TW200413077A - Method and device for condensing materials with a boiling point higher than that of water from an exhaust - Google Patents

Method and device for condensing materials with a boiling point higher than that of water from an exhaust Download PDF

Info

Publication number
TW200413077A
TW200413077A TW092114542A TW92114542A TW200413077A TW 200413077 A TW200413077 A TW 200413077A TW 092114542 A TW092114542 A TW 092114542A TW 92114542 A TW92114542 A TW 92114542A TW 200413077 A TW200413077 A TW 200413077A
Authority
TW
Taiwan
Prior art keywords
water
tower
exhaust
substance
boiling point
Prior art date
Application number
TW092114542A
Other languages
Chinese (zh)
Other versions
TWI255732B (en
Inventor
Yasuhito Kawase
Jiliang Li
Original Assignee
Nippon Refine 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 Nippon Refine Co Ltd filed Critical Nippon Refine Co Ltd
Publication of TW200413077A publication Critical patent/TW200413077A/en
Application granted granted Critical
Publication of TWI255732B publication Critical patent/TWI255732B/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
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • 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
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • 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
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • 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
    • B01D53/46Removing components of defined structure
    • B01D53/72Organic compounds not provided for in groups B01D53/48 - B01D53/70, e.g. hydrocarbons
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/10Inorganic adsorbents
    • B01D2253/102Carbon

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • General Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Analytical Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Treating Waste Gases (AREA)
  • Separation Of Particles Using Liquids (AREA)
  • Gas Separation By Absorption (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
  • Secondary Cells (AREA)

Abstract

One objective of the present invention is to provide a method and a device for concentrating volatile chemical materials (such as water soluble solvent) with a boiling point higher than water from an exhaust, in which volatile chemical matters are substituted by steam in order to be effectively recycled, while the exhaust is purified. Another objective of the present invention is to provide a method and a device, in which thermal energy in a high temperature (100DEG C ~120DEG C) exhaust generally discharged from a process for producing a lithium ion battery is recycled by evaporating water introduced from the outside so that volatile water soluble chemical matters having boiling points higher than water in the exhaust are condensed. That is, a component in the exhaust is substituted by water. Thus, the component can be effectively recovered while the exhaust is purified by the absorption by the replenished water at a lower temperature. A third objective of the present invention is to provide a method and a device, in which a powder containing active carbon etc. is used to absorb chemical matters (e.g. dioxin, etc.) contained in an exhaust in order to purify the exhaust. A method and a device for concentrating matters having boiling points higher than water from exhaust are characterized in that: a tower plate has a structure where a gas can not go through the tower plate without first goes through the water exists in the tower plate. An exhaust containing matter(s) having a boiling point higher than water is introduced into the lower part of a multilayered distillation tower multi-sectionally installed with the tower plate or a packing tower packed with a hydrophilic packing; and on the other end, water is supplied from the top part of the tower. So that the matter(s) having a boiling point higher than water is concentrated at the lower part of the tower due to a gas-liquid equilibrium relationship between the exhaust and water; and the matter(s) remained in the exhaust is further transferred to water at the top part of the tower.

Description

200413077 五、發明說明(1) 發明所屬之技術領域: 本發明係有關於一種將廢氣中所含有的沸點較水高之 物質’利用和水的沸點之差異而加以濃縮、回收,同時將 廢氣淨化的方法。 先前技術: 以往’將含有沸點較水高的水溶性溶劑之廢氣加以淨 化處理的情形,係由吸收塔的下部送入含有水溶性溶劑之 廢氣,並由吸收塔的上部流入大量的水以洗滌前述廢氣。200413077 V. Description of the invention (1) The technical field to which the invention belongs: The present invention relates to a method for concentrating and recovering a substance that has a higher boiling point than water contained in exhaust gas and utilizing the difference between the boiling point of water and purifying the exhaust gas. Methods. Prior technology: In the past, when the exhaust gas containing a water-soluble solvent with a higher boiling point is purified, the exhaust gas containing a water-soluble solvent is sent from the lower part of the absorption tower, and a large amount of water flows into the upper part of the absorption tower for washing. The aforementioned exhaust gas.

這種洗滌方法,於洗滌上需要大量的水,由於廢水中所包 含的溶劑之濃度極低,而需要溶劑回收成本,因此有實際 上無法回收溶劑、且需要進行廢水處理的問題點。 作為另一種先前技術係,一邊旋轉填充著沸石等的吸 附劑之橫向配置的滾筒,一邊通入冷卻至室溫左右的前述 廢氣’通過氣體的一部分就直接排放至大氣中,另一部分 則於加熱(為了趕出吸附於吸附劑的成分)之後,再通至填 充著‘述彿石等的吸附劑之橫向配置的滾筒,使吸附於吸 附齊]的溶劑脫附’將包含高濃度脫附的溶劑之處理氣體再This washing method requires a large amount of water for washing. Since the concentration of the solvent contained in the waste water is extremely low, and the cost of solvent recovery is required, there are problems that the solvent cannot be recovered in practice and waste water treatment is required. As another prior art system, while rotating a horizontally arranged drum filled with an adsorbent such as zeolite, the aforementioned exhaust gas cooled to room temperature is passed through, and a part of the gas is directly discharged into the atmosphere, and the other part is heated (In order to drive out the components adsorbed on the adsorbent), then pass to a roller arranged in a horizontal direction filled with the adsorbent such as the above mentioned stone to desorb the adsorbed substances. Solvent processing gas

^口以冷卻以回收溶劑。由於這種方法亦需要一次冷卻廢 氣、吸附處理後加熱、為了回收溶劑而再冷卻等的操作, 故能量效率極差。 π】云除由链電極的乾燥步驟所排放的廢 :包: = 刀子在則Ν—甲基-2-吡咯烷酮的吸Cool to recover solvent. Since this method also requires operations such as once-cooling the exhaust gas, heating after the adsorption treatment, and re-cooling in order to recover the solvent, the energy efficiency is extremely poor. π] Remove the waste discharged by the drying step of the chain electrode: package: = knife in the absorption of N-methyl-2-pyrrolidone

200413077 五、發明說明(2) 明顯下降的情形,故對於由前述乾燥步驟所排放 =1二ί氣施行冷卻的步驟是有其必要的,將Ν-甲基-2一 吸附於吸附劑之後’為了從吸附劑清除Ν一甲基 酮’此次相反地必需加熱操作。這種先前步驟 如第2圖所示。 驟:;:牛若依據先前方法’則必需有冷卻步驟、吸附步 驟的三項步驟’且將具相當溫度的廢氣冷卻之 後,會有伴隨著再加熱的大量能 發明内容 發明所欲 本發 由將廢氣 水溶性溶 氣淨化。 本發 常藉由對 放的向溫 予以蒸發 發性化學 換,藉此 補充水之 本發 包含著吸 解決的課題: 明的第1目的在於提供_ 中所包含的沸點較水高 劑與水蒸氣置換,而有 明的第2目的在於提供一 於從鋰離子電池電極製 廢氣的熱量加以利用, ,而使廢氣中所包含的 物質冷凝下來,亦即, ’有效地加以回收,同 吸收效果,而將廢氣淨 明的第3目的在於提供_ 附戴奥辛類等的化學物 一種方法與裝置,其中藉 之揮發性化學物質、例如 效地加以回收,同時將廢 一種方法與裝置,其中通 程等在1 〇 〇 °c〜1 2 0 °c所排 將由外部所導入的補充水 彿點較水高之水溶性的揮 將廢氣中的成分與水置 日守藉由附加上基於低溫的 化。 -種方法與裝置,其中由 負之活性碳等的粉體之廢200413077 V. Description of the invention (2) The situation of obvious decline, so it is necessary for the cooling step discharged from the aforementioned drying step = 12 liters of gas to adsorb N-methyl-2 after the adsorbent ' In order to remove N-methylketone 'from the adsorbent, a heating operation is necessary instead. This previous step is shown in Figure 2. Step:;: If the cattle according to the previous method 'three steps of cooling step and adsorption step are necessary', and after cooling the exhaust gas with a corresponding temperature, there will be a large number of re-heating accompanied by reheating. Purify the exhaust water-soluble gas. The hair is often replaced by evaporative chemical conversion to the temperature of the discharge to supplement the water. The hair contains the problem solved by absorption: The first purpose of the invention is to provide a boiling point higher than that of water and water contained in _. Steam replacement, and the obvious second purpose is to provide the use of heat from the lithium ion battery electrode exhaust gas, so that the substance contained in the exhaust gas is condensed down, that is, 'effective recovery, the same absorption effect, The third purpose of purifying the exhaust gas is to provide a method and device for attaching chemicals such as dioxins. Among them, volatile chemical substances such as effective recovery are used, and a method and device are discarded. At 100 ° C ~ 120 ° C, the supplementary water introduced from the outside will be more water soluble than the water. The water-soluble components of the exhaust gas and water will be added to the water by adding low-temperature based chemical. A method and device in which the waste of powders such as negative activated carbon is discarded

200413077 五、發明說明(3) 氣,以回收吸附戴奥辛類等的化 體,並將廢氣淨化。 予物貝之活性碳專的粉 用以解決課題的手段·· 本發明的第1項係有關於一種 物質濃縮之方法,其特徵在於:若、廢乳中彿點較水高之 水之中,則氣體無法穿通至上 =存在於塔板上的 設置此種塔板的多層蒸德塔 =塔板,由多段地 塔的下部導入含有沸點較水高的性填充物的填充 由塔上部供給水(通常為常溫 吳之廢氣;另一方面, 卻的能源),於塔下部,藉由=,不使用用以加熱或冷 係而將前述沸點較水高的精物#廢氣與#水之間的氣液平衡關 所殘留的廢氣中之前述物所=加以濃縮,同時使在塔上部 本發明的第2項係有關貝;:轉移至水中。 水高的物質濃縮之方法,复^員所述的將廢氣中沸點較 (a )揮發性化學物質、 ^ 述沸點較水高的物質係 本發明的第3項係^ 粉末狀物質。 水高的物質濃縮之方法,於第^項所述的將廢氣中沸點較 ^狀的物質,由塔上部所ς认耵述沸點較水高的物質係粉 資訊來加以控制,由 加、、Ό的水量係基於塔下部 幻,重量。下部所回收的前述物質之濃度 本發明的第4項係有 水高的物質濃縮之方法,關复於第—3項所述的將廢氣中沸點較 辛類的粉體。 ,、耵述粉末狀物質係吸附戴奥200413077 V. Description of the invention (3) Gas to recover adsorbed dioxin and other compounds and purify the exhaust gas. Means to solve the problem of the powder of active carbon of yogo shellfish. The first item of the present invention relates to a method for concentrating a substance, which is characterized in that: if the buddha in waste milk is higher than water, , The gas cannot pass through to the top = the multi-layer steamed tower on the tray where this type of tray is installed = the tray. The lower part of the multi-storied tower is filled with sexual fillers with a higher boiling point than water. (Usually the exhaust gas at room temperature Wu; on the other hand, but the energy), in the lower part of the tower, with =, do not use for heating or cooling system, the aforementioned boiling point is higher than water #EGR and # 水The foregoing in the exhaust gas remaining in the gas-liquid equilibrium barrier is concentrated, and at the same time, the second item of the present invention in the upper part of the tower is related to shellfish; it is transferred to water. The method for concentrating a substance having a high water content is a substance having a boiling point higher than (a) a volatile chemical substance in the exhaust gas, and a substance having a higher boiling point than the water. The third aspect of the present invention is a powdery substance. The method for concentrating substances with high water content is described in item ^. The substance with a relatively high boiling point in the exhaust gas is controlled by the information on the powder of the substance with a higher boiling point in the upper part of the tower. The amount of water in the scoop is based on the weight and weight of the lower part of the tower. Concentration of the aforementioned substance recovered in the lower part The fourth aspect of the present invention is a method for concentrating a substance with a high water content, which is related to the powder having a boiling point in the exhaust gas which is relatively stale as described in the third aspect. ,, said the powdery substance is adsorbed by Dior

2042-5666-PF(Nl);Tcshiau.ptd 第 頁 200413077 發明說明(4) 水高項方係/,關:中第:述 下部的濃度L由塔上部所供給的水量係基於塔 揮發的。控工:;為二下^ 本發明的第fi is # 士日日 . ^ 0 水高的物質濃缩之方、關於第5項所述的將廢氣中沸點較 質係由以下;t;;:::其中前述親水性、揮發性化學物 NMP(N-甲基-2:;比各I成的群組之中所選擇的溶劑類: 醇)、DEG(_H &胺)、DMS〇(二甲亞碉)、EG(乙二 t、叫;:醇、;=三甘醇 胺)、以及咖(二甘醇一D甲(1趟;_。丁-醇)、MEA( -乙醇 之濃i以r二有於關於-種對於沸點較水^ ^ π)甚T :寺在由以下裝置所構成·· 通至上部之構上的水之中’則氣體無法穿 餾塔或是填,充置此種塔板的多層蒸 設置(的2)ΛΤ置多段么 設置的供水裝置;真充層的上方’於前述填充塔内所 理氣(』)排於放多口層蒸館塔的上部或填充層的上部所設置的^ (4)於夕層瘵餾塔的下部或填充層的下部所設置的液2042-5666-PF (Nl); Tcshiau.ptd page 200413077 Description of the invention (4) Water high term system /, Off: Middle: Description The lower concentration L of water supplied from the upper part of the tower is based on the volatilization of the tower. Control engineer :; It is two times ^ fi is # 士 日 日 of the present invention. ^ 0 The method of concentrating substances with high water content, as described in item 5, the quality of the boiling point in the exhaust gas is as follows; t ;; ::: Among them, the aforementioned hydrophilic and volatile chemical NMP (N-methyl-2 :; than selected solvents in the group consisting of: alcohol), DEG (_H & amine), DMS. (Dimethylarsine), EG (ethylene glycol, called :: alcohol,; = triethylene glycol amine), and coffee (diethylene glycol-D methyl (1 trip; _. Butanol), MEA (-ethanol Concentration i and r are related to-a kind of boiling point is relatively water ^ ^ π) and even T: Temple is composed of the following devices ... the gas can not pass through the distillation tower or Filling and filling the multi-layer steaming installation of this type of tray (2) ΛΤ The water supply device of multiple stages is installed; the top of the true filling layer is arranged in the gas filling tower of the multi-port steaming tower. ^ (4) The liquid set in the lower part of the retort tower or the lower part of the packing layer

200413077 —— 五、發明說明(5) 體物質排放口 ; (5 )由液體物質排放口經由管路所連接的、含有沸點 較水高的物質之液體物質貯槽; (6 )用以對多層蒸餾塔内或填充塔内所設置的沸點較 水高的物質之系中濃度進行檢測的測定裝置; (7 )藉由來自前述測定裝置的資訊以控制來自前述供 水裝置的供水量之裝置。200413077 —— V. Description of the invention (5) Body substance discharge port; (5) Liquid substance storage tank connected with liquid substance discharge port through pipeline and containing substance with higher boiling point than water; (6) Used for multilayer distillation (7) A device for controlling the water supply amount from the water supply device by using the information from the measurement device.

本發明係一種對於通常大多具有相當高的溫度(例如 8 0〜1 2 0 °C )之廢氣熱量加以有效利用,於多層蒸餾塔内通 過廢氣的一項步驟,矸同時達成廢氣中所包含的沸點較水 雨的物質之回收與廢氣之處理的極具效率的方法與裝置。 本發明係,特別是若不通過存在於塔板上的水之中, =氣體無法穿通至上部之構造的塔板,由多段地設置此種 塔板2多層蒸餾塔或是填充親水性填充物的填充塔的下部 導入δ有由鐘離子電池電極製程所排放的N -曱基- 2 - 〇比略 烷酮之100〜120它的高溫廢氣;另一方面,由塔上部供給 水,於塔下部利用廢氣的熱量,使供給的水蒸發,相反° =使廢氣中所包含的沸點較水高、水溶性的Ν-甲基-2- 中的iir、f w田I 圪下σ卩,猎由將塔上部所殘留的廢氣 早雷I 2—吡咯烷酮再轉移至水中,則隨著對鋰 1子電池電極製程的廢氣料淨化,同時作為回收ν — 一2-吡咯烷酮的方法和裝置極為適合。 前述補充的水量係, 上部所排放的處理後廢氣 包含於廢氣處理後由多層蒸顧塔 ’從系中流出來的水量(Β)、以The invention relates to a method for efficiently utilizing the heat of exhaust gas, which usually has a relatively high temperature (for example, 80 to 120 ° C), and passes the exhaust gas in a multi-layer distillation tower to simultaneously achieve the content contained in the exhaust gas. A highly efficient method and device for recovering materials with boiling points that are more rainy and rainy and treating exhaust gas. In the present invention, especially if it does not pass through the water existing in the tray, the gas cannot pass through to the upper structured tray, such trays are set up in multiple stages, or the multilayer distillation column is filled with hydrophilic packing. In the lower part of the packed tower, δ has a high temperature exhaust gas of 100-120 N-fluorenyl-2- 2-biloxanone discharged by the electrode process of the bell ion battery; on the other hand, water is supplied from the upper part of the tower to the tower. The lower part uses the heat of the exhaust gas to evaporate the supplied water. Conversely, the exhaust point contained in the exhaust gas has a higher boiling point than the water and the water-soluble N-methyl-2-, iir, fw Tian I I 下 σ 卩, hunting by The residual exhaust gas I 2 -pyrrolidone remaining in the upper part of the tower is then transferred to water. With the purification of the waste gas in the lithium 1-cell electrode process, it is also very suitable as a method and a device for recovering ν-2-pyrrolidone. The above-mentioned supplementary water amount is the treated exhaust gas discharged from the upper part, which includes the amount of water (B) flowing out of the system from the multi-layer steaming tower after the exhaust gas treatment.

200413077 五、發明說明(6) ' 及隨著沸點較水高的揮發性化學物質的冷凝物一起從塔下 部流出來的水量((;),可補充此兩種水量的量(A )。換言 之,由於可為: "200413077 V. Description of the invention (6) 'and the amount of water ((;) flowing out from the lower part of the tower along with the condensate of volatile chemical substances with a higher boiling point than water, can supplement the two amounts of water (A). In other words , Because it can be: "

A =B +C 若相較於基於先前技術的水洗之廢氣處理法,則水的 1量大幅地減少,僅就這一點來看,可達成節省資源,同 日守原本品要進行廢水處理的廢水並未實際產生的這點亦為 一大優點。 塔頂部的溫度作成比外部空氣溫度更高者。由於飽和 含水里係溫度較咼者為較大,基於多層蒸餾塔内的廢氣中 _ 的水分經常很容易地低於飽和點,即使添加補充水也能夠 作出滿足Xac $ xs的條件。補充水的溫度係吸收效率較低者 為較佳’但若太低則塔内的流下水量不僅不足,而且需要 用以冷卻的能源。再者,外部空氣通常為不飽和,由於未 達到以濕度所表示的飽和之含水率存在著,故補充水的量 比飽和狀態更多。 作為本發明的沸點較水高之物質係(a)揮發性化學物 質、或(b )粉末狀物質。 作為沸點較水高之揮發性化學物質(a ),特別是沸點 較水高之水溶性溶劑為代表性的化學物質。 _ 作為這種溶劑類,係NMp(N_甲基_2—吡咯烷酮、Bp : 1 97 C )、DMF(N,N-二曱基甲醯胺、Bp :153。〇、 DMAC(N,N -二甲基乙醯胺、Bp :165。〇、DMS〇(二甲亞碉、 BP .189C)、EG(乙二醇、Bp :197。〇、DEG(二甘醇、A = B + C Compared with the waste water treatment method based on the previous technology, the amount of water is greatly reduced. From this point of view, it is possible to achieve resource conservation and the same day as the original wastewater to be treated for wastewater. The fact that this has not actually happened is also a great advantage. The temperature at the top of the tower was made higher than the outside air temperature. Because the temperature of the saturated water is higher than that of the water, the moisture in the exhaust gas in the multi-layer distillation column is often easily lower than the saturation point, and even if supplemental water is added, it can be made to meet the condition of Xac $ xs. The temperature of the make-up water is better if the absorption efficiency is lower ', but if it is too low, the amount of flowing water in the tower is not only insufficient, but also requires energy for cooling. Furthermore, the outside air is usually unsaturated, and since the moisture content that does not reach the saturation expressed by humidity exists, the amount of supplemental water is larger than the saturated state. The substance having a higher boiling point than water according to the present invention is (a) a volatile chemical substance or (b) a powdery substance. As a volatile chemical substance (a) having a boiling point higher than water, a water-soluble solvent having a boiling point higher than water is a representative chemical substance. _ As such solvents, they are NMp (N_methyl_2-pyrrolidone, Bp: 1 97 C), DMF (N, N-dimethylformamide, Bp: 155.0, DMAC (N, N -Dimethylacetamide, Bp: 165.0, DMS 0 (dimethylarsine, BP.189C), EG (ethylene glycol, Bp: 197.0, DEG (diethylene glycol,

2042-5666-PF(N1);Tcshiau.ptd 第10頁 200413077 發明說明(7) 7 二;45。〇、TEG(三甘醇、BP :278 t)、PGME(丙二醇-乙岵)、PG(丙二醇、BP : 188。〇、】,4_BD(l,“ BP : 235。〇、MEA(一乙醇胺、Bp : 17〇. 5。〇、以——予、 (二甘醇—甲轉)# ’不會與水共沸的性質者較為適 >作為前述(b)的粉末狀物質,可舉出:吸附焚化 氣中的戴奥辛類之活性碳粉體等。 a 法穿通Ϊ存在於前述塔板内的水之中,則氣體無 ΐ: ί造的塔板’可舉出:有從最早所使用的 泡罩板,除此之外,有其後所開發的多孔板等。 方面泡罩板較佳;而在成本方面則多孔板較佳。心疋[ 少在填充前述親水性填充物的填充塔中之親水性殖右物 係可為f則性填充物的形狀,亦可為不規則性填充物的形 狀,但若考慮壓力損失,則規則性填充物較佳。、填充 4=:“生,“表面積較大者、例如親水性的材質;; =孔性物質’具體而纟,可舉出:多孔性m隸 本發明係,特別是在鐘離子電池的製造 排放的廢亂之處理。如第i圖所示,為了去除 咯烷酮(NMP)溶劑,而從工廠外部輸入一般空5 ,土、、比 濾之後,利用鼓風機將加熱空氣輪送至乾燥步;。、迻 通常由工廠外部輸入的空氣係 、’ 外部空氣溫度t2042-5666-PF (N1); Tcshiau.ptd page 10 200413077 Description of the invention (7) 7 II; 45. 〇, TEG (triethylene glycol, BP: 278 t), PGME (propylene glycol-acetamidine), PG (propylene glycol, BP: 188. 0,], 4_BD (1, "BP: 235. 0, MEA (monoethanolamine, Bp: 17.0.5.0, with-I, (diethylene glycol-methyltransfer) # 'it is not suitable for azeotropy with water> As the powdery substance of the above (b), : Adsorption of dioxin-like activated carbon powder in incineration gas, etc. a method passes through the existence of water in the above tray, then the gas is free of 造: The tray can be made from the earliest used In addition to the blister plate, there are porous plates developed later. In terms of cost, blister plates are preferred; in terms of cost, perforated plates are preferred. The hydrophilic colony in the tower can be the shape of the regular filler, or the shape of the irregular filler, but if the pressure loss is considered, the regular filler is better., Fill 4 =: "" "Persons with a large surface area, such as hydrophilic materials; = Porous substances', specifically, can be exemplified by: porous m according to the present invention, especially in Zhongli Disposal of waste produced by the manufacture of sub-cells. As shown in Figure i, in order to remove the NMP solvent, the general air is input from the outside of the factory. 5 After the soil, specific filtration, the air wheel is heated by a blower. Send to the drying step; ..., move the air system usually input from outside the factory, 'outside air temperature t

200413077 五、發明說明(8) 流量 V N m3 / m i η 含水率 Xa kg/m3 水分量 VXa kg/min 在链離子電池製造工廠,由用以去除N-甲基-2-吼略烧酮 (NMP)溶劑的乾燥步驟所排放的廢氣係在 廢氣溫度 NMP含量 NMP流量 廢氣的流量 = 1 0 0 - 1 20 °C Cn =0· 0 0 0 5 〜0· 01 kg/m3200413077 V. Description of the invention (8) Flow rate VN m3 / mi η Moisture content Xa kg / m3 Moisture content VXa kg / min In the chain ion battery manufacturing plant, it is used to remove N-methyl-2-role ketone (NMP ) The exhaust gas discharged in the solvent drying step is the exhaust gas temperature at the NMP content, the NMP flow rate, and the exhaust gas flow rate = 1 0 0-1 20 ° C Cn = 0 · 0 0 0 5 ~ 0 · 01 kg / m3

(113〜2260ppm 、νο1·/νο1·) VCn kg/min V N m3 / m i η 水分量 VXa kg/min 的條件下由多層蒸餾塔(水置換塔)的下部送入。在水置換 塔内由所設置的多段的泡罩板或多孔板等的最上段,通常 以流$M kg/m i η來供給常溫例如扒的補充水。由水置換 ,上部所排放的處理後氣體(氣體溫度係,將r作為ΝΜρ 專的揮發性化學物質之回收率(重量分率), 排放量 V Nm3/min 計异含水量 VXa +〔μ —vCnR(l/Xn —1)〕 kg/min kg/m3 計算含水率 Λ +〔Μ -VCnR(l/Xn —1)〕/(113 ~ 2260ppm, νο1 · / νο1 ·) VCn kg / min V N m3 / m i η Moisture content VXa kg / min is fed from the lower part of the multilayer distillation column (water displacement column). In the water displacement tower, the uppermost stage of a multi-stage blister plate or perforated plate, etc., is usually supplied with supplemental water at a normal temperature such as squeegee at a flow of $ M kg / m i η. Replaced by water, the treated gas discharged from the upper part (gas temperature is the recovery rate (weight fraction) of volatile volatile chemicals with r as NMρ), the discharge amount V Nm3 / min is calculated as the different water content VXa + [μ — vCnR (l / Xn —1)] kg / min kg / m3 Calculate moisture content Λ + [Μ -VCnR (l / Xn —1)] /

氣體溫度h時,氣體飽和含水率:χ 作為控制條件,X < γ η士 ^ s 千 Xac = \日寸,本裝置可正常運轉。 方面’由水置換塔下部回收含有水的卜曱基一 2At the gas temperature h, the gas saturation moisture content: χ As a control condition, X < γ η ^ s thousand Xac = \ day inch, the device can operate normally. Aspect ’: Reclaiming water-containing Buchanji-1 from the lower part of the water replacement tower 2

2UU413U//2UU413U //

口比洛烧酮(液溫^ 實施方式: 以下舉出實 這些實施例所卩P⑹》對本發明加以說明,但本發明毫不受 %。 、h實施例中的%只要未指示,則為重量 實施例1 第1圖所示&田 酮(NMP)溶劑之=去除鋰離子電池的N—甲基-2-吼咯炫 J之乾步驟所輸入的空氣係Orbirazone (liquid temperature ^ Embodiment: The following is a description of these examples "P" "to illustrate the present invention, but the present invention is not affected by%. The% in the examples is weight unless otherwise indicated Example 1 The air shown in Figure 1 & Tanone (NMP) solvent = the air system input in the dry step of removing the N-methyl-2-Hydrogen of lithium ion batteries

1部空氣溫度t = 1 5 °c /;,L ^ V = 4 N m3 / m i η A匕、 έ火率 Xa = 〇 · 〇 1 2 8 k g / m3 (假定為飽和狀 m) 个刀置 VXa =0. 0512 kg/min 在鐘離子電池製造工薇,由用以去除N —曱基—2 —吼咯院酮 (NMP)溶劑的乾燥步驟所排放的廢氣係在 廢氣溫度 tl = :1 2 0 〇C NMP含量 Cn : = 0.0031 kg/m3 (70Oppm、vo 1 · /vo 1 ·) NMP流量 VCn =0. 012 4 kg/m i n 廢氣的流量 V = 4 N m3 / m i n 水分量 VXa = 0.0512 kg/min 的條件下由多層蒸餾塔(水置換塔)的下部送入。在水置換 塔内由所設置的多段的泡罩板的最上段,以Μ = 0 · 1 7 8 61 air temperature t = 1 5 ° c / ;, L ^ V = 4 N m3 / mi η A, fire rate Xa = 〇 · 〇 1 2 8 kg / m3 (assuming saturated m) VXa = 0.0512 kg / min In the Zhongwei battery manufacturing industry, the exhaust gas emitted by the drying step to remove the N-fluorenyl-2—NMP solvent is at an exhaust gas temperature tl =: 1 2 0 〇C NMP content Cn: = 0.0031 kg / m3 (70Oppm, vo 1 · / vo 1 ·) NMP flow rate VCn = 0.012 4 kg / min exhaust gas flow rate V = 4 N m3 / min moisture content VXa = 0.0512 Under the condition of kg / min, it is fed from the lower part of the multilayer distillation column (water displacement column). In the water displacement tower, the uppermost stage of the multi-stage blister plate is set with M = 0 · 1 7 8 6

2042-5666-PF(Nl);Tcshiau.ptd 第13頁 200413077 五、發明說明(10) kg/min的流量來供給水溫t3 =20 °C的補充水。由水置換塔 上部所排放的處理後氣體(氣體溫度t2 = 4 2 °C )係 排放量 V=4 Nm3/min 計算含水量 VXa +〔M —VCnR(l/Xn 一1)〕= 0.2180 kg/min 計算含水率 xac =xa +〔M —VCnR(i/xn 一1)〕/V =0· 0 545 kg/m3 體溫度t2 = 4 2 °C時,氣體飽和含水率:& = 0.0565 kg/m32042-5666-PF (Nl); Tcshiau.ptd Page 13 200413077 V. Description of the invention (10) The flow rate of kg / min is used to supply make-up water with water temperature t3 = 20 ° C. The treated gas (gas temperature t2 = 4 2 ° C) discharged from the upper part of the water replacement tower is V = 4 Nm3 / min. The calculated water content is VXa + [M —VCnR (l / Xn-1)] = 0.2180 kg / min Calculate moisture content xac = xa + [M —VCnR (i / xn-1)] / V = 0 · 0 545 kg / m3 at body temperature t2 = 4 2 ° C, gas saturation moisture content: & = 0.0565 kg / m3

因而,thus,

Xac = 0. 0545kg/m3 ^Xs = 0. 0565kg/m3 NMP 含量Cn(l —R) = 〇. 〇〇〇i5kg/m3 本裝置可正常運轉。Xac = 0. 0545kg / m3 ^ Xs = 0. 0565kg / m3 NMP content Cn (l-R) = 〇. 〇〇〇i5kg / m3 This device can operate normally.

另一方面’在下述條件下可由水置換塔下部回收含有 水的N -曱基- 2 -吡咯烷酮(液溫t4 = 8 0 °C )。 t4 = 8 (TCOn the other hand, under the following conditions, N-fluorenyl-2-pyrrolidone containing water can be recovered from the lower part of the water displacement column (liquid temperature t4 = 80 ° C). t4 = 8 (TC

收集液中的水 VCnR(l/Xn —1) =0. 0118 kg/min 收集液中的NMP VCnR =0. 0118 kg/min NMP的回收率 R =0· 95(重量分率) NMP濃度 Xn =0· 50(重量分率) 再者’水置換塔質量平衡係如第2圖所示。 發明效果: (1)基於本發明,能夠達成顯著的步驟簡化與節省能Water VCnR (l / Xn — 1) in the collection solution = 0.11818 kg / min NMP VCnR in the collection solution = 0.11818 kg / min Recovery of NMP R = 0.95 (weight fraction) NMP concentration Xn = 0.50 (weight fraction) Furthermore, the mass balance system of the water replacement tower is shown in FIG. 2. Effects of the Invention: (1) Based on the present invention, significant step simplification and energy saving can be achieved.

-PF(Nl);Tcshiau.ptd 第14頁 200413077-PF (Nl); Tcshiau.ptd Page 14 200413077

上 牡冗刚万法中係採用對於應回收的溶劑成分耸 广:給水,使溶劑溶解於該水中而 成專由 牯,由於系的溫度高,則、、六 木叼衣置。此 給至洗滌塔的水需事先冷^二水的溶劑再度揮發,故/ 卻的能源。另一方面,=右。因而需要用作, 故供給至濃縮裝置的廢氣1 ^月有效利用廢氣的哉 這麼直接供給,故熱效;=需要加熱或冷卻,而能二: (3 )若依據本發明,In the above method, the system adopts a wide range of solvent components that should be recovered: feed water, so that the solvent is dissolved in the water to form an exclusive 牯, because the temperature of the system is high, then, the Roppongi clothes are placed. The water supplied to the washing tower needs to be cooled beforehand, and the solvent of the second water will be volatilized again, so the energy will be reduced. On the other hand, = right. Therefore, it needs to be used, so the exhaust gas supplied to the concentrating device effectively utilizes the exhaust gas 月 for one month, so it is directly supplied, so the thermal efficiency; = heating or cooling is required, and two: (3) If according to the present invention,

補充水即可,‘然先前技術由:需所使用的水,僅需要—处 :明相較於先前方法’水的用量可減: 故Just add water, ‘then the prior art: the water used, only need—where: compared with the previous method’, the amount of water can be reduced:

2042-5666-PF(Nl);Tcshiau.ptd 第15頁 2004130772042-5666-PF (Nl); Tcshiau.ptd Page 15 200413077

2042-5666-PF(Nl);Tcshiau.ptd 第16頁2042-5666-PF (Nl); Tcshiau.ptd Page 16

Claims (1)

200413077 六、申請專利範圍 徵在1於·· 二弗點較水高之物質濃縮之方法,其特 通至上部於塔板上的水之中,則氣體無法穿 館塔或是填充:水充::此f塔板的多層蒸 下部,芦1:, 另—方面,由塔上部供給水,於塔 水高的“力之=氣液平衡關係而將前述彿點較 前述物質進一使在塔上部所殘留的廢氣中之 之物2質所述的將廢氣中沸點較水高 發性化學物質、或⑻粉末點較水高之物質係⑷揮 之物3質 的物質,由塔上部所供:::量弗之物質係粉末狀 來:以控制,由塔下部所回收的前;:濃度資訊 1〜30重量%。 負之》辰度控制為 之物質濃縮:K乾::%項所述的將廢氣中沸點較水高 的粉體。 /、中則述粉末狀物質係吸附戴奥辛類 5.如申請專利範圍第丨項所述的 之物質濃縮之方法,其中前述沸點、* 沸點較水高 f:發性化學物質,由塔上部所二:ΐ質係親水 1的濃度資訊來加以控制’由塔下部所回:=係基於塔下 發性化學物質的濃度控制為20〜100重量%的親水性、揮 第17頁 2042-5666-PF(Nl);Tcshiau.ptd 200413077200413077 VI. The method of concentrating the patent application scope is 1 ~ 2. The method of concentrating a substance higher than water at the point of 2nd point is specially connected to the water on the tray, so the gas cannot pass through the tower or be filled: water filling :: The multi-layer steamed lower part of this f tray, Lu 1 :, On the other hand, the water is supplied from the upper part of the tower, and the "focal force = gas-liquid equilibrium relationship" in the tower water is higher, and the aforementioned Buddha points are further added to the tower. The remaining substance in the upper part of the exhaust gas is the substance with a boiling point higher than that of water in the exhaust gas, or the substance with a higher powder point than the water is the substance 3, which is provided by the upper part of the tower: : The amount of the substance is in powder form: before the control, recovered from the lower part of the tower ;: concentration information 1 ~ 30% by weight. The content of the negative control is concentrated: K dry::% A powder having a higher boiling point in the exhaust gas than water. /, The powdery substance is a substance that adsorbs dioxin. 5. A method for concentrating a substance as described in item 丨 of the patent application scope, wherein the aforementioned boiling points and * boiling points are higher than water f: Hair chemicals, from the upper part of the tower Controlled by the concentration information of Hydrophilic 1 'Returned from the lower part of the tower: = Based on the control of the concentration of the chemical compounds emitted from the tower to 20 to 100% by weight of hydrophilicity. Vol.17, 2042-5666-PF (Nl); Tcshiau .ptd 200413077 6·如申請專利範圍第5項 之物質濃縮之方法,其中前、述的將廢氣中沸點較水高 由以下化合物所形成的群纟且二t、揮發性化學物質係 甲基-2-吡咯烷酮)、DMF(N Γ斤=擇的溶劑類·1ΜΡ(Ν- 二甲基乙醯胺)、DMS0(二甲亞楓)U醯胺)、D_,N-甘醇)、TEG(三甘醇)、PGMe( 乙一醇)、DEG( — 醇卜 14L4— 丁二醇)、二7%二喊)、PG(丙二 酬(二甘醇一甲謎)。嶋(一乙醇胺)、以及6. The method of concentrating substances as described in the scope of application for patent No. 5, wherein the above-mentioned group of voluminous compounds whose boiling point is higher than that of water is formed by the following compounds, and the two volatile, chemical substances are methyl-2-pyrrolidone ), DMF (N Γ ^ = selected solvents · 1MP (N-dimethylacetamide), DMS0 (dimethylmethylene maple) amine), D_, N-glycol), TEG (triethylene glycol) ), PGMe (ethylene glycol), DEG (— alcohol 14L4 — butanediol), 27% dioxin), PG (propylene glycol (diethylene glycol monomethylamine). 嶋 (monoethanolamine), and 7· —種對於沸點較水高的物皙 於:由以下裝置所構成,〜縮裳置,其特徵在 、甬至(i 不^過存在於丨合板上的水之中,則氣體無法穿 ^ #之構仏的塔板,由多段地設置此種塔板的多層墓 餾塔或是填充親水性填充物的填充塔; (2)係前述多段塔板的上方,於前述多層基餾塔内所 設置的供水裝置;或係填充層的上方,於前述填充塔内所 設置的供水裝置; (3 )於多層蒸餾塔的上部或填充層的上部 置的處 理氣體排放口;7 · —A kind of material with a higher boiling point than water: It is composed of the following devices, ~ shrinkage set, which is characterized by, 甬 to (i does not exceed the water in the plywood, then the gas cannot pass through ^ # 之 仏 The trays are composed of a multi-layer tomb distillation tower or a packed tower filled with hydrophilic fillers in multiple stages; (2) It is above the multi-stage tray and above the multi-layer base distillation tower. A water supply device provided inside; or a water supply device provided above the filling layer in the aforementioned filling tower; (3) a processing gas discharge port provided on the upper part of the multilayer distillation tower or the upper part of the filling layer; (4) 於多層蒸餾塔的下部或填充層的下 體物質排放口; (5) 由液體物質排放口經由管路所連接的、含有沸點 較水高之物質的液體物質貯槽; (6) 用以對多層蒸餾塔内或填充塔内所設置的沸點較 水高之物質的系中濃度進行檢測的測定裳置; ^(4) The lower body substance discharge port at the lower part of the multi-layer distillation column or the packed layer; (5) a liquid substance storage tank connected to the liquid substance discharge port via a pipeline and containing a substance having a higher boiling point than water; (6) used for Determination of the concentration in a system of a substance with a higher boiling point than water set in a multilayer distillation column or a packed column; ^ 2042-5666-PF(Nl);Tcshiau.ptd2042-5666-PF (Nl); Tcshiau.ptd 200413077 六、申請專利範圍 (7)藉由來自前述測定裝置的資訊以控制來自前述供 水裝置的供水量之裝置。 iiiii 2042-5666-PF(Nl);Tcshiau.ptd 第19頁200413077 6. Scope of Patent Application (7) The device for controlling the water supply from the aforementioned water supply device by using the information from the aforementioned measurement device. iiiii 2042-5666-PF (Nl); Tcshiau.ptd p. 19
TW092114542A 2003-01-29 2003-05-29 Method and device for condensing materials with a boiling point higher than that of water from an exhaust TWI255732B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2003020725A JP4030439B2 (en) 2003-01-29 2003-01-29 Method and apparatus for concentrating substances having higher boiling point than water in exhaust gas

Publications (2)

Publication Number Publication Date
TW200413077A true TW200413077A (en) 2004-08-01
TWI255732B TWI255732B (en) 2006-06-01

Family

ID=32950276

Family Applications (1)

Application Number Title Priority Date Filing Date
TW092114542A TWI255732B (en) 2003-01-29 2003-05-29 Method and device for condensing materials with a boiling point higher than that of water from an exhaust

Country Status (4)

Country Link
JP (1) JP4030439B2 (en)
KR (1) KR100981073B1 (en)
CN (1) CN100563788C (en)
TW (1) TWI255732B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4593264B2 (en) * 2004-01-30 2010-12-08 三菱化学エンジニアリング株式会社 N-methyl-2-pyrrolidone recovery device and recovery method thereof
JP4778403B2 (en) * 2006-11-08 2011-09-21 日本リファイン株式会社 A method and apparatus for purifying exhaust gas by collecting and concentrating VOC from exhaust gas containing VOC.
CN101791509B (en) * 2010-03-31 2011-12-28 苏州巨联科技有限公司 Ternary cycle DMF waste gas recovery method and device
JP6180704B2 (en) 2011-12-12 2017-08-16 日本リファイン株式会社 Gas-liquid contact device
JP6665063B2 (en) 2015-11-24 2020-03-13 株式会社西部技研 Drying equipment
CN107715651A (en) * 2017-10-17 2018-02-23 华南理工大学 A kind of efficient low damage solvent for being used to absorb toluene and flow

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2134890Y (en) * 1992-07-31 1993-06-02 张家港市化肥厂 Ring-edge sealed bubble-cap tower
JPH11253733A (en) * 1997-12-25 1999-09-21 Chiyoda Corp Method for two stage wet detoxification treatment of incinerator gas
JP4183331B2 (en) * 1999-03-05 2008-11-19 日本リファイン株式会社 Shelf type gas-liquid contact device
JP2003024736A (en) * 2001-07-11 2003-01-28 Fuji Photo Film Co Ltd Gas-liquid contact apparatus and freezing, concentration, and separation method

Also Published As

Publication number Publication date
JP2004230265A (en) 2004-08-19
JP4030439B2 (en) 2008-01-09
CN100563788C (en) 2009-12-02
CN1517144A (en) 2004-08-04
KR100981073B1 (en) 2010-09-08
KR20040069939A (en) 2004-08-06
TWI255732B (en) 2006-06-01

Similar Documents

Publication Publication Date Title
TW541201B (en) Method and device for cleaning air
CN103990351B (en) A kind of purification recovery device of volatile organic waste gas
JP4778403B2 (en) A method and apparatus for purifying exhaust gas by collecting and concentrating VOC from exhaust gas containing VOC.
CN101596392B (en) Adsorption tower for fluidized floating bed solvent recovering device and air flow adjusting method thereof
CN101439236A (en) Device for executing recovery processing of organic discharge gas produced in coating procedure
CN106540508A (en) Reclaim the device and method of volatility organic chloride gas
JP5576723B2 (en) Solvent recovery device
CN102489106A (en) Method for cycle collection of exhaust gas by adopting secondary adsorption
JP5248767B2 (en) Concentrator for volatile organic compounds
TW200413077A (en) Method and device for condensing materials with a boiling point higher than that of water from an exhaust
CN108096984A (en) Knockdown volatile organic matter resource regeneration processing unit and method
CN102476013A (en) Novel organic waste gas recovery method and system
JP2009066530A (en) Voc recovery apparatus
CN105732378B (en) A kind of method that organic-aqueous mixture carries out dehydration purification
CN207025002U (en) Shell fills multiple field organic waste gas treatment device in parallel
JP2009273975A (en) System for treatment of gas containing organic solvent
CN110508085A (en) A kind of processing method and processing unit of brombutyl tail gas
CN110227329A (en) Waste gas treatment process in a kind of production of cyanate ester resin
TWI373366B (en)
CN101439237A (en) Device for processing organic discharge gas produced in coating procedure
CN209093032U (en) Residual heat utilization-type organic waste gas recycling system
TWI362961B (en)
CN205517071U (en) Waste water recycling device of VOCs waste gas recovery in -process
JP2005246218A (en) Concentration method for substance with higher boiling point than that of water in exhaust gas and apparatus therefor
WO2014208936A1 (en) Method for regenerating ammonium bicarbonate solution in forward osmotic pressure type water treatment apparatus and regeneration apparatus therefor

Legal Events

Date Code Title Description
MK4A Expiration of patent term of an invention patent