concentrated gas is then passed through the fourth desorbed concentrated gas conveying pipe connected to the other end of the fourth
另,下一步進行的步驟S240焚燒氣體回收輸送:將經過
焚燒後之氣體透過與該直燃式焚燒爐10之出氣口12所連接的第一焚燒熱氣回收管路32輸送到該第一熱交換器30之第一熱側管路302的一端,再由該第一熱交換器30之第一熱側管路302的另一端所連接的第一熱氣回收管路31輸送到該第二熱交換器40之第二熱側管路402的一端。而完成上述步驟S240後即進行下一步驟S250。
In addition, the next step S240 incineration gas recovery and transportation: will pass
The incinerated gas is transported to the end of the first
另,下一步進行的步驟S150焚燒氣體再輸送:將輸送到該第二熱交器40之第二熱側管路402的焚燒後之氣體,再經由與該第二熱交換器40之第二熱側管路402的另一端所連接的第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502的一端,並再透過與該第三熱交換器50之第三熱側管路502的另一端所連接的第四熱氣回收管路62來輸送到該第四熱交換器60之第四熱側管路602的一端,且再透過與該第四熱交換器60之第四熱側管路602的另一端所連接的第五熱氣回收管路71來輸送到該第五熱交換器70之第五熱側管路702的一端。而完成上述步驟S250後即進行下一步驟S260。
In addition, in the next step S150, the incineration gas is delivered again: the incinerated gas delivered to the second hot-
另,下一步進行的步驟S260經過除塵設備回收:將輸送到該第五熱交器70之第五熱側管路702的焚燒後之氣體,再經由與第五熱交換器70之第五熱側管路702的另一端所連接的除塵進氣管路81來輸送到該除塵設備80,並再透過該除塵設備80所連接的除塵出氣管路82來輸送到該廢氣進氣管路21的一端。其中該除塵出氣管路82係設有一風車821,以能將該除塵出氣管路82內的氣體推向該廢氣進氣管路21內。
In addition, the next step S260 is recovered through the dust removal equipment: the incinerated gas delivered to the fifth hot-
藉此,讓該吸附轉輪20之脫附區203所脫附下來的脫附
濃縮氣體能透過該脫附濃縮氣體管路26來傳輸到該第四熱交換器60之第四冷側管路601來進行熱交換(如第6圖至第8圖所示),再透過該第四脫附濃縮氣體輸送管路61來傳輸到該第三熱交換器50之第冷側管路501來進行熱交換,並再透過該第三脫附濃縮氣體輸送管路51來傳輸到該第一熱交換器30之第一冷側管路601來進行熱交換。再讓經由該第一熱交換器30之第一冷側管路601所輸送的脫附濃縮氣體能透過該第一脫附濃縮氣體輸送管路33來輸送到該直燃式焚燒爐10的進氣口11,再將經過該直燃式焚燒爐10所燃燒後之氣體能由該出氣口12來透過該第一焚燒熱氣回收管路32來輸送到該第一熱交換器30之第一熱側管路302內進行熱回收,並經由該第一熱氣回收管路31來輸送到該第二熱交換器40之第二熱側管路402內進行熱回收,且再經由該第三熱氣回收管路52來輸送到該第三熱交換器50之第三熱側管路502內進行熱回收,並再經由該第四熱氣回收管路62來輸送到該第四熱交換器60之第四熱側管路602內來進行熱回收。另由該第四熱交換器60之第四熱側管路602來透過該第五熱氣回收管路71輸送到該第五熱交換器70之第五熱側管路702進行熱回收,再透過該除塵進氣管路81來輸送到該除塵設備80內以進行粉塵或二氧化矽(SiO2)等氧化物的分離,最後再將由該除塵設備80所輸出的氣體輸送到該廢氣進氣管路21,使燃燒後的氣體能進入該吸附轉輪20之吸附區201循環利用,而不經過該煙囪90來進行排放,讓該煙囪90的排放量能降低,並使有機廢氣的處理效率能提升。
In this way, the desorbed concentrated gas desorbed by the
由以上詳細說明,可使熟知本項技藝者明瞭本發明的確可達 成前述目的,實已符合專利法之規定,爰提出發明專利申請。 From the above detailed description, it will be apparent to those skilled in the art that the present invention is indeed accessible In order to achieve the aforementioned purpose, it has actually complied with the provisions of the Patent Law.
惟以上所述者,僅為本發明之較佳實施例而已,當不能以此限定本發明實施之範圍;故,凡依本發明申請專利範圍及發明說明書內容所作之簡單的等效變化與修飾,皆應仍屬本發明專利涵蓋之範圍內。 However, the above are only preferred embodiments of the present invention, which should not be used to limit the scope of implementation of the present invention; therefore, simple equivalent changes and modifications made according to the scope of the patent application of the present invention and the content of the invention description , Should still fall within the scope of this invention patent.
S100‧‧‧吸附區吸附 S100‧‧‧adsorption zone adsorption
S110‧‧‧冷卻區冷卻 S110‧‧‧cooling in cooling zone
S120‧‧‧脫附區脫附 S120‧‧‧Desorption zone desorption
S130‧‧‧脫附濃縮氣體輸送 S130‧‧‧Desorption concentrated gas delivery
S140‧‧‧焚燒氣體回收輸送 S140‧‧‧Incineration gas recovery and transportation
S150‧‧‧焚燒氣體再輸送 S150‧‧‧Incineration gas retransmission
S160‧‧‧經過除塵設備回收 S160‧‧‧Recycled through dust removal equipment
Claims (18)
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW108102219A TWI694226B (en) | 2019-01-21 | 2019-01-21 | Direct combustion return high-efficiency organic waste gas treatment system and method |
CN201910276149.5A CN111457398A (en) | 2019-01-21 | 2019-04-08 | Direct-combustion backflow high-efficiency organic waste gas treatment system and method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
TW108102219A TWI694226B (en) | 2019-01-21 | 2019-01-21 | Direct combustion return high-efficiency organic waste gas treatment system and method |
Publications (2)
Publication Number | Publication Date |
---|---|
TWI694226B true TWI694226B (en) | 2020-05-21 |
TW202028659A TW202028659A (en) | 2020-08-01 |
Family
ID=71677523
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
TW108102219A TWI694226B (en) | 2019-01-21 | 2019-01-21 | Direct combustion return high-efficiency organic waste gas treatment system and method |
Country Status (2)
Country | Link |
---|---|
CN (1) | CN111457398A (en) |
TW (1) | TWI694226B (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101773763A (en) * | 2009-01-09 | 2010-07-14 | 杰智环境科技股份有限公司 | Method and device used for optimized running control of concentration runner system |
TW201417871A (en) * | 2012-08-29 | 2014-05-16 | Thyssenkrupp Uhde Gmbh | A method for scrubbing sulfur-containing gases with a ammonia-containing scrubbing solution guided in circular flow |
CN104096450A (en) * | 2013-04-07 | 2014-10-15 | 王汉培 | Efficient rotating wheel adsorption device for waste gas treatment |
TW201600163A (en) * | 2014-06-19 | 2016-01-01 | Eastern Rainbow Engineering Co Ltd | Processor for volatile organic compound |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE19716877C1 (en) * | 1997-04-22 | 1998-12-10 | Schedler Johannes | Thermally-efficient incinerator plant for cost-effective destruction of volatile organic compounds contaminating air |
CN101362041A (en) * | 2007-08-06 | 2009-02-11 | 华懋科技股份有限公司 | Exhaust emission device and method |
CN101435582B (en) * | 2007-11-15 | 2011-06-08 | 华懋科技股份有限公司 | Low-pollution concentrating heat storage cremating apparatus |
CN101893248B (en) * | 2009-05-21 | 2012-10-03 | 杰智环境科技股份有限公司 | Energy-saving device for volatile organic waste gas treatment system |
CN205760473U (en) * | 2016-05-13 | 2016-12-07 | 广州市怡森环保设备有限公司 | A kind of zeolite runner cleaning equipment for waste organic gas |
CN208194044U (en) * | 2018-03-01 | 2018-12-07 | 上海嘉园环保科技有限公司 | Zeolite runner Adsorption Concentration cleaning equipment |
-
2019
- 2019-01-21 TW TW108102219A patent/TWI694226B/en active
- 2019-04-08 CN CN201910276149.5A patent/CN111457398A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101773763A (en) * | 2009-01-09 | 2010-07-14 | 杰智环境科技股份有限公司 | Method and device used for optimized running control of concentration runner system |
TW201417871A (en) * | 2012-08-29 | 2014-05-16 | Thyssenkrupp Uhde Gmbh | A method for scrubbing sulfur-containing gases with a ammonia-containing scrubbing solution guided in circular flow |
CN104096450A (en) * | 2013-04-07 | 2014-10-15 | 王汉培 | Efficient rotating wheel adsorption device for waste gas treatment |
TW201600163A (en) * | 2014-06-19 | 2016-01-01 | Eastern Rainbow Engineering Co Ltd | Processor for volatile organic compound |
Also Published As
Publication number | Publication date |
---|---|
CN111457398A (en) | 2020-07-28 |
TW202028659A (en) | 2020-08-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN210772223U (en) | High-efficiency organic waste gas treatment system for direct-combustion backflow heat recovery | |
TWI741341B (en) | Organic waste gas concentrated heat storage combustion backflow system and method | |
CN210206363U (en) | Organic waste gas treatment system with high efficiency of backflow heat recovery | |
TWM579063U (en) | Thermal oxidation backflow high-efficiency organic waste gas processing system | |
TWM590068U (en) | Organic waste gas concentrated heat storage and combustion reflux cooling system | |
TWM583922U (en) | High-efficiency organic exhaust gas processing system with energy recovery function | |
TWI694226B (en) | Direct combustion return high-efficiency organic waste gas treatment system and method | |
TWI704951B (en) | High-efficiency organic waste gas treatment system and method for direct combustion reflux heat recovery | |
TWI701409B (en) | Reflux heat recovery high-efficiency organic waste gas treatment system and method | |
TWM586337U (en) | Organic waste gas concentrated heat storage combustion reflux system | |
CN211384442U (en) | Direct-combustion flow-dividing high-efficiency organic waste gas treatment system | |
TWM587727U (en) | High-efficiency organic waste gas treatment system with heat storage and reflux | |
CN210410092U (en) | Backflow high-efficiency organic waste gas treatment system | |
TWI718521B (en) | Reflux high-efficiency organic waste gas treatment system and method | |
TWI756748B (en) | Energy-saving dual-rotor cold side bypass temperature control system and method thereof | |
TWM591443U (en) | Organic waste gas treatment system with highly efficient catalyst backflow | |
TWI722522B (en) | Heat storage reflux high-efficiency organic waste gas treatment system and method | |
TWI740186B (en) | Organic waste gas concentrated heat storage combustion reflux cooling system and method | |
TWI714201B (en) | Catalyst refluxing high-efficiency organic waste gas treatment system and method | |
TW202204823A (en) | Energy-saving type dual-wheel high-concentration cold-side bypass over-temperature control system and method thereof capable of preventing a direct-fired thermal oxidizer from overheating due to excessively high furnace temperature during the treatment of organic waste gas | |
TWI738444B (en) | Energy-saving single-rotor high-concentration cold side passing temperature control system and method | |
TWM606376U (en) | Energy-saving single-runner high-concentration cold side bypass temperature control system | |
TWM608581U (en) | Energy-saving dual-wheel high-concentration heat-bypass temperature control system |