TW200304850A - Method and device for treating organic exhaust - Google Patents

Method and device for treating organic exhaust Download PDF

Info

Publication number
TW200304850A
TW200304850A TW092106925A TW92106925A TW200304850A TW 200304850 A TW200304850 A TW 200304850A TW 092106925 A TW092106925 A TW 092106925A TW 92106925 A TW92106925 A TW 92106925A TW 200304850 A TW200304850 A TW 200304850A
Authority
TW
Taiwan
Prior art keywords
cooling
condensate
condensing
condenser
exhaust gas
Prior art date
Application number
TW092106925A
Other languages
Chinese (zh)
Other versions
TWI265822B (en
Inventor
Masahiko Aikou
Kazuyuki Hayashi
Original Assignee
Matsushita Environmental & Air Conditioning Engineering Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Environmental & Air Conditioning Engineering Co Ltd filed Critical Matsushita Environmental & Air Conditioning Engineering Co Ltd
Publication of TW200304850A publication Critical patent/TW200304850A/en
Application granted granted Critical
Publication of TWI265822B publication Critical patent/TWI265822B/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)
  • Activated Sludge Processes (AREA)
  • Treatment Of Sludge (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)

Abstract

The present invention provides a technology for treating the organic components in an organic exhaust while recycling and performing a waste disposal treatment at the same time. The method comprises the first cooling and condensing process of cooling and condensing an organic exhaust; the second cooling and condensing process of cooling and condensing the exhaust processed by the first cooling and condensing process; a process for recycling and regenerating the condensate in the first cooling and condensing process; and a process of using an active sludge to treat the condensate in the second cooling and condensing process.

Description

200304850200304850

五、發明說明(i) [發明所屬之技術領域] 本發明係有關於一種在液晶及半導體製程等中被排出‘ 的有機廢氣之處理方法。 [先前技術] 在液晶及半導體製程等中,所謂被排出的有機廢氣 是,來自以光阻(photoresist)的剝除製程等所蒸發"的剝 除液來的氣體荨。剝除液大多含有自單甲乙醇胺 〉 (monoethanolamine、MEA)及二曱基亞楓 (dimethylsulfoxide、DMS0)所構成的有機溶劑。此剝除 液是,由於在剝除製程中被以6 0 t ~ 8 0 °C加熱,所以其中 7%的左右會被蒸發,而被導入廢氣通路。廢氣組成是,不 只在製程中所被使用的材料,製程中的處理環境也會被影 響。例如’在一般的清淨室(c 1 e a n r ο 〇 m )中,被控制在2 5 °C、60%RH的程度。 又’廢氣是被控制在,處理環境約為2 5 左右、 RH5 0〜60%的程度,所以產生的廢氣會變得比較高溫(35艺 程度)。 從上述事情得知,例如,來自剝除製程的廢氣是,和 水蒸氣相同,作為有機廢氣,大多含有單甲乙醇胺(ME A) 或二曱基亞楓(DMS0)等。 [發明内容] (發明所欲解決的課題)V. Description of the invention (i) [Technical field to which the invention belongs] The present invention relates to a method for treating organic waste gas which is discharged in a liquid crystal, semiconductor manufacturing process, and the like. [Prior art] In the liquid crystal and semiconductor manufacturing processes, the organic waste gas to be discharged is a gas net from a stripping solution evaporated by a photoresist stripping process or the like. Most of the stripping solution contains an organic solvent composed of monoethanolamine (MEA) and dimethylsulfoxide (DMSO). This stripping liquid is heated at 60 t to 80 ° C during the stripping process, so about 7% of it will be evaporated and introduced into the exhaust gas path. The composition of the exhaust gas is not only the materials used in the manufacturing process, but also the processing environment in the manufacturing process. For example, 'in a general clean room (c 1 e a n r ο 〇 m), it is controlled to about 25 ° C and 60% RH. Also, the exhaust gas is controlled, and the processing environment is about 2 5 and RH5 is about 0 to 60%, so the exhaust gas generated will become relatively high temperature (35 degrees). From the above, it is known that, for example, the exhaust gas from the stripping process is the same as water vapor, and as the organic exhaust gas, most of them contain monomethylethanolamine (ME A) or dimethyzene (DMS0). [Summary of the Invention] (Problems to be Solved by the Invention)

200304850 五、發明說明(2) 在液晶及半導體製造製程中所被排出的有機廢氣是大 量。特別是,由於在液晶製程中所被使用的基板尺寸也很 大,所以剝除液也很多,因此所產生的廢氣更是大量。而 且,自成本的觀點上看,是以回收再利用為較佳的。冷卻 冷凝較多被使用在來自此有機廢氣的有機成分的分離^ 收。然而,由於處理大量的廢氣,需要大量的冷水。亦 即,存在著由於水及冷卻所需的成本負擔變大的問題。因 此’一直到現在,未能得到有效的回收再生率。 另一方面,從環境的觀點上看,處理方法是把有機廢 氣直接通過刷洗器(scrubber),然而需要大量的水及中^ 藥液,藉由刷洗器的運轉管理狀況,容易產生臭氣的問 存在。又,在刷洗器的處理水是作為排水處理,被導入於 活性污泥處理裝置,然而由於流動B〇D負擔的高濃度、 理水,裝置變成過於巨大,在此管理方法方面,也存的, 題。自上述觀點,分離回收有機成分後,藉由刷洗器 性污泥等處理後廢棄及排出為較佳的。 的/ 然而,直到目前為止,不管是將有機廢氣作為資 效利用’有效率的經過排水處理作為廢棄處理,抑 Φ X明疋以提供處理技術為目的,具能 成有機廢氣的有機成分的再利用和廢棄處理。# 供能同時達成上述右嬙#八μ = 以提 i Α γ 7 有機成分的再利用、及廢氣處理、3 i 加上廢氣的臭氣對第的q 及再 τ朿的3點的處理技術,作為其他目的200304850 V. Description of the invention (2) The organic waste gas discharged in the liquid crystal and semiconductor manufacturing process is a large amount. In particular, since the size of the substrate used in the liquid crystal manufacturing process is also large, there are also many stripping liquids, and thus a large amount of exhaust gas is generated. Moreover, from a cost standpoint, recycling is better. Cooling and condensation are mostly used in the separation of organic components from this organic waste gas. However, since a large amount of exhaust gas is processed, a large amount of cold water is required. That is, there is a problem that the cost burden required for water and cooling becomes large. Therefore, until now, effective recovery rates have not been obtained. On the other hand, from an environmental point of view, the treatment method is to directly pass the organic waste gas through the scrubber. However, a large amount of water and traditional Chinese medicine liquid are required. Due to the operation and management status of the scrubber, odor is easily generated. Ask for existence. In addition, the treated water in the scrubber is introduced into the activated sludge treatment device as a drainage treatment. However, due to the high concentration of the flowing BOD and the water treatment, the device becomes too large, and this management method also exists. , question. From the above viewpoints, it is preferable to separate and recover the organic components, and then discard and discharge them by treatment with scrubbing sludge and the like. / However, up to now, regardless of the use of organic waste gas as an asset, it has been effectively treated as a waste water and treated as a waste treatment. It is important to provide treatment technology for the purpose of reusing the organic components of organic waste gas. And disposal. # Supplying energy at the same time to achieve the above right # 八 μ = to improve the reuse of organic components of Α γ 7 and waste gas treatment, 3 i plus the odor of waste gas to the three points q and re τ 朿 treatment technology For other purposes

200304850 五 、發明說明(3) (用以解決課題的手段) 本發明者等是,為了解決上述課題, 氣的有機成分的分離回收製程時,藉由檢时有關有機廢 製程中的處理内容,發現能一舉達』二工夫在冷卻冷凝 廢棄處理,又,再加上排出氣體 、成=的再利用及 策,完成本發明。 衣見(臭氣)的環境對 亦即,根據本發明,提供如下的方法。 、 (1)有機廢氣之處理方法,包括:冷卻 的第1冷卻冷凝製程;儲留在第一冷卻冷凝製程中的ς J 液的製程;冷卻冷凝經過此第1冷卻冷凝製程的廢氣二第2 冷卻冷凝製程;以及儲留在第2冷卻冷凝製程中的冷凝液 的製程。 (2 )如(1 )所記載的方法,更包括在上述第2冷卻冷凝 製程之前,經過上述第1冷卻冷凝製程的廢氣的霧氣分離 製程。 (3 )如(1 )或(2 )所記載的方法,其中在上述第1冷卻冷 凝製程中’將上述有機廢氣所含有的水蒸氣冷卻至飽和蒸 氣壓的溫度的附近。 (4 )如(1)〜(3 )任1項所記載的方法,其中在上述第1冷 卻冷凝製程中,將上述有機廢氣所含有的有機成分的 70wt%以上90wt%以下回收,在上述第2冷卻冷凝製程中’ 將上述有機廢氣所含有的有機成分的l〇wt%以上20wt%以下 回收。 (5)如(1)〜(4)任1項所記載的方法,更包括:將上述200304850 V. Description of the invention (3) (Means to solve the problem) In order to solve the above problems, the inventors of the organic waste gas process in the process of separation and recovery of gas in order to solve the above problems, It was found that the two processes of cooling and condensing waste disposal in one stroke, coupled with exhaust gas, reuse, and strategy, have completed the present invention. The environment of Yomi (odor). That is, according to the present invention, the following method is provided. (1) A method for treating organic waste gas, including: a first cooling and condensing process for cooling; a process for making J liquid stored in the first cooling and condensing process; and cooling and condensing the exhaust gas that has passed through the first cooling and condensing process. A cooling condensation process; and a process of condensate stored in the second cooling condensation process. (2) The method according to (1), further comprising a mist separation process of the exhaust gas that has passed through the first cooling and condensation process before the second cooling and condensation process. (3) The method according to (1) or (2), wherein in the first cooling and condensing process, the water vapor contained in the organic exhaust gas is cooled to a temperature near a saturated vapor pressure. (4) The method according to any one of (1) to (3), wherein in the first cooling and condensation process, 70% by weight or more and 90% by weight or less of the organic components contained in the organic waste gas are recovered, and the 2 In the process of cooling and condensing, 10 wt% to 20 wt% of the organic components contained in the organic waste gas are recovered. (5) The method according to any one of (1) to (4), further comprising:

2042-5565-PF(Nl);Ahddub.ptd 第8頁 200304850 五、發明說明(4) 第1冷卻冷凝製程的冷凝液回收、再生的製程;以及將上 述第2冷卻冷凝製程的冷凝液回收、排水處理的製程。 (6 )如(1 )〜(5 )任1項所記載的方法,更包括處理經過 上述第2冷卻冷凝製程的廢氣的製程。 (7) 有機廢軋之處理方法,包括:冷卻冷凝有機廢氣 的製程;將含有高濃度有機成分的冷凝液再生的再生製 程,以及將含有低濃度有機成分的冷凝液排水處理的製 程。2042-5565-PF (Nl); Ahddub.ptd Page 8 200304850 V. Description of the invention (4) The process of recovering and regenerating the condensate from the first cooling and condensing process; and recovering the condensate from the second cooling and condensing process, Process of drainage treatment. (6) The method according to any one of (1) to (5), further comprising a process for treating exhaust gas that has passed through the second cooling and condensation process. (7) Organic waste rolling treatment methods include: a process for cooling and condensing organic waste gas; a regeneration process for regenerating a condensate containing a high concentration of organic components; and a process for draining a condensate containing a low concentration of organic components.

(8) 如(7)所記載的方法,更包括處理在上述冷凝製程 中未能冷凝剩下的廢氣的製程。 (9) 有機廢氣之處理裝置包括:冷凝有機廢氣的第1冷 凝器;冷凝經過上述第1冷凝器的廢氣的第2冷凝器;儲留 自第1冷凝器所產生的冷凝液的第1儲留部;以及儲留自第 2冷凝器所產生的冷凝液的第2儲留部。 (1 0 )如(9)所記載的裝置,其中上述冷凝裝置是,以 廢氣可通過的方式連通上述第1儲留部及第2儲留部。 (11) 如(9 )或(1 〇 )所記載的裝置,其中上述第1儲留部 及第2儲留部是,藉由霧氣分離裝置被連通。(8) The method according to (7), further comprising a process for treating the exhaust gas that fails to condense in the above-mentioned condensation process. (9) The organic waste gas treatment device includes: a first condenser for condensing organic waste gas; a second condenser for condensing exhaust gas passing through the first condenser; and a first reservoir for condensate generated from the first condenser A retention section; and a second retention section that stores condensate generated from the second condenser. (10) The device according to (9), wherein the condensing device communicates the first storage section and the second storage section so that the exhaust gas can pass through. (11) The device according to (9) or (10), wherein the first storage section and the second storage section are connected by a mist separation device.

(12) 如(9)〜(11)任一項所記載的裝置,其中上述第1 冷凝器及上述第2冷凝器和上述第1儲留部及上述第2儲留 部都被單元化。 (1 3 )如(9 )〜(1 2 )任一項所記載的襞置,其中上述第i 冷凝部和上述第2冷凝部各自具備冷凝器内溫度檢測裝 置。(12) The device according to any one of (9) to (11), wherein the first condenser and the second condenser, and the first storage unit and the second storage unit are all unitized. (1 3) The apparatus according to any one of (9) to (1 2), wherein each of the i-th condensing unit and the second condensing unit is provided with a temperature detecting device in a condenser.

2042-5565-PF(Nl);Ahddub.ptd 第9頁 200304850 五、發明說明(5) 液0(22:(9) (13)任—項所記載的裝置,更包括將冷凝 液回收再生的裝置、及將冷凝液排水的裝置。 器的u所疋,的裝置,其中來自上述第1冷凝 方六;I供二σ 上述第2冷凝器的冷凝液是以可轉換的 方式=給於上述回收再生裝置及上述排水處理的裝置。 生壯署用:或(15)所記載的裝置,其中在上述回收再 密性發揮裝置。 述排水處理裝置的配管具備水 過上(』7第)m6)任—項所記載的裝置,更包括處理經 過上述第2冷凝裔的廢氣的廢氣處理裝置。 —(18)如(17)所記載的裝置,其中上述回收再生裝 配官具備維持配管内的冷凝狀態的裝置。 ^ (19)如(9)〜(18)任一項所記載的裝置,其中 1冷凝器供給有機廢氣的配管以及/或者是自上第 二排出廢氣的配管’具備霧氣捕捉裝置及/或者是冷ί裝2042-5565-PF (Nl); Ahddub.ptd Page 9 200304850 V. Description of the invention (5) Liquid 0 (22: (9) (13) Any of the devices described in the item, including the recovery of condensate The device and the device for draining the condensate. The device of the device u, which comes from the above-mentioned first condensing party; I for two σ The condensate of the above-mentioned second condenser is convertible = to the above Recovery and regeneration device and the above-mentioned drainage treatment device. For use by the Health and Welfare Department: or the device described in (15), in which the recovery and re-tightness is exerted. The device described in any one of (1) and (2) further includes an exhaust gas treatment device that treats exhaust gas that has passed through the second condensate. -(18) The device according to (17), wherein the recovery and regeneration installation officer is provided with a device for maintaining a condensed state in the piping. ^ (19) The device according to any one of (9) to (18), wherein the 1 pipe for supplying organic exhaust gas from the condenser and / or the pipe for exhausting the second exhaust gas from the upper side is provided with a mist capture device and / or Cold

根據這些方法,相對於有機廢氣,藉由實 f置及第2冷凝裝置,能分離回收 分第:J m污泥處理的各自製程的冷凝液(有=二)再生因利 月匕有效率巧且有效的實現再生利用及廢棄處理。 又,根據這些裝置,相對於有機廢氣,能 :回收程度的冷凝製程。因此,對於回收再1: 處理裝置能各自供給適當的冷凝液。又 收再生裝置及活性污泥處理裝置等的排水處理匕、::According to these methods, it is possible to separate and recover the condensate of each process of the Jm sludge treatment (there is 2) with respect to the organic waste gas by using a real and second condensing device. And effectively realize recycling and disposal. Further, according to these devices, it is possible to perform a condensation process with a degree of recovery with respect to the organic waste gas. Therefore, the recycling apparatus can supply appropriate condensate for each recycling. Drainage treatment daggers for reclamation equipment, activated sludge treatment equipment, etc. ::

2042-5565-PF(Nl);Ahddub.ptd 第10頁 200304850 五、發明說明(6) 易且同時的達成各自的機能 [實施方式] 有關本發明的實施形態,詳細說明如下。 #的發人明的有機廢氣之處理方法包括:冷卻冷凝有機廢 卻冷凝製程;储留在第1冷卻冷凝製程中的冷凝 = : 冷卻冷凝經過此第1冷卻冷凝製程的廢氣的第2 凝製程;以及儲留在第2冷卻冷凝製程中的冷凝液 或者是包括:冷卻冷凝有趟、敗^ ^制如 _ ^ , . ΛΑ ^ , ,機廢虱的製程;將含有高濃 度有機成分的冷凝液再生的再生製程;以及 有機成分的冷凝液經過活性污泥 '又 程。 ^ 1 Θ /尼荨排水處理的廢棄處理製 乙作為實施這些方法的較佳裝置, ^麻ί喊有機廢氣的第1冷凝器;冷凝經過上述第丨冷凝器 則留部;以及健留自第的冷凝液的 儲留部的裝置,特別是包括::戶二的的第2 儲留部;和此第i冷凝液儲留部連二第第1冷凝液 同時一 以實施 隔,^通上述第2冷凝器的第24凝液儲留部方式被£ 冗:本發明的有機廢氣之處理方法說 日有關本發明的裝置’其作為較佳的裝置群 此處理方法中所包含的各製裎。 第1圖係記載本發明的方法或裝置的概略構成2042-5565-PF (Nl); Ahddub.ptd Page 10 200304850 V. Description of the invention (6) Easy and simultaneous realization of each function [Embodiment] The embodiment of the present invention will be described in detail below. # 的 人人 明 organic waste gas treatment method includes: cooling and condensing organic waste and condensing process; condensation stored in the first cooling and condensing process =: cooling and condensing the exhaust gas that has passed through this first cooling and condensing process, and the second condensing process ; And the condensate stored in the second cooling and condensing process may include: cooling and condensing, such as _ ^,. ΛΑ ^,, the process of machine waste lice; condensing containing high concentration of organic components The regeneration process of liquid regeneration; and the condensate of the organic component passes through the activated sludge. ^ 1 Θ / Ninett waste treatment of waste treatment system B as a better device for implementing these methods, ^ Ma ll called the first condenser of organic waste gas; condensate after the above 丨 condenser is left; The device of the condensate storage section includes, in particular: the second storage section of the second household; and the i-th condensate storage section connected to the second first condensate at the same time to implement the isolation, as described above. The 24th condensate storage section method of the second condenser is redundant. The organic waste gas treatment method of the present invention is related to the device of the present invention, and it is a preferred device group. . FIG. 1 shows a schematic configuration of a method or an apparatus of the present invention.

200304850200304850

在第1圖中所表示的處理 冷卻冷凝製程及第2冷卻冷凝 製程的概要。 (有機廢氣) 方法是表示,以為了實施第】 襄私以裝置2作為中心的處理 本發 自半導體 製造製程 施的各種 理,因此 溫度控制 清淨室所 °C左右, 即使 有經過微 所被排出 程的廢氣 氣,因為 入其他的 有機 成分之外 機廢氣是 189 〇C)等 成分。 較佳為適用於, 的電子零件等的 自清淨室内所實 一定的溫度管 明的冷凝製程的 制在25 °C左右的 度是在30 °C〜40 機成分。 是,能適用於含 光阻的剝除製程 。來自此剝除製 為高濃度的廢 方面,比較難混 用。 機溶媒等的溶劑 製程所產生的有 及DMAS0(b·ρ·約 下度)的溶劑 明是’能適用於各種有機廢氣, 元件、液晶顯示器、印刷基板等 所排出的有機廢氣。更佳為,來 製造製程的廢氣。此廢氣是,有 月匕比車父容易的實施用以實施本發 。特別是,能較佳地適用於在控 ^生的廢氣。在此時,廢氣的溫 精由冷卻冷凝能有效率的回收有 是在電子零件製造製程中,特別 影(?11〇1:〇1丨1:11〇忌^01^)製程後的 的剝除液成分的有機廢氣為較佳 是和自清淨室所排出的廢氣相同 會大量產生廢氣。又,在此廢氣 有機成分,因此較方便於再生利 廢氣一般是除了製程中汽化的有 ’含有水蒸氣。經過光阻的剝除 ’例如,含有MEA(b.p·約171。〇 沸點比較高(1 5 〇 °c以上〜2 0 0 °c以 又’有機廢氣是,在剝除製程實施方面,大多以每分The outline of the processing cooling condensation process and the second cooling condensation process shown in the first figure. (Organic waste gas) The method is for the purpose of implementing the first principle. The device 2 is used as the center to deal with the various principles issued by the semiconductor manufacturing process. Therefore, the temperature is controlled in a clean room at around ° C, even if it is discharged through a micro-chamber. Exhaust gas from the process, because other organic components outside the machine exhaust is 189 ° C) and other components. The condensing process at a temperature of about 25 ° C is preferably applied at a temperature of about 30 ° C to 40 machine components in a self-cleaning room suitable for electronic parts such as electronic components. Yes, it can be applied to the stripping process with photoresist. From this aspect, stripping is a high concentration of waste, which is more difficult to mix. Solvents such as organic solvents and solvents produced by DMAS0 (b · ρ · approximately below) are ‘applicable to various organic waste gas, organic waste gas emitted from components, liquid crystal displays, and printed circuit boards. More preferably, the exhaust gas from the manufacturing process is used. This exhaust gas is easier to implement than the driver to implement this hair. In particular, it can be preferably applied to controlled exhaust gas. At this time, the temperature of the exhaust gas can be efficiently recovered by cooling and condensing. In the electronic component manufacturing process, the peeling after the special process (? 1101: 〇1 丨 1: 11〇) The organic off-gas of the deliquoring component is preferably the same as the off-gas discharged from the clean room, and a large amount of off-gas is generated. In addition, because the exhaust gas has organic components, it is more convenient to regenerate the waste gas. Generally, the exhaust gas contains water vapor in addition to those vaporized during the manufacturing process. After photoresist stripping, for example, it contains MEA (bp · approximately 171 °. Boiling point is relatively high (150 ° C or higher to 200 ° C or higher). Organic waste gas is mostly used in the implementation of the stripping process. Per minute

2042-5565-PF(Nl);Ahddub.ptd 第12頁 200304850 五、發明說明(8) 1 5 m3的程度被排出。 (預備的或追加的冷卻冷凝製程) 在實施本發明中的第1冷卻冷凝製程之前,為了有效 率的回收有機廢氣中的有機成分,實施預備的冷卻冷凝製 程為較佳的。藉由實施此冷卻冷凝製程,能積極的回收有 機廢氣在到達本來的冷卻冷凝製程的配管中也許會產生的 冷凝液,在到達冷凝製程之前的階段,能減低有機廢氣中 的冷凝液(霧氣)。而且,此製程亦可稱呼為霧氣捕捉製 程0 又,藉由自配管將藉由實施此製程所捕捉的霧氣及發 _ 生的冷凝液除去’能防止冷凝液或廢氣的逆流至有機廢氣 的發生源的半導體製造裝置,而造成污染。 又,藉由本製程,能達成將製造製程中所排出的各種 濃度或者成分的有機排水調整為一定的組成或濃度的 热。 又 此預備的冷卻冷凝製程是’除了能在自有機廢氣的 生源的半導體製造製程等至冷凝製程為止的 外,冷凝製程後,例如,即使是 Λ ^ ^ ^ ^ ^ ^ 丨使疋以至刷洗态等的廢氣處2042-5565-PF (Nl); Ahddub.ptd Page 12 200304850 V. Description of the invention (8) The degree of 15 m3 is discharged. (Preparative or additional cooling and condensing process) Before implementing the first cooling and condensing process in the present invention, it is preferable to implement a preliminary cooling and condensing process in order to efficiently recover organic components in the organic waste gas. By implementing this cooling and condensing process, it is possible to actively recover the condensate that may be generated in the pipes that reach the original cooling and condensing process. At the stage before the condensing process, the condensate (mist) in the organic waste gas can be reduced. . In addition, this process can also be referred to as the mist capture process. The removal of the mist and condensate generated by the implementation of this process through self-piping can prevent the backflow of condensate or exhaust gas to the occurrence of organic exhaust gas. Source of semiconductor manufacturing equipment and cause pollution. In addition, with this process, it is possible to achieve heat for adjusting the organic drainage of various concentrations or components discharged during the manufacturing process to a certain composition or concentration. In addition, the prepared cooling-condensation process is' in addition to the semiconductor manufacturing process from the source of organic waste gas to the condensation process, after the condensation process, for example, even Λ ^ ^ ^ ^ ^ ^ Waiting place

1紅的配e中也月b Λ施。因此能減輕對廢氣處 擔(在冷凝製程後,能特別白勺稱作追加的冷卻冷凝^程) 〃此預備的e追加的冷凝製程是,也可以使凝哭 成,藉由使用散熱性較好的:的冷卻.裝置的構 使冷凝產生。又,特的冷卻等的自然冷卻 別疋在霧“捕捉方面,能在有機1 red match e in the same month b Λ Shi. Therefore, the burden on the exhaust gas can be reduced (after the condensation process, it can be called an additional cooling condensation process). 追加 This additional e condensation process can also make condensation, by using heat dissipation. OK: Cooling. The structure of the device causes condensation to occur. In addition, natural cooling, such as special cooling

200304850 --------- 五、發明說明(9) —-- 氣的移動方向設置壁障使其衡突。產生的冷凝液是,凝水 (管後自然排出或是藉由幫浦強制棑出等,自適當的配 第1圖所表示的形態中,藉由將自複數的製造裝置4連 續的&或#斷續的被排出的有機廢氣一但使其集合於集合配管 1二二易罢地霄施預備的冷卻冷凝製程。在此形'態中,t 為冷減衣置是,利用在集合配管6内中的有機廢氣的自然 時,集合配管6 *,以散熱性高的不鐘鋼等的金 屬製(較佳為具有耐蝕性)構成為較佳的。 狄根〜據此構成’除了使來自各製造裝置4的有機廢氣配 吕5集a同時能混合各廢氣而均一化,藉由冷卻冷凝共 通的央雜成分而除去。而且,以安定的組成供給廢氣於後 ’又的冷部T凝製程。又,也可以調節廢氣的供給量。 姑」能採用第2圖所表示的構成。,亦即,自製造 ^向i供廢氣配管5的上方設置集管狀的集合配管6, 方^的中':室的有機廢氣的上方’以排出有機廢氣的 於集合配;配成内。在此物,能將對 預期的冷凝液的最高液面位的二 -度位置、。精由此構成,即使臨時 位的方式的既定 止因冷凝液對製造裝置2的污染。χ,相令凝液時,能防 的5機廢氣,因為集合配管6的内壁變成2於自側方供給 的霧氣捕捉裝此;!内壁可說是有作為;;有機 <罝的機能),除了使霧氣(為衝揸構件200304850 --------- V. Description of the invention (9) --- A barrier is set in the moving direction of the air to balance it. The generated condensate is condensed water (naturally discharged from the tube or forced out by a pump, etc.). From the configuration shown in FIG. 1, the self-plurality of manufacturing equipment 4 is continuously & Or # Intermittently discharged organic waste gas once it is collected in the collection piping, and the cooling and condensing process is prepared. In this form, t is a cold sublimation device and is used in the collection. When the organic waste gas in the piping 6 is natural, the piping 6 * is preferably made of a metal (such as stainless steel, preferably with corrosion resistance), which has high heat dissipation properties. The organic waste gas from the manufacturing apparatuses 4 can be uniformly mixed with each other at the same time, and can be homogenized, and removed by cooling and condensing the common central impurity components. In addition, the waste gas is supplied to the cooling section in a stable composition. T condensation process. Also, the amount of exhaust gas supply can be adjusted. The structure shown in Fig. 2 can be adopted. That is, a self-manufactured ^ is provided to the exhaust gas supply pipe 5 above the collecting pipe 6 ^ In the ': above the organic waste gas in the chamber' to discharge organic waste gas In this case, the composition can be adjusted. In this object, the two-degree position of the highest liquid level of the expected condensate can be adjusted. The fine structure is thus formed, even if the temporary position of the condensate is produced by the condensate. Pollution of device 2. χ, when the condensate is condensed, the exhaust gas of 5 units can be prevented, because the inner wall of the collection pipe 6 becomes 2 to capture the mist from the side supply;! The inner wall can be said to be useful; organic < The function of 罝), in addition to making the mist

2042-5565-PF(Nl);Ahddub.ptd _ 滴)附著於内 200304850 五、發明說明(10) 壁車乂合易捕捉之外’同時藉由接觸於散熱性較好的配管 的壁部,變的較容易被冷凝。 又’圖中是將有機廢氣的配管5連結於集合配管6的側 部作為例子表示,然而若在集合配管6的上方側時,可以 防止冷凝液逆流至製造裴置4側。 又,也可採用第3圖中表示的構成。此構成中,定向 f供給自了方的有機廢氣的上方,具備排出有機廢氣的配 二的^ ^室形成於集合配管6内。而且’將有機廢氣的供 、,,口配官5的開口在此中空室内的既定高度位置的方式,將 此供給配管5以突出狀設置於中空室β,相對於此開口, 依既定間隔將有機廢氣的衝撞構件6a作為霧氣捕捉裝置, 對;^置。藉由採用此構成,特別是,容易捕捉有機廢 ,中所含的冷凝成分(霧氣)於此集合配管6。此一結果, 月t*供給減低霧氣的有機廢氣於冷卻冷凝裝置。 士 ’ &採用各種作為此種霧氣捕捉裝置的㈣構件6 a 的形悲和設置樣態。在有機廢氣的供給部位以對向狀設 衝突構件。在有機廢氣的供給部位及排出部位 凝液的範圍内,能採用各種的樣態。 此 7 如此新捕主捉的霧氣及產生的冷凝液是,以再生利用為 目的’ u暫時儲留於回收廢液槽8内的方式為較佳。 又,作為霧氣捕捉或冷凝裝置的第2圖及^3圖°中 不的構成,不管哪一種,都是有關自製造裝置2供仏 廢氣至集合配管6的樣態,然而並不限於此,也^ ^ 用於至冷卻冷凝製程為止的配管途中。亦即,不Sb是採用 1一將2042-5565-PF (Nl); Ahddub.ptd _ drops) attached to the inside 200304850 V. Description of the invention (10) The wall car is easy to catch outside of it, and at the same time by contacting the wall of the pipe with better heat dissipation, Becomes easier to condense. In the figure, the side of the organic waste gas pipe 5 is connected to the collection pipe 6 as an example. However, when the upper side of the collection pipe 6 is connected, the condensate can be prevented from flowing back to the side of the production pipe 4. The configuration shown in FIG. 3 may be adopted. In this configuration, the directional f is supplied above the organic waste gas from the side, and a ^^ chamber provided with a discharge chamber for discharging the organic waste gas is formed in the collecting pipe 6. In addition, the opening of the organic waste gas supply port 5 is positioned at a predetermined height position in the hollow chamber, and the supply pipe 5 is provided in the hollow chamber β in a protruding shape. The opening is set at a predetermined interval with respect to the opening. The collision member 6a of the organic exhaust gas serves as a mist capturing device, and is set. By adopting this structure, in particular, it is easy to capture the organic waste, and the condensed components (mist gas) contained in the organic waste are collected in the collecting pipe 6. As a result, the organic waste gas with reduced mist is supplied to the cooling and condensing device at month t *. The taxi '& adopts various shapes and settings of the cymbal member 6 a as such a mist capturing device. A conflicting member is provided at the supply position of the organic waste gas in an opposed manner. Various forms can be adopted within the range of the condensate at the supply and discharge locations of the organic waste gas. The mist and the condensate generated by the new catcher in this way are preferably stored temporarily in the recovery waste liquid tank 8 for the purpose of recycling. In addition, the structures not shown in Figs. 2 and 3 of the mist trapping or condensing device are both related to the state in which the exhaust gas is supplied from the manufacturing device 2 to the collecting pipe 6, but it is not limited to this. ^ ^ It is also used for piping to the cooling and condensing process. That is, not Sb is adopted

2042-5565-PF(Nl);Ahddub.ptd 200304850 五、發明說明(11) 自製造裝置的有機廢氣配管5集合的集合配管6的形態,若 採用具備架在配管的一部的中空室構造的構成,也能適用 在配管途中的霧氣捕捉或是冷凝的構成。 又’第2圖及弟3圖所表示的構成,都是預備的冷卻冷 凝製程中的實施樣態,在廢氣處理製程的前段實施追加的 冷卻冷凝製程的場合中,也能適用作為追加的冷卻冷凝製 程的實施樣態。亦即,因為可將自製造裝置2的有機廢氣 配管5置換為自後述的第2冷卻冷凝製程的1或2以上的廢氣 的供給用配管’所以也能適用追加的冷卻冷凝製程。 (第1的冷卻冷凝製程) < 藉由將有機廢氣導入第1冷凝器1 〇,實施第1冷卻冷凝 2程。先將第1冷凝器1 〇作為後述的第2冷凝器4〇是,不限 定於習知的各種冷凝器而能使用,在冷凝器丨〇、4〇中,能 使用各種冷卻廢氣的裝置,可採用多管式、線圈(c〇ii) 式、螺旋UpriaU式等各種,較佳為採用板 … f 1 η )型的冷卻裝置。 ρ 因此在凝製程中’大量的導入高濃度的廢氣。 定較佳的溫度及=本點上來看’希望能設 收冷、S α 特別疋在第1冷卻冷凝製程中,回 條件為較佳。#給再利用的製程,卻設定有效的溫度 分冷:i較Γ則:Γΐ”組成,有效率地只使有機成 水蒸氣到飽和I胃:疋在廢氣中被含有及被預測的 “堡的程度的溫度條件。在此溫度條件 2〇42-5565.PF(Nl);Ahddub.ptd 第16頁2042-5565-PF (Nl); Ahddub.ptd 200304850 V. Description of the invention (11) The form of the collective piping 6 assembled by the organic waste gas piping 5 of the self-manufacturing device, if a hollow chamber structure with a portion of the piping is used The structure can also be applied to a structure for capturing or condensing mist in the middle of piping. The structures shown in FIG. 2 and FIG. 3 are implementation examples in the preliminary cooling and condensing process. When an additional cooling and condensing process is performed in the first stage of the exhaust gas treatment process, it can also be applied as additional cooling. Implementation of the condensation process. In other words, since the organic exhaust gas pipe 5 from the manufacturing apparatus 2 can be replaced with one or more exhaust gas supply pipes from the second cooling and condensing process described later, an additional cooling and condensing process can also be applied. (First cooling and condensing process) < The first cooling and condensing process is performed by introducing organic waste gas into the first condenser 10. The first condenser 10 is used as the second condenser 40 described later. The condenser is not limited to a variety of conventional condensers, and various condensers for cooling exhaust gas can be used in the condensers. Various types of cooling devices, such as a multi-tube type, a coil (coi) type, and a spiral UpriaU type, may be used, and a plate ... f 1 η) type cooling device is preferably used. ρ Therefore, a large amount of high-concentration exhaust gas is introduced in the condensation process. Set a better temperature and = From this point of view, I hope to set the cooling, S α, especially in the first cooling condensation process, the return conditions are better. # Gives the recycling process, but sets an effective temperature to separate the cold: i is more than Γ: Γΐ ", which effectively only makes the organic water vapor to saturation. I stomach: 疋 is contained in the exhaust gas and predicted" Fort The degree of temperature conditions. At this temperature condition 2042-5565.PF (Nl); Ahddub.ptd page 16

200304850 五、發明說明(12) 下,能以最大限度防止水的冷凝的狀態下,使有機成分冷 凝。 例如,來自光阻的剝除製程的廢氣是,以大約35〜4〇 。(:的溫度被供給於第1冷卻冷凝製程。此時,也藉由廢氣 的組成,例如,供給約7 °c〜1 0 °c的冷水,基於上述所X厂、 最適當的溫度條件’設定冷凝器内的溫度為較佳。特Z, 此溫度條件被控制在25 °C、60%RH且自清淨室被排出,並& 在含有DMS0及MEA的廢氣中是為較佳的條件。 " 為了實現在冷凝器10、40中的有效且有效率的冷 凝製程,各自的冷凝器1 〇、40内具備溫度檢測裝置丨2、^ 為較佳。在監測被供給的有機廢氣溫度下,藉由調整冷 水的供給量等,能賦予一定或適切的溫度條件 :, 在第i冷卻冷凝器10中,由於被供給的廢氣的濃度很高 者有變動幅度’藉“置溫度檢縣置i 2,能實施有效 的冷卻冷凝製程。X ’具備檢測被供給 置於冷凝器10、40為較佳。 凰度的凌 又,基於藉由溫度檢測裝置i 2、42被檢測的溫度,者 施冷卻水的供給量控制時,具備 = 各自的冷凝器1。、4。為較佳。也能檢、二:”衣置在 -冷卻水流量的比例栌制H ^檢測冷郃水机® ’溫度 在第1 Α说、人 制軚佳為作為PID控制是有效的。 令令凝製程所產生的冷凝液是,儲留i;/v、钱 器10連通的第1冷凝液儲留邻Μ 狹农疋與冷凝 # ,1 ^ ^ a r, ^ Λ Λ * V ^1 ^ f ^ 所以較後段的第2冷卻冷凝樂;"濃度的廢氣而被得到’ |々規表私所產生的冷凝液為高濃度200304850 V. Description of the invention (12) The organic components can be condensed in a state where water condensation is prevented to the greatest extent. For example, the exhaust gas from the stripping process of photoresist is about 35 ~ 40. (: The temperature is supplied to the first cooling and condensing process. At this time, also based on the composition of the exhaust gas, for example, cold water of about 7 ° c to 10 ° c is supplied, based on the above-mentioned plant X, the most appropriate temperature conditions. It is better to set the temperature in the condenser. Special Z, this temperature condition is controlled at 25 ° C, 60% RH and discharged from the clean room, and it is a better condition in the exhaust gas containing DMS0 and MEA. &Quot; In order to achieve an effective and efficient condensing process in the condensers 10 and 40, it is preferable that each of the condensers 10 and 40 is provided with a temperature detection device 2 and ^. The temperature of the supplied organic exhaust gas is monitored. Next, by adjusting the supply of cold water, etc., a certain or appropriate temperature condition can be provided: In the i-th cooling condenser 10, the concentration of the supplied exhaust gas has a high fluctuation range, and the borrowing temperature can be adjusted If i 2 is set, an effective cooling and condensing process can be implemented. It is better to have X 'to detect and supply it to the condensers 10 and 40. Lingdu Ling is based on the temperature detected by the temperature detection devices i 2, 42. When applying cooling water supply control, have = Self-condensers 1., 4. are better. Can also detect, two: "Clothing-Cooling water flow ratio (H) ^ Detection of cold water chiller ® 'Temperature at 1 Α, man-made 軚Jiawei is effective as a PID control. Let the condensate produced by the condensation process be stored in the first condensate that is connected to the coin holder 10 and adjacent to the small farm and condensate #, 1 ^ ^ ar, ^ Λ Λ * V ^ 1 ^ f ^ So the 2nd cooling condensate in the later stage is obtained with the concentration of the exhaust gas.

2042-5565-PF(Nl);Ahddub.ptd $ 17頁 200304850 五、發明說明(13) ----- 的有機成分。 在第1冷卻冷凝製程產生的冷凝液是,儲留於第丨儲留 部16,其後,透過配管18能供給至回收廢液槽8。其後, 能供給至具備未圖示的再生裝置的再生製寿呈。根據第i冷 部冷凝製矛呈’在有效率的範圍内,為了能得到含有高濃度 的有機成分的冷凝液,藉由再生此冷凝液,能夠實現有效 的再利用。 又’雖然未圖示’然而配管丨8是,必須對應來自第1 儲留部1 6的冷凝液,而構成以可切換方式供給至作為排水 處理裝置的活性污泥處理設備5 8。 在此裝置2的末端,設置用以將大量廢氣排出至大氣 的送風機(blower)。因此,儲留部16、46的内部有負壓的 傾向。此時’為了控制藉由自回收廢液槽8及處理裝置5 8 側注入環境至上述儲留部1 6、4 6的溫度條件等的變動,使 其具備水密機能發揮裝置19、49,在儲留部16、46及回收 廢液槽8、及活性污泥處理設備58之間,使其發揮氣體的 遮斷作用為較佳。在第1圖所示的水密發揮裝置丨9、4 9, 藉由將配管1 8、48設計成以可儲留冷凝液的u字狀的部 分,使其發生水密機能。又,根據此配管構造,也能有效 果地防止由回收廢液槽8及來自活性污泥處理設備58的液 體逆流至負壓的儲留部16、46。 又,儲留部1 6、46成為負壓時,由來自儲留部1 6、46 至回收廢液槽8及活性污泥處理設備58的路徑,藉由自然 落下的方式排出廢液也很有可能變困難。為了廢液的自然2042-5565-PF (Nl); Ahddub.ptd $ 17 200304850 V. Description of the invention (13) ----- Organic ingredients. The condensate generated in the first cooling and condensing process is stored in the first storage section 16 and can be supplied to the recovery waste liquid tank 8 through the pipe 18 thereafter. After that, it can be supplied to a regenerative life system including a regenerative device (not shown). According to the i-th cold section condensation method, in order to obtain a condensate containing a high concentration of organic components within the effective range, by regenerating the condensate, effective reuse can be achieved. "Although not shown", the piping 8 needs to correspond to the condensate from the first storage unit 16 and be configured to be switchably supplied to the activated sludge treatment equipment 58 as a drainage treatment device. A blower is provided at the end of the device 2 to discharge a large amount of exhaust gas to the atmosphere. Therefore, there is a tendency that the inside of the storage portions 16, 46 is under a negative pressure. At this time, in order to control changes in temperature conditions such as the temperature of the environment from the recovery waste liquid tank 8 and the processing device 5 8 side to the above-mentioned storage sections 16 and 46, water-tightness function display devices 19 and 49 are provided. It is preferable that the storage portions 16, 46, the recovered waste liquid tank 8, and the activated sludge treatment equipment 58 play a gas blocking function. In the watertight display devices 9 and 4 9 shown in Fig. 1, the pipes 18 and 48 are designed to have a U-shaped portion capable of storing condensate, so that the watertight function is generated. In addition, according to this piping structure, it is possible to effectively prevent the liquid from the recovered waste liquid tank 8 and the activated sludge treatment equipment 58 from flowing backward to the negative-pressure storage portions 16, 46. In addition, when the storage portions 16 and 46 become negative pressure, the path from the storage portions 16 and 46 to the recovered waste liquid tank 8 and the activated sludge treatment equipment 58 is also discharged by naturally falling down. It may become difficult. For the nature of waste liquid

2042-5565-PF(Nl);Ahddub.ptd 第18頁 200304850 五、發明說明(14) 落下’未能採用必要的斜率時 的齒輪傳動㈣是有效的Η ^具備上述的遮斷作用 又’在配管18中,且供 檢測裝m =機用曲以檢測第1冷凝液的組成的 佳。根據具備此檢測裝置, .刀檢測咸置為較 給以將冷凝液再生利用作為機成分及水分濃度’供 能判斷是否供給至用於廢氣二=廢液槽8, ’或者, 裝置是,能自i锸羽a x礼處理的活性污泥設備58。檢測 月匕自各種I知的檢測裝置適 較佳為使用導電率滚度測定裝置P “擇而使用’然而 第1冷卻冷凝製程是, 匕 機成分的7〇wt%以上9〇wt%以的方二回收有機廢氣的有 圍内’以作為再生用等回收的方:式二,。在此回收率範 凝液的有機成分濃度:凝製程所產生的冷 中的污泥的負;理= 為約8 0 %。 V死的女疋處理。較佳 (第2冷卻冷凝製程) 經過第1冷卻冷凝掣鞋而 的廢氣是,被供⑼W 破部分除去的有機成分 扪&轧疋被供給於第2冷卻冷凝製程。 第2冷卻冷凝製程是,由 所以被供給含有相對的低:農产、的^ 了第1冷卻冷凝製程, 度或組成的廢氣。而:低:J 成分,且是安定的濃 凝製程產生的冷凝液含有低濃度的;較第1冷卻冷 在第2冷卻冷凝製程所產生的冷有疑機液成/,主要以供給2042-5565-PF (Nl); Ahddub.ptd Page 18 200304850 V. Description of the invention (14) Drop 'Gear transmission when the necessary slope is not adopted is effective. ^ With the above-mentioned blocking function, it is In the piping 18, it is preferable that the detection device is set to be used for detecting the composition of the first condensate. According to the detection device, the knife detection device is more suitable for regenerating the condensate as an organic component and the moisture concentration. 'Energy supply is used to determine whether it is supplied to the waste gas tank 2 = waste liquid tank 8,' or the device is, can Activated sludge equipment 58 from i 锸 羽 ax ceremony. The detection device for detecting the moon dagger is suitable to use the conductivity roll measurement device P "select and use '. However, the first cooling and condensation process is 70% to 90% by weight of the dagger component. The second method is to recover the organic waste gas within the bounds, which is used as a recycling method: Formula II. The recovery rate in this range is the organic component concentration of the condensate: the negative of the sludge produced in the condensation process; reason = It is about 80%. V dead son-in-law treatment. Better (second cooling and condensing process) The exhaust gas that passes through the first cooling and condensing switch is the organic component that is removed by the broken part and is supplied. The second cooling and condensing process. The second cooling and condensing process is because it is supplied with exhaust gas that contains relatively low: agricultural products, the first cooling and condensing process, degree or composition. And: low: J component, and is The condensate produced by the stable thickening process contains a low concentration; compared with the first cooling and cooling, the cold produced in the second cooling and condensing process is suspected to be liquid / mainly supplied.

2042-5565-PF(Nl);Ahddub.ptd 第19頁 200304850 五、發明說明(15) 於活性污泥處理箄的窳 凝液是低濃度及安定=處=程的方式為較佳。此冷 擔,或是能較為能減輕對於活性污泥的負 第2冷卻冷凝、w 設計為較佳。例如皿自度^是,自此觀點作為條件 成,例如,設^冷凝冷卻冷凝製程的廢氣組 是~内的溫度在約7〜10 t為較佳。 、LI 冷凝製程的廢氣在到達第2冷凝哭40 除霧器等的霧氣分離裝置24為較:。夢 ㈣©於二部、凝製程所產生的冷凝液(第2冷凝液)是, ”4°的下部且與冷凝器4◦連通的第2冷,疑 2、六。、在第2冷卻冷凝製程中所得到的冷凝液是, ,在令繁1二凝製程產生的冷凝液為低濃度的有機成分。 在第2冷部冷凝製程產生的冷凝液是,儲留於第2冷凝 部46後’透過配管48能供給於活性污泥處理設備 58。在活性巧泥處理設備58中,藉由活性污泥的作用,分 解有機Π ’能將排水清淨化。根據本處理法,由於對於 >可泥的負擔被減輕,或者是被調節,所以能圓滑地施行活 陡f /尼,里、又,其規模也能小型(c 0 m P a c t)化。另外, 配笞4 8疋為因應需要而將冷凝液能供給於廢槽液8的方 式’被形成為可切換供給源頭。 、上在配=48設置用以檢測第2冷凝液的組成的檢測裝置 為杈,。藉,檢測有關第2冷凝液的有機成分及/或水分濃 度,能判斷是供給於用以再生利用第2冷凝液的廢液槽8或2042-5565-PF (Nl); Ahddub.ptd page 19 200304850 V. Description of the invention (15) The condensate of the plutonium treated with activated sludge is low in concentration and stable = process = process is preferred. This cooling load, or the second cooling condensation and w which can reduce the burden on the activated sludge, is better designed. For example, it is preferable to set the temperature from this point of view. For example, it is better to set the temperature of the exhaust gas group in the condensation cooling condensation process to about 7 to 10 t. When the exhaust gas from the LI condensation process reaches the second condensing cry 40, the mist separation device 24 such as a mist eliminator is more suitable. Nightmare © Yu Erbu, the condensate (second condensate) produced during the condensation process is the second colder, which is the lower part of 4 ° and communicates with the condenser 4, and the second cooler is condensed in the second cooler. The condensate obtained in the production process is such that the condensate produced in the second and second condensation processes is a low-concentration organic component. The condensate produced in the second cold section condensation process is stored in the second condensation section 46 'It can be supplied to the activated sludge treatment equipment 58 through the piping 48. In the activated sludge treatment equipment 58, the organic sludge is decomposed by the action of activated sludge', and the wastewater can be purified. According to this treatment method, since > However, the burden of mud can be reduced or adjusted, so it can smoothly perform live steep f / ni, and the scale can also be reduced in size (c 0 m P act). In addition, 笞 4 8 疋 is a response The method of supplying the condensate to the waste tank liquid 8 as needed is formed as a switchable supply source. The detection device for detecting the composition of the second condensate is set to 48. By the way, the detection is related The organic component and / or water concentration of the second condensate can be determined as being supplied to In the second recycling tank 8 the waste liquid condensate or

200304850200304850

是供給以廢氣處理為目的的活性污泥裝置5 8。特別是,關 於第2冷凝液,可作此判斷,所以能對有機成分有效利 用〇 當連續實施第1冷卻冷凝製程及第2冷卻冷凝製程時, 並沒有特別限定其裝置構成,例如,可採用第丨圖所表示 的裝置構成。 ’、It is an activated sludge device 5 8 for the purpose of exhaust gas treatment. In particular, the second condensate can be judged so that it can effectively use organic components. When the first cooling and condensing process and the second cooling and condensing process are continuously performed, the device configuration is not particularly limited. For example, it is possible to use The structure of the device shown in FIG. ’,

在第1圖所表示的裝置2中,第1冷凝儲留部丨6和第2冷 凝液儲留部46是,藉由區隔裝置2〇遮斷各冷凝液的接觸: 又,第1冷凝儲留部1 6和第2冷凝液儲留部4 6是,被一體化 形成一個儲留槽狀。且,以連通於各儲留部16、46的方 式,裝備冷凝器10、40在各自的儲留部16、46的上方。 另一方面,經過第1冷卻冷凝製程的廢氣是能通過自 冷凝儲留部16至第2冷凝液儲留部46而可通氣。特別 是,在第1圖所表示的構成中,此通氣的部分是藉由霧氣 分離裝置24而構成’經過以冷卻冷凝製程的廢氣是,能 伴隨著移動至第2冷凝器40側通過霧氣分離裝置24。又, 作為霧氣分離裝置24是,能使用過濾器(futer)、篩網 (mesh)、多孔質體等的各種多孔狀體。 (廢氣處理製程)In the device 2 shown in FIG. 1, the first condensate storage section 6 and the second condensate storage section 46 block the contact of each condensate by the partitioning device 20, and the first condensation The storage portion 16 and the second condensate storage portion 46 are integrated into a single storage tank shape. The condensers 10 and 40 are provided above the respective storage portions 16 and 46 so as to communicate with the respective storage portions 16 and 46. On the other hand, the exhaust gas that has passed through the first cooling-condensation process can be ventilated through the condensate storage section 16 to the second condensate storage section 46. In particular, in the configuration shown in FIG. 1, the vented portion is configured by the mist separation device 24. The exhaust gas that has passed through the cooling and condensing process can be separated by the mist as it moves to the second condenser 40 side.装置 24。 Device 24. In addition, as the mist separation device 24, various porous bodies such as a filter, a mesh, and a porous body can be used. (Exhaust gas treatment process)

經,第2冷卻冷凝製程的廢氣是,被減低更多的有相 ^刀。較佳為將此廢氣供給於廢氣處理製程。在廢氣處 — 々矹的各種淨化裝置。例·如,在廢 中添加中和樂液,以水洗潘,佶路 \ ^ ,^ , w 无淨使殘存的有機成分溶解於As a result, the exhaust gas in the second cooling and condensing process is reduced even more. This exhaust gas is preferably supplied to an exhaust gas treatment process. At the exhaust — various purifiers. For example, if you add a neutralizing solution to the waste, wash the pan with water, Kushiro \ ^, ^, w without dissolving the remaining organic ingredients in

水,能有效果的減低或险丰皇、齑 ^ L -乂除去昊孔。較佳為實施藉由刷洗Water can effectively reduce or remove Hao Kong from Fengfeng Huang and 齑 ^ L-乂. Preferably by brushing

200304850 五、發明說明(17) 的廢氣處理製程。 藉由經過本發明的冷卻冷凝製, 有機成分,所以能在之後心氣處:自廢 良好的除去,所以即使放出是有機成分被 低,又,當然臭氣也被減低。%i 兄及生態的影響被減 =第2冷卻冷凝製程的廢氣是 通 離裝置60後,供給於廢氣處理製程 ^通過務氧分 除液的有機溶劑-冷凝時,由於黏性車=° 2是構成制 能除去在廢氣處理製程的黏質製程。又, 當實施自第2冷卻冷凝製程曼麻女的/粒子。 並未特別限定其裝置的形離' ' 处理製程為止時, 的形態。 〜、彳如’能採用第1圖所表示 在第1圖所表示的裝置2中, # 。 裝置60在第2冷凝器4〇的上而、示務器等的霧氣分離 等的廢氣處理褒置70。經氣’其』=具備刷洗器 放出在大氣中。又,麻 孚虱處理裝置7〇的廢軋是,被 液)是被形成可供給於活性Τ裝置70的廢氣處理液(洗淨 達成藉由有機成分的活性污了 /備58。藉由此,可 =的有機成分的供給是性 般,=!;=1=巧7〇的配管62中’如上述 汊疋冷凝裝置,能實施追加的冷卻 第22頁 2042.5565-PF(Nl);Ahddub.ptd 200304850200304850 V. Exhaust gas treatment process of invention description (17). By cooling and condensing the organic components of the present invention, the organic components can be removed afterwards: self-waste is well removed, so even if the organic components are released, the odor is of course reduced. % I Brother and ecological impacts are reduced = The exhaust gas from the second cooling and condensation process is passed through the device 60 and then supplied to the exhaust gas treatment process. It is a viscous process that can remove the waste gas treatment process. In addition, when the second cooling and condensing process is carried out, the particles are used. There is no particular limitation on the shape of the device at the time of the processing process. ~, 彳 如 ’can be shown in FIG. 1 In the device 2 shown in FIG. 1, #. The device 60 is installed on the second condenser 40, and an exhaust gas treatment unit 70 such as mist separation of a display unit or the like. Jingqi’its ”= has a scrubber and releases it to the atmosphere. In addition, the waste liquid of the mosquito lice treatment device 70 is a coating liquid) which is formed into an exhaust gas treatment liquid (cleaned to achieve an active soiling / preparation with an organic component 58) that can be supplied to the active T device 70. With this, The supply of organic components that can be = is natural, =!; = 1 = Qiao 7〇 in the pipe 62 'as in the above-mentioned condensing device, additional cooling can be implemented. Page 22 2042.5565-PF (Nl); Ahddub. ptd 200304850

冷凝製耘。藉此能減輕至廢氣處理裝置的負擔。 經過冷凝器40的廢氣也有變成 1〇、; 二夂溫二Γ冷凝程度的方式為較佳^ 度期間專下降過度時,管内的水分會更 杈2佳,又,在夏天期間,在管外側會產生結露 題存在的緣故。作為此冷凝狀態維持裝置64是!例 裝著於西己管的们盖(㉟熱)裝置,或者是溫度 的空調裝置等。 吕衣戈兄 ^,當供給冷卻水於第丨冷卻冷凝製程及第2冷卻冷 製程時,首先’供給冷卻水於第2冷卻冷凝製程,使其經 過,其次藉由供給冷卻水於第丨冷卻冷凝製程,能有效 地回=有機成分,且使冷卻水有效率的使用水量的運轉變 在上述形態中,已例示 置的活性污泥的處理製程或 能採用將其他的化學的微生 性污泥的處理製程或是裝置 有關以作為排水處理製程或裝 疋裝置’然而目的不限於此, 物的製程或是裝置替換藉由活 又’有關再生製程或是再生裝置並未特別詳述, 能適用習知的技術。 根據本發明,除了能達成自有機廢氣的有機成分的再 利用和廢棄處理以外,同時減輕對於這些的必要設備,能 小型化。又,根據具備廢棄處理製程或是廢氣處理裝置= 本處理技術,能有效果的減低廢氣處理製程後的廢氣中的 有機成分。因此,可減低還原於大氣的氣體對於環境及生Condensation. This can reduce the burden on the exhaust gas treatment device. The exhaust gas that has passed through the condenser 40 also becomes 10 °; the temperature of the two degrees of condensation is better. When the temperature drops excessively, the moisture in the tube will be better. Also, during the summer, outside the tube, Will cause the existence of condensation problems. As this condensation state maintaining device 64 is! For example, a lid (heating) device mounted on a west tube or a temperature-controlled air conditioner. Brother Lu Yige ^ When supplying cooling water to the second cooling condensation process and the second cooling and cooling process, first supply cooling water to the second cooling and condensation process and let it pass, and then supply cooling water to the first cooling The condensing process can effectively return organic components, and make the operation of the cooling water efficiently use the amount of water. In the above-mentioned form, the activated sludge treatment process that has been exemplified may use other chemical microbiological sludge. The treatment process or device is related to the drainage treatment process or the decoration device. However, the purpose is not limited to this. The process or device replacement of the material is not specifically described in detail, and can be applied. Known technology. According to the present invention, in addition to the reuse and disposal of organic components from organic waste gas, necessary equipment for these can be reduced, and the size can be reduced. In addition, if the waste treatment process or the exhaust gas treatment device is provided, this treatment technology can effectively reduce the organic components in the exhaust gas after the exhaust gas treatment process. Therefore, it can reduce the environmental and

200304850 五、發明說明(19) 態的不好影響(臭氣)。而且,根據此技術,加上有機成分 的再利用及廢棄處理,也能同時且容易的實現廢氣的淨 化。 (發明的效果) 根據本發明,提供一種處理技術,其能達成自有機廢 氣的有機成分的再利用和廢棄處理。200304850 V. Description of invention (19) Bad influence of state (odor). In addition, according to this technology, together with the reuse and disposal of organic components, the purification of exhaust gas can be achieved simultaneously and easily. (Effects of the Invention) According to the present invention, there is provided a processing technology capable of achieving reuse and disposal of organic components from organic waste gas.

2042-5565-PF(N1);Ahddub.ptd 第24頁 200304850 圖式簡單說明 第1圖係表示有關本發明的處理技術的製程及裝置的 概略圖。 第2圖(a)至第2圖(b)係表示霧氣捕捉裝置或是冷凝裝 置的一形態圖。 第3圖係表不霧氣捕捉裝置或是冷凝裝置的另一形態 圖0 符號說明: 4〜半導體製造裝置, 6〜集合配管, 8〜回收廢液槽, 1 2、42〜溫度檢測裝置 18、48、62、72〜配管 20〜區隔裝置, 5 8〜活性污泥處理裝置 6 4〜冷凝狀態維持裝置2042-5565-PF (N1); Ahddub.ptd Page 24 200304850 Brief Description of Drawings Figure 1 is a schematic diagram showing a process and an apparatus related to the processing technology of the present invention. Figures 2 (a) to 2 (b) are diagrams showing one form of a mist capture device or a condensation device. Fig. 3 shows another form of the mist capture device or the condensing device. 0 Symbol description: 4 ~ semiconductor manufacturing device, 6 ~ collection piping, 8 ~ recovered waste liquid tank, 1 ~ 42 ~ temperature detection device 18, 48, 62, 72 ~ Piping 20 ~ Separation device, 5 8 ~ Activated sludge treatment device 6 4 ~ Condensation state maintenance device

2〜廢氣處理裝置’ 5〜有機廢氣配管, 7〜有機廢氣配管, 1 0、4 0〜冷凝器’ 16、46〜冷凝液儲留部, 1 9、4 9〜水密性發揮裝置 24〜霧氣分離裝置, 6 0〜霧氣分離裝置, 70〜廢氣處理裝置。2 ~ Exhaust gas treatment device '5 ~ Organic waste gas piping, 7 ~ Organic waste gas piping, 1 0, 4 0 ~ Condenser' 16, 46 ~ Condensate reservoir, 19, 4 9 ~ Water tightness display device 24 ~ Mist Separation device, 60 to mist separation device, 70 to exhaust gas treatment device.

Claims (1)

200304850200304850 ΐ· 一種有機廢氣之處理方法,包括· 冷卻冷凝有機廢氣的第1冷卻冷凝製程; 儲留在該第1冷卻冷凝製程中的冷=的製程; 冷卻冷凝在該第1冷卻冷凝製较卢_ Μ Α ^ Μ & 〇人 冷凝製程;以及 喊衣私處理的廢氣的弟2冷卻 儲留在該第2冷卻冷凝製程中的冷凝液的製程。 2. 如申請專利範圍第1項所述的方法,立中更包括 氣分離製m以分離在上述^冷卻冷凝製程被處理 的廢軋的霧氣,此霧氣分離製程是在上 程之前被實施。 Aΐ · A method for treating organic waste gas, comprising: · a first cooling and condensation process for cooling and condensing organic waste gas; a process of cold = stored in the first cooling and condensation process; cooling and condensation in the first cooling and condensation process Μ Α ^ Μ & 0 people condensation process; and the process of cooling the condensate stored in the second cooling and condensing process. 2. According to the method described in item 1 of the scope of patent application, Lizhong further includes a gas separation system m to separate the waste rolled mist processed in the above-mentioned cooling and condensation process. This mist separation process is implemented before the previous process. A 3. 如申請專利範圍第i項或第2項所述的方法,其中在 上述第1冷卻冷凝製程中,冑±述有機廢氣所含有的水基 氣的蒸氣壓和飽和?泰氣壓《乎一致的溫度的附近為止,'冷 4·如中請專利範圍第i或2項所述的方法’其中在上述 第1冷卻冷凝製程中’將上述有機廢氣所含有的有機成分 的70wt%以上90wt%以下回收,在上述第2冷卻冷凝製程 中’將上述有機廢氣所含有的有機成分的1〇wt%以上2〇wt% 以下回收。 5 ·如申請專利範圍第1或2項所述的方法,其中更包 _ 括: 將上述第1冷卻冷凝製程的冷凝液回收,且將被回收 的冷凝液再生的製程;以及 回收上述第2冷卻冷凝製程的冷凝液,將被回收的冷3. The method according to item i or item 2 of the scope of patent application, wherein in the first cooling and condensation process, the vapor pressure and saturation of the water-based gas contained in the organic waste gas are almost equal Up to the vicinity of the temperature, 'Cold 4 · The method described in item i or 2 of the patent scope' in which the first cooling and condensing process described above is performed in which the organic waste gas contained in the organic waste gas is 70% by weight or more and 90% by weight or less. In the second cooling and condensing process described below, 10% by weight or more and 20% by weight or less of the organic components contained in the organic waste gas are recovered. 5 · The method according to item 1 or 2 of the scope of patent application, further comprising: a process of recovering the condensate from the first cooling and condensation process and regenerating the recovered condensate; and recovering the second Cooling the condensate of the condensing process, the cold 200304850 六 申請專利範圍 凝液排水的製程。 6 ·如申請專利範圍第1或2項所述的方法,其中更包括 處理在上述第2冷卻冷凝製程處理的廢氣的製程。 7 · —種有機廢氣之處理方法,包括: 冷卻冷凝有機廢氣的製程; 將含有高濃度有機成分的冷凝液再生的製程;以及 將s有低濃度有機成分的冷凝液排水的製私。 8 ·如申請專利範圍第7項所述的方法,其中具備處理 在上述冷凝製程中未能冷凝剩下的廢氣的製程。 9· 一種有機廢氣之處理裝置,包括: 第2冷凝器 第1儲留部 第1冷凝器,冷凝有機廢氣; 冷凝在上述第1冷凝器處理的廢氣; 及 儲存自該第1冷凝器所產生的冷凝液;以 真:1 ΐ自該第2冷凝器所產生的冷凝液。 及第2儲留部了互;/ t圍第9項所述的裝置,其中上述第1 及第Z儲“疋互相連通,冑氣可 11 ·如申請專利範圍第9或丨〇 厂曰。 第1及第2儲留部是藉由霧裹;、述的裝置,其中上述 ^…請專Λ圍霧心 第1及第2冷凝器和上述第〗及 員所述的裝置,其令上述 13·如申請專利範圍第9 2留部都被單元化。 第1及第2冷凝部各自設置冷凝器、所述的裝置,其令上述 14·如申請專利範圍第9或/〇=溫度檢測裝置。 _ __ 所述的裝置,其t更包 2042-5565-PF(Nl);Ahddub.ptd 第27頁 200304850 六、申請專利範圍 括將冷魏回收再生的裝置、及將冷凝液排水的裝置。 15·如申印專利範圍第η項所述的裝置,其中 述第1冷凝器的冷凝液和來自上述第2冷凝器的冷 / 相對於上述回收再生襄置及上述排水處理 ^, 性地供給。 I 也璉擇 1 6 ·如申請專利範圍第丨4或丨5項所述的裝 包括配官遮斷裝置(水密性發揮裝置),該配管齡、更 被設置在,使該第1儲留部和該回收再生裝置連、、、衣置是 管和使該第2儲留部和該排水裝置連通的第2配^第1配 其中一者。 &中的至少200304850 Six Patent Application Process of condensate drainage. 6. The method according to item 1 or 2 of the scope of patent application, further comprising a process for treating the exhaust gas treated in the second cooling and condensation process. 7-A method for treating organic waste gas, including: a process for cooling and condensing organic waste gas; a process for regenerating a condensate containing a high concentration of organic components; and a system for draining condensate having a low concentration of organic components. 8. The method according to item 7 of the patent application scope, further comprising a process for treating the exhaust gas that has not been condensed in the above-mentioned condensation process. 9. · An organic waste gas treatment device, comprising: a second condenser, a first condenser, a first condenser, which condenses organic waste gas; an exhaust gas which is condensed in the first condenser, and stored in the first condenser The condensate produced by this second condenser is true: 1 ΐ. And the second storage department has a mutual exchange; the device described in item 9 above, wherein the first and the second storage units are connected to each other, and the radon gas can be 11 · Such as the patent application scope of the 9th or 丨 factory. The first and second storage sections are wrapped by mist; the device described above, where the above ^ ... please specifically surround the first and second condensers of the mist center and the device described in the above section, which makes the above 13. If the patent application scope is 9th, the 2 remaining parts are unitized. The first and second condensation units are each provided with a condenser and the device described above, which makes the above 14 · such as the patent application scope 9th or / 〇 = temperature detection Device. The device described by _ __ includes t 2042-5565-PF (Nl); Ahddub.ptd page 27 200304850 6. The scope of the patent application includes the device for recovering and regenerating the cold Wei and the device for draining the condensate 15. The device as described in item η of the scope of the application for printing, wherein the condensate from the first condenser and the cold from the second condenser are relative to the above-mentioned recovery and regeneration and the above-mentioned drainage treatment. Supply I also choose 1 6 · The equipment as described in the scope of patent application No. 丨 4 or 丨 5 includes the official blocking device (Watertightness display device), the piping age is further provided so that the first storage section is connected to the recovery and regeneration device, and the clothing is a tube, and the second storage section is connected to the drainage device Match 2 ^ Match 1 of at least one of & 1 7 ·如申清專利範圍第9或丨〇項所述的裝置,1 括用以處理在上述第2冷凝器所處理的廢氣的裝置、。千更包 18. 如申請專利範圍第17項所述的裝置,其中 用以冷凝在上述第2冷凝器所處理的廢氣的另一裝匕 另一裝置是被設置在使該第2冷凝器和上述廢氣處事= 連通的配管中。 处王衣置 19. 如申請專利範圍第9或1〇項所述的裝置,其中1 7 · The device as described in item 9 or 10 of the patent application scope, 1 includes a device for processing the exhaust gas processed in the second condenser. Thousands of packages 18. The device according to item 17 of the scope of patent application, wherein another device for condensing the exhaust gas processed by the second condenser is provided in the second condenser and The above-mentioned waste gas service = in the connected piping. Chuan Yizhi 19. The device according to item 9 or 10 of the patent application scope, wherein 括霧氣捕捉裝置及冷凝裝置中的至少一者,其是被配置$ 上述第1冷凝器供給有機廢氣的配管以及自上述第2冷 排出廢氣的配管中的至少一者。 ^ "At least one of the mist trap device and the condensing device is at least one of a pipe to which the first condenser supplies organic exhaust gas and a pipe to which the second cold exhaust gas is discharged. ^ "
TW092106925A 2002-04-04 2003-03-27 Method and device for treating organic exhaust TWI265822B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002103004A JP3842161B2 (en) 2002-04-04 2002-04-04 Organic exhaust gas treatment method and apparatus

Publications (2)

Publication Number Publication Date
TW200304850A true TW200304850A (en) 2003-10-16
TWI265822B TWI265822B (en) 2006-11-11

Family

ID=28786282

Family Applications (1)

Application Number Title Priority Date Filing Date
TW092106925A TWI265822B (en) 2002-04-04 2003-03-27 Method and device for treating organic exhaust

Country Status (4)

Country Link
JP (1) JP3842161B2 (en)
KR (1) KR100909210B1 (en)
CN (1) CN1285394C (en)
TW (1) TWI265822B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4490908B2 (en) * 2005-03-17 2010-06-30 シャープ株式会社 Wastewater treatment equipment
JP4860563B2 (en) * 2007-07-05 2012-01-25 パナソニック株式会社 Solvent recovery device
CN101337134B (en) * 2008-08-07 2012-11-14 韩富生 Recovery method and device of enamelling technique tail-gas
US20100143222A1 (en) * 2008-11-10 2010-06-10 Phil Chandler Exhaust condensate removal apparatus for abatement system
JP2010142792A (en) * 2008-12-22 2010-07-01 Toyobo Co Ltd Wastewater treatment system
CN116550111A (en) * 2023-06-08 2023-08-08 郑州义兴彩印有限公司 Water-based ink printing waste gas treatment recovery system

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6148003U (en) 1984-08-29 1986-03-31 璋 伊東 Organic solvent recovery equipment
KR100385984B1 (en) * 2001-01-08 2003-06-02 삼성전자주식회사 Carrier recovery apparatus of liquid electrophotographic printer
KR200259352Y1 (en) * 2001-10-10 2001-12-29 문준식 Compressing Storaged & Cooling Condensed Type Volertile Organic Vapor Recovery

Also Published As

Publication number Publication date
CN1285394C (en) 2006-11-22
KR100909210B1 (en) 2009-07-23
JP3842161B2 (en) 2006-11-08
KR20030079797A (en) 2003-10-10
TWI265822B (en) 2006-11-11
JP2003299935A (en) 2003-10-21
CN1448208A (en) 2003-10-15

Similar Documents

Publication Publication Date Title
US9821320B2 (en) Wet electrostatic precipitator and related methods
KR102056088B1 (en) Apparatus for Processing waste water concentration of wastewater reduction type with low temperature diffusion
CN109806713A (en) A kind of toluene waste gas processing method
CN107792907A (en) A kind of new evaporation concentration system that hc effluent is handled using fume afterheat
IE891145L (en) Process and device for reducing the content of non-condensable components which are soluble in condensable components in fumes containing condensable components
CN107583428B (en) Recycling device for heavy metal industrial waste gas
TW200304850A (en) Method and device for treating organic exhaust
CN101759246A (en) Method for treatment of waste water containing organic solvents and treatment device
CN105289231A (en) Waste gas treatment system
US20180326350A1 (en) Dichloromethane recovery system
JP2009090228A (en) Concentrator and concentration method
JPH09510295A (en) Light radioactive waste incineration gas cleaning method and plant
CN216630263U (en) VOCs exhaust treatment device
KR101131991B1 (en) Apparatus and method of oil mist treatment
TWI373366B (en)
JP3692325B2 (en) Soil purification equipment
CN104200861A (en) Waste liquid evaporation treatment device and waste liquid treatment method
JP4789902B2 (en) Concentrator
CN209286999U (en) A kind of organic exhaust gas dehumidification equipment
JP2002336841A (en) Method for vaporizing and treating oily waste water
PL191963B1 (en) Apparatus for removing impurities from vapours, in particular steam, of a recirculated liquid
TW200413077A (en) Method and device for condensing materials with a boiling point higher than that of water from an exhaust
JP3935910B2 (en) Purification method and apparatus for contaminated soil
CN211725267U (en) Gas peculiar smell removing system
CN212504083U (en) Ammonia distillation device for high ammonia-nitrogen wastewater

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees