CN104587834A - Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution - Google Patents
Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution Download PDFInfo
- Publication number
- CN104587834A CN104587834A CN201510040321.9A CN201510040321A CN104587834A CN 104587834 A CN104587834 A CN 104587834A CN 201510040321 A CN201510040321 A CN 201510040321A CN 104587834 A CN104587834 A CN 104587834A
- Authority
- CN
- China
- Prior art keywords
- low
- organic matter
- pervaporation
- aqueous solution
- membrane
- Prior art date
- Legal status (The legal status 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 status listed.)
- Pending
Links
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
本发明公开了一种利用渗透汽化-分级冷凝耦合工艺从低浓度水溶液中分离回收高沸点、水溶性有机物并直接获得高纯度液态有机物的装置及方法。首先通过真空泵在渗透汽化膜下游形成低压气氛,利用渗透汽化膜作为传质分离介质将稀溶液中的高沸点有机物进行选择性富集,之后将透过渗透汽化膜并在膜下游侧富集的低压混合蒸汽进行分级冷凝;高沸点有机物蒸汽首先被截留在第一级冷凝器中生成高纯度液态有机物,未被冷凝的水蒸汽与小部分有机蒸汽被截留在第二级冷凝器中,通过循环泵送回原料槽中。本发明通过渗透汽化-分级冷凝耦合工艺,无需添加化学试剂,消除了二次污染,且不受气液平衡限制,操作简单、快捷、高效,可以直接获得纯度大于99.9wt %的高沸点液态有机物。
The invention discloses a device and a method for separating and recovering high-boiling point and water-soluble organic matter from low-concentration aqueous solution and directly obtaining high-purity liquid organic matter by utilizing a pervaporation-staged condensation coupling process. First, a vacuum pump is used to form a low-pressure atmosphere downstream of the pervaporation membrane, and the pervaporation membrane is used as a mass transfer separation medium to selectively enrich the high-boiling point organics in the dilute solution, and then the pervaporation membrane is enriched on the downstream side of the membrane The low-pressure mixed steam is condensed in stages; the high-boiling organic vapor is first trapped in the first-stage condenser to generate high-purity liquid organic matter, and the uncondensed water vapor and a small part of organic vapor are trapped in the second-stage condenser. Pump back into raw material tank. The invention adopts pervaporation-staged condensation coupling process without adding chemical reagents, eliminates secondary pollution, is not limited by gas-liquid balance, is simple, fast and efficient to operate, and can directly obtain high-boiling liquid organic matter with a purity greater than 99.9wt%.
Description
技术领域 technical field
本发明涉及一种从低浓度水溶液中分离回收高沸点有机物的装置及方法,属于化学工程分离技术领域。 The invention relates to a device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution, and belongs to the technical field of chemical engineering separation.
背景技术 Background technique
从稀溶液中回收高沸点有机物在生物质燃料提取、废水净化等领域应用范围广泛。糠醛和苯胺分别是胺类和呋喃环系最具代表性的高沸点有机物之一,从稀溶液中分离直接获得高纯度糠醛和苯胺具有重要的价值。 The recovery of high-boiling point organics from dilute solutions has a wide range of applications in the fields of biomass fuel extraction and wastewater purification. Furfural and aniline are one of the most representative high-boiling point organic compounds of amines and furan ring systems respectively, and it is of great value to directly obtain high-purity furfural and aniline from dilute solutions.
糠醛(学名呋喃甲醛)的生产是通过酸性水解生物质(玉米芯、棉子壳等)原料中的半纤维素物质得到。经水解后的水解液中糠醛的质量百分含量约为2~8 wt%,目前国内糠醛厂采用蒸馏法从水解液中分离提纯糠醛,第一次为初精馏,可以将糠醛浓度提高至90 wt%~92 wt%(水与糠醛恒沸点时的浓度),然后再采用多级精馏进行糠醛的精制。精馏过程会消耗大量的蒸汽,因此能耗占糠醛生产成本的很大比重,如何降低糠醛分离回收的能耗是研究的热点。 The production of furfural (scientific name: furan formaldehyde) is obtained by acid hydrolyzing the hemicellulose material in the raw material of biomass (corncob, cottonseed hull, etc.). The mass percentage of furfural in the hydrolyzed solution after hydrolysis is about 2~8 wt%. At present, domestic furfural factories use distillation to separate and purify furfural from the hydrolyzed solution. The first time is primary rectification, which can increase the concentration of furfural to 90 wt%~92 wt% (concentration at the constant boiling point of water and furfural), and then use multi-stage rectification to refine furfural. The rectification process consumes a large amount of steam, so energy consumption accounts for a large proportion of furfural production cost. How to reduce the energy consumption of furfural separation and recovery is a research hotspot.
中国专利CN103214439A公开了一种利用装填有非极性大孔吸附树脂的固定床吸附水解液中的糠醛,然后再通过洗脱剂解吸得到较高浓度的糠醛洗脱液,最后再经过处理后得到糠醛目标产品,该吸附-解吸的工艺较繁琐,设备投资大。中国专利CN103254158A公开了利用生物质水解耦合渗透汽化分离生产糠醛的方法及装置:渗透汽化膜对水解液中糠醛具有高的吸附选择性,当膜吸附平衡后在膜的下游通过抽真空将膜中优先吸附的糠醛和少量水以低压混合蒸汽的形式解吸出来,最后再将糠醛与水蒸汽冷凝收集,此工艺收集的糠醛仍然需要进一步精制,并且糠醛的精制过程耗能很大。 Chinese patent CN103214439A discloses a fixed bed filled with non-polar macroporous adsorption resin to absorb furfural in the hydrolyzate, and then desorb the eluent to obtain a higher concentration of furfural eluate, and finally obtain The target product of furfural, the adsorption-desorption process is cumbersome and requires a large investment in equipment. Chinese patent CN103254158A discloses a method and device for producing furfural using biomass hydrolysis coupled with pervaporation separation: the pervaporation membrane has high adsorption selectivity for furfural in the hydrolyzate, and when the membrane adsorption is balanced, the downstream of the membrane is vacuumed to remove the furfural in the membrane. The preferentially adsorbed furfural and a small amount of water are desorbed in the form of low-pressure mixed steam, and finally the furfural and water vapor are condensed and collected. The furfural collected by this process still needs to be further refined, and the refining process of furfural consumes a lot of energy.
苯胺是化工行业重要的中间体之一,在染料、农药、橡胶助剂等行业中具有广泛应用,废水中苯胺含量较高(质量分数1wt%~3wt%),目前工业上常用的苯胺废水处理手段有萃取法、吸附法。吸附法不适宜处理浓度较高的苯胺废水,并且吸附剂的再生较困难,经过几次再生后,吸附容量损失较大。萃取法 (CN1600696A、CN102936079A)容易造成水体的二次污染,需要多级萃取,设备投资大,并且难以得到可以回用的高纯度苯胺。 Aniline is one of the important intermediates in the chemical industry. It is widely used in dyestuffs, pesticides, rubber additives and other industries. The content of aniline in wastewater is relatively high (mass fraction 1wt%~3wt%). Currently, aniline wastewater treatment commonly used in industry Methods include extraction and adsorption. The adsorption method is not suitable for treating high-concentration aniline wastewater, and the regeneration of the adsorbent is difficult. After several regenerations, the adsorption capacity will be greatly lost. Extraction method (CN1600696A, CN102936079A) is easy to cause secondary pollution of water body, requires multi-stage extraction, equipment investment is large, and it is difficult to obtain high-purity aniline that can be reused.
发明内容 Contents of the invention
针对糠醛生产能耗大、苯胺废水处理工艺繁琐这种现状,本发明旨在提供一种低能耗、流程简单的渗透汽化-分级冷凝耦合装置及工艺分离回收低浓度水溶液中的高沸点、水溶性有机物—糠醛与苯胺。 Aiming at the current situation that the production of furfural consumes a lot of energy and the treatment process of aniline wastewater is cumbersome, the present invention aims to provide a pervaporation-staged condensation coupling device with low energy consumption and simple flow process, and the process separates and recovers high boiling point and water solubility in low-concentration aqueous solution. Organic matter - furfural and aniline.
本发明提供的一种从低浓度水溶液中分离回收高沸点有机物的装置,包括渗透汽化段和分级冷凝段,所述渗透汽化段包括原料储槽、料液循环泵、渗透汽化槽,渗透汽化槽内设有渗透汽化膜组件;所述分级冷凝段包括第一级冷凝器和第二级冷凝器,第一级冷凝器和第二级冷凝器串联连接,第二级冷凝器末端与真空泵连接,第一级冷凝器下端连接第一储料罐,第二级冷凝器下端连接第二储料罐,第二储料罐通过循环泵连接原料储槽。 The present invention provides a device for separating and recovering high-boiling-point organics from low-concentration aqueous solutions, including a pervaporation section and a graded condensation section. The pervaporation section includes a raw material storage tank, a material-liquid circulation pump, a pervaporation tank, and a pervaporation tank There is a pervaporation membrane module inside; the graded condensation section includes a first-stage condenser and a second-stage condenser, the first-stage condenser and the second-stage condenser are connected in series, and the end of the second-stage condenser is connected to a vacuum pump, The lower end of the first-stage condenser is connected to the first storage tank, the lower end of the second-stage condenser is connected to the second storage tank, and the second storage tank is connected to the raw material storage tank through a circulation pump.
本发明提供的一种从低浓度水溶液中分离回收高沸点有机物的方法,包括以下步骤: A method for separating and recovering high-boiling-point organics from low-concentration aqueous solutions provided by the invention comprises the following steps:
(1) 将低浓度有机物的水溶液通入渗透汽化槽,与具有选择性分离有机物功能的渗透汽化膜在膜的上游侧充分接触并达到吸附动态平衡; (1) Pass the aqueous solution of low-concentration organic matter into the pervaporation tank, and fully contact the pervaporation membrane with the function of selectively separating organic matter on the upstream side of the membrane to achieve adsorption dynamic equilibrium;
(2) 通过真空泵在渗透汽化膜下游产生低压真空,使上游侧吸附在膜表面的高沸点有机物-水发生汽化,并透过膜在渗透汽化膜的下游侧脱附形成有机物-水低压混合蒸汽; (2) A vacuum pump is used to generate a low-pressure vacuum downstream of the pervaporation membrane, so that the high-boiling organic matter-water adsorbed on the surface of the membrane on the upstream side is vaporized, and desorbed through the membrane on the downstream side of the pervaporation membrane to form organic matter-water low-pressure mixed steam ;
(3) 将膜的下游侧富集的有机物-水低压混合蒸汽依次通入两个串联的冷凝器,依据绝压数值大小选择第一冷凝器温度范围,在第一级冷凝器中获得高纯度液态高沸点有机物,纯度大于99.9wt%; (3) Pass the organic matter-water low-pressure mixed steam enriched on the downstream side of the membrane into two series-connected condensers in sequence, select the temperature range of the first condenser according to the absolute pressure value, and obtain high purity in the first-stage condenser Liquid high-boiling organic matter with a purity greater than 99.9wt%;
(4)未被冷凝的水蒸汽与小部分有机蒸汽被截留在第二级冷凝器中,第二级冷凝器与渗透汽化槽连接,将小部分有机蒸汽输送到渗透汽化槽中进行二次分离回收。 (4) The uncondensed water vapor and a small part of organic vapor are trapped in the second-stage condenser, and the second-stage condenser is connected to the pervaporation tank, and a small part of organic vapor is sent to the pervaporation tank for secondary separation Recycle.
上述方案中,所述低浓度水溶液为有机物浓度在0.1~8 wt%范围的水溶液。 In the above scheme, the low-concentration aqueous solution is an aqueous solution with an organic concentration in the range of 0.1 to 8 wt%.
上述方案中,所述高沸点有机物为沸点在150~230 ℃范围的胺类和呋喃环系常温液态有机物。 In the above scheme, the high-boiling-point organic matter is an amine and a furan ring system room-temperature liquid organic matter with a boiling point in the range of 150-230°C.
上述方案中,所述高沸点有机物为糠醛或苯胺。所述糠醛水溶液的浓度为:1wt%~8wt%;苯胺水溶液的浓度为:0.1wt%~4wt%。 In the above scheme, the high-boiling organic matter is furfural or aniline. The concentration of the furfural aqueous solution is: 1wt%-8wt%; the concentration of the aniline aqueous solution is: 0.1wt%-4wt%.
上述方案中,所述的具有选择性分离有机物功能的渗透汽化膜为聚醚嵌段聚酰胺膜。 In the above solution, the pervaporation membrane with the function of selectively separating organic matter is a polyether block polyamide membrane.
上述方案中,所述渗透汽化膜下游的低压真空条件为:绝压在30~2000 Pa范围。 In the above scheme, the low-pressure vacuum condition downstream of the pervaporation membrane is: the absolute pressure is in the range of 30-2000 Pa.
上述方案中,所述的第一级冷凝器温度控制在 -30~30 ℃;第二级冷凝器的温度为-200~-50 ℃。 In the above scheme, the temperature of the first stage condenser is controlled at -30~30°C; the temperature of the second stage condenser is -200~-50°C.
上述方案中,所述低浓度有机物的水溶液的初始温度为30~95 ℃。 In the above scheme, the initial temperature of the aqueous solution of low-concentration organic matter is 30-95°C.
由于本发明提供的渗透汽化膜分离过程具有分离效率高、能耗低、工艺简单、无二次污染等优点,而且:(1)苯胺是高沸点、水溶性有机物,可以通过渗透汽化-分级冷凝耦合工艺直接从低的水溶液中回收到高纯度无色苯胺液体;(2)糠醛是高沸点(161.7℃)水溶性有机物,水解液中的糠醛可以通过渗透汽化-分级冷凝的工艺一步回收到高纯度无色糠醛液体,此法降低了从稀水解液中分离回收糠醛的能耗,具有很重要的工业应用价值。 Because the pervaporation membrane separation process provided by the present invention has the advantages of high separation efficiency, low energy consumption, simple process, and no secondary pollution, and: (1) aniline is a high-boiling, water-soluble organic substance that can be condensed through pervaporation-gradation The coupling process directly recovers high-purity colorless aniline liquid from the low water solution; (2) furfural is a water-soluble organic compound with a high boiling point (161.7°C), and the furfural in the hydrolyzed solution can be recovered to high Purity colorless furfural liquid, this method reduces the energy consumption of separating and recovering furfural from dilute hydrolyzate, has very important industrial application value.
本发明的工作原理:由于渗透汽化膜分离具有不受汽液平衡限制的优点,具有高吸附选择性渗透汽化膜优先吸附低浓度水溶液中的有机物,然后膜的另一侧抽真空使吸附的有机物与少量水汽化,最后将被膜富集的低压有机蒸汽(有机物具有较高的沸点)与水蒸汽进行分级冷凝,容易冷凝的有机蒸汽首先被截留在第一级冷凝器中,未被冷凝的水蒸汽与小部分有机蒸汽被截留在第二级冷凝器中。通过渗透汽化-分级冷凝工艺,其中高沸点、水溶性的苯胺、糠醛从各自低浓度水溶液中被提取出来,并且回收的糠醛与苯胺的纯度均大于99.9wt%。 The working principle of the present invention: because the pervaporation membrane separation has the advantage of not being limited by the vapor-liquid equilibrium, it has high adsorption selectivity. The pervaporation membrane preferentially adsorbs organic matter in low-concentration aqueous solution, and then the other side of the membrane is vacuumed to make the adsorbed organic matter Vaporize with a small amount of water, and finally condense the low-pressure organic vapor enriched by the film (organic matter has a higher boiling point) and water vapor in stages. The easily condensed organic vapor is first trapped in the first-stage condenser, and the uncondensed water Vapor and a small part of organic vapor are trapped in the second stage condenser. Through the pervaporation-fractional condensation process, the high-boiling, water-soluble aniline and furfural are extracted from their respective low-concentration aqueous solutions, and the purity of the recovered furfural and aniline is greater than 99.9wt%.
本发明的有益效果: Beneficial effects of the present invention:
(1)通过渗透汽化-分级冷凝耦合工艺可以从低浓度水溶液中直接分离获得高纯度高沸点液态有机物; (1) High-purity and high-boiling-point liquid organic compounds can be directly separated from low-concentration aqueous solutions through the pervaporation-staged condensation coupling process;
(2)分离过程无需添加化学试剂,无二次污染; (2) There is no need to add chemical reagents during the separation process, and there is no secondary pollution;
(3)分离过程中原料液的温度控制在较低的温度(低于95 ℃)下操作,能耗低且分离效率高; (3) During the separation process, the temperature of the raw material liquid is controlled at a relatively low temperature (less than 95°C), with low energy consumption and high separation efficiency;
(4)耦合工艺流程简单、操作方便,获得的高纯度有机物无需进一步纯化; (4) The coupling process is simple and easy to operate, and the obtained high-purity organic matter does not need further purification;
(5)首次将分级冷凝工艺应用于渗透汽化法回收高沸点有机物,增加了第二级冷凝器,使苯胺或糠醛产品的回收利用率高。 (5) For the first time, the staged condensation process is applied to the pervaporation method to recover high-boiling organic matter, and a second-stage condenser is added to increase the recovery rate of aniline or furfural products.
附图说明 Description of drawings
图1是本发明渗透汽化-分级冷凝工艺流程示意图。 Fig. 1 is a schematic flow chart of the pervaporation-fractionated condensation process of the present invention.
图中:1-原料储槽;2-料液循环泵;3-渗透汽化槽;4-第一级冷凝器;5-第二级冷凝器;6-真空泵;7-阀门,8-第一储料罐;9-第二储料罐;10-残液循环泵。 In the figure: 1-raw material storage tank; 2-material liquid circulation pump; 3-pervaporation tank; 4-first-stage condenser; 5-second-stage condenser; 6-vacuum pump; 7-valve, 8-first Storage tank; 9-the second storage tank; 10-residual liquid circulation pump.
具体实施方式 Detailed ways
下面通过实施例来进一步说明本发明,但不局限于以下实施例。 The present invention is further illustrated by the following examples, but not limited to the following examples.
实施例1:从低浓度水溶液中分离回收高沸点有机物的装置 Embodiment 1: The device that separates and recovers high-boiling-point organic matter from low-concentration aqueous solution
如图1所示,包括渗透汽化段和分级冷凝段,所述渗透汽化段包括原料储槽1、料液循环泵2、渗透汽化槽3,渗透汽化槽3内设有渗透汽化膜组件;所述分级冷凝段包括第一级冷凝器4和第二级冷凝器5,第一级冷凝器4和第二级冷凝器5串联连接,第二级冷凝器5与真空泵6连接,即在两级冷凝器末端连接真空泵,第一级冷凝器4下端通过阀门7连接第一储料罐8,第二级冷凝器5下端通过阀门连接第二储料罐9,第二储料罐9通过残液循环泵10连接原料储槽1。冷凝后产品通过阀门控制进入到储料罐中。 As shown in Figure 1, it includes a pervaporation section and a graded condensation section. The pervaporation section includes a raw material storage tank 1, a feed liquid circulation pump 2, and a pervaporation tank 3, and a pervaporation membrane module is arranged in the pervaporation tank 3; The graded condensation section includes a first-stage condenser 4 and a second-stage condenser 5, the first-stage condenser 4 and the second-stage condenser 5 are connected in series, and the second-stage condenser 5 is connected with a vacuum pump 6, that is, in two stages The end of the condenser is connected to a vacuum pump, the lower end of the first-stage condenser 4 is connected to the first storage tank 8 through a valve 7, the lower end of the second-stage condenser 5 is connected to the second storage tank 9 through a valve, and the second storage tank 9 passes through the residual liquid The circulation pump 10 is connected to the raw material storage tank 1 . After condensation, the product enters into the storage tank through valve control.
采用上述装置分离回收高沸点有机物的工艺过程为: The technological process of adopting the above-mentioned device to separate and recover high-boiling point organic matter is as follows:
由于渗透汽化膜分离具有不受汽液平衡限制的优点,具有高吸附选择性渗透汽化膜优先吸附低浓度水溶液中的有机物,然后膜的另一侧抽真空使吸附的有机物与少量水汽化,最后将被膜富集的低压有机蒸汽(有机物具有较高的沸点)与水蒸汽进行分级冷凝,容易冷凝的有机蒸汽首先被截留在第一级冷凝器中,冷凝后进入第一储料罐中,未被冷凝的水蒸汽与小部分有机蒸汽被截留在第二级冷凝器中,冷凝后进入第二储料罐中,第二储料罐中的液体经残液循环泵进入到原料储槽中。通过渗透汽化-分级冷凝工艺,其中高沸点、水溶性的苯胺、糠醛从各自低浓度水溶液中被提取出来,并且回收的糠醛与苯胺的纯度均大于99.9wt%。 Because pervaporation membrane separation has the advantage of not being limited by vapor-liquid equilibrium, it has high adsorption selectivity. Pervaporation membrane preferentially adsorbs organic matter in low-concentration aqueous solution, and then the other side of the membrane is vacuumed to vaporize the adsorbed organic matter and a small amount of water, and finally The low-pressure organic vapor (organic matter has a higher boiling point) enriched by the membrane is condensed in stages with water vapor. The organic vapor that is easy to condense is first trapped in the first-stage condenser, and then enters the first storage tank after condensation. The condensed water vapor and a small part of organic vapor are trapped in the second-stage condenser and enter the second storage tank after condensation. The liquid in the second storage tank enters the raw material storage tank through the raffinate circulation pump. Through the pervaporation-fractional condensation process, the high-boiling, water-soluble aniline and furfural are extracted from their respective low-concentration aqueous solutions, and the purity of the recovered furfural and aniline is greater than 99.9wt%.
实施例2:从低浓度水溶液中分离回收高沸点糠醛 Embodiment 2: Separation and recovery of high boiling point furfural from low concentration aqueous solution
(1) 将浓度为2 wt%的糠醛水溶液加热至80℃,通过料液循环泵将糠醛水溶液以流速120 L/h循环通入渗透汽化槽中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the furfural aqueous solution with a concentration of 2 wt% to 80°C, and circulate the furfural aqueous solution into the pervaporation tank at a flow rate of 120 L/h through the feed liquid circulation pump, so that the membrane adsorption reaches equilibrium, and the pervaporation in the membrane module The area of the membrane is 20.4 cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,,使膜下游压力维持在绝压30 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is evacuated to maintain the pressure downstream of the membrane at an absolute pressure of 30 Pa;
(3)将糠醛与水的低压混合蒸汽引入温度为-29℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的糠醛与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃; (3) Introduce the low-pressure mixed steam of furfural and water into the first-stage condenser with a temperature of -29°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of furfural and water that has not been condensed into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C;
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的糠醛纯度为99.92 wt%,收集速率为240 g/(m2·h);第二级冷凝器中收集的糠醛纯度为25 wt%,收集速率为610 g/(m2·h)。 (4) The purity of furfural collected in the first-stage condenser was 99.92 wt%, and the collection rate was 240 g/(m 2 h) measured by Karl Fischer moisture meter; the purity of furfural collected in the second-stage condenser was 25 wt%, the collection rate is 610 g/(m 2 ·h).
实施例3:从低浓度水溶液中分离回收高沸点糠醛 Embodiment 3: Separation and recovery of high boiling point furfural from low concentration aqueous solution
(1) 将浓度为3 wt%的糠醛水溶液加热至60℃,用泵将糠醛水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the furfural aqueous solution with a concentration of 3 wt% to 60 °C, and circulate the furfural aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h with a pump, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,,使膜下游压力维持在绝压250 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is vacuumed to maintain the pressure downstream of the membrane at an absolute pressure of 250 Pa;
(3)将糠醛与水的低压混合蒸汽引入温度为-8℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的糠醛与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of furfural and water into the first-stage condenser with a temperature of -8°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of furfural and water that has not been condensed into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的糠醛纯度为99.94 wt%,收集速率为270 g/(m2·h);第二级冷凝器中收集的糠醛纯度为27 wt%,收集速率为320 g/(m2·h)。 (4) The purity of furfural collected in the first-stage condenser was 99.94 wt%, and the collection rate was 270 g/(m 2 h) as measured by Karl Fischer moisture meter; the purity of furfural collected in the second-stage condenser was 27 wt%, the collection rate is 320 g/(m 2 ·h).
实施例4:从低浓度水溶液中分离回收高沸点糠醛 Embodiment 4: Separation and recovery of high boiling point furfural from low concentration aqueous solution
(1) 将浓度为5 wt%的糠醛水溶液加热至70℃,用泵将糠醛水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the furfural aqueous solution with a concentration of 5 wt% to 70 °C, and circulate the furfural aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h with a pump, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,使膜下游压力维持在绝压1000 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is vacuumed to maintain the pressure downstream of the membrane at an absolute pressure of 1000 Pa;
(3)将糠醛与水的低压混合蒸汽引入温度为10 ℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的糠醛与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of furfural and water into the first-stage condenser with a temperature of 10 °C and a heat exchange area of 0.1 m2 , and introduce the low-pressure mixed steam of furfural and water that has not been condensed into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的糠醛纯度为99.95 wt%,收集速率为492 g/(m2·h);第二级冷凝器中收集的糠醛纯度为29 wt%,收集速率为510 g/(m2·h)。 (4) The purity of furfural collected in the first-stage condenser was 99.95 wt%, and the collection rate was 492 g/(m 2 h) measured by Karl Fischer moisture meter; the purity of furfural collected in the second-stage condenser was 29 wt%, the collection rate is 510 g/(m 2 ·h).
实施例5:从低浓度水溶液中分离回收高沸点苯胺 Embodiment 5: Separation and recovery of high boiling point aniline from low concentration aqueous solution
(1) 将浓度为1 wt%的苯胺水溶液加热至80℃,用泵将苯胺水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the aniline aqueous solution with a concentration of 1 wt% to 80°C, and use a pump to circulate the aniline aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,,使膜下游压力维持在绝压50 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is evacuated to maintain the pressure downstream of the membrane at an absolute pressure of 50 Pa;
(3)将苯胺与水的低压混合蒸汽引入温度为-25℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的苯胺与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of aniline and water into the first-stage condenser with a temperature of -25°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of uncondensed aniline and water into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的苯胺纯度为99.91 wt%,收集速率为395 g/(m2·h);第二级冷凝器中收集的苯胺纯度为1 wt%,收集速率为410 g/(m2·h)。 (4) The purity of the aniline collected in the first-stage condenser was 99.91 wt%, and the collection rate was 395 g/(m 2 h) as measured by the Karl Fischer moisture meter; the purity of the aniline collected in the second-stage condenser was 1 wt%, the collection rate is 410 g/(m 2 ·h).
实施例6:从低浓度水溶液中分离回收高沸点苯胺 Embodiment 6: Separation and recovery of high boiling point aniline from low concentration aqueous solution
(1) 将浓度为0.2 wt%的苯胺水溶液加热至70℃,用泵将苯胺水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the aniline aqueous solution with a concentration of 0.2 wt% to 70°C, and circulate the aniline aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h with a pump, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,使膜下游压力维持在绝压500 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is evacuated to maintain the pressure downstream of the membrane at an absolute pressure of 500 Pa;
(3)将苯胺与水的低压混合蒸汽引入温度为3℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的苯胺与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of aniline and water into the first-stage condenser with a temperature of 3°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of uncondensed aniline and water into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的苯胺纯度为99.94 wt%,收集速率为50 g/(m2·h);第二级冷凝器中收集的苯胺纯度为10 wt%,收集速率为400 g/(m2·h)。 (4) The purity of the aniline collected in the first-stage condenser was 99.94 wt% measured by Karl Fischer moisture meter, and the collection rate was 50 g/(m 2 h); the purity of the aniline collected in the second-stage condenser was 10 wt%, the collection rate is 400 g/(m 2 ·h).
实施例7:从低浓度水溶液中分离回收高沸点苯胺 Embodiment 7: Separation and recovery of high boiling point aniline from low concentration aqueous solution
(1) 将浓度为3 wt%的苯胺水溶液加热至60℃,用泵将苯胺水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the aniline aqueous solution with a concentration of 3 wt% to 60°C, and circulate the aniline aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h with a pump, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,,使膜下游压力维持在绝压1200 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is evacuated to maintain the pressure downstream of the membrane at an absolute pressure of 1200 Pa;
(3)将苯胺与水的低压混合蒸汽引入温度为13℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的苯胺与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of aniline and water into the first-stage condenser with a temperature of 13°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of uncondensed aniline and water into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的苯胺纯度为99.93 wt%,收集速率为90 g/(m2·h);第二级冷凝器中收集的苯胺纯度为12 wt%,收集速率为380 g/(m2·h)。 (4) The purity of the aniline collected in the first-stage condenser was 99.93 wt%, and the collection rate was 90 g/(m 2 h) as measured by the Karl Fischer moisture meter; the purity of the aniline collected in the second-stage condenser was 12 wt%, the collection rate is 380 g/(m 2 ·h).
实施例8:从低浓度水溶液中分离回收高沸点苯胺 Embodiment 8: Separation and recovery of high boiling point aniline from low concentration aqueous solution
(1) 将浓度为2 wt%的苯胺水溶液加热至50℃,用泵将苯胺水溶液以流速120 L/h循环通入渗透汽化膜组件中,使膜吸附达到平衡,膜组件中渗透汽化膜的面积为20.4cm2; (1) Heat the aniline aqueous solution with a concentration of 2 wt% to 50°C, and circulate the aniline aqueous solution into the pervaporation membrane module at a flow rate of 120 L/h with a pump, so that the membrane adsorption reaches equilibrium, and the pervaporation membrane in the membrane module The area is 20.4cm 2 ;
(2)在膜的下游侧,两级冷凝器的末端抽真空,,使膜下游压力维持在绝压250 Pa; (2) On the downstream side of the membrane, the end of the two-stage condenser is vacuumed to maintain the pressure downstream of the membrane at an absolute pressure of 250 Pa;
(3)将苯胺与水的低压混合蒸汽引入温度为20℃、换热面积为0.1 m2的第一级冷凝器中,未被冷凝的苯胺与水的低压混合蒸汽引入与第一级冷凝器串联的第二级冷凝器中,第二级冷凝器温度为-196℃。 (3) Introduce the low-pressure mixed steam of aniline and water into the first-stage condenser with a temperature of 20°C and a heat exchange area of 0.1 m 2 , and introduce the low-pressure mixed steam of uncondensed aniline and water into the first-stage condenser In the second-stage condenser connected in series, the temperature of the second-stage condenser is -196°C.
(4)采用卡尔费休水分仪测得第一级冷凝器中收集的苯胺纯度为99.96 wt%,收集速率为104 g/(m2·h);第二级冷凝器中收集的苯胺纯度为47 wt%,收集速率为395 g/(m2·h)。 (4) The purity of the aniline collected in the first-stage condenser was 99.96 wt%, and the collection rate was 104 g/(m 2 h) as measured by the Karl Fischer moisture meter; the purity of the aniline collected in the second-stage condenser was 47 wt%, the collection rate is 395 g/(m 2 ·h).
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510040321.9A CN104587834A (en) | 2015-01-27 | 2015-01-27 | Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510040321.9A CN104587834A (en) | 2015-01-27 | 2015-01-27 | Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution |
Publications (1)
Publication Number | Publication Date |
---|---|
CN104587834A true CN104587834A (en) | 2015-05-06 |
Family
ID=53114093
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510040321.9A Pending CN104587834A (en) | 2015-01-27 | 2015-01-27 | Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104587834A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108176072A (en) * | 2017-12-29 | 2018-06-19 | 苏州浙远自动化工程技术有限公司 | Automatic control method for impurity removal of alcohol rectifying tower in traditional Chinese medicine production process |
CN110538480A (en) * | 2019-09-25 | 2019-12-06 | 上海电气集团股份有限公司 | condensing system and condensing method |
CN111115939A (en) * | 2020-02-24 | 2020-05-08 | 上海电气集团股份有限公司 | Organic wastewater treatment system and method |
CN111203109A (en) * | 2020-01-15 | 2020-05-29 | 南京工业大学 | Novel pervaporation circulation heat exchange system and method |
CN112537873A (en) * | 2020-10-12 | 2021-03-23 | 太原理工大学 | Treatment process and device for coal chemical wastewater containing fine dust |
CN114716098A (en) * | 2022-03-25 | 2022-07-08 | 上海电气集团股份有限公司 | Treatment method and treatment system for crystalline silicon texturing wastewater |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5385647A (en) * | 1988-02-11 | 1995-01-31 | Deutsche Carbone Ag | Process for the reduction of the alcohol content of alcoholic beverages |
CN1373181A (en) * | 2002-03-14 | 2002-10-09 | 南京大学 | Process for preparing low-alcohol or non-alcohol beverage from raw juice fermented wine |
CN201873680U (en) * | 2010-07-07 | 2011-06-22 | 中国石油化工股份有限公司 | System device for ethanol fermentation and separation and coupling based on pervaporation membrane |
CN103254158A (en) * | 2013-05-21 | 2013-08-21 | 北京化工大学 | Method and device for producing furfural by using biomass hydrolysis coupling pervaporation separation technology |
CN103657458A (en) * | 2013-12-25 | 2014-03-26 | 大连欧科膜技术工程有限公司 | PEBA (Polyether block amide) composite film as well as preparation method and application thereof |
-
2015
- 2015-01-27 CN CN201510040321.9A patent/CN104587834A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5385647A (en) * | 1988-02-11 | 1995-01-31 | Deutsche Carbone Ag | Process for the reduction of the alcohol content of alcoholic beverages |
CN1373181A (en) * | 2002-03-14 | 2002-10-09 | 南京大学 | Process for preparing low-alcohol or non-alcohol beverage from raw juice fermented wine |
CN201873680U (en) * | 2010-07-07 | 2011-06-22 | 中国石油化工股份有限公司 | System device for ethanol fermentation and separation and coupling based on pervaporation membrane |
CN103254158A (en) * | 2013-05-21 | 2013-08-21 | 北京化工大学 | Method and device for producing furfural by using biomass hydrolysis coupling pervaporation separation technology |
CN103657458A (en) * | 2013-12-25 | 2014-03-26 | 大连欧科膜技术工程有限公司 | PEBA (Polyether block amide) composite film as well as preparation method and application thereof |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108176072A (en) * | 2017-12-29 | 2018-06-19 | 苏州浙远自动化工程技术有限公司 | Automatic control method for impurity removal of alcohol rectifying tower in traditional Chinese medicine production process |
CN110538480A (en) * | 2019-09-25 | 2019-12-06 | 上海电气集团股份有限公司 | condensing system and condensing method |
CN110538480B (en) * | 2019-09-25 | 2024-09-17 | 上海电气集团股份有限公司 | Condensing system and condensing method |
CN111203109A (en) * | 2020-01-15 | 2020-05-29 | 南京工业大学 | Novel pervaporation circulation heat exchange system and method |
CN111115939A (en) * | 2020-02-24 | 2020-05-08 | 上海电气集团股份有限公司 | Organic wastewater treatment system and method |
CN112537873A (en) * | 2020-10-12 | 2021-03-23 | 太原理工大学 | Treatment process and device for coal chemical wastewater containing fine dust |
CN114716098A (en) * | 2022-03-25 | 2022-07-08 | 上海电气集团股份有限公司 | Treatment method and treatment system for crystalline silicon texturing wastewater |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104587834A (en) | Device and method for separating and recovering high-boiling-point organic matter from low-concentration aqueous solution | |
CN105001056B (en) | A kind of pressure swing rectification separates the method of isobutanol and n-heptane azeotropic system | |
CN104027996A (en) | A pervaporation rectification coupled system and a use thereof | |
US20110237833A1 (en) | Recovery and purification process for organic molecules | |
CN103551036A (en) | High-efficiency permeation and evaporation device and technology of ceramic molecular sieve membrane | |
CN104891591B (en) | Carbon fiber production wastewater separation treatment and resource utilization process method and device | |
CN106045872A (en) | Recovery system and method for dimethylformamide waste liquid by pervaporation method | |
JP2013018748A (en) | Nmp purification system in electrode production process | |
CN114315641A (en) | Purification and recovery method of acetonitrile waste liquid | |
CN107778166B (en) | A kind of method of heat pump rectification system recovery of acetic acid from low-concentration acetic acid wastewater | |
CN109180614B (en) | Purification process of tetrahydrofuran in mixture of hexane, tetrahydrofuran and water | |
CN105541553B (en) | A kind of high-efficient liquid phase chromatogram HPLC solvent prepares purification process and device | |
CN111943811A (en) | Energy-saving absolute ethyl alcohol membrane separation refining method | |
CN102764559B (en) | Combined technique of separating and recycling VOCS (volatile organic compounds) from industrial waste gas by adsorption-desorption-rectification-pervaporation | |
CN107011246B (en) | Method for dehydrating and desalting triacetonamine synthetic liquid | |
CN104923026A (en) | Polysilicon tail gas recovering method and device thereof | |
CN106631744B (en) | A kind of method for extraction-pressure swing rectification coupling separation water-acetone-isopropyl ether ternary system | |
CN214680074U (en) | Three-effect thermal coupling molecular sieve dehydration energy-saving system | |
CN106986769B (en) | Separation and integration system and separation and integration method of ethyl acetate-water system | |
WO2019061593A1 (en) | Method for extracting high-purity ethoxyquinoline by using multistage molecular distillation technology | |
CN220531232U (en) | Ethanol membrane separation dehydration purification device | |
CN113372242A (en) | Purification method of water-containing acetonitrile | |
CN110787638B (en) | Concentration system and concentration method of pentanediamine | |
CN102557900B (en) | Method for refining aldehydes by pervaporation dehydration | |
CN205528523U (en) | High performance liquid chromatography HPLC solvent preparation purification device |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20150506 |
|
RJ01 | Rejection of invention patent application after publication |