CN114989019A - Acidic ionic liquid recovery method based on bipolar membrane electrodialysis-ultrafiltration - Google Patents
Acidic ionic liquid recovery method based on bipolar membrane electrodialysis-ultrafiltration Download PDFInfo
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- 238000000108 ultra-filtration Methods 0.000 title claims abstract description 57
- 239000012528 membrane Substances 0.000 title claims abstract description 47
- 239000011831 acidic ionic liquid Substances 0.000 title claims abstract description 45
- 238000011084 recovery Methods 0.000 title claims abstract description 36
- 238000000034 method Methods 0.000 title claims abstract description 29
- RTZKZFJDLAIYFH-UHFFFAOYSA-N Diethyl ether Chemical compound CCOCC RTZKZFJDLAIYFH-UHFFFAOYSA-N 0.000 claims abstract description 38
- 239000002253 acid Substances 0.000 claims abstract description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 34
- 238000000909 electrodialysis Methods 0.000 claims abstract description 30
- 239000007788 liquid Substances 0.000 claims abstract description 28
- 238000002156 mixing Methods 0.000 claims abstract description 26
- 239000002608 ionic liquid Substances 0.000 claims abstract description 21
- 239000000706 filtrate Substances 0.000 claims abstract description 20
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000000203 mixture Substances 0.000 claims abstract description 12
- 239000006228 supernatant Substances 0.000 claims abstract description 12
- 150000007522 mineralic acids Chemical group 0.000 claims abstract description 10
- 150000002894 organic compounds Chemical group 0.000 claims abstract description 10
- 229920005610 lignin Polymers 0.000 claims abstract description 9
- 239000002994 raw material Substances 0.000 claims abstract description 8
- 239000007795 chemical reaction product Substances 0.000 claims abstract description 6
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 6
- 239000012535 impurity Substances 0.000 claims abstract description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 25
- 239000012153 distilled water Substances 0.000 claims description 14
- 238000006243 chemical reaction Methods 0.000 claims description 12
- 238000002390 rotary evaporation Methods 0.000 claims description 10
- 238000000605 extraction Methods 0.000 claims description 6
- 230000002378 acidificating effect Effects 0.000 claims description 5
- JNONJXMVMJSMTC-UHFFFAOYSA-N hydron;triethylazanium;sulfate Chemical compound OS(O)(=O)=O.CCN(CC)CC JNONJXMVMJSMTC-UHFFFAOYSA-N 0.000 claims description 5
- 230000035484 reaction time Effects 0.000 claims description 3
- 238000005406 washing Methods 0.000 claims 1
- 238000011069 regeneration method Methods 0.000 abstract description 10
- 230000008929 regeneration Effects 0.000 abstract description 6
- 238000005192 partition Methods 0.000 abstract 1
- ZMANZCXQSJIPKH-UHFFFAOYSA-N Triethylamine Chemical compound CCN(CC)CC ZMANZCXQSJIPKH-UHFFFAOYSA-N 0.000 description 99
- 239000000243 solution Substances 0.000 description 49
- -1 hydrogen ions Chemical class 0.000 description 12
- 239000002028 Biomass Substances 0.000 description 8
- 239000008367 deionised water Substances 0.000 description 6
- 229910021641 deionized water Inorganic materials 0.000 description 6
- 239000001257 hydrogen Substances 0.000 description 6
- 229910052739 hydrogen Inorganic materials 0.000 description 6
- 239000012046 mixed solvent Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 4
- 150000002500 ions Chemical class 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 239000002904 solvent Substances 0.000 description 4
- ZMANZCXQSJIPKH-UHFFFAOYSA-O triethylammonium ion Chemical compound CC[NH+](CC)CC ZMANZCXQSJIPKH-UHFFFAOYSA-O 0.000 description 4
- 150000001450 anions Chemical class 0.000 description 3
- 150000001768 cations Chemical class 0.000 description 3
- 238000005119 centrifugation Methods 0.000 description 3
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- 239000005457 ice water Substances 0.000 description 3
- 239000011802 pulverized particle Substances 0.000 description 3
- IAZDPXIOMUYVGZ-WFGJKAKNSA-N Dimethyl sulfoxide Chemical compound [2H]C([2H])([2H])S(=O)C([2H])([2H])[2H] IAZDPXIOMUYVGZ-WFGJKAKNSA-N 0.000 description 2
- 238000005481 NMR spectroscopy Methods 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 239000003014 ion exchange membrane Substances 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- ZNNXXAURXKYLQY-UHFFFAOYSA-N 1-butyl-3-methyl-2h-imidazole;sulfuric acid Chemical compound OS(O)(=O)=O.CCCCN1CN(C)C=C1 ZNNXXAURXKYLQY-UHFFFAOYSA-N 0.000 description 1
- IQQRAVYLUAZUGX-UHFFFAOYSA-N 1-butyl-3-methylimidazolium Chemical compound CCCCN1C=C[N+](C)=C1 IQQRAVYLUAZUGX-UHFFFAOYSA-N 0.000 description 1
- 238000005160 1H NMR spectroscopy Methods 0.000 description 1
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000003011 anion exchange membrane Substances 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 239000000383 hazardous chemical Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 238000002329 infrared spectrum Methods 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 150000002892 organic cations Chemical class 0.000 description 1
- 239000012266 salt solution Substances 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
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Abstract
本发明涉及酸性液体回收再生技术领域,是一种基于双极膜电渗析‑超滤的酸性离子液体回收方法,步骤包括:将木质纤维素原料和待处理的酸性离子液体混合进行水热反应;反应产物用乙醇洗涤,再浓缩得到浓缩液;将水加入浓缩液中,使木质素从浓缩液中析出,得到上清液;通过超滤去除上清液中的大分子杂质,通过电渗析对超滤滤液进行处理,之后将电渗析混合室的溶液通过乙醚萃取得到有机化合物部分,将电渗析酸室溶液去除水分得到无机酸部分;将有机化合物部分和无机酸部分混合得到再生酸性离子液体;本发明对组成复杂的酸性离子液体对不同的离子成分进行分区回收,提高了离子液体的回收率和处理速度。
The invention relates to the technical field of acid liquid recovery and regeneration, and relates to an acid ionic liquid recovery method based on bipolar membrane electrodialysis-ultrafiltration. The steps include: mixing a lignocellulose raw material and an acid ionic liquid to be treated to perform a hydrothermal reaction; The reaction product is washed with ethanol, and then concentrated to obtain a concentrated solution; water is added to the concentrated solution to precipitate lignin from the concentrated solution to obtain a supernatant; the macromolecular impurities in the supernatant are removed by ultrafiltration, and electrodialysis The ultrafiltration filtrate is treated, then the solution in the electrodialysis mixing chamber is extracted with ether to obtain the organic compound part, and the water in the electrodialysis acid chamber solution is removed to obtain the inorganic acid part; the organic compound part and the inorganic acid part are mixed to obtain a regenerated acidic ionic liquid; The present invention recovers different ionic components by partition for the acidic ionic liquid with complex composition, thereby improving the recovery rate and processing speed of the ionic liquid.
Description
技术领域technical field
本发明涉及酸性液体回收再生技术领域,涉及一种基于双极膜电渗析-超滤的酸性离子液体回收方法,尤其是生物质预处理及转化过程中作为溶剂和催化剂的酸性离子液体使用后的回收与再生的技术。The invention relates to the technical field of acid liquid recovery and regeneration, and relates to a method for recovering acid ionic liquid based on bipolar membrane electrodialysis-ultrafiltration, in particular to the recovery method of acid ionic liquid used as solvent and catalyst in biomass pretreatment and conversion process. Technology for recycling and regeneration.
背景技术Background technique
突出的特点和优良的溶剂性能使酸性离子液体成为生物质加工和转化等生物质高值化过程的有效溶剂和催化剂。成本问题和有效回收手段的匮乏是制约酸性离子液体规模化用于生物质加工的主要因素。Outstanding features and excellent solvent properties make acidic ionic liquids effective solvents and catalysts for biomass high-value processes such as biomass processing and conversion. Cost issues and lack of effective recovery methods are the main factors restricting the large-scale use of acidic ionic liquids for biomass processing.
酸性离子液体如三乙铵硫酸氢盐([TEA][HSO4])、1-丁基-3-甲基咪唑硫酸氢盐([Bmim][HSO4])等,由于在溶液中会电离出有机阳离子、硫酸根离子和氢离子三种离子,用于生物质加工后难以直接全组分有效回收并再生。Acidic ionic liquids such as triethylammonium bisulfate ([TEA][HSO 4 ]), 1-butyl-3-methylimidazole bisulfate ([Bmim][HSO 4 ]), etc., will ionize in solution Organic cations, sulfate ions and hydrogen ions are produced, and it is difficult to directly recover and regenerate all components after biomass processing.
超滤技术广泛应用于工业废水净化、医药行业提纯、工业水处理等过程。超滤技术是由压力差推动溶液中的不同物质经过超滤膜,由于超滤膜对不同大小的物质的拦截能力的差异,实现对溶液中特定分子量范围物质的截留。Ultrafiltration technology is widely used in industrial wastewater purification, pharmaceutical industry purification, industrial water treatment and other processes. Ultrafiltration technology is to push different substances in the solution through the ultrafiltration membrane by the pressure difference. Due to the difference in the interception ability of the ultrafiltration membrane to substances of different sizes, the interception of substances in a specific molecular weight range in the solution is realized.
双极膜电渗析广泛应用于环境、化工、生物等领域。双极膜电渗析器膜堆由双极膜和阴阳离子膜通过一定的顺序排列。当膜堆两侧施加电压后,双极膜可将水解离,在膜两侧分别得到氢离子和氢氧根离子。同时在电场和离子交换膜对离子的选择性迁移作用下,电渗析器进料液中的阴阳离子可以和水解离的形成的氢离子和氢氧根离子进行组合。这为盐溶液中不同离子的回收、盐类转化以及酸、碱的合成提供了可能。Bipolar membrane electrodialysis is widely used in environmental, chemical, biological and other fields. The bipolar membrane electrodialyzer membrane stack consists of bipolar membranes and anion and cation membranes that pass through a certain order. When a voltage is applied on both sides of the membrane stack, the bipolar membrane can dissociate water, and hydrogen ions and hydroxide ions are obtained on both sides of the membrane, respectively. At the same time, under the selective migration of ions by the electric field and the ion exchange membrane, the anions and cations in the feed liquid of the electrodialyser can be combined with the hydrogen ions and hydroxide ions formed by the dissociation of water. This provides the possibility for the recovery of different ions in the salt solution, the conversion of salts, and the synthesis of acids and bases.
发明内容SUMMARY OF THE INVENTION
本发明克服了现有技术的不足,提出一种基于双极膜电渗析-超滤的酸性离子液体回收方法。The invention overcomes the deficiencies of the prior art, and proposes an acidic ionic liquid recovery method based on bipolar membrane electrodialysis-ultrafiltration.
为了达到上述目的,本发明是通过如下技术方案实现的。In order to achieve the above objects, the present invention is achieved through the following technical solutions.
一种基于双极膜电渗析-超滤的酸性离子液体回收方法,包括以下步骤:A method for recovering acidic ionic liquids based on bipolar membrane electrodialysis-ultrafiltration, comprising the following steps:
1)将木质纤维素原料和待处理的酸性离子液体混合进行水热反应。1) The lignocellulose raw material and the acidic ionic liquid to be treated are mixed for hydrothermal reaction.
2)将得到的反应产物用乙醇洗涤,再浓缩得到浓缩液。2) Wash the obtained reaction product with ethanol, and then concentrate to obtain a concentrated solution.
3)将水加入浓缩液中,使木质素从浓缩液中析出,得到上清液。3) Water is added to the concentrate to precipitate lignin from the concentrate to obtain a supernatant.
4)通过超滤去除上清液中的大分子杂质,得到超滤滤液。4) The macromolecular impurities in the supernatant are removed by ultrafiltration to obtain an ultrafiltration filtrate.
5)通过电渗析对超滤滤液进行处理,之后将电渗析混合室的溶液通过乙醚萃取得到有机化合物部分,将电渗析酸室溶液去除水分得到无机酸部分。5) The ultrafiltration filtrate is treated by electrodialysis, then the solution in the electrodialysis mixing chamber is extracted with ether to obtain the organic compound part, and the water in the electrodialysis acid chamber solution is removed to obtain the inorganic acid part.
6)将有机化合物部分和无机酸部分混合得到再生酸性离子液体。6) The organic compound part and the inorganic acid part are mixed to obtain a regenerated acidic ionic liquid.
优选的,步骤1)中,酸性离子液体中加入蒸馏水,酸性离子液体-蒸馏水混合物中酸性离子液体质量分数为45%-95%;酸性离子液体-蒸馏水混合物和木质纤维素原料的质量比为:1-20:1。Preferably, in step 1), distilled water is added to the acidic ionic liquid, and the mass fraction of the acidic ionic liquid in the acidic ionic liquid-distilled water mixture is 45%-95%; the mass ratio of the acidic ionic liquid-distilled water mixture to the lignocellulose raw material is: 1-20:1.
优选的,水热反应的温度为100-170℃,反应时间为10-50分钟。Preferably, the temperature of the hydrothermal reaction is 100-170° C., and the reaction time is 10-50 minutes.
优选的,超滤处理条件为:分子量截留为1K Da-0.65K Da,温度10-50℃,跨膜压100-700 kPa,错流流速:0.1-5.0 ms-1。Preferably, the ultrafiltration treatment conditions are: molecular weight cutoff of 1K Da-0.65K Da, temperature of 10-50°C, transmembrane pressure of 100-700 kPa, and cross-flow flow rate of 0.1-5.0 ms -1 .
优选的,超滤滤液用蒸馏水进行稀释处理,使超滤滤液中的有机离子浓度降低至0.01-2.0 mol/L。Preferably, the ultrafiltration filtrate is diluted with distilled water to reduce the organic ion concentration in the ultrafiltration filtrate to 0.01-2.0 mol/L.
优选的,电渗析处理采用三室双极膜电渗析装置,极室进料液为Na2SO4溶液,浓度为1.0-10.0 wt.%;混合室进料液为超滤滤液,酸室进料液为稀硫酸溶液,浓度与混合室进料液相同。Preferably, the electrodialysis treatment adopts a three-chamber bipolar membrane electrodialysis device, the electrode chamber feed liquid is Na 2 SO 4 solution with a concentration of 1.0-10.0 wt.%; the mixing chamber feed liquid is ultrafiltration filtrate, and the acid chamber feed The liquid is a dilute sulfuric acid solution with the same concentration as the feed liquid in the mixing chamber.
更优的,三室双极膜电渗析装置各室溶液初始体积均为0.5-3.0 L,施加电流密度为1-100 mA/cm2,各区溶液流速均为1.0-30.0 L/h。More preferably, the initial volume of the solution in each chamber of the three-chamber bipolar membrane electrodialysis device is 0.5-3.0 L, the applied current density is 1-100 mA/cm 2 , and the solution flow rate in each zone is 1.0-30.0 L/h.
进一步的,乙醚萃取后得到的乙醚相采用旋转蒸发分离乙醚和有机化合物部分;电渗析酸室溶液采用旋转蒸发除去酸室溶液中的水分,得到无机酸。Further, the ether phase obtained after the ether extraction adopts rotary evaporation to separate the ether and the organic compound part; the electrodialysis acid chamber solution adopts rotary evaporation to remove the water in the acid chamber solution to obtain the inorganic acid.
进一步的,步骤6)所述的混合是将无机酸部分和有机化合物部分按1:0.5-1:2摩尔比进行混合反应。Further, in the mixing described in step 6), the inorganic acid part and the organic compound part are mixed and reacted at a molar ratio of 1:0.5-1:2.
进一步的,待处理的酸性离子液体为三乙铵硫酸氢盐离子液体。Further, the acidic ionic liquid to be treated is triethylammonium hydrogen sulfate ionic liquid.
进一步的,步骤1)所述的水热反应的反应温度为100-170℃,反应时间为10-50分钟。Further, the reaction temperature of the hydrothermal reaction in step 1) is 100-170° C., and the reaction time is 10-50 minutes.
本发明相对于现有技术所产生的有益效果为:The beneficial effects that the present invention produces relative to the prior art are:
1)本发明采用了基于膜分离技术的处理方式对组成复杂的酸性离子液体对不同的离子成分进行分区回收,提高了离子液体的回收率和处理速度。同时降低了离子液体的回收成本。1) The present invention adopts the treatment method based on membrane separation technology to recover the different ionic components of the acidic ionic liquid with complex composition, which improves the recovery rate and processing speed of the ionic liquid. At the same time, the recycling cost of the ionic liquid is reduced.
2)将组成复杂的酸性离子液体的回收与再生过程转化不同离子成分的分区回收,如将酸性离子液体中的三乙铵硫酸氢盐-[TEA][HSO4]中的三乙铵根和硫酸根分别转化为三乙胺和硫酸进行回收。为后面离子液体的再生过程提供了基础。2) The recovery and regeneration process of complex acidic ionic liquids is converted into partitioned recovery of different ionic components, such as triethylammonium hydrogen sulfate in acidic ionic liquids-[TEA][HSO 4 ] triethylammonium and Sulfate is converted into triethylamine and sulfuric acid for recovery. It provides the basis for the regeneration process of ionic liquids.
3)该方法所需设备简单、工艺简便、处理时间短、条件温和且不会造成附加的环境危害,对于拓展这些组成复杂的酸性离子液体以及其他类似组成的电解质的实际应用具有参考性和指导性。3) This method requires simple equipment, simple process, short processing time, mild conditions and no additional environmental hazards, which is of reference and guidance for expanding the practical application of these complex acidic ionic liquids and other electrolytes with similar compositions sex.
附图说明Description of drawings
图1为本发明实施例1、2、3所采用的双极膜电渗析装置示意图。FIG. 1 is a schematic diagram of the bipolar membrane electrodialysis device used in Examples 1, 2, and 3 of the present invention.
图2为本发明实施例1、2、3所得再生酸性离子液体样本的傅立叶变换红外(KBr压片法)测试图。FIG. 2 is a Fourier transform infrared (KBr tablet method) test chart of the regenerated acidic ionic liquid samples obtained in Examples 1, 2, and 3 of the present invention.
图3为本发明实施例1、2、3所得再生酸性离子液体样本1H-NMR核磁(DMSO-d6为溶剂)测试图。FIG. 3 is a test chart of 1 H-NMR nuclear magnetic resonance (DMSO-d6 is the solvent) of the regenerated acidic ionic liquid samples obtained in Examples 1, 2, and 3 of the present invention.
图4为本发明所采用的双极膜电渗析所用离子交换膜的型号及参数。Figure 4 shows the model and parameters of the ion exchange membrane used in the bipolar membrane electrodialysis used in the present invention.
具体实施方式Detailed ways
为了使本发明所要解决的技术问题、技术方案及有益效果更加清楚明白,结合实施例和附图,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。下面结合实施例及附图详细说明本发明的技术方案,但保护范围不被此限制。In order to make the technical problems, technical solutions and beneficial effects to be solved by the present invention clearer, the present invention will be further described in detail with reference to the embodiments and the accompanying drawings. It should be understood that the specific embodiments described herein are only used to explain the present invention, but not to limit the present invention. The technical solutions of the present invention will be described in detail below with reference to the embodiments and the accompanying drawings, but the protection scope is not limited by this.
实施例1:一种基于双极膜电渗析-超滤的酸性离子液体回收与再生方法,具体步骤如下:Embodiment 1: a kind of acidic ionic liquid recovery and regeneration method based on bipolar membrane electrodialysis-ultrafiltration, the concrete steps are as follows:
1)将酸性离子液体与蒸馏水按比例混合,混合溶剂中酸性离子液体质量分数为:80%。木质纤维素原料粉碎、烘干后,混合溶剂与木质纤维素粉碎颗粒按5g/1g比例混合。混合均匀后,在反应釜中于150℃反应30分钟。1) Mix the acidic ionic liquid with distilled water in proportion, and the mass fraction of the acidic ionic liquid in the mixed solvent is: 80%. After the lignocellulose raw material is pulverized and dried, the mixed solvent and the lignocellulose pulverized particles are mixed in a ratio of 5g/1g. After mixing uniformly, the reaction was carried out at 150° C. for 30 minutes in a reactor.
2) 反应结束后,用热乙醇洗涤反应产物并用布氏漏斗过滤,滤液通过旋蒸除去乙醇得到浓缩液。浓缩液加去离子水后静置过夜,然后通过离心分离析出的木质素,上清液通过分子量截留为0.65K Da的超滤膜过滤,超滤处理使用的超滤膜过滤预处理木质素离心分离后得上清液,超滤处理条件为:温度25℃,跨膜压400 kPa,错流流速:2.4 ms-1。2) After the reaction, the reaction product was washed with hot ethanol and filtered with a Buchner funnel, and the filtrate was evaporated to remove ethanol to obtain a concentrated solution. The concentrated solution was added with deionized water and left to stand overnight, and then the precipitated lignin was separated by centrifugation. The supernatant was filtered through an ultrafiltration membrane with a molecular weight cut-off of 0.65K Da, and the ultrafiltration membrane used for ultrafiltration treatment pretreated lignin by centrifugal The supernatant was obtained after separation, and the ultrafiltration treatment conditions were: temperature 25°C, transmembrane pressure 400 kPa, cross-flow flow rate: 2.4 ms -1 .
3) 超滤处理所得滤液用蒸馏水进行稀释处理,处理目标为溶液中三乙铵根离子浓度降低至0.1 mol/L。3) The filtrate obtained by ultrafiltration treatment is diluted with distilled water, and the treatment goal is to reduce the concentration of triethylammonium ions in the solution to 0.1 mol/L.
4) 电渗析处理采用BP-A-BP型三室双极膜电渗析装置,极室进料液为Na2SO4溶液,浓度为5.0 wt.%。混合室进料液为稀释处理后得超滤滤液,浓度以三乙铵根离子摩尔浓度计。酸室进料液为稀硫酸溶液,浓度与混合室进料液相同。4) The electrodialysis treatment adopts a BP-A-BP three-chamber bipolar membrane electrodialysis device, and the electrode chamber feed liquid is Na 2 SO 4 solution with a concentration of 5.0 wt.%. The feed liquid of the mixing chamber is the ultrafiltration filtrate obtained after the dilution treatment, and the concentration is calculated by the molar concentration of triethylammonium ions. The acid chamber feed liquid is a dilute sulfuric acid solution with the same concentration as the mixing chamber feed liquid.
5) 电渗析器各室溶液初始体积均为1.0 L,电渗析器施加电流密度为25 mA/cm2,各区溶液流速均为15.0 L/h。5) The initial volume of the solution in each chamber of the electrodialyzer is 1.0 L, the applied current density of the electrodialyzer is 25 mA/cm 2 , and the flow rate of the solution in each zone is 15.0 L/h.
6)电渗析处理结束后,收集混合室溶液并用300 ml乙醚萃取分三次萃取,萃取结束后合并乙醚相,并采用旋转蒸发分离乙醚和三乙胺。同时,收集电渗析器的酸室溶液,采用旋转蒸发除去酸室溶液中的水分,得到浓硫酸。6) After the electrodialysis treatment, the solution in the mixing chamber was collected and extracted three times with 300 ml of ether. After the extraction, the ether phases were combined, and the ether and triethylamine were separated by rotary evaporation. At the same time, the acid chamber solution of the electrodialyzer is collected, and the water in the acid chamber solution is removed by rotary evaporation to obtain concentrated sulfuric acid.
7) 采用浓硫酸缓慢滴入三乙胺的方式,将所得浓硫酸三乙胺按1:1摩尔比于冰水浴含有一定量去离子水的烧瓶中反应, 滴加结束后保温3小时。得到淡黄色液体,在旋转蒸发仪上除去水分,即得到淡黄色酸性离子液体三乙铵硫酸氢盐-[TEA][HSO4]。7) The triethylamine is slowly dripped with concentrated sulfuric acid, and the obtained concentrated sulfuric acid triethylamine is reacted in a flask containing a certain amount of deionized water in an ice-water bath at a molar ratio of 1:1, and the dropwise addition is completed and incubated for 3 hours. A light yellow liquid was obtained, and the water was removed on a rotary evaporator to obtain a light yellow acidic ionic liquid triethylammonium hydrogen sulfate-[TEA][HSO 4 ].
该实施例对酸性离子液体[TEA][HSO4]回收率可以达到93.9%,回收过程电渗析器电流效率为87.4%,回收能耗为12.4 kwh/kg。In this example, the recovery rate of the acidic ionic liquid [TEA][HSO 4 ] can reach 93.9%, the current efficiency of the electrodialyzer in the recovery process is 87.4%, and the recovery energy consumption is 12.4 kwh/kg.
实施例2:一种基于双极膜电渗析-超滤的酸性离子液体回收与再生方法,具体步骤如下:Embodiment 2: a kind of acidic ionic liquid recovery and regeneration method based on bipolar membrane electrodialysis-ultrafiltration, the concrete steps are as follows:
1)将酸性离子液体与蒸馏水按比例混合,混合溶剂中酸性离子液体质量分数为:80%。木质纤维素原料粉碎、烘干后,混合溶剂与木质纤维素粉碎颗粒按5g/1g比例混合。混合均匀后,在反应釜中于150℃反应30分钟。1) Mix the acidic ionic liquid with distilled water in proportion, and the mass fraction of the acidic ionic liquid in the mixed solvent is: 80%. After the lignocellulose raw material is pulverized and dried, the mixed solvent and the lignocellulose pulverized particles are mixed in a ratio of 5g/1g. After mixing uniformly, the reaction was carried out at 150° C. for 30 minutes in a reactor.
2) 反应结束后,用乙醇洗涤反应产物并用布氏漏斗过滤,滤液通过旋蒸除去乙醇得到浓缩液。浓缩液加去离子水后静置过夜,然后通过离心分离析出的木质素,上清液通过分子量截留为0.65K Da的超滤膜过滤,超滤处理使用的超滤膜过滤预处理木质素离心分离后得上清液,超滤处理条件为:温度25℃,跨膜压400 kPa,错流流速:2.4 ms-1。2) After the reaction, the reaction product was washed with ethanol and filtered with a Buchner funnel, and the filtrate was evaporated to remove ethanol to obtain a concentrated solution. The concentrated solution was added with deionized water and left to stand overnight, and then the precipitated lignin was separated by centrifugation. The supernatant was filtered through an ultrafiltration membrane with a molecular weight cut-off of 0.65K Da, and the ultrafiltration membrane used for ultrafiltration treatment pretreated lignin by centrifugal The supernatant was obtained after separation, and the ultrafiltration treatment conditions were: temperature 25°C, transmembrane pressure 400 kPa, cross-flow flow rate: 2.4 ms -1 .
3) 超滤处理所得滤液用蒸馏水进行稀释处理,处理目标为溶液中三乙铵根离子浓度降低至0.2 mol/L。3) The filtrate obtained by ultrafiltration treatment is diluted with distilled water, and the treatment target is to reduce the concentration of triethylammonium ion in the solution to 0.2 mol/L.
4) 电渗析处理采用BP-A-BP型三室双极膜电渗析装置,极室进料液为Na2SO4溶液,浓度为5.0 wt.%。混合室进料液为稀释处理后得超滤滤液,浓度以三乙铵根离子摩尔浓度计。酸室进料液为稀硫酸溶液,浓度与混合室进料液相同。4) The electrodialysis treatment adopts a BP-A-BP three-chamber bipolar membrane electrodialysis device, and the electrode chamber feed liquid is Na 2 SO 4 solution with a concentration of 5.0 wt.%. The feed liquid of the mixing chamber is the ultrafiltration filtrate obtained after the dilution treatment, and the concentration is calculated by the molar concentration of triethylammonium ions. The acid chamber feed liquid is a dilute sulfuric acid solution with the same concentration as the mixing chamber feed liquid.
5) 电渗析器各室溶液初始体积均为1.0 L,电渗析器施加电流密度为25 mA/cm2,各区溶液流速均为15.0 L/h。5) The initial volume of the solution in each chamber of the electrodialyzer is 1.0 L, the applied current density of the electrodialyzer is 25 mA/cm 2 , and the flow rate of the solution in each zone is 15.0 L/h.
6)电渗析处理结束后,收集混合室溶液并用300 ml乙醚萃取分三次萃取,萃取结束后合并乙醚相,并采用旋转蒸发分离乙醚和三乙胺。同时,收集电渗析器的酸室溶液,采用旋转蒸发除去酸室溶液中的水分,得到浓硫酸。6) After the electrodialysis treatment, the solution in the mixing chamber was collected and extracted three times with 300 ml of ether. After the extraction, the ether phases were combined, and the ether and triethylamine were separated by rotary evaporation. At the same time, the acid chamber solution of the electrodialyzer is collected, and the water in the acid chamber solution is removed by rotary evaporation to obtain concentrated sulfuric acid.
7) 采用浓硫酸缓慢滴入三乙胺的方式,将所得浓硫酸和三乙胺按1:1摩尔比于冰水浴含有一定量去离子水的烧瓶中反应,滴加结束后保温3小时。得到淡黄色液体,在旋转蒸发仪上除去水分,即得到淡黄色酸性离子液体三乙铵硫酸氢盐-[TEA][HSO4]。7) The method of slowly dripping triethylamine with concentrated sulfuric acid, react the obtained concentrated sulfuric acid and triethylamine in a flask containing a certain amount of deionized water in an ice-water bath at a molar ratio of 1:1, and keep the temperature for 3 hours after the dripping is completed. A light yellow liquid was obtained, and the water was removed on a rotary evaporator to obtain a light yellow acidic ionic liquid triethylammonium hydrogen sulfate-[TEA][HSO 4 ].
该实施例对酸性离子液体[TEA][HSO4]回收率可以达到95.4%,回收过程电渗析器电流效率为89.4%,回收能耗为26.8 kwh/kg。In this example, the recovery rate of the acidic ionic liquid [TEA][HSO 4 ] can reach 95.4%, the current efficiency of the electrodialyzer in the recovery process is 89.4%, and the recovery energy consumption is 26.8 kwh/kg.
实施例3:一种基于双极膜电渗析-超滤的酸性离子液体回收与再生方法,具体步骤如下:Embodiment 3: a kind of acidic ionic liquid recovery and regeneration method based on bipolar membrane electrodialysis-ultrafiltration, the concrete steps are as follows:
1)将酸性离子液体与蒸馏水按比例混合,混合溶剂中酸性离子液体质量分数为:80%。木质纤维素原料粉碎、烘干后,混合溶剂与木质纤维素粉碎颗粒按5g/1g比例混合。混合均匀后,在反应釜中于150℃反应30分钟。1) Mix the acidic ionic liquid with distilled water in proportion, and the mass fraction of the acidic ionic liquid in the mixed solvent is: 80%. After the lignocellulose raw material is pulverized and dried, the mixed solvent is mixed with the lignocellulose pulverized particles at a ratio of 5g/1g. After mixing uniformly, the reaction was carried out at 150° C. for 30 minutes in a reactor.
2) 反应结束后,用乙醇洗涤反应产物并用布氏漏斗过滤,滤液通过旋蒸除去乙醇得到浓缩液。浓缩液加去离子水后静置过夜,然后通过离心分离析出的木质素,上清液通过分子量截留为0.65K Da的超滤膜过滤,超滤处理使用的超滤膜过滤预处理木质素离心分离后得上清液,超滤处理条件为:温度25℃,跨膜压400 kPa,错流流速:2.4 ms-1。2) After the reaction, the reaction product was washed with ethanol and filtered with a Buchner funnel, and the filtrate was evaporated to remove ethanol to obtain a concentrated solution. The concentrated solution was added with deionized water and left to stand overnight, and then the precipitated lignin was separated by centrifugation. The supernatant was filtered through an ultrafiltration membrane with a molecular weight cut-off of 0.65K Da, and the ultrafiltration membrane used for ultrafiltration treatment pretreated lignin by centrifugal The supernatant was obtained after separation, and the ultrafiltration treatment conditions were: temperature 25°C, transmembrane pressure 400 kPa, cross-flow flow rate: 2.4 ms -1 .
3) 超滤处理所得滤液用蒸馏水进行稀释处理,处理目标为溶液中三乙铵根离子浓度降低至0.3 mol/L。3) The filtrate obtained by ultrafiltration treatment is diluted with distilled water, and the treatment target is to reduce the concentration of triethylammonium ion in the solution to 0.3 mol/L.
4) 电渗析处理采用BP-A-BP型三室双极膜电渗析装置,极室进料液为Na2SO4溶液,浓度为5.0 wt.%。混合室进料液为稀释处理后得超滤滤液,浓度以三乙铵根离子摩尔浓度计。酸室进料液为稀硫酸溶液,浓度与混合室进料液相同。4) The electrodialysis treatment adopts a BP-A-BP three-chamber bipolar membrane electrodialysis device, and the electrode chamber feed liquid is Na 2 SO 4 solution with a concentration of 5.0 wt.%. The feed liquid of the mixing chamber is the ultrafiltration filtrate obtained after the dilution treatment, and the concentration is calculated by the molar concentration of triethylammonium ions. The acid chamber feed liquid is a dilute sulfuric acid solution with the same concentration as the mixing chamber feed liquid.
5) 电渗析器各室溶液初始体积均为1.0 L,电渗析器施加电流密度为20 mA/cm2,各区溶液流速均为15.0 L/h。5) The initial volume of the solution in each chamber of the electrodialyzer is 1.0 L, the applied current density of the electrodialyzer is 20 mA/cm 2 , and the flow rate of the solution in each zone is 15.0 L/h.
6)电渗析处理结束后,收集混合室溶液并用300 ml乙醚萃取分三次萃取,萃取结束后合并乙醚相,并采用旋转蒸发分离乙醚和三乙胺。同时,收集电渗析器的酸室溶液,采用旋转蒸发除去酸室溶液中的水分,得到浓硫酸。6) After the electrodialysis treatment, the solution in the mixing chamber was collected and extracted three times with 300 ml of ether. After the extraction, the ether phases were combined, and the ether and triethylamine were separated by rotary evaporation. At the same time, the acid chamber solution of the electrodialyzer is collected, and the water in the acid chamber solution is removed by rotary evaporation to obtain concentrated sulfuric acid.
7)采用浓硫酸缓慢滴入三乙胺的方式,将所得浓硫酸和三乙胺按1:1摩尔比于冰水浴含有一定量去离子水的烧瓶中反应, 滴加结束后保温3小时。得到淡黄色液体,在旋转蒸发仪上除去水分,即得到淡黄色酸性离子液体三乙铵硫酸氢盐-[TEA][HSO4]。7) Using the method of slowly dripping triethylamine with concentrated sulfuric acid, the obtained concentrated sulfuric acid and triethylamine were reacted in a flask containing a certain amount of deionized water in an ice-water bath at a molar ratio of 1:1, and the dripping was completed and incubated for 3 hours. A light yellow liquid was obtained, and the water was removed on a rotary evaporator to obtain a light yellow acidic ionic liquid triethylammonium hydrogen sulfate-[TEA][HSO 4 ].
该实施例对酸性离子液体[TEA][HSO4]回收率可以达到95.8%,回收过程电渗析器电流效率为90.3%,回收能耗为43.4 kwh/kg。In this example, the recovery rate of the acidic ionic liquid [TEA][HSO 4 ] can reach 95.8%, the current efficiency of the electrodialyzer in the recovery process is 90.3%, and the recovery energy consumption is 43.4 kwh/kg.
从图1可以看出,酸性离子液体如[TEA][HSO4],在溶液中会电离出TEA+(三乙铵根)、H+、SO4 2-三种离子。在生物质处理后,副产物生物质基阳离子CX+和生物质基阴离子AX-,与TEA+、SO4 2-和H+共同维持溶液的电荷平衡。通过如图1所示三室双极膜电渗析装置,当膜堆两侧施加电场后,混合室进料液中的SO4 2-在电场作用下通过阴离子交换膜转移至酸室(右室),与酸室产生的H+形成硫酸溶液。同时混合室(左室)生成的OH-会先后中和溶液中的H+和TEA+,生成水和三乙胺(TEA),混合室发生的主要反应如下所示。随后通过乙醚萃取、蒸馏等手段分离三乙胺,并与硫酸反应生成[TEA][HSO4]的水溶液。进一步除去多余水分即可得到[TEA][HSO4]。It can be seen from Figure 1 that acidic ionic liquids such as [TEA][HSO 4 ] will ionize three ions of TEA + (triethylammonium), H + and SO 4 2- in solution. After biomass treatment, by-product biomass-based cation C X+ and biomass-based anion A X- , together with TEA + , SO 4 2- and H + maintain the charge balance of the solution. Through the three-chamber bipolar membrane electrodialysis device shown in Figure 1, when an electric field is applied on both sides of the membrane stack, SO 4 2- in the feed liquid of the mixing chamber is transferred to the acid chamber (right chamber) through the anion exchange membrane under the action of the electric field. , forming a sulfuric acid solution with H + produced in the acid chamber. At the same time, the OH - generated in the mixing chamber (left chamber) will neutralize H + and TEA + in the solution successively to generate water and triethylamine (TEA). The main reactions that occur in the mixing chamber are shown below. Then, triethylamine is separated by ether extraction, distillation, etc., and reacted with sulfuric acid to generate an aqueous solution of [TEA][HSO 4 ]. Further removal of excess water yields [TEA][HSO 4 ].
OH-+H+→H2O (1)OH - +H + → H 2 O (1)
OH-+TEA+→H2O+ TEA (2)OH - +TEA + → H 2 O + TEA (2)
从图2可以看出,本发明实施例1、2、3所回收再生的酸性离子液体[TEA][HSO4]样品与原始的[TEA][HSO4]样品的红外谱图吸收峰位置相吻合。说明实施例1-3回收再生的酸性离子液体样品具有与原始离子液体样品一致的特征官能团。从图3可以看出,本发明实施例1、2、3所回收再生的酸性离子液体[TEA][HSO4]样品的核磁氢谱液与原始的[TEA][HSO4]样品的核磁氢谱出峰位置一致,进一步说明本发明对样品的回收可以保持其原有化学结构和组成,即通过本发明所述基于双极膜电渗析-超滤的酸性离子液体回收与再生方法可以实现酸性离子液体[TEA][HSO4]样品的有效回收与再生。It can be seen from Figure 2 that the absorption peak positions of the IR spectra of the acid ionic liquid [TEA][HSO 4 ] samples recovered and regenerated in Examples 1, 2 and 3 of the present invention are similar to those of the original [TEA][HSO 4 ] samples. match. It is illustrated that the acid ionic liquid samples recovered and regenerated in Examples 1-3 have characteristic functional groups consistent with the original ionic liquid samples. It can be seen from Fig. 3 that the H NMR liquid of the acid ionic liquid [TEA][HSO 4 ] sample recovered and regenerated in Examples 1, 2 and 3 of the present invention is the same as that of the original [TEA][HSO 4 ] sample. The peak positions of the spectrum are consistent, which further shows that the recovery of the sample in the present invention can maintain its original chemical structure and composition, that is, the acid ionic liquid recovery and regeneration method based on bipolar membrane electrodialysis-ultrafiltration according to the present invention can achieve acidity. Efficient recovery and regeneration of ionic liquid [TEA][HSO 4 ] samples.
以上内容是结合具体的优选实施方式对本发明所做的进一步详细说明,不能认定本发明的具体实施方式仅限于此,对于本发明所属技术领域的普通技术人员来说,在不脱离本发明的前提下,还可以做出若干简单的推演或替换,都应当视为属于本发明由所提交的权利要求书确定专利保护范围。The above content is a further detailed description of the present invention in combination with the specific preferred embodiments, and it cannot be considered that the specific embodiments of the present invention are limited to this. Below, some simple deductions or substitutions can also be made, all of which should be regarded as belonging to the invention and the scope of patent protection determined by the submitted claims.
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CN111848409A (en) * | 2020-06-30 | 2020-10-30 | 浙江工业大学 | A kind of bipolar membrane electrodialysis-assisted method for preparing tetraethylammonium tetrafluoroborate |
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CN107285534A (en) * | 2017-07-08 | 2017-10-24 | 华东理工大学 | A kind of process for handling the organic wastewater containing free acid and quaternary ammonium salt |
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CN118184517A (en) * | 2024-05-14 | 2024-06-14 | 山东海化集团有限公司 | Method for recycling triethylamine through vinylene carbonate byproduct triethylamine hydrochloride |
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