TW200420857A - Heat recovery method for a regenerative thermal oxidizer - Google Patents
Heat recovery method for a regenerative thermal oxidizer Download PDFInfo
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- TW200420857A TW200420857A TW092108224A TW92108224A TW200420857A TW 200420857 A TW200420857 A TW 200420857A TW 092108224 A TW092108224 A TW 092108224A TW 92108224 A TW92108224 A TW 92108224A TW 200420857 A TW200420857 A TW 200420857A
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- 230000001172 regenerating effect Effects 0.000 title claims abstract description 62
- 238000011084 recovery Methods 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims abstract description 23
- 239000007800 oxidant agent Substances 0.000 title claims abstract 6
- 238000002485 combustion reaction Methods 0.000 claims abstract description 129
- 239000007789 gas Substances 0.000 claims abstract description 100
- 239000010815 organic waste Substances 0.000 claims abstract description 57
- 238000005338 heat storage Methods 0.000 claims abstract description 45
- 238000006243 chemical reaction Methods 0.000 claims abstract description 35
- 230000000694 effects Effects 0.000 claims abstract description 15
- 239000000126 substance Substances 0.000 claims abstract description 6
- 230000008569 process Effects 0.000 claims abstract description 5
- 230000001105 regulatory effect Effects 0.000 claims description 28
- 239000000446 fuel Substances 0.000 claims description 10
- 238000007254 oxidation reaction Methods 0.000 claims description 9
- 230000009471 action Effects 0.000 claims description 6
- 230000003647 oxidation Effects 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 5
- 239000000779 smoke Substances 0.000 claims description 5
- 239000011232 storage material Substances 0.000 claims description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- 238000010521 absorption reaction Methods 0.000 claims description 4
- 239000012855 volatile organic compound Substances 0.000 claims description 4
- 241001465754 Metazoa Species 0.000 claims description 3
- 239000012530 fluid Substances 0.000 claims description 2
- 238000007084 catalytic combustion reaction Methods 0.000 claims 3
- 244000025254 Cannabis sativa Species 0.000 claims 1
- 235000012766 Cannabis sativa ssp. sativa var. sativa Nutrition 0.000 claims 1
- 235000012765 Cannabis sativa ssp. sativa var. spontanea Nutrition 0.000 claims 1
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims 1
- 241001674048 Phthiraptera Species 0.000 claims 1
- 235000009120 camo Nutrition 0.000 claims 1
- 235000005607 chanvre indien Nutrition 0.000 claims 1
- 238000004891 communication Methods 0.000 claims 1
- 229910052731 fluorine Inorganic materials 0.000 claims 1
- 239000011737 fluorine Substances 0.000 claims 1
- 239000011487 hemp Substances 0.000 claims 1
- 230000007935 neutral effect Effects 0.000 claims 1
- 150000002894 organic compounds Chemical class 0.000 claims 1
- 229910052573 porcelain Inorganic materials 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 abstract description 5
- 239000002912 waste gas Substances 0.000 abstract description 4
- 230000001590 oxidative effect Effects 0.000 abstract description 3
- 238000005086 pumping Methods 0.000 abstract 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 7
- 238000010586 diagram Methods 0.000 description 7
- 238000005516 engineering process Methods 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 229910010293 ceramic material Inorganic materials 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000003960 organic solvent Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000012495 reaction gas Substances 0.000 description 2
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 1
- 235000008612 Gnetum gnemon Nutrition 0.000 description 1
- 240000000018 Gnetum gnemon Species 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 238000006864 oxidative decomposition reaction Methods 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 230000004044 response Effects 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- -1 thermal incineration Substances 0.000 description 1
- 238000006276 transfer reaction Methods 0.000 description 1
Classifications
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- 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
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/25—Process efficiency
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- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
Abstract
Description
200420857 五、發明說明(1) 【發明之技術領域】 本發明係有關一種蓄熱式燃燒爐(R e g e n e r a t i v e Thermal Oxidizer,RTO),特別是,本發明提出一種蓄 熱式燃燒爐的熱能回收法,其熱交換器(heat exchanger)在不需使用風車誘引下,藉由高低溫之密度 差煙1¾效應及氣體流動之動能(速度能)差效應而自然產生 氣流擾動及流動,即可將燃燒爐之燃燒室中所產生的熱再 次於燃燒室封閉回路(C 1 〇 s e L ο ο p)中達到高效率熱能回收 再利用之功能,有別於一習用技術之開放回路。 【先前技術】 各國對於揮發性有機溶劑(V〇lat丨le 〇rganic compounds; VOCs)皆有一定的管制標準,揮發性有機溶劑 在工業界廣泛被使用。以中華民國為例:環保署在八十九 年已公告實施半導體製造業空氣污染管制及排放標準。直 揮發性有機廢氣強制要求其V0Cs削減率應大於9〇%。有機' 廢氣的處理方法很多,如熱焚化、觸媒焚化、蓄熱 燒、轉輪濃縮焚化、活性碳吸附、冷凝回收等。… 其中蓄熱式燃燒爐配置有單個或多個蓄熱床 (Regenerative beds),蓄熱床内充填蓄熱材、、、,使 有機廢氣流經蓄熱床預熱(此時蓄熱材釋出熱能),而^f 發性有機廢氣進入高溫氧化區(> 8〇〇它)(即燃燒室 中)。此時,由於燃燒爐燃料嘴嘴產生辅助熱能 量及V0CS成分氧化分解產生的熱量,使燃燒室保持一供定熱的200420857 V. Description of the invention (1) [Technical field of the invention] The present invention relates to a regenerative thermal furnace (RTO). In particular, the present invention proposes a thermal energy recovery method for a regenerative combustion furnace. Without the use of a windmill to induce the heat exchanger, natural gas flow disturbance and flow can be generated by the high temperature and low temperature density difference smoke effect and the kinetic energy (velocity energy) difference effect of gas flow, which can burn the combustion furnace. The heat generated in the chamber reaches the function of high-efficiency thermal energy recovery and reuse in the closed loop of the combustion chamber (C 10 se L ο ο p), which is different from the open circuit of a conventional technology. [Previous technology] Various countries have certain regulatory standards for volatile organic solvents (VOCs), and volatile organic solvents are widely used in the industrial world. Take the Republic of China as an example: In 1989, the Environmental Protection Agency announced the implementation of air pollution control and emission standards for semiconductor manufacturing. The direct volatile organic waste gas compulsorily requires that its V0Cs reduction rate should be greater than 90%. There are many methods for treating organic 'waste gas, such as thermal incineration, catalyst incineration, regenerative combustion, rotary incineration of rotors, adsorption of activated carbon, and condensation recovery. … The regenerative combustion furnace is equipped with a single or multiple Regenerative beds. The thermal storage bed is filled with thermal storage materials, so that organic waste gas flows through the thermal storage bed to preheat (at this time, the thermal storage material releases heat) f Generating organic waste gas enters the high-temperature oxidation zone (> 800) (that is, in the combustion chamber). At this time, due to the auxiliary thermal energy generated by the burner fuel nozzle and the heat generated by the oxidative decomposition of the V0CS component, the combustion chamber is maintained at a constant heating temperature.
200420857 五、發明說明(2) 溫度,在一定的停留時間中有機廢氣所含的VOCs成份被完 全氧化成無害的H2 0及C 0 2,其代表性反應如下: C7H8+ 9 02-> 7 C02+ 4 H20 2 C8H10+ 21 02— 16 C02+ 1〇 H2〇 2 C6H6+ 15 02— 12 C02+ 6 H20200420857 V. Description of the invention (2) Temperature, VOCs components contained in organic waste gas are completely oxidized into harmless H2 0 and C 0 2 within a certain residence time. The representative reactions are as follows: C7H8 + 9 02- > 7 C02 + 4 H20 2 C8H10 + 21 02— 16 C02 + 1〇H2〇2 C6H6 + 15 02— 12 C02 + 6 H20
Frank M· Colag iovanni 在美國專利案號:11.3· patent 5, 2 9 7, 9 54中所提之蓄熱式燃燒爐即為一般傳統所 使用之多塔蓄熱式燃燒爐。其燃燒爐係包含有三組蓄熱 床’藉由三組蓄熱床之交替使用來儲存燃燒v〇Cs後所釋放 出之能量,作為輔助熱能之使用。此外,含高溫之v〇Ca· 由IΪ f換器將熱能做再進一步的回收,如此廢氣便可降 ΐ m服度後再排放。以下使用一般雙塔蓄熱式燃燒爐做 為例子以說明之。 揪換,拥,為一般傳統雙塔蓄熱式燃燒爐丨〇 ( rt〇)搭配 圖、Γ1 ΐ氣ί通16(Hot Gas By—Pass)熱回收之結構示意 二庆π* ί畜熱式燃燒爐1 〇主要含有兩組蓄熱床[第一蓄 i &蓄熱床123、廢氣燃燒室15及其相連之廢氣 向調節閥#。更詳細的說製程風機28自廢氣 來源鈿抽排有機廢氣20( V0Cs Lad = = 入口的進風門心^ 5二FF ”),可有兩種模式進入燃燒室中反應。第一 续廢氣2"以下簡稱V〇CS2〇)藉由-進風門26 (此i的筮分別經由第一流向調節閥2 1進入第二蓄熱床1 2 (守的弟二流向調節閥22和第三流向調節閥23為〇FF[關 200420857 五、發明說明(3) 閉]狀態)。在通過第二蓄熱床12後,VOCs20在燃燒室13 中由燃料噴嘴14提供一燃僥用火焰15將VOCs20經氧化反應 形成H20及C02。其燃燒室13内部之燃燒溫度可達攝氏溫度 8 0 0〜9 5 0°C,在燃燒過程中第二蓄熱床1 2可儲存反應之熱 量用以預熱而後的VOCs20進入燃燒室中進行反應,如此, 便可降低火焰1 5的能量損耗。反應後之VOCs 2 0 ( 9 0%以上 由水和二氧化碳所組成)流經由第一蓄熱床11、第四流向 調節閥24,由送風機27排出至大氣中。第二種模式:VOCs 由進風門2 6進入管線,分別經由第三流向調節閥2 3 (此時 Φ 的第—流向調節閥2 1和第四向量調節閥24為OFF狀態)進 中$ —蓄熱床U。在通過第一蓄熱床丨丨後V〇Cs在燃燒室I3 由燃燒喷嘴14提供一燃燒用火焰15將v〇Cs2〇氧化成H20 及C 0 9 節間 V0Cs20除可選擇第一流向調節閥21和第三流向調 於适進出外’蓄熱式燃燒爐丨〇包含有一熱氣旁通管丨6相連 之、f機2 7之管線,其旁通管亦有第五流量控制閥2 5控制 此路徑僅供雙塔蓄熱式燃燒爐1 〇 ( RT〇)系統停機 \狀況枯 、 :使用’並非V 〇 c S 2 0燃燒之正常路線。The regenerative combustion furnace referred to by Frank M. Colag iovanni in U.S. Patent No. 11.3 · patent 5, 2 9 7, 9 54 is a multi-tower regenerative combustion furnace which is generally used conventionally. The combustion furnace system includes three groups of heat storage beds', which alternately uses the three groups of heat storage beds to store the energy released after burning vOCs as auxiliary heat energy. In addition, the high-temperature v0Ca · is further recovered by the IΪf converter, so that the exhaust gas can be discharged after reducing the temperature. The following uses a general double-tower regenerative combustion furnace as an example to illustrate. Change, hold, it is the general traditional double-tower regenerative combustion furnace 丨 〇 (rt〇) matching diagram, Γ1 ΐ 气 ί 通 16 (Hot Gas By-Pass) heat recovery structure diagram Second celebration π * ί animal thermal combustion The furnace 10 mainly includes two sets of heat storage beds [the first heat storage bed 123, the exhaust gas combustion chamber 15 and the connected exhaust gas direction regulating valve #. In more detail, the process fan 28 extracts organic waste gas 20 from the waste gas source (V0Cs Lad = = inlet air inlet core ^ 5 two FF "), there are two modes to enter the combustion chamber and react. The first continuous exhaust gas 2 " Hereinafter referred to as V〇CS2〇) through -inlet valve 26 (this i respectively enters the second heat storage bed 1 through the first flow direction control valve 21 1 (the second flow direction control valve 22 and the third flow direction control valve 23 〇FF [Close 200420857 V. Description of the invention (3) Closed]). After passing through the second thermal storage bed 12, VOCs 20 is provided by the fuel nozzle 14 in the combustion chamber 13 with a flame 15 and the VOCs 20 is formed by oxidation reaction H20 and C02. The combustion temperature inside the combustion chamber 13 can reach 80 ° C ~ 9 50 ° C. During the combustion process, the second heat storage bed 12 can store the heat of reaction for preheating and the VOCs20 enters the combustion. The reaction is performed in the chamber, so that the energy loss of the flame 15 can be reduced. After the reaction, the VOCs 20 (more than 90% composed of water and carbon dioxide) flow through the first heat storage bed 11 and the fourth flow to the regulating valve 24, It is discharged into the atmosphere by the blower 27. The second mode: VOCs are introduced by the wind 2 6 enters the pipeline and passes through the third flow direction regulating valve 2 3 (at this time, the first flow direction regulating valve 21 and the fourth vector regulating valve 24 of Φ are in the OFF state), and the heat storage bed U. After passing the first heat storage, After the bed, the VOCs are provided in the combustion chamber I3 by the combustion nozzle 14 and a combustion flame 15 is used to oxidize vOCs20 to H20 and C0. In addition to the internode V0Cs20, the first flow direction regulating valve 21 and the third flow direction regulating valve can be selected. The regenerative combustion furnace is suitable for entering and exiting. It contains a hot gas bypass pipe, which is connected to 6 and the f machine 2 7 pipeline. The bypass pipe also has a fifth flow control valve. 2 5 This path is only for double tower heat storage. Type burner 1 〇 (RT〇) system shutdown \ condition is dry,: using 'not V oc S 2 0 normal route of combustion.
存反Ϊ似於第一種模式,在燃燒過程中第一蓄熱床1 1可儲 應。2之熱1用以預熱而後的VOCs20進入燃燒室中進行反 節間應後之¥〇(^廢氣流經由第二蓄熱床1 2、第二流向調 其、+、2 ’由送風機2 7排出至大氣3 5中。 床及第 ★ ^ 一種模式定時循環做切換保持第^一畜熱 材多為—^熱床可維持高溫用以預熱反應氣體。其中蓄熱 1 i材料所組成。通常若製程上須要會對廢氣The storage reaction is similar to the first mode, and the first heat storage bed 11 can be stored during the combustion process. 2 of the heat 1 is used to preheat the VOCs 20 after entering the combustion chamber for anti-intersection response. 〇 Exhaust gas flows through the second heat storage bed 1 2. The second flow direction is adjusted by +, 2 'by the blower 2 7 Exhaust to the atmosphere 3 5. The bed and the first ★ ^ a mode timing cycle to switch to maintain the first animal heat material is mostly-^ hot bed can maintain high temperature to preheat the reaction gas. Of which heat storage 1 i material. Usually If the process requires
第8頁 200420857 五、發明說明(4) VOCs20所含之熱能經 燒室1 3旁會連接一個 exchanger),其熱交 溫後的VOCs20排至大 熱交換器30内部設置 管束31中含有流動的 加熱後所形成之熱氣 熱資源回收的目的。 機廢氣(VOCs Laden 而排出。有些熱交換 源的回收(圖中未示 器將大幅增加燃燒爐 當此熱交換器損壞或 才能維護所述熱交換 方法不需依賴送風機 收的目的。 氧化燃燒後進行再 管路至一熱交換器 換器30另有管線連 氣中。V 0 C s 2 0經由 有熱交換管束3 1口及 空氣3 2進行熱交換 可運用於工廠中的 可注意的是,經過 a i r ) 2 0係由送風機 器亦設計位於蓄熱 ),此種設計的缺 氣流流動路徑之風 阻塞時,需對蓄熱 器。本發明提出一 風壓驅動即可達到 次回收,30(heat 接於送風 熱交換器 收熱能, 動作。空 工作機台 熱交換器 2 7產生之 材之中來 點在於所 壓損而耗 式燃繞爐 高效内置 原有較高 因此在燃 機2 7將降 3 0時,其 其熱交換 氣3 2經由 ,以達到 30中的有 風壓引導 進行熱資 述熱交換 損能源及 進行拆裝 式熱交換 效率熱回 【發明内容】 本發明的主要目的在於提供一種蓄熱式燃 回收法’係利用煙Hi效應及壓差效應使反應後的八古…月匕 氣體自動通過熱交換器巾。也就是說藉由高低,熱的 煙自效應及氣體流動之動能(速度能)差效應而=妙=度f 流擾動及流動,即可將燃燒爐之燃燒室 ^生氣 生生的熱再次Page 8 200420857 V. Description of the invention (4) The thermal energy contained in the VOCs20 will be connected to an exchanger by the firing chamber 1 and 3), and the VOCs 20 after the heat temperature is discharged to the large heat exchanger 30. The tube bundle 31 contains flowing Purpose of recovering hot gas and heat resources formed after heating. The exhaust gas from the machine (VOCs Laden is discharged. Some heat exchange sources are recovered (not shown in the figure will greatly increase the combustion furnace when this heat exchanger is damaged or the heat exchange method can be maintained without relying on the purpose of the blower to collect the heat.) After oxidative combustion Re-piping to a heat exchanger converter 30 and another line of air. V 0 C s 2 0 heat exchange via heat exchange tube bundle 31 and air 3 2 can be used in the factory. Note that After passing through the air) 2 0, the blower is also designed to be located in the heat storage). When the wind of this design lacks the flow path of the air is blocked, the heat storage is required. The present invention proposes that the secondary recovery can be achieved by one wind pressure drive, and 30 (heat is connected to the air supply heat exchanger to collect heat energy and act. The material generated by the air work machine heat exchanger 27 is the pressure loss and consumption type. The combustion coil furnace is built with high efficiency, so when the gas turbine 27 will drop 30, its heat exchange gas 32 will pass through to achieve 30% of the wind pressure to guide the heat exchange energy loss and demolition. Packaged heat exchange efficiency and heat recovery [Content of the invention] The main purpose of the present invention is to provide a regenerative combustion recovery method that uses the smoke Hi effect and the pressure difference effect to make the reacted Bagu ... moon dagger gas automatically pass through the heat exchanger towel That is to say, by the effect of high and low, hot smoke self-effect and gas flow kinetic energy (velocity energy) difference effect = wonderful = degree f flow disturbance and flow, you can regenerate the heat generated by the combustion chamber of the combustion furnace again.
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於燃燒室封閉回路(cl〇se Loop)中達到高效率熱能 利用之功能,有別於一習用技術之開放回路。 收再 本發 於蓄熱式 以熱氣端 回收。使 熱氣於燃 首先,其 送風機抽 一蓄熱床 (VOCs)在 程後有機 氧化反應 床通過再 部分而溫 體流動之 溫的管束 資源回收 動的熱傳 反應後乾 氣接續經 時廢氣的 而排放至 明的再一目的在 燃燒爐中蓄熱材 並聯流方式建構 有機廢氣在煙囪 燒室中自動並聯 有機廢氣(V0C; 送進入燃燒爐之 加熱廢氣後,有 燃燒室中氧化反 廢氣接著進入第 之熱量進行熱回 進入燃燒室之有 有機廢氣接續藉 動能(速度能)差 式熱回收熱交換 的目的。其進入 導介質藉由間接 淨且高溫有機廢 由第二蓄熱床, 溫度已降至安全 空氣中。 於提所供之管束式熱交 之上方燃燒室的水平位 一管束式熱交換器用以 及動壓差之雙效應作用 進出熱交換器與燃燒室 3 Laden Air)的途徑係 管線進入第一蓄熱床。 機廢氣中之揮發性有機 應成無害之H20及C02。 二蓄熱床,其第二蓄熱 收’用以預熱之後先從 機廢氣。在燃燒室中其 由高低溫之密度差煙囪 效應’而自然擾動進入 ,中,進行熱交換動作 官束式熱回收熱交換器 ,有機廢氣間接接觸的 氣^熱能,反應後的乾 由送風機抽送排出至大 溫度及且淨化率亦達至 進行熱能 下,部分 〇 為:由一 在通過第 物質 在機燒過 床可儲存 第二蓄熱 燃繞後之 效應及氣 相對較低 以達到熱 中含有流 機會吸收 淨有機廢 氣中,此 環保要求The function of achieving high-efficiency thermal energy utilization in the closed loop of the combustion chamber is different from the open loop of a conventional technology. Recycling The hair is regeneratively recovered by the hot gas end. Let the hot gas burn. First, its blower draws a heat storage bed (VOCs). After the process, the organic oxidation reaction bed recovers the heat transfer reaction through the partially bundled tube bundle resource. The dry gas continues to pass through the exhaust gas. Another purpose of Zhiming is to construct organic waste gas in parallel flow of heat storage materials in the combustion furnace. The organic waste gas is automatically paralleled in the combustion chamber of the chimney (V0C; after the heated exhaust gas sent into the combustion furnace, there is an oxidation anti-exhaust gas in the combustion chamber and then enters the first. The heat is re-entered into the combustion chamber for the purpose of organic waste gas, which then borrows kinetic energy (speed energy) for differential heat recovery and heat exchange. It enters the conducting medium through indirect net and high-temperature organic waste from the second heat storage bed, and the temperature has been reduced to safety. In the air, the level of the combustion chamber above the tube bundle heat transfer provided is a tube bundle heat exchanger and the dual effect of dynamic pressure difference into and out of the heat exchanger and combustion chamber (3 Laden Air) is the pipeline entering the first A thermal storage bed. The volatile organic compounds in the exhaust gas of the machine should be harmless H20 and C02. Two heat storage beds, whose second heat storage is used for preheating the exhaust gas from the machine. In the combustion chamber, it is naturally disturbed by the high and low temperature density chimney effect. In the middle, the heat exchange action is performed in the beam-type heat recovery heat exchanger. The gas indirectly contacted by the organic waste gas is thermal energy, and the dry air after the reaction is pumped by the blower. Discharge to a large temperature and the purification rate also reaches thermal energy, part 0 is: the effect of the second heat storage and combustion can be stored by the first material in the machine-burned bed, and the gas is relatively low to achieve heat-containing flow Opportunity to absorb net organic waste gas, this environmental requirement
200420857 五、發明說明(6) 【實施方式】 本發明在蓄熱式燃燒爐上製作出熱交換器使有機廢氣 能自動進出熱轉換器,其實施例以雙塔蓄熱式燃燒爐作為 實施例用以說明本發明之精神。 首先,參考圖二所示,其為雙塔蓄熱式燃燒爐 (RT0)之結構100示意圖。其中蓄熱式燃燒爐100主要由 兩組蓄熱床(第一蓄熱床1 1 0和第二蓄熱床1 2 0)、廢氣燃 燒室150及其相連之廢氣進出管線等。有機廢氣2 0 0 ( VOCs Laden Air)的進出方式如下所述: 有機廢氣2 0 0 ( VOCs Laden Air ;以下簡稱VOCs 2 0 0)由一進風門2 6 0控制進入燃燒爐管線,分別經由第一 流向調節閥2 1 0進入第二蓄熱床1 2 0 (此時的第二流向調節 閥220和第三流向調節閥2 3 0為OFF [關閉]狀態)。在通過 第二蓄熱床120後V0Cs 2 0 0在燃燒室130中由燃料喷嘴140提 供一燃燒用火焰1 50將VOCs經氧化反應形成無害的H20及 C02。燃料喷嘴1 4 0提供所述燃燒室熱能之裝置亦可以電熱 器或及電漿產生器或及其他可提供熱能之設施或及不須此 裝置等其中之一所組成。此燃料喷嘴1 4 0之裝置位置亦可 於蓄熱式燃燒爐之入口處(圖中未示)。其燃燒室1 3 0内 部之燃燒溫度可達攝氏溫度6 0 0〜9 5 0°C或是其它的溫度 (依所燃燒物質而定),在經過燃燒過程後之高溫廢氣則 進入第一蓄熱床110,其第一蓄熱床110可儲存反應之熱量 作為熱能回收,用以預熱而後先進入第一蓄熱床1 1 0之200420857 V. Description of the invention (6) [Embodiment] The present invention produces a heat exchanger on a regenerative combustion furnace to allow organic waste gas to automatically enter and exit the heat exchanger. The embodiment uses a double-tower regenerative combustion furnace as an example to The spirit of the present invention will be described. First, referring to FIG. 2, it is a schematic diagram of the structure 100 of a double-tower regenerative combustion furnace (RT0). The regenerative combustion furnace 100 is mainly composed of two sets of regenerative beds (the first regenerative bed 110 and the second regenerative bed 120), the exhaust gas combustion chamber 150, and the exhaust gas inlet and outlet pipelines connected thereto. The way of entering and exiting the organic waste gas 2 0 (VOCs Laden Air) is as follows: The organic waste gas 2 0 (VOCs Laden Air; hereinafter referred to as VOCs 2 0 0) is controlled by an inlet damper 2 6 0 and enters the combustion furnace pipeline, respectively through the first The one-way control valve 2 1 0 enters the second heat storage bed 1 2 0 (the second flow direction control valve 220 and the third flow direction control valve 2 3 0 at this time are in the OFF state). After passing through the second thermal storage bed 120, VOCs 2 0 0 is provided by a fuel nozzle 140 in the combustion chamber 130 with a combustion flame 1 50 and the VOCs are oxidized to form harmless H20 and C02. The fuel nozzle 140 can provide a device for providing the heat energy of the combustion chamber, which may also be composed of an electric heater or a plasma generator or other facilities capable of providing heat energy, or one of which is not required. The position of the fuel nozzle 140 can also be located at the entrance of the regenerative burner (not shown). The combustion temperature in the combustion chamber of 130 can reach 60 ° C ~ 950 ° C or other temperature (depending on the substance to be burned). The high-temperature exhaust gas after the combustion process enters the first heat storage. In the bed 110, the first heat storage bed 110 can store the heat of the reaction as heat energy for recovery, and is used for preheating and then enters the first heat storage bed 1 1 0
第1ί頁 200420857 五、發明說明(7) VOCs 2 0 0,再進入燃燒室1 3〇中進行反應,如此,便可降低 燃燒喷嘴1 4 0的能ΐ相耗。其中第二蓄熱床j 2 〇及第一蓄熱 床1 1 0係由蜂槽狀、&馬輕形或圓柱形等的陶瓷材料所組 成,其具有良好的蓄熱能力,其陶瓷材料的孔洞結構可使 反應的有機廢氣V〇Cs20〇通過蓄熱床1 2〇及1丨〇進入燃燒室 1 3 0。所述之第一流向調節閥2丨〇、第二向量調節閥2 2 〇、 第三流向調節閥2 3 0、第四流向調節閥2 4 〇分別接有電動閥 或及氣動閥’以能作相互之開關切換動作。在燃燒室丨3 〇 正上方含有熱氣管線通道17 0及1 6 0使高溫熱氣自然通往位 於燃燒至1 3 0上方的管束式熱交換器3〇〇( Tube bundles heat exchanger),其管束式熱交換器3 0 0的溫度較低, 反應後的VOCs20 0便會自動擴散至溫度較低的管束式熱交 換器3 0 0中而形成密度差異之煙囪效應之自然對流流動現 象。就管束式熱交換器3 0 0及燃燒室1 3 0周圍之廢氣密度而 言,反應後之有機廢氣VOCs 2 0 0於管束式熱交換器3 0 0的廢 氣密度自然低於燃燒室1 3 0内之廢氣密度,且管束式熱交 換器3 0 0高於燃燒室1 3 0之上,因此自然有煙囪效應的自然 對流流動現象存在。此外,反應後的有機廢氣V 〇 C s 2 0 0亦 會因廢氣流動所產生離開第一蓄熱床1 1 0或第二蓄熱床1 2 〇 的風速之動壓力(velocity pressure)影響而進入管束 式熱交換器3 0 〇進行熱交換的動作。其上所述,便是本發 明的重點所在。 其管束式熱交換器3 0 0中包含有螺旋狀之管路3 1 0和一 供VOCs2 0 0廢氣進出之結構體340。熱交換管束管路310中Page 1ί 200420857 V. Description of the invention (7) VOCs 2 0 0, and then enter the combustion chamber 1 30 for reaction. In this way, the energy phase consumption of the combustion nozzle 1 40 can be reduced. The second thermal storage bed j 2 0 and the first thermal storage bed 1 10 are composed of honeycomb-shaped, & horse-shaped or cylindrical ceramic materials, etc., which have good heat storage capacity, and the pore structure of the ceramic material. The reacted organic waste gas VOCs20 can pass through the thermal storage beds 120 and 120 and enter the combustion chamber 130. The first flow direction regulating valve 2 丨 〇, the second vector adjustment valve 2 2 0, the third flow direction regulating valve 2 3 0, and the fourth flow direction regulating valve 2 4 〇 are respectively connected with an electric valve or a pneumatic valve to enable Switch between each other. There are hot gas pipeline channels 17 0 and 160 directly above the combustion chamber. The high temperature hot gas will naturally lead to the tube bundle heat exchanger 300, which is located above the combustion, and its tube bundle type The temperature of the heat exchanger 300 is low, and the VOCs 200 after the reaction will automatically diffuse into the lower temperature tube bundle heat exchanger 300 and form the natural convection flow phenomenon of the chimney effect with different density. As far as the exhaust gas density around the tube bundle heat exchanger 300 and the combustion chamber 130 is concerned, the organic exhaust gas VOCs 2 0 0 in the tube bundle heat exchanger 3 0 0 is naturally lower than the combustion chamber 1 3 The exhaust gas density within 0, and the tube bundle heat exchanger 300 is higher than the combustion chamber 130, so the natural convection flow phenomenon with a chimney effect exists naturally. In addition, the reacted organic waste gas V 0 C s 2 0 will also enter the tube bundle due to the influence of the velocity pressure of the wind speed leaving the first heat storage bed 1 10 or the second heat storage bed 1 2 0 caused by the flow of the waste gas. The heat exchanger 300 performs heat exchange operation. This is the focus of the present invention. The tube-bundle heat exchanger 300 includes a spiral-shaped pipe 3 10 and a structure 340 for VOCs 2 0 exhaust gas to enter and exit. Heat exchange tube bundle pipe 310
第12頁 200420857 五、發明說明(8) 填充有流動的熱傳導介質3 2 〇,以進行熱交換動作。而可 加入之熱傳導介質3 2 0包括有:空氣、蒸汽、水及熱媒油 …等任何形態之流體。其所述螺旋狀之管路3 1 0可為其它 形狀之管路所構成,其目的在增加管路在結構體中3 4 〇與 高溫之VOCs2 0 0的接觸面積。而熱傳導介質32〇經由加熱後 所形成之熱氣、高溫蒸汽、熱水及熱媒油,可經由不同的 方法加以利用,以達到熱資源回收的目的。其進入管束式 熱交換器3 0 0之熱傳導介質3 2 〇之初始溫度不受限制,但需 低於燃燒至3 0 0的反應溫度,其出管束式熱交換器3 〇 〇之熱 傳導介貝3 2 0控制在1 8 0〜3 0 0°C之間(隨順工廠内機台要求 而作變更)。但可注意的是,熱傳導介質32〇之初始溫度 與燃燒室3 0 0的溫度差異越大,其熱交換效益亦越高。 此外,在熱交換管束之管路310進出管束式熱交換器3〇〇會 多加一旁通管3 3 0 ( bypass),並有一第六流量調節閥33〇 位於旁通官上(如圖二所示)用以調節熱傳導介質32〇吸 收太多熱能導致溫度過高時,將未經過管束式埶交換器 3 0 0的熱傳導介質3 2 0 (未吸收熱量的熱傳導介^ 32〇/ 接經過旁通管3 3 0達到控溫之功效。 、 &與前述傳統蓄熱式 、第四流向調節閥 反應後之有機廢氣VOCs20 〇其路 燃燒爐1 〇相同流經由第一蓄熱床1! 0 240,由送風機2 7 0排出至大氣中。 其VOCS20 0亦可由進風門26〇進入管線,分別經由第三 流向調節闕230進入第一蓄熱床丨丨〇,其以吸收埶 蓄熱床uo可預熱V〇Cs2〇〇。在通過第—蓄熱床‘、u〇後v〇CsPage 12 200420857 V. Description of the invention (8) It is filled with a flowing heat conducting medium 3 2 0 for heat exchange action. The heat transfer medium 3 2 0 that can be added includes: air, steam, water, heat medium oil, etc., in any form of fluid. The helical pipe 3 10 can be composed of other shapes of pipes, and the purpose is to increase the contact area of the pipe in the structure between 3 40 and the high-temperature VOCs 2000. The heat gas, high-temperature steam, hot water, and heat medium oil formed after heating can be used in different ways to achieve the purpose of heat resource recovery. The initial temperature of the heat conduction medium 3 2 0 entering the tube bundle heat exchanger 300 is not limited, but it needs to be lower than the reaction temperature of combustion to 300, and the heat conduction medium of the tube bundle heat exchanger 300 3 2 0 is controlled between 180 ° ~ 300 ° C (changes with the requirements of the machine in the factory). However, it can be noticed that the larger the difference between the initial temperature of the heat conducting medium 32 and the temperature of the combustion chamber 300 is, the higher the heat exchange efficiency is. In addition, a bypass pipe 3 3 0 (bypass) is added to the pipe 310 of the heat exchange tube bundle in and out of the tube bundle heat exchanger 300, and a sixth flow regulating valve 33 is located on the bypass officer (as shown in Figure 2). (Shown) Used to adjust the heat conduction medium 32〇 When too much heat energy is absorbed and the temperature is too high, the heat conduction medium 3 2 0 (the heat conduction medium without heat absorption ^ 32〇 / The through pipe 3 3 0 achieves the effect of temperature control. &Amp; Same as the organic waste gas VOCs 20 after the reaction of the traditional thermal storage type and the fourth flow direction regulating valve 〇 The same way the combustion furnace 1 〇 flows through the first thermal storage bed 1 0 240, It is discharged into the atmosphere by the blower 2 70. The VOCS20 0 can also enter the pipeline through the air inlet valve 26 and enter the first heat storage bed through the third flow direction adjustment 阙 230. It can be used to preheat V by absorbing the heat storage bed uo. 〇Cs200. After passing the first heat storage bed ', u〇s
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五、發明說明(9) 在燃燒室130中由燃燒喷嘴14〇提供一燃燒用火焰15〇將 VOfs經氧化反應形成無害的H2〇及c〇2。在經過燃燒過程後 之高溫廢氣則進入第二蓄熱床1 2 0,其可儲存反應之熱量 作為熱肖b回收,用以預熱而後先進入第二蓄熱床I? 〇之 VOCS2 0 0。此時的反應的v〇Cs2 0 0亦會如依所述之方式進入 &束式熱父換器300中進行熱交換動作,在此不再重複說 明之。反應後之VOCs2 0 0流經由第二蓄熱床12〇、第二流量 調節閥2 2 0,由送風機2 70排出至大氣中,第二蓄熱床ι2〇 亦會吸收VOCs20 0之部分熱能,因此排出大氣3 5 〇中的 VOCs 2 0 0可降至安全溫度及濃度排放。 其上述之有機廢氣V〇Cs20 0流動方向(於第一蓄熱床 1 1 0或第二蓄熱床1 2 0進行反應)定時做切換保持第一蓄熱 床及第二蓄熱床可維持高溫用以預熱反應氣體,如此熱能 回收率即可達到9 3 %以上,同時淨化率可達到9 5%〜9 9%以V. Description of the invention (9) In the combustion chamber 130, a combustion flame 150 is provided by a combustion nozzle 14o, and VOfs is oxidized to form harmless H20 and co2. After the combustion process, the high-temperature exhaust gas enters the second thermal storage bed 1220, and the heat of the stored reaction can be recovered as the heat b, used to preheat and then enter the VOCS2 0 0 of the second thermal storage bed I? 0. The reaction v0Cs2 0 0 at this time will also enter the & beam heat parent switch 300 for heat exchange action as described above, and will not be repeated here. After the reaction, the VOCs 2 0 0 flows through the second heat storage bed 12 0 and the second flow regulating valve 2 2 0 and is discharged into the atmosphere by the blower 2 70. The second heat storage bed 2 2 will also absorb part of the heat energy of VOCs 2 0 and is discharged. VOCs 2 0 0 in the atmosphere 3 5 can be reduced to safe temperature and concentration emissions. The flow direction of the above-mentioned organic waste gas V0Cs20 0 (reacting on the first thermal storage bed 110 or the second thermal storage bed 120) is periodically switched to maintain the first thermal storage bed and the second thermal storage bed to maintain high temperatures for the purpose of predicting Thermal reaction gas, so that the thermal energy recovery rate can reach more than 93%, and the purification rate can reach 95% to 99%.
、有機廢氣V〇Cs 2 0 0除可選擇第一流向調節閥21〇和第三 流向調節閥2 3 0進出外,蓄熱式燃燒爐1 〇 〇包含有一旁通管 相連於送風機2 7 0之管線,其旁通管亦有第五流量控制閥 25峨制之,但此路徑僅供雙塔蓄熱式燃燒爐1〇( RT〇)系 統仔機之狀況使用’並非v〇cs 2 〇 〇燃燒反應之正常路線。 本,明之管束式熱交換器可運用在任何一種形式之燃燒爐 或氧化爐或反應爐中,且不需其他額外的導入裝置,在本 發明之實施例僅以雙塔蓄熱式燃燒爐說明之。本發明所述 之參考例子係在特定領域中之特定實施例,因此熟知此技In addition to the organic exhaust gas VOCs 2 0 0, in addition to the choice of the first flow direction regulating valve 21 0 and the third flow direction regulating valve 2 30, the regenerative combustion furnace 1 100 includes a bypass pipe connected to the blower 2 7 0 The pipeline and its bypass pipe also have a fifth flow control valve made of 25 ohms, but this path is only for the condition of the twin tower regenerative combustion furnace 10 (RT〇) system. 'Not v〇cs 2 〇〇 combustion The normal course of reaction. In the present, the tube bundle heat exchanger of Ming can be used in any kind of combustion furnace or oxidation furnace or reaction furnace, and does not require other additional introduction devices. In the embodiment of the present invention, only the double-tower regenerative combustion furnace is used to describe it. . The reference examples described in the present invention are specific embodiments in a specific field, so the technology is well known
第14頁 200420857 五、發明說明(ίο) 藝的人士應能明瞭本發明要義所在,進行適當、些微的調 整和應用,仍將不失本發明之要義所在。接續的申請專利 範圍中係包含在本發明中所有此類的應用、調整。 綜上所述,本發明實施之具體性,誠已符合專利法中所規 定之發明專利要件,謹請 貴審查委員惠予審視,並賜准 專利為禱。Page 14 200420857 V. The person skilled in the art should be able to understand the essence of the present invention, and make appropriate and slight adjustments and applications without losing the essence of the present invention. The scope of subsequent patent applications includes all such applications and adjustments in the present invention. In summary, the specificity of the implementation of the present invention has already met the requirements of the invention patent stipulated in the Patent Law. Your reviewers are invited to review it and grant the patent as a prayer.
第15頁 200420857 圖式簡單說明 圖示簡要說明: 圖一係為傳統雙塔蓄熱式燃燒爐搭配熱氣旁通熱回收之結 構示意圖。 圖二係為本發明實施例中雙塔蓄熱式燃燒爐搭配熱回收之 結構示意圖。 圖號說明: 1 0蓄熱式燃燒爐11第一蓄熱床 1 2第二蓄熱床1 3燃燒室 1 4燃料喷嘴1 5火焰 2 0有機廢氣2 1第一流向調節閥 2 2第二流向調節閥2 3第三流向調節閥 24第四流向調節閥25第五流量調節閥 2 6進風門2 7送風機 3 0熱交換器31熱交換管束 3 2熱傳導介質1 0 0蓄熱式燃燒爐 110第一蓄熱床120第二蓄熱床 1 3 0燃燒室1 4 0燃料喷嘴 15 0火焰2 0 0有機廢氣 2 1 0第一流向調節閥2 2 0第二流向調節閥 2 3 0第三流向調節閥24 0第四流向調節閥 2 5 0第五流量調節閥2 6 0進風門 2 7 0送風機3 0 0管束式熱交換器 3 1 0熱交換管束管路3 2 0熱傳導介質 3 3 0第六流量調節閥3 4 0結構體Page 15 200420857 Brief description of the diagram Brief description of the diagram: Figure 1 is a schematic diagram of the structure of a traditional double-tower regenerative combustion furnace with hot gas bypass heat recovery. FIG. 2 is a schematic structural diagram of a double-tower regenerative combustion furnace with heat recovery according to an embodiment of the present invention. Description of drawing number: 1 0 regenerative combustion furnace 11 first regenerator bed 1 2 second regenerator bed 1 3 combustion chamber 1 4 fuel nozzle 1 5 flame 2 0 organic waste gas 2 1 first flow direction regulating valve 2 2 second flow direction regulating valve 2 3 third flow direction regulating valve 24 fourth flow direction regulating valve 25 fifth flow regulating valve 2 6 air inlet valve 2 7 blower 3 0 heat exchanger 31 heat exchange tube bundle 3 2 heat conducting medium 1 0 0 regenerative combustion furnace 110 first heat storage Bed 120 Second heat storage bed 1 3 0 Combustion chamber 1 4 0 Fuel nozzle 15 0 Flame 2 0 0 Organic exhaust gas 2 1 0 First flow direction regulating valve 2 2 0 Second flow direction regulating valve 2 3 0 Third flow direction regulating valve 24 0 Fourth flow direction regulating valve 2 5 0 Fifth flow regulating valve 2 6 0 Intake valve 2 7 0 Fan 3 0 0 Tube bundle heat exchanger 3 1 0 Heat exchange tube bundle pipe 3 2 0 Heat transfer medium 3 3 0 Sixth flow regulating valve Valve 3 4 0 structure
第16頁 200420857 圖式簡單說明Page 16 200420857 Schematic description
第17頁Page 17
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Cited By (3)
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CN108317525A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of pharmaceutical technology emission-control equipment and processing method |
CN108317524A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of the heat accumulating type incineration device and its application process of oxidation furnace exhaust |
CN108317526A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of organic waste gas treatment device |
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KR100709749B1 (en) * | 2006-11-21 | 2007-04-24 | 주식회사세진환경 | Hot blast producing system using waste heat of regenerative thermal oxidizer |
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KR101476270B1 (en) * | 2013-05-13 | 2014-12-24 | 주식회사 엔바이온 | Regenerative Thermal Oxidizer |
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-
2003
- 2003-04-10 TW TW092108224A patent/TWI293359B/en not_active IP Right Cessation
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2004
- 2004-01-08 KR KR1020040001255A patent/KR20040089460A/en not_active Application Discontinuation
Cited By (3)
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CN108317525A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of pharmaceutical technology emission-control equipment and processing method |
CN108317524A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of the heat accumulating type incineration device and its application process of oxidation furnace exhaust |
CN108317526A (en) * | 2017-01-17 | 2018-07-24 | 恩国环保科技(上海)有限公司 | A kind of organic waste gas treatment device |
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KR20040089460A (en) | 2004-10-21 |
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