Study on adsorption performance of polyethyleneimine amino- modified polyvinylidene fluoride grafting acrylic acid fiber membrane for reactive brilliant red X-3B
CHANG Hui, FAN Wen-juan*
College of Biology & Chemical Engineering, Panzhihua University, Panzhihua 617000, China
Abstract:The acrylic acid (AA) was grafted onto polyvinylidene fluoride (PVDF) via solution polymerization method to prepare the PVDF-g-PAA copolymer. Then PVDF-g-PAA was modified by amination with polyethyleneimine (PEI) to prepare PEI amino-modified PVDF-g-PAA copolymer (PEI-PVDF-g-PAA). Then, PEI-PVDF-g-PAA fiber membrane was prepared by the method of electrostatic spinning. The microscopic morphology of PEI-PVDF-g-PAA fiber membrane was characterized by scanning electron microscope (SEM). The results showed that the diameter of fiber in fiber membrane was 30-50nm, and there were a large number of micropores on the surface. The simulated dye (reactive brilliant red X-3B) in waste water was adsorbed with PEI-PVDF-g-PAA fiber membrane as absorbent material, and its adsorption kinetics, adsorption isotherm model and adsorption thermodynamics were investigated. The results indicated that the adsorption efficiency of PEI-PVDF-g-PAA fiber membrane was much higher than that of pure PVDF fiber membrane and PVDF-g-PAA fiber membrane. The adsorption equilibriumwas reached at 70min under the following conditions: the initial mass concentration of reactive brilliant red X-3B was 150mg/L, pH=1, and the dosage of adsorbent was 0.015g. The equilibrium adsorption capacity was 494.95mg/g. The adsorption process of PEI-PVDF-g-PAA fiber membrane for reactive brilliant red X-3B were in accordance with the pseudo second-order kinetic model and Langmuir isotherm adsorption model, which indicated that the adsorption process belonged to monolayer adsorption based on chemical adsorption. The theoretical equilibrium adsorption capacity and theoretical saturated adsorption capacity was 526.32mg/g and 500.00mg/g, respectively. The results of adsorption thermodynamics implied that the adsorption process of PEI-PVDF-g-PAA fiber membrane for reactive brilliant red X-3B was a spontaneous endothermic reaction, and the entropy value of solid-liquid interface increased in this process.
Moradi S E.Microwave assisted preparation of sodium dodecyl sulphate (SDS) modied ordered nanoporous carbon and its adsorption for MB dye[J].Journal of Industrial and Engineering Chemistry,2014,20(1):208-215.
[2]
Shi C M,Tao F R,Cui Y Z.Evaluation of nitriloacetic acid modified cellulose film on adsorption of methylene blue[J].International Journal of Biological Macromolecules,2018,114:400-407.
[3]
Gao Y,Deng S Q,Jin X,et al.The construction of amorphous metal-organic cage-base solid for rapid dye adsorption and time-dependent dye separation from water[J].Chemical Engineering Journal,2019,35:129-139.
[4]
Zou X Q,Zhang H,Chen T,et al.Preparation and characterization of polyacrylamide/sodium alginate microspheres and its adsorption of MB dye[J].Colloids and Surfaces A,2019,567:184-192.
[5]
Kaur R,Kaur A,Umar A,et al.Metal organic framework (MOF) porous octahedral nanocrystals of Cu-BTC:synthesis,properties and enhanced adsorption properties[J].Materials Research Bulletin,2019,109:124-133.
[6]
Khorasani A C,Shojaosadati S A.Magnetic pectin-chlorella vulgaris biosorbent for the adsorption of dyes[J].Journal of Industrial and Engineering Chemistry,2019,7:103062.
[7]
杨梅,孙润军,王红红.静电纺壳聚糖/PVA纳米纤维膜对甲基橙的吸附特性[J].合成纤维,2019,48(1):15-20.YANG Mei,SUN Run-jun,WANG Hong-hong.Adsorption characteristics of chitosan/PVA nanofiber membrane on methyl orange[J].Synthetic Fiber in China,2019,48(1):15-20.
[8]
Lou T,Yan X,Wang X J.Chitosan coated polyacrylonitrile nanofibrous mat for dye adsorption[J].International Journal of Biological Macromolecules,2019,135:919-925.
[9]
Lu X H,Wang X K,Cuo L,et al.Preparation of PU modified PVDF antifouling membrane and its hydrophilic performance[J].Journal of Membrane Science,2016,520:993-940.
[10]
Xie X L,Gao H L,Luo X,et al.Polyethyleneimine modified activated carbon for adsorption of Cd(II) in aqueous solution[J].Journal of Environmental Chemical Engineering,2019,7(3):103183.
[11]
李山山.PAMAM改性PVDF膜的制备及重金属离子吸附研究[D].天津:天津工业大学,2018.
[12]
王家宏,尹小龙,吉艳芬.聚乙烯亚胺改性氧化石墨对水中Cr(VI)的吸附[J].无机化学学报,2015,31(6):1185-1193.WANG Jia-hong,YIN Xiao-long,JI Yan-fen.Cr(VI) adsorption on polyethyleneimine modified graphite oxide[J].Chinese Journal of Inorganic Chemistry,2015,31(6):1185-1193.
[13]
Ma F Q,Nian J R,Bi C L,et al.Preparation of carboxylated graphene oxide for enhanced adsorption of U(VI)[J].Journal of Solid State Chemistry,2019,277:9-16.
[14]
Zang Y A,Yue Q Y,Kan Y J,et al.Research on adsorption of Cr(VI) by poly-epichlorohydrin-dimethylamine (EPIDMA) modified weakly basic anion exchange resin D301[J].Ecotoxicology and Environmental Safety,2018,101:467-473.
[15]
颜博.改性苎麻麻骨对活性艳红与亚甲基蓝的吸附性能研究[D].武汉:武汉纺织大学,2013.
[16]
范文娟.磁性Fe3O4/活性炭对电镀废水中Cr(VI)吸附性能的研究[J].表面技术,2018,47(2):48-54.FAN Wen-juan.The adsorption property of magnetic Fe3O4/active carbon for Cr(VI) in electroplating waste water[J].Surface Technology,2018,47(2):48-54.
[17]
Wang N,Jin R N,Omer A M,et al.Adsorption of Pb(II) from fish sauce using carboxylated cellulose nanocrystal:isotherm,kinetics,and thermodynamic studies[J].International Journal of Biological Macromolecules,2017,102:232-240.
[18]
Ho Y S,McKay G.Pseudo-second order model for sorption processes[J].Process Biochem.,1999,34(5):451-465.
[19]
邢云,王贵芳.交联羧甲基壳聚糖的合成及其对Pb2+、Cd2+和Co2+的吸附行为[J].冶金分析,2013,33(11):6-11.XING Yun,WANG Gui-fang.Synthesis of cross-linked carboxymethyl chitosan and its adsorption capacity for Pb2+,Cd2+ and Co2+[J].Metallurgical Analysis,2013,33(11):6-11.
[20]
ZHANG Qian,LI Ke-pei,ZHANG Hui-yun,et al.Preparation of 3D graphene aerogel and its adsorption properties on Rhodamine B[J].China Dyeing & Finishing,2018,44(10):1-7.
[21]
Fakhri A,Adami S.Adsorption and thermodynamic study of cephalosporins antibiotics from aqueous solution onto MgO nanoparticles[J].Journal of the Taiwan Institute of Chemical Engineers,2014,45(3):1001-1006.